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Tolerance of Wildlife Outside Protected Areas

Permanent Link: http://ufdc.ufl.edu/UFE0042045/00001

Material Information

Title: Tolerance of Wildlife Outside Protected Areas Predicting Intention to Allow Elephants in Maasai Group Ranches Around Amboseli National Park, Kenya
Physical Description: 1 online resource (283 p.)
Language: english
Creator: Browne-Nunez, C
Publisher: University of Florida
Place of Publication: Gainesville, Fla.
Publication Date: 2010

Subjects

Subjects / Keywords: africa, amboseli, attitudes, behavior, cognitive, culture, elephants, evaluation, intentions, interventions, kenya, maasai, methods, norms, theory, tolerance, values, wildlife
Wildlife Ecology and Conservation -- Dissertations, Academic -- UF
Genre: Wildlife Ecology and Conservation thesis, Ph.D.
bibliography   ( marcgt )
theses   ( marcgt )
government publication (state, provincial, terriorial, dependent)   ( marcgt )
born-digital   ( sobekcm )
Electronic Thesis or Dissertation

Notes

Abstract: The majority of Kenya s wildlife is found outside protected areas and depends on public tolerance for survival. This study examines residents willingness to allow elephants (Loxodonta africana) in group ranches bordering Amboseli National Park, Kenya. Several interventions aimed at fostering positive attitudes and tolerance of elephants have been implemented to address the increasing level of human-elephant conflict. I (1) test social psychological theory and research methods used in North American human dimensions research, and (2) provide information for planning and evaluating elephant conservation interventions. My review of wildlife attitude survey research in Africa revealed limited use of theory and great variation in research methods. Using the cognitive hierarchy as a theoretical framework, I examined the predictive influence of wildlife values, attitudes, norms, and additional variables on intention to vote to allow elephants in group ranches. Key informant interviews, focus groups, and program record reviews were conducted to develop an interview questionnaire. Results based on personal interviews with 569 group ranch residents indicate that 53% of respondents would vote to allow elephants in group ranches. General attitudes toward elephants, specific attitudes toward allowing elephants, and norms for allowing elephants explained 62% of the variance in intention. Three wildlife value dimensions were identified and predicted attitudes, with a dimension representing indifference to wildlife demonstrating the most predictive ability. Gender, group ranch of residence, knowledge of elephants, level of worry about elephants, and awareness of human-elephant conflict mitigation interventions contributed to the prediction and understanding of wildlife value dimensions, attitudes, and norms. This study demonstrates the transferability of social psychological theory and methods to a rural African setting and provides empirical support for expanding the cognitive hierarchy to include additional predictors of behaviors toward wildlife. Results show the importance and utility of understanding the constructs related to tolerance of wildlife. Recommendations include increasing awareness of human-elephant conflict interventions, increasing actual and perceived elephant-related benefits, providing an education program on elephants based on traditional and scientific information, and implementing land-use policy that would limit land use that is incompatible with wildlife conservation.
General Note: In the series University of Florida Digital Collections.
General Note: Includes vita.
Bibliography: Includes bibliographical references.
Source of Description: Description based on online resource; title from PDF title page.
Source of Description: This bibliographic record is available under the Creative Commons CC0 public domain dedication. The University of Florida Libraries, as creator of this bibliographic record, has waived all rights to it worldwide under copyright law, including all related and neighboring rights, to the extent allowed by law.
Statement of Responsibility: by C Browne-Nunez.
Thesis: Thesis (Ph.D.)--University of Florida, 2010.
Local: Adviser: Jacobson, Susan K.
Electronic Access: RESTRICTED TO UF STUDENTS, STAFF, FACULTY, AND ON-CAMPUS USE UNTIL 2011-08-31

Record Information

Source Institution: UFRGP
Rights Management: Applicable rights reserved.
Classification: lcc - LD1780 2010
System ID: UFE0042045:00001

Permanent Link: http://ufdc.ufl.edu/UFE0042045/00001

Material Information

Title: Tolerance of Wildlife Outside Protected Areas Predicting Intention to Allow Elephants in Maasai Group Ranches Around Amboseli National Park, Kenya
Physical Description: 1 online resource (283 p.)
Language: english
Creator: Browne-Nunez, C
Publisher: University of Florida
Place of Publication: Gainesville, Fla.
Publication Date: 2010

Subjects

Subjects / Keywords: africa, amboseli, attitudes, behavior, cognitive, culture, elephants, evaluation, intentions, interventions, kenya, maasai, methods, norms, theory, tolerance, values, wildlife
Wildlife Ecology and Conservation -- Dissertations, Academic -- UF
Genre: Wildlife Ecology and Conservation thesis, Ph.D.
bibliography   ( marcgt )
theses   ( marcgt )
government publication (state, provincial, terriorial, dependent)   ( marcgt )
born-digital   ( sobekcm )
Electronic Thesis or Dissertation

Notes

Abstract: The majority of Kenya s wildlife is found outside protected areas and depends on public tolerance for survival. This study examines residents willingness to allow elephants (Loxodonta africana) in group ranches bordering Amboseli National Park, Kenya. Several interventions aimed at fostering positive attitudes and tolerance of elephants have been implemented to address the increasing level of human-elephant conflict. I (1) test social psychological theory and research methods used in North American human dimensions research, and (2) provide information for planning and evaluating elephant conservation interventions. My review of wildlife attitude survey research in Africa revealed limited use of theory and great variation in research methods. Using the cognitive hierarchy as a theoretical framework, I examined the predictive influence of wildlife values, attitudes, norms, and additional variables on intention to vote to allow elephants in group ranches. Key informant interviews, focus groups, and program record reviews were conducted to develop an interview questionnaire. Results based on personal interviews with 569 group ranch residents indicate that 53% of respondents would vote to allow elephants in group ranches. General attitudes toward elephants, specific attitudes toward allowing elephants, and norms for allowing elephants explained 62% of the variance in intention. Three wildlife value dimensions were identified and predicted attitudes, with a dimension representing indifference to wildlife demonstrating the most predictive ability. Gender, group ranch of residence, knowledge of elephants, level of worry about elephants, and awareness of human-elephant conflict mitigation interventions contributed to the prediction and understanding of wildlife value dimensions, attitudes, and norms. This study demonstrates the transferability of social psychological theory and methods to a rural African setting and provides empirical support for expanding the cognitive hierarchy to include additional predictors of behaviors toward wildlife. Results show the importance and utility of understanding the constructs related to tolerance of wildlife. Recommendations include increasing awareness of human-elephant conflict interventions, increasing actual and perceived elephant-related benefits, providing an education program on elephants based on traditional and scientific information, and implementing land-use policy that would limit land use that is incompatible with wildlife conservation.
General Note: In the series University of Florida Digital Collections.
General Note: Includes vita.
Bibliography: Includes bibliographical references.
Source of Description: Description based on online resource; title from PDF title page.
Source of Description: This bibliographic record is available under the Creative Commons CC0 public domain dedication. The University of Florida Libraries, as creator of this bibliographic record, has waived all rights to it worldwide under copyright law, including all related and neighboring rights, to the extent allowed by law.
Statement of Responsibility: by C Browne-Nunez.
Thesis: Thesis (Ph.D.)--University of Florida, 2010.
Local: Adviser: Jacobson, Susan K.
Electronic Access: RESTRICTED TO UF STUDENTS, STAFF, FACULTY, AND ON-CAMPUS USE UNTIL 2011-08-31

Record Information

Source Institution: UFRGP
Rights Management: Applicable rights reserved.
Classification: lcc - LD1780 2010
System ID: UFE0042045:00001


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1 TOLERANCE OF WILDLIFE OUTSIDE PROTECTED AREAS : PREDICT ING INTENTION TO ALLOW ELEPHANTS I N MAASAI GROUP RANCHES AROUND AMBOSELI NATIONAL PARK, KENYA By CHRISTINE M. BROWNE NUEZ A DISSERTATION PRESENTED TO THE GRADUATE SCHOOL OF THE UNIVERSITY OF FLORIDA IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY UNIVERSITY OF FLORIDA 2010

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2 2010 Christine M. Browne Nuez

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3 To the people and wildlife of Amboseli, and all those working for their continued coexistence

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4 ACKNOWLEDGEMENTS I have many people to thank for the inspiration, support, and encouragement that enabled me to pursue my doctoral studies. First, I would like to express my deepest gratitude to my advisor, Susan Jacobson, who provided guidance while at the same time allowing me the freedom to develop and follow my own path. Her demonstration of confidence in my abilities, and the professional and acad emic opportunities she provided me, allowed me to further explore and develop my professional strengths and interests. I am indebted to all of the members of my dissertation committee, who provided guidance and encouragement throughout. Thanks to Drs. Mart ha Monroe, Mark Hostetler and Colin Chapman who have participated in this project since I arrived at UF. Thank you, Colin, for staying on even after your move to McGill. You gave me some great advice early on about choosing nice people with whom to work, w hich I try to live by and often share with others. To Dr. Jerry Vaske, my masters advisor at Colorado State University and dissertation committee courtesy member, I am grateful to you for sharing so much time and knowledge in teaching and assisting me wit h research methods, theory, and statistical analysis. I would like to thank Dr. Janaki Alavalapati for serving as a committee member in the early years before he moved on to Virginia Tech. Finally, to Dr. Mike Moulton, who I have had the pleasure of know ing since I served as one of his teaching assistants in 2003 (what a fun gig!), thanks for graciously agreeing to review my dissertation and to sit in on my defense at the last minute. This journey started in Nairobi, Kenya, in 1995, when I had the good f ortune to be selected to serve as a volunteer with the International Foundation for Education and Self Help Teachers for Africa Program. It was here that I met some amazing women on whose shoulders I stand today. I could write pages on all they have give n me, including knowledge, opportunities, friendship, support, and encouragement. Thank you to Dr. Mary Okello, Susan Carvalho, Sandy

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5 Owen, Louise Martin, Dame Daphne Sheldrick, and Cynthia Moss. Special thanks to Daphne for bringing me into the world of e lephants and trusting me to help with operations at the elephant orphanage. I learned so much during my tenure at the David Sheldrick Wildlife Trust and will treasure the memories of our many conversations over glasses of wine, our trip to Tsavo, and the a mazing time I was privileged to spend with the elephants. I am also grateful to you for providing me Cynthia Mosss phone number. Without this little tidbit, this study may not have happened. I owe my deepest debt of gratitude to Cynthia, who I rang up out of the blue in 1996 and asked if there might be a role for me in her elephant research project in Amboseli. She invited me to her home office to help out with some clerical tasks and sought other opportunities for me, but I needed training in higher educa tion to make any further contributions. Fourteen years later, I am completing my dissertation on human elephant interactions in Amboseli a dream of a lifetime! Cynthia, thank you for supporting me from the beginning and suggesting a follow up to Kadzos study. Thank you for sharing your home, your camp, and your friendship. Your generosity and dedication are truly remarkable. There are many organizations and individuals, in addition to those mentioned above, in Kenya, which made this study possible. Fir st, thank you to the Government of Kenya for authorizing this research. I am grateful to Dr. Patrick Omondi of the Kenya Wildlife Service (KWS) for being supportive since our first meeting in 2002. Patrick provided me with important information on humanel ephant conflict in Kenya and helpful advice on conducting research in Amboseli. Additional thanks goes to KWS for granting access to the humanelephant conflict occurrence books in Loitokitok and for allowing me to come and go from Amboseli National Park o n a daily basis. The scientists and staff at the Amboseli Trust for Elephants provided support of all kinds, including providing me with all the benefits associated with being a research

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6 associate with the Amboseli Elephant Research Project, including offi ce space in Nairobi, a tent in the beautiful AERP research camp, help with obtaining a research permit, and a car during my preliminary research. Thanks so much for all of your support, advice, and assistance. I extend immense thanks to Cynthia Moss, Joyce Poole, Harvey Croze, and Purity Waweru, among others. Special thanks to Cynthia and Harvey for conducting critical negotiations during a challenging moment of this project. Additional thanks go to Harvey for his assistance in creating maps. Thank you to a ll of the individuals at various conservation organizations who met with me and provided program records and reports. To my fantastic team, I am so grateful for your hard work, dedication, and determination. Deepest thanks go Grace Majakusi, George Ole Lu pempe, Paul Mutero Majakusi, Moses Tetile Ntipapa, Kitesho Soila Peninah, Naisanti Jackline Oloishiro, and Saibulu Ole Kalama. I appreciate the sacrifices each of you made, including being away from your homes and families for extended periods of time. I am profoundly grateful to the people of Olgulului and Kimana Group Ranches for their tremendous generosity with time and information. I find it truly remarkable that people in this world are still willing to take a large portion of time out of their day to sit down and graciously answer a foreigners long list of questions, and even offer a cup of chai. Your politeness, patience, and skill in conversation, are a great example to many hurried Westerners. I only hope that the results of this research will be nefit you in at least some small way. Ashe oleng! This project had several generous sources of funding. First, I am grateful to the University of Florida and several programs and departments at the university for funding my doctoral studies and my prelimi nary research, including my preliminary fieldwork in Kenya in 2002. University funding included a four year UF Alumni Fellowship, a Jennings Scholarship

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7 from the Department of Wildlife Ecology and Conservation, a Niddrie Award from Center for African Studi es, and a field research grant from the Tropical Conservation and Development Program. My fieldwork in 20042005 was supported by the U.S. Fulbright Program, the Disney Wildlife Conservation Fund, the Sea World & Busch Gardens Conservation Fund, and the Li ncoln Park Zoo Conservation Fund. I am grateful to all of my friends and fellow graduate students for good times, stimulating conversation, and for keeping me going in my extended version of the pursuit for a Ph.D. Special thanks go to my dear friend, Dr. Sandra Jonker, who reviewed the earliest version of my research proposal during our shared time at Colorado State and continued to be involved in the process throughout, including joining me as a coauthor to publish one of the chapters in this document. S andra has been the most generous of friends and colleagues, and I am fortunate to be able to call her my friend. My family has been the foundation upon which I could stand and reach for my dreams. I thank my parents, Gaylord and Kathy Browne, for their multiple forms of support, especially the moral support that has endured as I have pursued my goals and lived my dreams throughout the years. Now that I too am a parent, I can truly appreciate the difficulty of supporting a dream that takes a child far away. To my sister, Jenny, thank you for your continuous support and words of encouragement. Your confidence in my abilities always seemed to surpass my own. My grandmother, Barbara Burlingame, provided additional motivation by her excitement and interest in my research, her shared love of elephants, and her without a doubt belief that I would succeed in completing this dissertation. I am so grateful that each of you was able to visit Kenya either during my volunteer days or during my fieldwork, so that you coul d experience the beauty of Africa.

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8 I am deeply grateful to my husband, Richard, who has sacrificed at every step of the way so that I could see this project through. This included giving up tenure to relocate during my write up and taking a year of leave t o serve as the official driver for my project. Thank you for sharing the joys and trials all along the way, and always working to keep me focused on the positive. You have been my staunchest supporter, for which I will be forever grateful. Your calm and st eady nature kept me from going over the deep end on more than one occasion. Thank you for being patient as the writing stage dragged on and for continuing to encourage me when I became cynical about completing this document. Most of all, thank you for taki ng precious care of our beautiful children so that I could dedicate the majority of my time to writing during the last several months. Finally, thanks go to Mara and Kai, who joined our family during the latter part of my doctoral studies. You have added so much joy to life. I look forward to someday sharing with you the beauty of Kenya, its people and its wildlife.

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9 TABLE OF CONTENTS page ACKNOWLEDGEMENTS .............................................................................................................4 LIST OF TABLES .........................................................................................................................13 LIST OF FIGURES .......................................................................................................................14 LIST OF ABBREVIATIONS ........................................................................................................15 ABSTRACT ...................................................................................................................................16 CHAPTER 1 INTRODUCTION ..................................................................................................................18 2 STUDY AREA AND GENERAL METHODS .....................................................................23 Study Area ..............................................................................................................................23 Biophysical Description ..................................................................................................23 Amboselis Elephants ......................................................................................................24 The Human Context ........................................................................................................26 A Brief Histor y ................................................................................................................26 Human Elephant Conflict ................................................................................................29 Interventions ....................................................................................................................30 Methods ..................................................................................................................................33 Stages of Data Collectio n ................................................................................................33 Attitude Survey ................................................................................................................35 Creating a sampling frame .......................................................................................35 Selecting a sample ....................................................................................................37 Questionnaire design ................................................................................................38 Enumerators .............................................................................................................39 Managing bias ..........................................................................................................40 Follow up Interviews .......................................................................................................40 GPS Mapping of HEC Locations ....................................................................................41 3 ATTITUDES TOWARD WILDLIFE AND CONSERVATION ACROSS AFRICA: A REVIEW OF SURVEY RESEARCH ....................................................................................49 Introduction .............................................................................................................................49 Methods ..................................................................................................................................51 The Science of Survey Research ............................................................................................52 Reliability and Validity ...................................................................................................53 Conceptualization and Theory .........................................................................................54 Survey Quality ........................................................................................................................60 Coverage and Sampling Error .........................................................................................60

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10 Response Bias ..................................................................................................................65 Interviewer Bias ...............................................................................................................65 Other Error .......................................................................................................................66 Equivalence, Comparability, and Cultural Sensitivity ...........................................................66 Discussion ...............................................................................................................................68 Conclusions .............................................................................................................................71 Recommendations ...................................................................................................................72 4 THE MAASAI ELEPHANT RELATIONSHIP: THE EVOLUTION AND INFLUENCE OF CULTURE, LAND USE, AND ATTITUDES .........................................82 Introduction .............................................................................................................................82 Attitudes, Behavior, and Wildlife Conservation.....................................................................83 The Elephant in Traditional Maasai Culture ..........................................................................85 The Maasai, Pastoralism, and Wildlife Conservation ............................................................90 Being Maasai ...............................................................................................................90 Maasai Pastoralism ..........................................................................................................91 The Maasai as Conservationists ......................................................................................93 Fr om Early Attitudes toward Elephants to Modern Attitudes and Interactions .....................96 Early Attitudes .................................................................................................................96 Measures of Attitudes ......................................................................................................98 Change, Conflict, and Intervention .................................................................................99 Current Attitudes ...........................................................................................................105 The Future of the Maasai and Elephants of Amboseli .........................................................107 EconomicOopportunities and Other Benefit s ................................................................110 Land Use Planning ........................................................................................................111 Conclusion ............................................................................................................................112 5 PREDICTING INTENTION TO ALLOW ELEPHANTS ON PRIVATE LAND: AN INTEGRATED MODEL OF COGNI TIVE AND CONTEXTUAL VARIABLES ............113 Introduction ...........................................................................................................................113 Humans and Elephants .........................................................................................................114 Conceptual and Theoretical Framework ...............................................................................119 The Cognitive Hierarchy ...............................................................................................119 Value Orientations .........................................................................................................120 Attitudes ........................................................................................................................121 Norms ............................................................................................................................123 External Variables .........................................................................................................124 Demographic variables ...........................................................................................124 Prior expe rience ......................................................................................................127 Knowledge of elephants .........................................................................................127 Risk perceptions .....................................................................................................130 HEC mitigation interventions .................................................................................131 Me thods ................................................................................................................................133 Study Area .....................................................................................................................133 Sampling Procedure .......................................................................................................136

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11 Questionnaire Design ....................................................................................................137 Variables of the Cognitive Hierarchy ............................................................................138 Variables External to the Hierarchy ..............................................................................140 Future Land Use ............................................................................................................143 Validity and Reliability .................................................................................................143 Analysis ................................................................................................................................144 Results ...................................................................................................................................145 Voting Intention and Dem ographics .............................................................................146 Wildlife Value Orientations ..........................................................................................147 General Attitudes toward Elephants ..............................................................................149 Specific Attitude toward Allowing Elephants in Group Ranches .................................151 Subjective Norm ............................................................................................................153 Prior Experience ............................................................................................................154 Knowledge of Elephants ................................................................................................155 Risk Perceptions ............................................................................................................156 HEC Mitigation Interventions .......................................................................................158 The Model .....................................................................................................................162 Future Livelihood Activity ............................................................................................165 Discussion .............................................................................................................................166 Wildlife Value Orientations ..........................................................................................166 General Attitudes Toward Elephants .............................................................................169 Specific Attitudes toward Allowing Elephants in Group Ranches ...............................170 Subjective Norm ............................................................................................................171 Demographics ................................................................................................................172 Prior Experience ............................................................................................................174 Knowledge of E lephants ................................................................................................175 Risk Perceptions ............................................................................................................175 HEC Mitigation Interventions .......................................................................................177 The Model .....................................................................................................................180 Future Livelihood Activity ............................................................................................181 A No te on Gender ..........................................................................................................182 Limitations and Future Research ..........................................................................................183 Conclusions ...........................................................................................................................186 6 CONCLUSIONS ..................................................................................................................209 General Results and Implications for Elephant Conservation ..............................................209 Predicting Tolerance of Elephants .................................................................................209 Mitigating Human Elephant Conflict ............................................................................213 Theory and Methods in Attitude Research in Africa ............................................................215 Feedback from Respondents .................................................................................................217 APPENDIX A PRELIMINARY RESEARCH REPORT OCTOBER 1, 2002 ............................................219 B GPS DATA COLLECTION WORKSHEET .......................................................................223

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12 C ATTITUDE QUESTIONNAIRE ENGLISH VERSION ..................................................226 REFERENCES ............................................................................................................................251 BIOGRAPHICAL SKETCH .......................................................................................................283

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13 LIST OF TABLES Table page 21 Population of Kajiado District 19691999 .........................................................................42 22 AERP c onsolation payments ..............................................................................................42 51 Kellerts typology of attitudes toward animals ................................................................187 52 Demographic characteristics by voting intention groups .................................................191 53a Age set representation in the study sample .....................................................................192 53b Person type .......................................................................................................................192 53c Young and older age groups for analysis .........................................................................192 54 Factor a nalysis of basic b eliefs about w ildlife .................................................................193 55 Wildlife values orientations, attitudes, and norms by voting intention groups ...............194 57 Comparisons of mean expectancy, evaluation, and belief evaluation product scores between respondents for and against allowing elephants in Group Ranches ..................198 58 Prior experience with elephants and voting intention groups ..........................................199 59 Locations where respondents see and like to see elephants .............................................199 510 Correct responses to ten knowledge statements regarding elephants ..............................200 511 HEC risk beliefs by v oting intention groups ....................................................................201 512 Knowledge and beliefs regarding HEC mitigation by voting intention groups ...............202 513 Frequencies for awareness organizations with HEC interventions ..................................203 514 Multiple regression analysis results for attitude and norm variables ...............................205 516 Current and future primary livelihood activity ................................................................208

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14 LIST OF FIGURES Figure page 21 Map of study area Amboseli National Park and surrounding group ranches, with Maasai enkangs in red. .......................................................................................................43 22 Participatory mapping activity in Olgulului Group Ranch. ..............................................44 23 Focus group with women in Olgulului Group Ranch. .......................................................45 24 Wildlife identification cards. .............................................................................................46 25 Livelihood cards depicting a teacher, wildlife conservation workers, pastoralism, cultivation, selling produce, selling handicrafts, and beekeeping. ....................................47 26 Follow up interview with an elder conducted by George ole Lupempe. ...........................48 51 The cognitive hierarchy model of human behavior. ........................................................187 52 Hypothesizes model of predictors of willingness to allow elephants on private land .....188 53 The Gerontocratic Model: Distribution of Status by Age and Gender. ...........................189 54 Map of study area Amboseli National Park and surrounding group ranches, with Maasai enkangs in darkened circles. ................................................................................190 55 Mean belief expectancy and evaluation scores for voting groups regarding potential outcomes of allowing elephants in group ranches. ..........................................................196 56 Mean belief evaluation products for voting groups regarding potential outcomes of allowing elephants in the group ranches. .........................................................................197 57 Relationships between wildlife value orientations, attitudes, norms, and behavioral intentions, with external variables shown in gray ............................................................204

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15 LIST OF ABBREVIATION S AERP Amboseli Elephant Research Project AWF African Wildlife Foundation HEC Human elephant conflict KWS Kenya Wildlife Servic e PA Protected area TRA Theory of Reasoned Action

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16 Abstract of Dissertation Presented to the Graduate School of the University of Florida in Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy TOLERANCE OF WILDLIFE OUTSIDE PROTECTED AREAS : PREDICTING INTENTION TO ALLOW ELEPHANTS IN MAASAI GROUP RANCHES AROUND AMBOSELI NATIONAL PARK, KE NYA By Christine M. Browne Nuez August 2010 Chair: Susan K. Jacobson Major: Wildlife Ecology and Conservation The major ity of Kenya s wildlife is found outside protected areas and depends on public tolerance for survival This study examines residents willingness to allow elephants ( Loxodonta africana) in group ranches bordering Amboseli National Park Kenya Several interventions aimed at fostering positive attitudes and tolerance of elephants have been implemented to address the i ncreas ing level of humanelephant conflict. I (1) test social psychological theory and research methods used in North American human dimensions research, and (2) provide information for planning and evaluating elepha nt conservation interventions. My review of wildlife attitude survey research in Africa revealed limited use of theory and great variation in research methods. Using the cognitive hie rarchy as a theoretical framework, I examined the predictive influence of wildlife values, attitudes, norms and additional variables on intention to vote to allow elephants in group ranches. Key informant interviews, focus groups, and program record reviews were conducted to develop a n interview questionnaire Results based on personal interviews with 569 group ranch residents indicate t hat 53% of respondents would vote to allow elephants in group ranches. General attitudes toward elephants, specific attitudes toward allowing elephants, and norm s for allowing elephants explained 62% of

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17 the variance in intention. Three wildlife value dimen sions were identified and predicted attitudes with a dimension representing indifference to wildlife demonstrating the most predictive ability G ender, group ranch of residence, knowledge of elephants level of worry about elephants and awareness of human elephant conflict mitigation interventions contributed to the prediction and understanding of wildlife value dimensions, attitudes, and norms This study demonstrate s the transferability of social psychological theory and methods to a rural African setti ng and provides empirical support for expanding the cognitive hierarchy to include additional predictors of behaviors toward wildlife. Results show the importance and utility of understanding the constructs related to tolerance of wildlife Recommendations include increasing awareness of human elephant conflict interventions, increasing actual and perceived elephant related benefits, providing an education program on elephants based on traditional and scientific information, and implementing land use policy that would limit land use that is incompatible with wildlife conservation.

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18 CHAPTER I INTRODUCTION Protected areas (PAs) comprise approximately 12% of the planets land surface and are a critical strategy for conserving species and ecosystems (UNEP WCMC 2008). The importance of PAs in sustaining the multiple and diverse values (e.g., ecological, cultura l, aesthetic) of the eco regions of the globe cannot be overemphasized. However, PAs alone are insufficient for conserving species, ecosystems, and their human values. Ecosystems generally extend beyond the boundaries of PAs, where land is often inhabited by humans, often requiring that natural resources be actively conserved on private land. For migratory and dispersing wildlife, tolerance of local people is often essential to their conservation. This situation is exemplified by the African elephant ( Loxo donta africana), the largest land animal on earth whose dietary requirements necessitate foraging across vast areas. It is believed that 70% of elephants range lies outside protected areas (Blanc et al. 2007), highlighting the importance of maintaining pr ivate lands as viable elephant habitat. Therefore, conservation efforts aimed at protecting the African elephant and securing habitat for its long term survival need to be based on both ecological and human dimensions information People and elephant s hav e coexisted for millennia with varying levels and types of interaction. People have hunted elephants for meat and ivory, elephants have posed threats to human interests (e.g., destroying crops, livestock, and other property, and posing a threat to human sa fety), and in some places, such as Maasailand in East Africa, where nomadic and semi nomadic pastoralism were the primary, if not exclusive, land uses, people and elephant s co existed with low levels of interaction. Today, legal hunting of elephants is hig hly regulated and limited mainly to southern Africa, although poaching remains a significant threat. Crop depredation, the most common form of humanelephant conflict (HEC), is a critical issue in

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19 elephant conservation as more land is converted to agricult ure. In pastoral areas such as Maasailand, coexistence is threatened as a result of the evolving socio economic landscape. It is evident that people have and will determine the fate of the elephant. Ongoing ecological and social science research is needed in the varied settings that people and elephants coexist in order to provide information for monitoring and adapting methods for protecting both species. This dissertation explores the human factors that have facilitated coexistence between people and elep hant s over time in an area historically dominated by Maasai pastoralism. I provide an historical and cultural foundation for understanding the Maasai elephant relationship in what was once open rangeland before examining modern predictors of tolerance of e lephants on Maasai group ranches around Amboseli National Park, Kenya. The area that is now Amboseli National Park received its first PA designation in 1948, when the colonial government created the 3,260 km2 Maasai Amboseli Game Reserve. The boundaries and size of the area have changed a number of times until, in 1971, it became the 390 km2 park that exists today (see Chapter 2). This process resulted in land alienation for the traditionally pastoral Maasai, who have occupied the Amboseli region for hundreds of years. The creation of the relatively small national park also created artificial boundaries between people and wildlife, with implications for both. The Maasai not only lost land but also access to prime resources, including water in the springfed swamps within the parks borders. The migratory wildlife of the ecosystem now depend on the tolerance of the local people, which now includes immigrants ( mostly farmers) from other ethnic groups, to gain wet season access to grazing land outside the park. Many conservation interventions are aimed at improving the attitudes of local people toward wildlife and conservation, especially where local people bear a disproportionate amount

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20 of the costs of conservation. One approach has been to create economic benefits for local communities through integrated conservation and development programs (ICDPs). Amboseli National Park is the site of one of the first attempts to integrate conservation and development. In its early stages, it was touted as a model for local participation (Western 1994), but the history of conservation in Amboseli is one of broken promises and many failed projects ICDPs aspire to develop the conservation of natural areas and the welfare of local communities (Michaelidou et al. 2002), and thus overcome the inequities and ineffectiveness that have typified conservation efforts in the developing world (Stankey 1989). Conservation efforts within ICDPs have ranged from promoting sustainable use of resources within conservation areas to enforcing s trict limitations on resources use. Development activities have ranged from broad human development initiatives to specific compensation programs. While some view efforts to link conservation and development as beneficial for both ecosystems and human comm unities (Alpert 1996; Sibanda and Omwega 1996), others call attention to limitations and shortcomings (Wells et al. 1992). Amboseli provides a special case for considering the drivers of coexistence between people and elephants. Until very recently, the A mboseli elephants have lived a comparatively undisturbed existence, responding primarily to environmental conditions rather than to the effects of human development (Moss 2001). They comprise arguably the most well known, free ranging elephant populati on in the world, having been the subjects of the Amboseli Elephant Research Project since 1972 (Moss 2001). S imilarly, the Maasai are among the most wellknown cultural groups in Africa, and, until recently, noted for their steadfastness in maintaining the ir traditional lifestyle in a rapidly changing world, a culture that has been credited for the abundant and diverse wildlife found in Maasailand. T here is a history, until recent decades, of coexistence

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21 in an environment of little change. This historical r elationship and the more recent period of change provide an opportunity to consider the roles of traditional culture and outside intervention on local human wildlife interactions. This dissertation had two broad purposes, one academic and the other appli ed. From an academic perspective, this study extends and tests theory and methods often used in North American human dimensions of wildlife research to a rural African setting. Human dimensions research draws from several fields in the social sciences, including anthropology, economics, psychology, and especially social psychology (Whittaker 2000). A great deal of this research is concerned with attitudes and related social psychological constructs. Using this approach, I surveyed the attitudes of people li ving around Amboseli National Park toward el ephants and allowing elephants in group ranches adjacent to the park. I tested an integrated predictive model of cognitive and contextual variables including attitudes, to explain variation in local peoples wil lingness to accept elephants on the private lands around Amboseli National Park. From an applied perspective, the results of the research will provide local stakeholders with information on the human dimensions of humanelephant interactions around Ambosel i. Specifically, conservationists can use this information to augment ecological research on elephants in order to make more informed decisions on how to conserve elephants in this evolving, human dominated landscape. Findings can be used to evaluate and m odify existing conservation interventions and to plan future initiatives. Data for the dissertation come from a mixed methods study that was conducted from 2001 through 2005. The details of the study area, including a brief history, and general methods f or the study ( from preliminary research to the final year of fieldwork) are provided in Chapter 2. Chapters 3 and 4 are based on my preliminary research. They were prepared for specific

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22 publications and, therefore, are designed to stand alone. Chapter 3 wa s prepared as a journal article for Human Dimensions of Wildlife (Browne Nuez and Jonker 2008) and examines the use of attitude survey research in African wildlife conservation. It includes a brief overview of scientific principles and methodological issu es of survey research and discusses how researchers have addressed these issues in rural African settings. The chapter closes with recommendations for future cross cultural attitude research. Chapter 4 was written as a chapter for the forthcoming book The Amboseli Elephants: A LongTerm Perspective on a Long Lived Mammal and explores the Maasai elephant relationship over time by reviewing historical and more recent accounts of Maasai attitudes and behaviors toward elephants in the Amboseli region. It discus ses the notion of the Maasai as conservationists and considers the role of culture, livelihood, conservation, and land use change in influencing the Maasai elephant relationship. Chapter 5 reports the results of the questionnaire survey which was based on the theoretical model. It examines the predictors of willingness to allow elephants on private land and discusses the transferability of research theory and methods Chapter 6 summarizes the overall results, conclusions, and recommendations for future res earch. A set of appendices includes a summary of the preliminary fieldwork, research aids (e.g., census worksheets, picture cards), and the survey questionnaire. These items are included in order to provide sufficient disclosure to allow the study to be fu lly evaluated and replicated. While this research is focused on humanelephant interactions around Amboseli National Park, the overall findings are important in the wider context of conserving elephants on private lands, and, more broadly, to making decis ions regarding wildlife conservation in settings of humanwildlife conflict.

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23 CHAPTER 2 STUDY AREA AND GENER AL METHODS Study Area Biophysical D escription The Greater Amboseli Ecosystem is located in the Kajiado District of southern Kenya at the north foot of Mt. Kilimanjaro. At the heart of the ecosystem is Amboseli National Park ( Figure 2 1), on the Kenya Tanzania border, encompassing a 390 km2 area of the approximately 8,000 km2 ecosystem W ater availability is a critical limiting facto r in this semiarid savanna, which only receives an average of 350mm of rainfall annually, with a high level of temporal and spatial variability (Croze et al. 2007). Rainfall generally occurs during two seasons, October December and March May ( Western and Maitumo 2004). The park lies within the Amboseli Basin, a former Pleistocene lake bed and serves as the dry season concentration area for wildlife (Western and Sindiyo 1972). The ecosystems boundaries are defined by the dispersal area of its large mammal community (Western 1973, 1975), with s everal species of the parks wildlife including elephants, migrat ing seasonally along with Maasai livestock, between the basin and the surrounding rangelands. These rangelands are divided into Maasai group ranches w hich contain various forms of land tenure and use. Today, a small area, referred to as Lake Amboseli, floods seasonally, with a maximum level of only a few centimeters during the rains (Croze et al. 2007). This water, however, is saline due to the salts on the surface of the lake bed (Irungu 1992). Oscillations in the lake level, attributable to shifts in the climate, have occurred since 20,000 BP (Fol ey 1981). The writings and maps of early missionaries and explorers suggest there may have been an extensive, permanent lake (referred to Lake Njiri /Nyiri or Lake Luaya) as recently as the late 19th and early 20th century (Bannerman 1910; Rebmann 1850; Schillings 1906; Von H hnel 1894). The only

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24 permanent fresh water sources exist in the form of spring fed swamps with water originating in the forests of Mt. Kilimanjaro. Two of these swamps serve as critical wildlife habitat inside the park, while two other swamps to the east of the park, Namelok and Kimana, are heavily utilized for intensive agriculture by Maasai and other ethnic groups. There are also numerous seasonal dams, wells, and boreholes throughout the ecosystem which reduce pressure on the c entr al swamps (Croze et al. 2007). The study area is dominated by grassland to the north of the park, Acacia woodland to the south, and wooded and bush grassland in locations with seasonal water (Croze et al. 2007). In addition to the variation in water th roughout the study area, there are different soil types which influence vegetation and human landuse. The volcanic activity that produced Mt. Kilimanjaro left some areas covered with volcanic soils that allow rain fed agriculture to the east of the park, but the majority of the study region is not suitable for cultivation. The temporal and spatial variation in resource availability makes transhumant pastoralism which involves seasonal movements of people with their livestock, and wildlife conservation the most viable land use options for this area (Bulte et al. 2008; Fratkin 1994; Galaty 1992; Homewood and Rodgers 1984) Amboselis E lephants Amboseli is one of the most popular parks in Kenya (Okello et al. 2001) and is a top earner among the countrys park s (Bulte et al. 2008; Croze et al. 2007). The combination of wildlife viewing, cultural experience, and an extraordinary view of Mt. Kilimanjaro, makes Amboseli a unique and highly desirable tourist destination. The Amboseli elephants are a key component of this ecosystem. As the subjects of several documentaries and multiple research projects carried out under the the Amboseli Elephant Research Project they are the m ost well-

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25 known, free ranging elephant population in the world (Moss 2001) and t hey are emblematic of the critical and complex role of elephants at the local, national, and international level coexisting with pastoral people for thousands of years, increasingly in conflict with transitioning human neighbors, and drawing attention and revenue from abroad Based on fossil evidence, elephants have been present in the region for at least tens of thousands of years and probably much longer (K. Behrensmeyer, pers. comm.). Local elephant numbers have likely fluctuated significantly as a result of resource availability and human activity, especially in the last two centuries. In 1850, Rebmann stated that much ivory is to be found (p. 309) on the banks of Lake Luaya, but just over thirty years later, when describing the marvellous abundance of wi ldlife on the Njiri Plain (the area north of Amboseli), Thomson (1883, p. 276) made no mention of elephants, possibly indicating a decline in numbers during a period of intense hunting for the ivory (see Wimmelbcker 2002 for statistics on ivory trade duri ng the19th century) Evidence of this comes from Krapf (1860) and Schillings (1906, p. 153) who stated, by the end of the last century [the land] was denuded entirely of ivory and elephants. While the high demand for ivory at this time no doubt took a toll on the regions elephants, some variation in observed elephant numbers may be attributable to seasonal migration and shifts in ecological and hydrological conditions. Maasai elders have stated that elephants only moved into the Amboseli basin after woodlands spread across the basin around the turn of the century likely corresponding to a lowering of the lake (Western and Sindiyo 1972). B y 1975 there were approximately 480 elephants in the Amboseli population (Moss 1977). During the time of my attitude survey there were approximately 1,500 elephants in the population, with over 1,000 primarily using the private lands outside t he park (C. Moss, pers. comm.).

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26 The Human C ontext The Maasai moved into the Amboseli area approximately 400 years ago ( Jacobs 1975, Kituyi 1990), but they were not the first pastoralists in the region. Other pastoral groups have occupied present day Maasailand,1 an area extending from north central Kenya south to the central rangelands of northern Tanzania, for thousands of years (Ehret 1971; Foley 1981; Jacobs 1975; Kesby 1977). There is an extensive literature on the history the Maasai and their predecessors (e.g., Bernsten 1980; Galaty 1981; Jacobs 1975; Low 1963) and a corresponding lack of agreement about how and when these groups (e.g, the Iloogalala noted by Fosbrooke 1948; Jacobs 1968; Galaty 1991), who practiced varying degrees of pastoralism, came to occupy present day Maasailand (Hodgson 2005). While the Maasai have been credited for the abundant wildlife in Maasailand, the explanations for this circumstance are largely anecdotal and have ranged from tolerant attitudes among the Maasai to the compatibility of pastoralism with wildlife conservation (see Chapter 4). Today, as the Maasai way of life undergoes rapid transformation, the implications of change for wildlife must be considered. Before interpreting current conditions, it is useful to gain an understanding of past events that have a bearing on the current state of affairs. While a complete discussion of Maasai history i s beyond the scope of this dissertation, a brief review will contribute to understanding the present and planning for the future (see Kangwana and BrowneNuez, in press, for a more detailed discussion) A B rief H istory The current range of the Maasai is largely the result of colonial interventions. It was recognized as early as 1904 that the Maasai regions of Kenya had the highest concentrations of wildlife. Meinertz hagen's (19 83) diary entry for 18 April 1904 reads: 1 Maasailand is not an administratively defined area, but is a loosely defined region occupied by diverse groups of Maa speaking peoples (Homewood et al. 2009, p. 1).

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27 In view of the likelihood of a vast invasion by European settlers it seems that the large game must disappear. I have suggested ....a structure for a very large area in country unsuitable for white settlement where game can exist forever. I think that the are a might be some three or four thousand square miles and possibly in Maasai country. The Maasai are good game preservers but are very wasteful of grazing lands. This statement was made following huge population crashes among pastoralists and livestock resul ting from a series of epidemics that occurred in the latter part of the 19th century (Enghoff 1990) The same year the colonial administration took steps to contain the Maasai in a defined area, mainly in order to free land for European settlers. A treaty was signed between the government and Olenana, a Maasai spiritual leader ( oloiboni ). The treaty confined the Maasa i to two reserves (Grandin 1986; Kituyi 1990), with the Maasai losing approximately 90% of their former territory (see Kituyi 1990). The Southern Reserve, a 27,700 km2 area, included what is now Amboseli (Croze et al. 2007). In 1948, a 3,260 km2 area of the reserve was desi g nated as the Maasai Amboseli G ame R eserve (Croze et al. 2007), where the Maasai and their livestock continued to coexist with wildlife. Almost 25 years later, in 1974, a much smaller area (390 km2) became what is now Amboseli National Park, from which the Maasai were excluded. There were several implications for the Maasai in the creation of the park, including eviction for those residing in the demarcated area and loss of access to critical water sources and grazing pastures. Outside of the park other changes in land tenure were underway which would affect the way the Maasai view land. Traditionally, the Maasai did not see land as something to be owned. It was a resource to be managed for livestock grazing, but, following independence in 1963, the Kenyan government began allocating land to influential members of the community in an effort to bring the area into the national livestock market (Fratkin and Mearns 2003). By 1968, many Maasai were becoming concerned about losing access to grazing land and agreed to a group ranch

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28 system, where groups of individuals were given legal title to land. The group ranches were communally operated until the 1980s when subdivision and privatization started to take place. The group ranches surrounding Amboseli resisted subdivision until recently. Present S tatus As of 2006, of the 52 group ranches in the Kajiado District, 32 had completed subdivision and 15 were in the process of subdivision, leaving only 5 that had not sta rted the process (BurnSilver and Mwangi 2007). Olgulului Lolar r ashi hereafter referred to a s Olgulului, and Kimana Tikondo, hereafter referred to as Kimana, were among the last to begin subdivision. Kimana completed the process in 2005, and in 2007, the rainfed and irrigated agricultural areas of Olgulului were being subdivided. The two group ranches comprise the current study area ( Figure 21). Immigration is another factor influencing Maasai culture and land use around Amboseli. In the last several decades the human population in the Kajiado district has grown at a high rate relative to the national rate (Table 2 1). Th is growth is largely the result of immigration by Kamba and Kikuyu farmers (Campbell et al. 2000; Fratkin and Mearns 2003) While the human population has grown, livestock numbers have remained relatively consistent (Bekure et al. 1991), meaning there are fewer livestock per capita and, therefore, pastoralists have become poorer (BurnSilver et al. 2008). Many Maasai are shifting from livestock based livelihoods to more diversified livelihood strategies, including agriculture and tourism enterprise Shifting livelihood strategies has implications for pastoralists and wildlife. For instance, s ettle ment of the better watered areas for agriculture has reduced the area available for dry season grazing and access to water for livest ock and w ildlife (Campbell et al. 2000) and affects wildlife migration corridors. The expansion of agriculture along with the growing huma n and elephant populations, has significant implications for Amboselis elephants.

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29 Human Elephant C onflict Human elephant conflict (HEC) is a growing problem across Africa (Ngure 1992; Waithaka 1993; Hoare 1995; Tchamba 1995; Thouless and Sakwa 1995; Barnes 1996). Deaths and injury to both humans and elephants occur as a result of this negative interaction. Most inciden ts of conflict with elephants involve crop raiding or competition for water and grazing resources. Humanelephant conflict is a costly problem both economically and psychologically for people living with wildlife. Elephants also suffer though loss of habit at and access to resources and through injuries and mortality caused by local people and wildlife management authorities. HEC in Amboseli is the result of the increasing human and elephant populations, and changing land use, described above. This conflict has resulted in injury and death of people, elephants, and livestock, and other losses, including crop losses and damaged water pipes. From 1993 to 2005, elephants killed 18 people and injured another 18 (Croze et al. 2007). Thouless et al. (2008) provide a review of figures on elephant mortality in Amboseli, with variation between the records of the Kenya Wildlife Service (KWS) and the Amboseli Elephant Research Project (AERP). Causes of mortality include accident, sickness, natural, HEC, KWS control shooting, poaching, and unknown. For the period of 19932001, figures for elephants killed in conflict range from 13 (KWS) to 41(AERP). During the same period, elephants killed by KWSs Problem Animal Control Unit range from 9 (AERP) to 19 (KWS). According to AERP, 133 animals died of unknown causes during this period. Thouless et al. (2008) speculate that the records of AERP are more accurate given that each individual in the Amboseli elephant population is known by AERP researchers. In the mid 1990s, KWS real ized it was shooting a large number of animals and has since tried to shift from their shoot oncontrol policy to using

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30 alternative methods, such as driving elephants from conflict areas with helicopters, and now KWS considers shooting elephants a last res ort (P. Omondi, KWS Elephant Programme Coordinator, pers. comm., 2002). With continued population growth, land use change, and no national landuse policy, it is likely that HEC in Amboseli will increase and pose a significant threat to people and elephants. S everal organizations are working to mitigate conflict and secure habitat for Amboselis elephants outside of the park by encouraging land use activities that are compatible with wildlife conservation, such as pastoralism and wildlife based tourism (P. Omondi, KWS, pers. comm.), and through interventions designed to reduce humanelephant conflict. Interventions Tourism enterpris e is often viewed as a viable alternative to pastoralism or as a source of supplemental income, especially given the popularity of Amboseli as a tourist destination. Moreover, the Maasai themselves are often viewed as a tourist attraction, evidenced by the use of their images in international tourism advertisements. To take advantage of this opportunity, the Maasai of Amboseli have created cultural bomas, Maasai homesteads where tourists can visit; observe demonstrations of daily activities, singing, and da ncing; and purchase souvenirs such as womens beadwork. The process of creating and improving these bomas has been supported by organizations such as KWS and the African Wildlife Foundation (AWF). There is a growing number of cultural bomas throughout the area, with a concentration of bomas along the southern border of the park in Olgulului Group Ranch. There have been many problems associated with the bomas, including a blocked elephant corridor (see Chapter 4 for further discussion). Other tourism related opportunities include employment at area lodges, and, at the group ranch level,

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31 revenue received from the Olgulului public campsite, lodges purchasing building materials, and rent and fees paid by tour companies and lodges. KWS is a government parastatal with a mandate to conserve and manage Kenyas wildlife. As mentioned, today KWS is using various strategies to manage conflict with elephants (Omondi et al. 2004) and increase tolerance of elephants. In Amboseli, these include electric fencing, community sensitization (increasing awareness of tourism benefits and discouraging agriculture), elephant drives, a school bursary fund, creation of community wildlife sanctuaries, and problem animal control activities (PAC), which include chasing, scaring, and shooting problem elephants (shooting is only done when human life is at risk) (P. Omondi, KWS, pers. comm.). Perhaps the most obvious intervention, depending on ones location, is the installation of two solar powered electric fences around Kimana (38 km) and Namelok (24 km) agricultural areas ( Figure 21). The fencing project funded by the E uropean U nion, was started in 1996 and completed in 2000 at a cost of 9,000 USD/km (Kioko et al. 2008). I ndividuals with shambas (farm plots) inside the fenced areas are r esponsible for electing fence management committees and financially supporting the monitoring and maintenance of the fences. In 2002, during the preliminary research for the current study, the fences were not fully operational, having been damaged by eleph ants and people e .g., theft of power unit components (pers. observ.). There were also insufficient funds for managing the fences. In 1998, AERP implemented a consolation scheme that pays for livestock (cattle, goats, and sheep) killed by elephants outside of the park in an effort to end th e retaliatory spearing of elephants (AERP made retro active payments for 1997, when negotiations for the cons olation program began). The term consolation was selected over compensation due to the concern of KWS for setting a precedent for other sites of HEC in Kenya. Furthermore, consolation

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32 communicates that AERP, as a neighbor in the ecosystem, recognizes and is sorry for the loss of a valued animal (Croze et al. 2007). At the beginning of the research reported here, AERP had paid out 1,684,000 KSh (approximately 22,000 USD) for 137 animals over the course of eight years (Table 2 2 ) and the director of AER P believed that the program was positively influencing Maasai attitudes and helping to reduce the number of elephants being speared (C. Moss, pers. comm.). Although the spearing of elephants has not completely stopped (Maasai ilm ur ran, or warriors spear elephants for other reasons2), retaliatory spearing of elephants due to HEC came to an end in the three group ranches participating in the program (both group ranches in the present study participate in the consolation scheme). Although not intended for elephant conservation, the Government of Kenya (GOK) has a compensation program for human injury or death caused by wildlife (GOK 1989). Prior to 1990, a national wildlife damage compensation program existed where people were compensated for loss of crops, livestock and human life, but this was abolished in 1989 due to inadequate funds and a high level of corruption (Lusiola 1996). The current compensation program pays for human injury (15,000 KSh approx. 194 USD) and loss of life (30,000 KSh app rox. 388 USD). There is no form of payment for losses of crops to wildlife. As part of its Heartlands Project, a landscape approach to conserving wildlife, the overall goal of AWF s Kilimanjaro program regarding elephants i s to ensure that the Maasai settl ement areas bordering the park are friendly to elephants (and other wildlife) by reducing conflicts between humans and elephants (AWF 1999) In 1999, AWF proposed an outreach program to be carried out at the neighborhood level, where the goal was to promote awareness and 2 Ilmurran have been known to spear elephants to test their courage and skill (Moss 1988). Elephants and other wildlife are sometimes speared in reaction to other events as a demonstration of discontent.

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33 communication through meetings, workshops and educational tours. Another goal was to promote benefit sharing. For example, one planned AWF activity was to assist the Maasai in improving the cultural bomas Methods The present study, following Kangwana (1993), was conducted in the two Maasai group ranches that immediately border the park, Olgulului and Kimana ( Figure 21). A multiple methods approach was used to 1) build on previous research, 2) address concerns with cross cultural res earch, 3) reduce the limitations of single methods research, 4) allow for community participation, 5) obtain supporting information for a deeper understanding of questionnaire data, and 6) to advance a standard framework for attitude research in developing countries. Methods employed in this study, to collect both qualitative and quantitative data, include multiple literature reviews, key informant interviews, a stakeholder analysis, participatory mapping, focus groups, GPS mapping, document reviews, intens ive enumerator training, twostage pretesting (questionresponse formats and survey instrument), a questionnaire survey, and follow up interviews. The use of multiple, comple mentary methods, can enrich overall findings and address limitations of certain me thods by providing crosschecks and new information ( Chapter 3 ). Stages of Data C ollection Data collection occurred in three stages. First, multiple literature reviews were conducted from 2001 and were periodically updated through the course of the study. Reviews covered theory and methods used in North American and African conservation attitude research (Chapter 3); the histories of the Maasai and the general study area (present chapter and Chapter 4); elephant conservation issues, including HEC (present chapter and Chapter 5); and pastoralism in Africa, with a focus on Maasai transhumant pastoralism (Chapters 3 and 4). The historical

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34 reviews were conducted because it is essential to develop a thorough understanding of the communitys history and current dynamics, particularly in relation to the authority structures which influence peoples behavior and the patterns of resource use which form the basis for both conflicts and opportunities in wildlife management (Kiss 1990, p. 25)3. The second stage of this project was the p reliminary fieldwork in Kenya, which took place in May June 2002 (a summary is provided in Appendix A). The research included key informant inte rviews, a stakeholder analysis, participatory mapping ( Figure 22) with residents of two Maasai group ranches and an initial review of stakeholder organizations program records and reports. Through these activities, I was able to assess the need for and feasibility of the research, gain a better understanding of the so cio political and ecological context of the study site establish key incountry contacts necessary for advancing the project, and assess the potential for a second, compari s on site .4 Finally, the main fieldwork for this study was conducted August 2004Ju ne 2005. The princ ipal research during this period was a questionnaire survey focusing on values, attitudes, and behaviors toward elephants. To support and augment the survey, other methods were used including focus groups, GPS mapping, document reviews, i ntensive enumerator training, two stage pretesting (question response formats and survey instrument), and follow up interviews My first task upon returning to Kenya in 2004 was to evaluate the current conditions in the study site, as two years had elapse d since the preliminary fieldwork. I met with representatives of conservation organizations working in the study area and reviewed current 3 Alexander and McGregor (2000) provide an example of where a lack of consideration of local history caused significant conflict in the implementation of a conservation and development program ( the Gwampa Valley CAMPFIRE programme). 4 Upon securing funding for fieldwork, it was decided there was not adequate time or financial resources to conduct the survey at a second site.

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35 project documents, where available. These included records of consolation payments made by AERP, project reports from AWF, and the HEC occurrence books of KWS (HEC occurrence data was collected by a research assistant in Loitokitok). I met with the newly elected members of the group ranch committees and the parks new warden to gain permission for the research. I hired a Maasai university student, Grace Masarie, who was from Kimana Group Ranch, to assist me with operating the project a political requirement and cultural and logistical necessity. She was later replaced with another local Maasai, George Ole Lupempe, who w as from Olgulului Group Ranch, when she returned to university. Attitude Survey The central part of the overall study was the attitude survey, which was built upon and supported by all other components of the study. The survey was designed and carried out to meet the theoretical, methodological, and applied goals of the project. Creating a sampling frame The effort to establish a random, representative sample was a challenging undertaking. Census lists were not available and, given the mobility of a large portion of the population, existing maps of Maasai settlements were out of date. Therefore, a map was created by collecting GPS waypoints for each residential site (explained below) in the study area. Two field assistants, with previous GPS data collectio n experience, were each equipped with Garmin GPS receivers and census worksheets (Appendix B ). They covered the entire study area on foot and by bi cycle, captur ing a total of 519 waypoints, along with data on household construction and composition. Waypoints were integrated into the AERP GIS database and a map of the study area including residences was created ( Figure 22) A waypoint could represent a traditional Maasai enkang; a manyata ( enkang of ilmurran/ warriors ) ; or a nontraditional, modern residence (Maasai or non Maasai) An

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36 enkang is typically a circular compound comprised of multiple houses ( enkaji ) all encircled by a thorny branch enclosure for protection from predators (livestock is kept within the enclosure at night). In the past, the enkang was comprised of approximately 6 12 polygamous households (Jacobs 1965 cited in Coast 2002), with each wife having her own house. Ea ch individual house (a structure made of mud and dung) is traditionally built, maintained, and occupied by a married woman, her children, and sometimes the husband. These polygamous households or families, referred to as olmarei are often used as the sampling unit in social research with the Maasai (Serneels et al. 2009). As with Maasai society in general, the composit ion of the enkang is changing. Coast (2002), citing several others, notes that the trend toward the single household enkang is increasingly evident. Today many men and some women (pers. observ.) are building their own modern, rectangular structures with g rass or mabati (corrugated iron) roofs (requiring money). Changing values and lifestyles, brought on by numerous factors, including increasing poverty, are influencing household composition (Cochrane et al. 2005). For example some women are seeking altern ative sources of income (e.g., selling beadw ork, agricultural products ) and are even leavi ng the home to do so (e.g., moving to cultural bomas see Chapter 4). The household count revealed a wide range of household compositions across the study area and, because a portion of the population moves seasonally with livestock, some settlement sites were classified as permanent and some as temporary. From the census sheets, we determined that there were 2,444 households in the study area: 1,606 (66%) in Olgulului and 838 (34%) in Kimana.5 5 A waypoint could represent a traditional enkang, comprised of single or multiple households, or a nontraditional, modern residence.

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37 Selecting a sample A multistage area sample (Weisburg et al. 1996) was selected to capture the increasing heterogeneity of the widely scattered, sometimes hard to reach, members of the population. Every effort was made to obtain a random, representative sample. Given the limits in resources and time, I selected the largest sample size possible to increase the possibilities of analysis and decrease the sampling error (P e i l et al. 1982). A sample of 293 households (12% of total) was selected, with the goal of interviewing two adults (one male, one female) in each household (n = 586). This was first stratified by group ranch, following Kangwana (1993). Therefore, 193 households (66%) were selected in Olgulului and 100 (34%) in Kim ana. While many studies seek to interview the household head, this limitation can cause serious bias, as the sample will likely be over represented by elderly men, who differ significantly from other adults living in the household (Piel et al. 1982). There fore, in addition to targeting both male and female respondents, I decided to select each respondent as randomly as possible. The following sampling procedure was employed: Defining study area Olgulului and Kimana Group Ranches were selected to comprise the study site following Kangwana (1993), who selected these areas because of their proximity to park and the resulting level of interaction with elephants Additionally, they were two separate political areas and they varied in predominant landuse. Defin ing geographic regions Using the census map, the group ranches were divided into regions based on spatial distribution or clustering of settlement areas, commonly referred to as neighborhoods. These areas were labeled OLG distant north, OLG nea r north, OLG west, OLG south, O L G east, KIM kimana fence, and KIM namelok fence. Determining proportions The total number of households in each of the regions was summed and divided by the total in the respective group ranch. This gave the percentage of households that each region contributed to the total. The percentage of each region was used to determine the percentage of interviews that should be done in each region. For example, in Kimana, where the desired number of sample households was 100, one region comprised 52% of the sample households, therefore 104 (52% of 200) was the desired number of interviewees from this cluster.

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38 Selecting clusters Within each region the neighborhoods were numbered and then neighborhoods were selected using a random number table. Selecting households Each enkang (term used here for convenience to indicate all types of residences) in a neighborhood was numbered. Every household in an enkang had an equal chance of being selected, as each enkang was assigned as many numbers as the number of households it contained. E nkangs were selected by using a random number table. Using this random technique, an enkang may not have any households selected or it may have had multiple households selected. Three alternate enkangs were selected in each neighborhood. Selecting individu als We visited each selected enkang the day before the anticipated interviews to seek permission to return the next day. We sought an elder or household head to select a random number or numbers, depending on the number of households to be selected, betw een 1 and the total number of households in the enkang. We then used the number(s) to count around the circle of huts to locate the household(s) where interviewees were to be selected. For example, if there were six households in an enkang in which two households were selected, we asked the elder to randomly choose two numbers from 1 to 6. So, if he said 2 and 4, we counted around the enkang, starting at the first house on the right from the gate we entered (an enkang has a gate for each olmarei ) to ide ntify the second and fourth households. We then asked the elder to give the adult composition of the household. We attempted to randomly select individuals (coin toss), if there was more than one adult female and one adult male associated with selected hou se and more than one was going to be present on the day of the interviews. This process was guided by an interviewee selection worksheet (Appendix B). Questionnaire design My assistant and I conducted nine focus groups (September 2004) to 1) elicit salien t beliefs about wildlife elephants in particular, and related issues and 2) acquire appropriate, culturally relevant, local vocabulary to develop the survey instrument ( Figure 23) This, in addition to the preliminary fieldwork, also helped in building rapport in the community. The focus groups took place in three locations Emeshenani (n orth ern Olgulului ), Enkongu Narok (s outhern Olgulului ) and Namelok ( Kimana ) with three focus groups in each location (one with women, one with elders, and one with ilmur ran) to capture variation by location, livelihood activity, and social standing as defined by ageset and gender. Questionnaire items were developed using the knowledge gained from the focus groups, the review of the records and documents of various organizations involved in elephant

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39 conservation in Amboseli, and key informant interviews. Attitudinal items were based on hypotheses, which were grounded in social psychological theory and previous research. The questionnaire started with general question s regarding wildlife, progressed to questions specific to elephants, and concluded with sociodemographic questions. Questions were a combination of openand fixed response (yes/no, true/false, agree/disagree, etc.) questions. Openended questions were ei ther field coded, where enumerators selected responses from pre coded lists, or were coded during data analysis (for longhand responses). Picture cards were used to elicit responses to questions regarding identification of wildlife that occurs in the group ranches ( Figure 2 4), wildlife that is liked/disliked (card sorting), problematic wildlife (ranking), and current and future livelihood activities ( Figure 2 5). Several methods were utilized to minimize error. The questionnaire underwent expert review by a panel of specialists with expertise in survey research theory and methods, elephant conservation, program evaluation, and local culture. Questionand answer formats were pretested before the final draft of the questionnaire underwent two stages of prete sting. The questionnaire was translated into Swahili (by my assistant and me) and Maa (by my assistant and another Maasai a former conservation project manager). The Swahili version was backtranslated by a language instructor at the Hekima Language Serv ices, Ltd., in Nairobi to check for accuracy and equivalence of meaning. The Maa version was reviewed by ten Maasai people from Amboseli who had completed secondary school and were fluent in Maa and English. Enumerators A pool of potential enumerators rec eived intensive training during a weeklong workshop. The final four selected to work on the project spent an additional week conducting closely supervised practice interviews among a subsample that was excluded from the analysis. Enumerators were closely supervised by my assistant and me on a daily basis and required to

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40 review and sign each questionnaire upon completion. They also answered a series of questions at the end of each questionnaire regarding the circumstances of the interview (e.g., did anyone interfere with the interview) and the respondents demeanor (e.g., was the respondent interested, cooperative, honest, etc.). Questionnaires were then reviewed by the field supervisor, who also signed the questionnaire to confirm it had been checked for er rors and completeness. Finally, I checked the questionnaires prior to data entry. My assistant and I promptly followed up with enumerators if there were any questions. Managing bias At the close of each interview, respondents were asked for their thoughts on the interview to provide an evaluation of potential bias. Questions included a general evaluation of the interview, who they thought we represented (respondents were informed at the beginning of the interview that we represented the University of Flori da), if they were interested in receiving information on the results of the study, and if they had been interviewed by other researchers. In an effort to distinguish the research team from other organizations working in the area, we wore matching T shirts with a Human Dimensions of Wildlife Research Project logo and had the same logo on the research vehicle used to move about the study area. Follow up I nterviews Follow up interviews were conducted in May 2005 with individuals and groups working and livi ng in the study area. The purpose of the interviews was to clarify and support information gathered in the survey of local residents. Interviewees included lodge managers, the Olgulului public campsite manager, members of the Olgulului Group Ranch Committe e, members of the Game Scouts Association, and senior elders from the community. Lodge managers were asked about their involvement in community and conservation projects (including the cultural bomas), and the number and types of positions held by local Ma asai in their lodge. The public camp

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41 manager was asked about the history of the campsite and the revenue generated by the camp. The group ranch committee was asked about their perceptions of conservation and development issues in the area, including wildlife in general, elephants in particular, subdivision of the group ranch, and future land use. The game scout interviews focused on the duties of the scouts, their interactions with people in the community, and perceptions of humanelephant conflict in the area. Finally, five senior elders were interviewed (one was apparently the oldest person in the region, stating he was 100+ years old) about the changes that have occurred in the Amboseli ecosystem since they were children, what wildlife means to the Maasai, and their perceptions of elephants ( Figure 26). GPS M apping of HEC L ocations In addition to the GPS mapping of settlement sites, a second team of GPS assistants collected waypoints for each site of HEC recorded in the KWS occurrence books in Loitokitok (for the years 19992004) and using data from AERPs consolation records (for the years 19972004). It is recognized that these records do not provide a complete record of each occurrence of HEC. It is likely that many cases go unreported, especially les s severe incidents. Nevertheless, because HEC is a highly salient issue, it is believed that a vast majority of cases are reported, providing an additional layer for analysis of the human dimensions of HEC in this region. Although it is not reported here, an examination of the reported sites of HEC and spatial variation in attitudinal variables examined in this dissertation should provide additional insight for stakeholders working to mitigate HEC.

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42 Table 2 1. Population of Kajiado District 19691999 ( adap ted from Campbell et al. 2000) Kajiado District Kenya Year Population Inter census growth (%) Avg. annual growth (%) Avg. annual growth(%) 1969 85,093a 1979 149,005a 75.1 5.76 3.8 1989 258,659 a 73.6 5.67 3.4 1999 405,000 b 56.6 4.58 2.9 a a Kenya Central Business of Statistics, Population Census 1969, 1979, 1989 b Ministry of Finance and Planning, February 2000. Provisional Results of the 1999 Population and Housing Census Table 2 2. AERP c onsolation payments Year Livestock killed Consolation payment 1997 7 75.000/ 1998 1 5,000/ 1999 4 30,000/ 2000 28 400,00/ 2001 3 35,000/ 2002 32 307,500/ 2003 18 250,000/ 2004 44 581,500/ Total 137 1,684,000/ Source: AERP records

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43 Figure 2 1. Map of study area Amboseli National Park and surrounding group ranches, with Maasai enkangs in red.

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44 Figure 2 2. Participatory mapping activity in Olgulului Group Ranch.

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45 Figure 23. Focus group with women in Olgulului Group Ranch.

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46 Figure 2 4. Wildlife identification cards.

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47 Figure 25. Livelihood cards depicting a teacher, wildlife conservation workers, pastoralism, cultivation, selling produce, selling handicrafts, and beekeeping.

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48 Figure 2 6. Follow up interview with an elder conducted by George ole Lupempe (pictured).

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49 CHAPTER 3 ATTITUDES TOWARD WIL DLIFE AND CONSERVATI ON ACROSS AFRICA: A REVIEW OF SURVEY RESEARCH1 Introduction Human wildlife conflict is increasing across Africa (Ngure 1992; Waithaka 1993; Hoare 1995; Tchamba 1995; Barnes 1996; Madden 2004). As human populations and demands for land increase throughout the continent, humanwildlife conflict will continue to incr ease and less land will likely be available for parks and protected areas. Outside of protected areas, wildlife will increasingly depend on dispersal areas occupied by people; therefore, enlisting the support of local people is, and will continue to be, cr itical to management and conservation efforts. Part of this process entails understanding peoples attitudes and beliefs as they are posited to influence human behavior (Fishbein and Ajzen 1975; Ajzen and Fishbein 1980); therefore, understanding individual s attitudes can help managers better predict the response and support of local people to wildlife policies. Data gathered from attitudinal surveys give guidance to management decisions and act as a baseline to test the effects of policy decisions. This information has shown to be effective in assessing the success of experimental policies such as increasing benefits to communities and using locally recruited game guards (Lewis, undated). Information that describes the origin and links between public attitudes toward wildlife and the acceptability of management actions provides wildlife officials and stakeholders with the data needed to discuss competing public beliefs, address potential misunderstandings, and develop solutions (Vaske and Donnelly 1999; 1 This chapter is reprinted by permission of the publisher, Taylor & Francis Ltd. The original citation is: Browne Nuez, C. and S.A. Jonker. 2008. Attitudes toward wildlife and conservation across Africa: A review of survey research. Human Dimensions of Wildlife 13(1): 4770.

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50 Zin n et al. 1998). Key to the successful application of survey data is to ensu re the rigor of the methodology. This article examines the use of attitude survey research in Africa, particularly in East and southern Africa where conservation attitude research i s increasingly utilized. We focus on Africa for a number of reasons. First, this review was originally part of the preliminary research for a project examining the attitudes of local people toward elephants in a humanelephant conflict area in Kenya. Secon d, the original literature review revealed a variety of methodological approaches in previous studies, which lead to several questions regarding the basic canons of empirical research such as measurement, testing of theories, reliability, and validity. Thi rd, we found that it is common practice in much of the literature to compare or lump findings from previous studies across cultures, regions, and countries leading to questions about their comparability or generalizability. This seems to be especially true of any discussions of Africa, scientific or otherwise. One often hears blanket statements about the continent, rather than specifics about a country, region, or culture. Another important issue that arose was that of sufficient disclosure to allow a study to be fully evaluated and replicated. Finally, with the growing body of literature in this area, we ask if it is possible, given the variation, to develop a standardized methodology for attitude research in Africa that can be extended to other developing regions.2 While survey research in Africa is not new (Richards 1935; Schapera 1935), it has only become a common tool in African wildlife conservation in the last few decades (Table 31, Table 32). It has been suggested that data from attitudinal studies such as these are useful for 2 While it is beyond the scope of this paper to include survey research from other developing regions of the world, we believe the issues raised here are applicable in the global context.

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51 comparing attitudes toward conservation in different regions and under different conditions (Hackel 1990, Harcourt et al. 1986). However, we caution that often only general trends in the data should be considered. Researchers face several difficulties when conducting social surveys in Africa language barriers and cultural differences between researchers and the local people, population dispersal, lack of census information, transportation limitations, potential respondents lack of experience with survey research and willingness to participate in surveys, and security concerns. Each of these concerns may affect methodology. Making meaningful comparisons when the specificity of methods and constructs vary or are unknown across studies may lead to misinformed decisions and recommendations. This review of attitudinal studies from different parts of Africa should reveal the strengths and weaknesses of survey data thus far and identify future research needs. We begin with a brief overview of scientific principles and methodological issues in survey research in general. We then consider these as they are transferred to other countries and used cross culturally. Next we examine if and how the studies in this review address these issu es. Additionally, we will attempt to answer the aforementioned questions raised during the literature review for the preliminary research using insight gleaned from the studies reviewed here and by looking to the expertise of researchers from various field s of social science inquiry. Methods As part of the preliminary research, a search was initially performed in 2001 in the Web of Science database using the keywords attitudes wildlife, conservation, and Africa. No limitations on time frame were implemented. Our initial search identified five attitude studies, with the earliest published in 1990. A follow up search was conducted in 2006 to obtain the most recent literature. Citations in the published studies were used to identify unpublished

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52 findi ngs. Where possible, copies of unpublished documents were solicited from the respective authors. Articles were excluded if they did not specifically use the term attitude (i.e., papers were excluded if they used opinion or perceptions), if the resear cher(s) did not use a questionnaire, and if the sampled population did not include local people. Cases were also excluded if they failed to provide an adequate account of their methods. Studies were then compared across several categories related to survey development and implementation. The Science of Survey Research The many disciplines in the social sciences offer a wide variety of research methods, but perhaps none is more widely shared than the survey. With its origins in sociology, scientists from numerous disciplines employ the questionnaire survey in their research today. Some key features of Western survey research have been random samples, standardized questions measuring demographic and sociological variables, trained interviewers, and statistica l analysis (Heath et al. 2005). As with all data collection techniques, survey research has advantages and disadvantages. Some strengths associated with surveys are that they permit large samples representative of populations; have the same questions and m eanings, at least in theory, being applied to all respondents making results more reliable; and provide quantitative data allowing for efficient and rigorous statistical analysis. On the down side, standardization limits flexibility, not only limiting what you ask, who you ask, and how you ask, but, more broadly, the research design must stay the same throughout, even if field conditions warrant adjustment. For these and other reasons, the survey may not always be the method of choice. Awareness of the stre ngths and weakness of a chosen method is the first step in selecting the best method and in mitigating threats to the quality of research. Our objective here is not to argue that one method is better or more appropriate than another, as it is up to the res earcher to determine the best methods depending on the research. Rather, we believe that the rapid increase in survey research in

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53 African wildlife conservation and its varied approaches warrants a review so that we may examine survey quality and consider t he implications for policy decisions for managing humanwildlife conflict and wildlife conservation in general. As in all areas of empirical investigation, researchers conducting surveys must work under the central tenets of scientific inquiry and strive to obtain data that is reliable, valid, representative, and generalizable. In doing so they can ensure that findings will not only stand up to scrutiny, but also contribute to well informed decisions and practices. Other important issues of empirical resear ch are conceptualization and the use of theory. Specific to survey research are the additional issues of survey quality such as coverage error, sampling error, nonresponse error, and measurement error (Groves 1987). What constitutes quality survey research has largely been defined by Western researchers, particularly those in the U.S. (Harkness 1999). While survey research has a longer history in the West, there still remain quality issues requiring ongoing refinement. In cross cultural research these issues must also be considered as they relate to translation and cultural appropriateness (Harkness 1999). While a thorough discussion of these concepts is not within the scope of this paper, we provide a brief overview, consider how quality issues can be exacerbated in developing countries, and examine these concepts in the context of the studies we review. Reliability and Validity We start with the concepts of reliability and validity as good research must be reliable and valid (Nunnally and Bernstein 1994). Data that is neither valid nor reliable is also not generalizable. Reliability refers to whether a particular technique, appl ied repeatedly to the same object, would yield the same result each time. (Babbie 1995, p. 124). A general definition of validity refers to the extent to which an empirical measure adequately reflects the real meaning of the concept under consideration ( Babbie 1995, p. 127). Several types of validity need

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54 to be considered that include, but are not limited to internal, external, content, and construct validity. Reliability and validity are important in all disciplines that engage in scientific inquiry and are considerations in every aspect of the research process. Conceptualization and Theory Carefully defining what is being measured, grounding research in theory, and developing measurement items that are reliable and valid are important first steps in attitude research. Deciding how to measure something depends on how we define it. Conceptualization is the process through which we specify what we will mean when we use particular terms (Babbie 1995, p.114). Many concepts measured in the social sciences are broad and varied in how they are defined. If we are to communicate logically about a given concept it is important that we agree upon its meaning and how to measure it. Conceptual definitions are most valuable when they are linked together to support theories that help to explain research results (Bernard 2002). The concept of attitude has been defined many ways, but a commonality among definitions is that attitudes are evaluations or feeling states about an attitude object. Individuals may hold attitudes toward a wide variety of objects, including social issues, natural resource issues, categories of people or situations, specific individuals, animals, and physical objects (Fazio 1995). Depending on how one defines attitude, there are several ways to measu re this construct. Bem (1970) defines an attitude using a simple evaluative statement such as I like apples or I dont like oranges. Under this definition, a survey could have a single indicator for an attitude. Responses to a single item indicator as measures of attitudes are suspect, since they do not have the built in potential of scales for reducing measurement error (Heberlein 1981). Moreover, these types of items merely ascertain single beliefs, rather than the organization of beliefs and affect w hich comprise an attitude. Another definition which captures the complexity of attitude, is the organization of beliefs, evaluative beliefs, and affect about the attitude object

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55 (Rokeach 1968). Under this definition, a combination of items, each measuring a different facet of attitude, would be used. A multiple item indicator or scale approach provides a more valid and reliable measurement. The definition of the concept being measured and the indicators being used in measurement are often determined by theory. For instance, many attitude behavior studies in the United States are based on the Theory of Reasoned Action (Fishbein and Ajzen 1975; Ajzen and Fishbein 1980). Theory is important as it extends the generalizations of findings, enhances the rigor and confidence of research, offers structure for building upon earlier findings, and enables researchers to move beyond descriptive studies. An underlying assumption of many attitude studies in Africa is that there is a direct link between attitudes and behaviors. Therefore, it is important that attitude research is based on a theoretical framework that helps explain the various cognitive processes that influence behaviors (Decker et al. 2001; McCleery 2006). Survey research is not new to Africa; nor is it limited to a specific discipline. Today, researchers in business/marketing; health sciences, especially related to HIV/AIDS; political science; education; and other fields frequently use the questionnaire survey to understand the values, knowledge, beliefs, a ttitudes, and behaviors of African peoples (Astrom and Okullo 2004; Jemmott et al. 2007; Murray Johnson et al. 20002001; Orkin 1998; Rani et al. 2004; Uzoka 2007). With this global expansion in survey research, researchers are becoming more aware of the challenges of transferring measurement techniques developed in monocultural settings to cross cultural research (Johnson 2006). We must consider the issues associated with exporting survey methods to other cultures, such as consistency of quality and, in the case of cross cultural comparisons, equivalence of meaning (Heath et al. 2005).

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56 Although there has been extensive attitude research and theory development in the U.S. regarding wildlife management/conservation, the transfer of theory developed in the We st to wildlife conservation studies in Africa has not been widely tested. However, other disciplines (e.g., tourism, health sciences, psychology) have successfully applied theories such as the Theory of Reasoned Action (Lepp 2007), the Theory of Planned Be havior ( Jemmott et al. 2007), and the Theory of Basic Human Values (Schwartz et al. 2007). In their study of the cross cultural validity of the Theory of Basic Human Values, Schwartz et al. (2007) found that although the theory di d not prove applicable in rural areas of less developed countries, the use of a different measurement instrument proved the theory more nearly universal than previous findings had suggested. While theories may not be completely universal, further research is needed to clarify the limits of their applicability (Schwartz et al. 2007). Most of the studies of attitudes toward wildlife and conservation in Africa are not based on theory and most do not define what is meant by the term attitude (Table 31). One exception is a study of local peoples attitudes toward wildlife in Botswana (Mordi 1987). In this study, the researcher recognized the multiplicity of definitions of attitude in existence and offered a generic definition in an effort to facilitate commu nication and promote shared usage. Kellerts (1985) typology of attitudes toward animals served as the conceptual framework (e.g., naturalistic, moralistic, utilitarian, etc.). The rationale for selecting Kellerts typology over several others employed in the West was that its categories are both mutually exclusive and collectively exhaustive of the universe of attitudes toward wild animals in Africa. As an African, Mordi found this framework lacking in one dimension fatalism which he states is ever present in most African cultures. Therefore, he added an eleventh dimension he termed theistic attitude.

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57 Although his study was grounded in Kellerts typology, Mordi used two theories on which to base his hypotheses: Rogers Diffusion of Innovation and M aslows Hierarchy of Needs. Mordis (1987) original survey instrument contained ten agree disagree statements for each item. Three pretests were conducted, and items that failed to yield consistent results were dropped. A different group of respondents wa s used in each pretest. The remaining fifty one items reliably differentiated among respondents in a consistent manner (Table 3 2). Mordis use of different individuals to infer reliability may be considered dubious. Standard measures of reliability, such as the internal consistency method and the split halves method, were not performed. Measures, such as the split halves method and the test retest method, involve using the same group of respondents. The other studies reviewed here (Table 3 1) did not de fine the concept of attitude nor ground their research in theory. For example, in a study of human elephant conflict in Amboseli, Kenya, Kangwana (1993) included an examination of the attitudes of the Maasai toward wildlife and Amboseli National Park. The study was exploratory and, therefore, was not based on findings of previous work or on theory. The researcher recognized other attitude studies done in Africa, but stated that these surveys were carried out with other peoples, implying that no comparisons could be made. Because of the exploratory nature of the research, Kangwana does not test hypotheses but puts forth four predictions. Of course, the most important consideration in question development is, Are you measuring what you think you are measuri ng? validity. Although there is no statistical procedure for measuring validity (Bernard 1995), factor analysis can be used to identify the number of constructs being measured by a set of items. Nevertheless, it is up to the researcher to define the nat ure of each construct. In Mordis analysis, factor analysis indicated that his eleven

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58 attitude types could only be explained by eight factors. The ecologistic, humanistic, and naturalistic attitudes were not identified as independent types. He offered poss ible explanations for this outcome: (1) some questions may have measured more than one attitude type and (2) some indicators may have had stronger links to factors other than those they were intended to measure. As Mordi pointed out, this could have been a voided had the instrument been more intensively pretested. In the end, the issue of validity is left to the researchers judgment and a review by recognized experts in the field of study. There are several ways to improve validity concerns that can be stan dardized across studies, such as improving external validity by drawing a random sample from the population, replicating the study, and so on. Prior to developing her questionnaire, Kangwana (1993) conducted a pilot survey, which involved group interviews using an interview schedule and free discussion. During the pilot survey the Maasai were unwilling to answer Likert scale, true/false, or agree/disagree questions. Some responses to these types of questions were, That is a question without a head or a tai l and, That depends therefore, questions on the final survey were open ended and the responses taken down in longhand. No tests for reliability were performed. Two questions each were asked to determine attitudes toward wildlife in general and elephant s in particular, and three questions were asked to determine attitudes toward the park (Table 31). As was mentioned earlier, attitudes are complex constructs, and, in order to obtain a more comprehensive representation of attitudes, questions need to be a sked that examine the various facets of an attitude, so, in this case, where there is a limited number of items measuring attitudes, results may be limited in contributing to the understanding of Maasai attitudes toward wildlife and Amboseli National Park.

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59 Pennington (1983) used seven Likert scale questions to measure attitudes (Table 3 1). No pretesting was undertaken, nor were any checks for reliability and validity performed. Throughout the thesis, Pennington refers to attitude toward wildlife and conser vation when all of her items are belief and opinion statements about Tanzanias national parks. To derive an aggregate attitude score, students were given points for their responses to each item, ranging from 2 (strongly agree) to 2 (strongly disagree), w ith not sure responses being assigned 0 points. No reliability analysis was conducted to test the internal consistency of this scale to ensure that all items were measuring the same concept. Newmark et al. (1993) and Parry and Campbell (1992) used a com bination of fixed response and openended questions. Parry and Campbell (1992) used eight questions to develop an attitude index in their investigation of attitudes toward animal wildlife in Botswana. Newmark et al. (1993) employed one question each to mea sure attitudes toward protected areas, protected area employees, and poaching. Infield (1988), Akama et al. (1995), Gillingham and Lee (1999), Infield and Namara (2001), and Kaltenborn et al. (2006) are examples of research that used a fixedresponse for mat. Infield selected this format for ease of interpretation of the data. He used two yes/no questions, ten agree/disagree statements, and five paired statements giving contradictory views in which the respondent was asked to pick the one with which they m ost agreed. In a study in Kenya (Akama et al. 1995), respondents were asked five questions related to their attitudes to an adjacent park. The questionnaires were supplemented with informal conversations. Several researchers used an open ended question format, including Omondi (1994), Hill (1998), De Boer and Baquete (1998), Holmes (2003), and Dickman (2005). Holmes (2003) only used one indicator to measure attitude toward a national park. De Boer and Baquete (1998)

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60 determined a positive attitude associate d with the term liking. Daily observations were conducted by De Boer and Baquete (1998) to validate the survey responses given by the local population. Hills (1998) rationale for the openended format was to elicit more extensive discussions of some of the issues raised. This reasoning is similar to Kangwana (1993) in wanting to minimize the loss of information (Kangwana 1993, p. 26). Survey Quality Coverage and Sampling Error The level of coverage of a study depends on its sampling frame. Coverage can be a significant issue in any study, but may be an exceptional challenge in the developing world. Cost can be a limiting factor in the West and developing countries. It limits some studies to individuals with telephones or, for face to face interviews, can limit access to distant or hard to reach areas. A frequent limiting factor in the developing world is lack of any population registers. The primary issue when there is lack of coverage is whether the sample differs from the nonsampled portion of the population. Sampling error reflects the effect of chance in the sampling process and is a measure of the degree to which a sample is unrepresentative of the target population. Confidence intervals and levels illustrate the degree of sampling error by relating how confident the researcher is that the sample statistics actually reflect the entire populations characteristics Adequate sample size provides greater confi dence of representativeness so that conclusions drawn to inform policy are more likely to reflect the attitudes of the population rather than a min ority or select few. When samples are smaller, the sampling error increases and this limitation need s to be r ecognized in many studies conducted in rural locations of developing countries Our review highlights the challenges in following standard sampling procedures in Africa (Table 3 2). Ensuring external validity may be one of the biggest challenges in developing

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61 appropriate sampling procedures. The challenge lies in dealing with variables such as seasonal and long term migration (e.g., moving with the rains) and lack of census information in developing countries. Unlike the typical U.S. survey, where an interview is conducted by phone or a mail survey is sent, in rural Africa where a majority of people do not have a phone, or a mailing address, researchers have to go directly to the respondent for personal interviews. For several studies examined in this paper, the sample unit was the household or family unit, with one person from each surveyed. The availability of population information varied, depending on location of the study. The following examples exemplify the variability in how researchers have addressed these issues. Mordi (1987) sampled eleven sites in an attempt to obtain a representative sample of the economic, ecological, geographical, and cultural diversity of Botswana. The sites were the city of Gaberone, the University of Botswana, and nine rura l areas. The population was stratified into age and gender subgroups. Each site required a different sampling method. Gaberone was divided into 103 geographical areas, of which thirty one were randomly selected. In each area, every fifth house on each stre et was selected, and, at each selected house, an agestratified schedule was used to select the target interviewee. At the university, one in every four students was selected from a composite list of all students. In large villages in the rural areas, one household in five was selected, and, in smaller villages, one in three was selected. At each hut, the respondent was selected if he/she met the statistics on a predefined questionnaire based on gender and age. Kangwana (1993) had a listing of Maasai elders who were heads of homesteads around Amboseli National Park in Kenya. The list of homesteads was divided into two economic activity categories, predominantly pastoralist and predominantly agriculturalist. Using random

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62 sequential sampling, homesteads were selected from the lists. Six homesteads were selected for a reserve list because of the fluid nature of Maasai settlement. To obtain a cross sectional point of view, interviews were conducted with members from three sections of traditional Maasai society: elders, ilmurran (warriors), and women. On arriving at a homestead, the elder was interviewed first, out of respect for the structure of Maasai society. The first ilmurran encountered was interviewed next. Ilmurran were not always present and, in the end, were under represented. Finally, the first woman encountered was interviewed. Pennington (1983) selected fourteen of 20 or so secondary schools in two regions. She did not explain how these two regions, or the fourteen schools, were selected. Because the Tanzanian government promotes de tribalization, a bussing program mixes stude nts from different regions/tribes; therefore, students at each school are not necessarily from that region. No further explanation of sampling methods was provided (e.g. selection of students within each school), although by the large sample size (n=800), it appears that each student present in each school was surveyed. Newmark et al. (1993) investigated conservation attitudes of people living adjacent to five protected areas in Tanzania. An estimate of population for each area was available from a census conducted five years before the study, but dispersal information was not available. A proportional random sampling design stratified by park was employed to obtain the sample size from each park and interviewees were selected by way of chance encounter. H ill (1998) examined attitudes towards elephants in an area where elephants no longer reside. Similar to the previous example, Hill (1998) obtained the total population count from a census conducted a few years prior to her research. She interviewed 3.4% of the local population,

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63 locating each participant by chance encounter while walking through the three villages in the study area, interviewing one adult per household. Akama et al. (1993) in Kenya did not have any knowledge of population size or dispersal. Their study involved surveying people living adjacent to two national parks regarding their attitudes toward the state wildlife conservation program in Kenya. They chose areas that were attracting new settlers and selected interviewees by chance encounter at homesteads, on foot trails, and in crop fields and livestock pastures. Parry and Campbell (1992) examined attitudes of people in rural communities toward wildlife and its utilization in two different areas of Botswana. In one area, recent aerial phot ographs were available. Using the photographs, all household clusters were identified and clusters were then randomly selected. All of the households within the selected clusters were surveyed. No photographs were available for the other area, therefore, a ll households in which a resident was at home were surveyed. Infield (1988) did not report the availability of population information in his study of attitudes of a rural community in South Africa towards conservation and a local conservation area. He est ablished a study area 10 km wide around the conservation area, with the idea that attitudes resulting from either positive or negative influences emanating from the conservation area will generally be most pronounced in those communities living in close p roximity. After dividing the study area into 140 numbered blocks, a simple random sample was taken. Thirteen households from each of the fourteen selected blocks were randomly selected. Some samples were driven by availability of villages/households/peo ple (Dickman, 2005; Gadd, 2005) or by wildlife activity (Lindsey, 2005). Sitati (2003) selected sampling areas by presence of human elephant conflict areas and then randomized selection of households within

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64 these areas. All but two of the remaining studie s under review (Omondi 1994; De Boer and Baquete 1998; Gillingham and Lee 1999; Holmes 2003; Weladji 2003) randomly selected households across villages or ranches (Table 32). Given the challenges of sampling in Africa, including obtaining an adequate lev el of coverage and large sample sizes it is imperative that researchers carefully assess at what level their results will be meaningful in informing policy. As is evidenced here, various degrees of population information are available throughout Africa and researchers have to be resourceful in developing appropriate sampling designs for their studies that are based on the experience of previous research and theory. As we strive to standardize methodology where possible, we must ensure the highest level of randomization and representativeness. Maintaining this standard enables us to have confidence that our data are valid and generalizable. Nonresponse Error A nother survey quality issue is nonresponse bias which occurs when researchers generalize to a pop ulation without recognizing differences between respondents and nonrespondents in attitudes, beliefs, and other related concepts This weakens the validity of the information collected from a sample and limits the generaliz ability of the results Response rates in the U.S. are declining (Heath et al. 2005) and the resulting non response bias is a major concern It is common practice in the U.S. to document nonresponse, but there is generally not good documentation in the global context (Heath et al. 2005) Most of the studies in this review did not address nonresponse, but of the few that did, the number of potential respondents that were unavailable or refused to be interviewed was low in each case. Given that survey s in Africa are most often done through one onone interviews and therefore may have low refusal rates, documentation may seem less important, but nonresponse should be accounted for in all contexts. D ocumentation of the number of contacts refusals,

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65 unattainables, etc. need s to be maintained in order to determine the occurrence of nonresponse bias. If it is an issue several statistical methods (e.g., weighting) are available to adjust the results so they are still valid and useful. Response Bias In addition, response bias can also impact survey results. It occurs when r espondents perceive social pressure to provide responses that they think the researchers want to hear and therefore their answers may not reflect their true beliefs. Or respondents may be wary of who or what organiza tion the researcher represents and may alter their responses accordingly, thereby biasing survey results. For example, in areas where conflict exists between local communities and the wildlife authority, respondents may fear retribution if they provide truthful responses when they believe the researcher is a representative of the wildlife authority. Newmark et al. (1993) state that some respondents in their study may have believed their interviewers, who were students and instructors at the College of Afric an Wildlife Management, were affiliated with the wildlife and national parks officials. This sort of situation can be mitigated by establishing rapport and building trust in the community prior to data collection. Interviewer Bias Interviewer bias can also affect survey results. It occurs when respondent answers are influenced by interviewer characteristics such as appearance, behavior, and sex. I n Africa, where researchers are often from another culture, this issue may be more pronounced. For example, wome n in rural Africa will likely feel more comfortable with a female enumerator; traditional people may be suspicious of people in Western clothing or those whose clothing is similar to government/wildlife officials; or when enumerators receive insufficient t raining, they are more likely to behave in ways that are inappropriate such as body language, prompting methods, and recording responses.

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66 Interviewer bias can be limited by first being aware of its potential sources. The researcher(s) should have a thoroug h understanding of the local culture. A standardized program should be provided to each enumerator on the research team. Training should cover t opics such as the purpose of the survey explanation of the questionnaire interviewing techniques and how to record answers. Other Error Finally, there are other potential sources of error. For example, we note that there is a high degree of variation in study length (<1 month to 2 years) across the studies reviewed here (Table 3 2). The duration of the data coll ection period is a concern in attitude research because the integrity of the data can be compromised. The longer the data collection period, the more likely it is for other variables, such as stochastic events, immigration, and emigration to influence or b ias study results. For example, Kangwanas (1993) interviews had to be completed before the Kenya Wildlife Service disbursed park revenue sharing benefits and started a new extension program. Equivalence Comparability and Cultural Sensitivity The globali zation of survey research not only brings additional challenges to standard measurement protocols, but also requires special attention to other cultural considerations. Equivalence is increasingly recognized as a critical concept in cross cultural research and lately has received significant attention by researchers across disciplines (Bulmer 1998; Heath et al. 2005; Johnson 2006; Pea 2007; Willgerodt 2003). Unfortunately, there is not a broad consensus on what this entails. Johnson (2006) provides a brief overview of various forms (n=62) of the concept he located in the literature. Examples include construct equivalence, cultural equivalence, linguistic equivalence, measurement equivalence, scale equivalence, and theoretical equivalence.

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67 To demonstrate the importance of equivalence, we consider one of the broader conceptualizations, equivalence of meaning or linguistic and conceptual equivalence. In exporting home grown instruments, researchers working cross culturally need to consider if a term or a concept used in one society has the same meaning in another, how equivalence issues affect the validity of research results, and if the issues under investigation are culturally relevant. These are not new considerations. Scheuch (1968) called for functional equivalence rather than literal conversion, but given the abundant recent literature on the issue, it is an ongoing concern. Due to the considerable disagreement, ambiguity, overlap, and contradiction among these various conceptualizations there is obvious ly a need for further research and discussion among those conducting cross cultural research (Johnson 2006, p. S17). Awareness or cultural sensitivity is the first step in dealing with equivalence and finding mechanisms for overcoming problems. For example in cases without an equal term or concept, equivalence may have to be achieved through circumlocution. A somewhat related topic often discussed in Western survey research is question wording. Survey researchers have found that even slight variations in question wording can produce dramatic changes in the distribution of answers (Weisburg et al. 1996). Given the challenges and limitations associated with survey research in the typically rural African settings we are dealing with in our review, we must consider the validity of cross cultural comparisons. It is likely safe to say that most studies are not designed with the intention of future comparisons with other studies. Even studies that are intended to be cross national, with standardized instruments, face the same difficulties highlighted in this paper, such as equivalence and sampling (Bulmer 1998; H arkness 1999; Heath et al. 2005; Jowell, 1998; Kuechler 1998;

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68 Scheuch 1989). With this in mind, we believe only broad comparisons can be made and, when doing so, variations and the resulting limitations of such comparisons should be reported. A disregard for culture by researchers has been observed in various settings around the world (Rogler 1999). This disregard may take many forms such as when foreign researchers visit an area, collect their data, and return to their home countries to publish their findings with little or no benefit to the local culture. Another example is when researchers utilize Western concepts, theories, and methods in a culture different from where they were developed. Rogler (1999) discusses how such practices as relying on expert opinion in the case of developing content validity, standardizing instruments, errors in translation, and transferring concepts are acts of cultural insensitivity. Citing Manson (1997, p. 251) he states that [standardized] instruments may be incomprehe nsible and unacceptable to respondents from a different culture, and sometimes they are downright irrelevant (Rogler 1999, p. 427). Considerations of cultural insensitivity not only fall under the scope of our methodological interests in this paper, they also require us to consider the ethics of some cross cultural research (Schooler et al. 1998). Adaptations must be made that span the entire research process (Rogler 1999, p. 430). Many of the considerations we propose in this paper should be part of this process. Discussion Good progress is being made in developing an understanding of Africans attitudes toward wildlife and wildlife conservation. The growing body of knowledge in this realm confirms the need for including social science research in A frican wildlife conservation and more specifically in mitigating human wildlife conflict. While there has been a strong and concerted effort to better understand peoples values, perceptions, knowledge, attitudes, and

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69 tolerance toward wildlife and conserva tion, the lack of a consistent methodology limits the generalizability of results. Some methodologies that have been successful in the West may have varying application in developing countries, as was exemplified in Kangwanas (1993) pretesting of questi on format and Mordis (1987) question modification. Given the existing global body of work on attitude research, we should avoid reinventing the wheel with each new attitude study. Future survey research in Africa should build upon existing theory and me thods, use the lessons learned in the reviewed studies, and incorporate the recommendations provided herein to develop a rigorous theoretical and methodological framework for human dimensions of wildlife research. The adaptability of the researchers discu ssed in this review speaks to their resourcefulness in uncharted territory. However, this also speaks to the challenge of ensuring these efforts are useful in the long term, both practically and in terms of improving and building upon theoretical frameworks. What does this variability in methodology mean for future research and application of information? This review highlights the varying conditions in which survey research is taking place, which can lead to differences in survey quality (Heath et al. 2005). It also highlights the many challenges when attempting to develop a standardized methodology and points to the need for a framework for standards of best practice. For instance, it should be standard practice in survey research to include procedures suc h as pre testing measurement instruments and checks for reliability and validity. Additional procedures such as sampling and the development of questionnaire items should also be a part of this framework. The more complex components of the framework will a lways have variability in culture and landscape, and require researchers to adapt accordingly. Again, any adaptations need to be grounded in theory and previous research. They also need to be well documented to allow for evaluation,

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70 comparability, and repl ication in order to ensure long term validity of the body of research that is being developed in Africa. We have established that survey research has limitations that can be more pronounced in cross cultural research. Using multiple methods is one way to strengthen a study. For example, focus groups can be used to develop culturally relevant instruments (Willgerodt 2003); Schumann and Presser (1981) recommend the use of supplementary open ended questions; and, in dealing with equivalence, King et al. (2004) propose the use of fictional vignettes. There is a whole literature on innovative, participatory methods that can be used by the survey researcher to bolster a study (e.g., Slocum et al. 1998). An example from one of the reviewed studies is provided by Infield and Namara (2001) who used a suite of methods, including rapid rural appraisal, key informant interviews, and other qualitative methods to provide supporting information for a deeper analysis of the questionnaire data (Infield and Namara 2001, p. 51). It is important to build a cohesive and enduring body of knowledge that can provide greater insight in conserving Africas natural resources for the long term. Often attitude studies in Africa are conducted in isolation. In order to achieve a compre hensive and robust understanding that will contribute to more effective conservation measures in both the short term, for which many projects are designed, and the long term, it is paramount for attitude studies in Africa to address the methodological issues we have discussed here. As described there are indeed challenges, but the groundwork has been laid by a multidisciplinary group of researchers who have conducted attitude surveys in numerous cultures around the world, including Africa. For example, scie ntists who conducted a survey in rural Mali concluded that it is possible to carry out in a rural, preindustrialized, nonWestern setting, using a representative sample of generally nonliterate respondents, a survey that parallels complex ones carried out in

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71 the United States and other industrialized countries (Schooler et al. 1998). This finding is confirmed by our own experience conducting an indepth survey in rural Kenya. Conclusions As outlined earlier, humanwildlife conflict situations are increas ing and several methods and tools need to be developed and applied in an attempt to decrease and resolve these management challenges (Madden 2004). Effective policy decisions rely on reliable and valid data. Especially in contentious conflict situations, t he evidence to support decisions becomes even more important. As human dimensions research in Africa continues to develop, it is a critical to ensure rigor is incorporated so that effective and informed decisions can be applied. The goal is to make the col lected information useful in effectively influencing human wildlife conflict situations. Coordinated efforts will be needed to ensure these goals of garnering valid and reliable long term data can be attained and have an impact on addressing human wildlife conflict in Africa. To further the science of human dimensions investigations in Africa, future studies should strive to attend to the most prominent characteristics of scientific inquiry: reliability, validity, representativeness, and generalizability. Additionally, more attention should be paid to survey quality that is guided by a framework for standards of best practice. The merit and integrity of studies in this realm of research will be judged on their ability to address these characteristics and th eir application in informing and driving policy. In addition to addressing methodological issues, researchers should strive to understand the why, i.e., the underlying constructs, of peoples attitudes, as knowledge of attitudes alone is limited in its application. Most of the studies reviewed here examined the relationship between attitude and demographic variables such as education and sex. Some included prior experience (Kangwana 1993). Attitudes are based on beliefs about the attitude object. Therefo re, gaining a

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72 complete understanding of peoples responses to wildlife and conservation requires looking at how all of these variables collectively influence attitudes. Developing a common theoretical framework will facilitate this understanding and allow for improved evaluation and comparison across studies. This review highlights the necessary knowledge needed for conducting human dimensions of wildlife research in Africa. As most managers of humanwildlife conflict are not trained in the social sciences, there is a growing call for increased collaboration between social scientists and ecologists in managing wildlife, especially as it relates to human wildlife conflict (Heberlein 2004; Manfredo and Dayer 2004; Mascia et al. 2003; Treves et al. 2006). There fore we believe that the growing field of human dimensions of wildlife, with its interdisciplinary specialists, offers opportunity to carry out this social science research within the realm of African wildlife conservation, particularly in mitigating human wildlife conflict. Recommendations Based on this review and borrowing from researchers in other disciplines, we offer a few recommendations for addressing the methodological issues covered in this paper. These suggestions are not intended to serve as a comprehensive list, but rather we propose them as a starting point for dialogue on methodological issues in cross cultural human dimensions of wildlife research. Additionally, we do not purport them to be original suggestions, only that they have not been applied on a consistent basis. Many of them are basic components of scientific inquiry. As already stated in this article, we need to build upon the knowledge and experience of researchers not only within wildlife conservation but also in the respective fie lds of social science investigation. In doing this, we need to avoid continuously reinventing the wheel (Scheuch 1989), while recognizing that some re engineering is needed (Harkness, 1999).

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73 Given the growing call for attention to be given to survey qua lity at the national and cross national level (Harkness 1999; Lynn 2003), we recommend the adoption of a framework for standards of best practice in survey research (Harkness 1999; Heath et al. 2005; Lynn 2003). The framework should include, but is not lim ited to the following components: conceptualization, use of theory, standards for question development; use of appropriate sampling techniques, pretesting, interviewer training; attention to reliability, validity, and generalizability; documentation for mo nitoring, evaluation, and replication (Harkness 1999; Pea 2007); use of multiple methods; inclusion of researchers from the culture being investigated, attention to cross cultural issues (e.g., equivalence, establishing rapport in communities sampled), an d others. Researchers with social science training have the capacity to contribute information essential for the design of policies for mitigating human wildlife conflict. For this to be realized, human dimensions researchers need to demonstrate the rigor of their methodology and the validity of their data. We believe this review provides key considerations for this area of research.

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74 Table 3 1. Comparison of use of concept and theory in attitudinal research studies conducted in Africa Citation Attitude object, Country Define Attitude Concept Theory Measurement of Attitude Sample Indicators Pennington 1983 Wildlife and conservation, Tanzania No No 7 Likert scale belief statements National park budgets should be increased National parks cost the government too much money Even if there were no tourists, national parks should continue Mordi 1987 Wildlife, Botswana Yes Yes 51 agree/disagree statements to form 11 attitude types Termites serve no useful purpose in the forest I agree with the person who says he dislikes lions I feel cattle are more important than wild animals Infield 1988 Conservation and conservation area, South Africa No, recognized complexity of attitude concept, used several questions for meas urement No 8 fixed response questions used to create index of general conservation attitude, 7 questions used to create index of attitude toward conservation authority is protection of animals a good or bad thing? it is important to keep a place where animals and plants can live the Conservation Area is a waste of land it would be good to give the Conservation Area to the people who need land Parry and Campbell 1992 Wildlife and wildlife utilization, Botswana No No ? ? Newmark et al. 1993 Protected area and PA employees, Tanzania No No 3 open ended questions, 1 question for ea. attitude object in question How would you feel if the park was abolished? What good things do people from the park do? Do poachers break the law?

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75 Table 3 1. Continued Citation Attitude object, Country Define Attitude Concept Theory Measurement of Attitude Sample Indicators Kangwana 1993 Wildlife and national park, Kenya No No 2 questions ea. for attitude toward wildlife in general and elephants, 3 questions for attitude toward park, all open ended How would you feel if all of the animals were removed? Are elephants the most dangerous animals? Should the park be abolished? Omondi 1994 Wildlife, PA, and wildlife authority, Kenya No No 3 open ended questions, 1 question for ea. attitude object in question What would you say about wildlife? Do you consider national parks/reserves as being of any value? What does the wildlife authority do? Akama et al. 1995 State wildlife conservation programs, Kenya No No 5 yes/no belief items, no scale created wildlife conservation is an appropriate use of land national park is an asset to the family park should be degazetted De Boer and Baquete 1998 Maputo Elephant Reserve, Mozambique indicated a positive attitude being expressed as liking No ? ? Hill 1998 Elephants, Uganda No No 3 open ended questions should elephants be protected in Uganda? would you like to see elephants living in Budongo? are elephants dangerous? Gillingham and Lee 1999 Wildlife and management institutions, Tanzania No No 5 yes/no belief items (4 were opposite statement pairs), 3 openended belief questions, no scale important to protect wildlife for children people who poach should be punished does wildlife benefit Tanzania, local people, you/your household?

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76 Table 3 1. Continued Citation Attitude object, Country Define Attitude Concept Theory Measurement of Attitude Sample Indicators Infield and Namara 2001 Conservation and Lake Mburo National Park, Uganda No No 9 agree disagree attitude statements about park and conservation, scored 1 or 1, combined all to create an attitude index; 1 openended question regarding feelin gs about the park what the people and their livestock need are more important than saving plants and wild animals it is important to protect the animals and plants so that our children may know and use them what are your feelings about Lake Mburo National Park? Holmes 2003 Katavi National Park, Tanzania No No 1 open ended question how would you feel if Katavi National Park was degazetted? Sitati 2003 Elephant conservation, Kenya No No 3 closed questions, no index created benefits from elephants what is the future of elephants in the area? do you wish to continue living with elephants as before? Weladji et al. 2003 Wildlife policy and Bnou Wildlife Conservation Area, Cameroon No No series of closed and openended questions, number and wording not reported ? Dickman 2005 Wildlife in general, protected area, carnivores, Tanzania No No 3 open ended questions, 1 for each attitude object what do you think about wild animals living in the area around your village? what do you think of Ruaha National Park What do you think of the following [carnivores]?

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77 Table 3 1. Continued Citation Attitude object, Country Define Attitude Concept Theory Measurement of Attitude Sample Indicators Gadd 2005 Wildlife/elephants, Kenya No No ? various questions regarding beliefs about wildlife are there any good things about or benefits that you personally receive from elephants? are any animals causing problems in your area? Lindsey et al. 2005 Wild dogs and other carnivores, South Africa No No 1 scale question per species (6 species) scored from 0 (very negative) to 5 (very positive) indicate how you feel about having [species X] on your property Kaltenborn et al. 2006 Wild and domestic animals, Tanzania No No 1 5 point Likert scale questions for 21 species (do not like at all to like very much) indicate the degree to which you like [animal] 1Although the authors were not explicit in defining a theoretical framework, they do cite the relevant literature.

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78 Table 3 2. Comparison of methodology use in attitudinal research studies conducted in Africa Citation Attitude object, Country Pretest Reliability and Validity Sampling Study Length Pennington, 1983 Wildlife and conservation, Tanzania ? No n = 800 secondary school students from schools in 2 regions 15 mos. (part of larger study) Mordi, 1987 Wildlife, Botswana Yes Yes original n = 1,279 urban areas oversampled, new sample = 555, 44 from urban area divided into 103 areas, using random number assignment, 31 areas selected, every 5th house selected, agestratified schedule used to select interviewee 3789 from ea of 9 rural areas, houses randomly selected interviewee selected by predetermined age sex schedule 38 from a university every 4th student selected from list 7 mos. Infield, 1988 Conservation and conservation area, South Africa No No n = 151, households selected though 2 phase random sample, study area divided into numbered blocks, from 14 selected blocks, 13 households randomly selected 7 mos. Parry and Campbell, 1992 Wildlife and wildlife utilization, Botswana No No n = 231, Site 1 every household w/adult present, Site 2 all households w/in randomly selected clusters (aerial photos were avail for this site) 1 mo.

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79 Table 3 2. Continued Citation Attitude object, Country Pretest Reliability and Validity Sampling Study Length Newmark et al., 1993 Protected area and PA employees, Tanzania No No n = 866 around 3 national parks and reserves, proportional random sampling stratified by park, interviewees selected on basis of chance encounter 2 yrs. Kangwana, 1993 Wildlife and national park, Kenya Yes No n = 175, households randomly selected from list of households in 2 group ranches bordering park, 1 elder, 1 warrior, 1 woman 2 mos. Omondi, 1994 Wildlife, PA, and wildlife authority, Kenya Yes No n=500 randomly selected heads of households from 5 of 13 group ranches near protected area randomization not explained 6 mos. Akama et al., 1995 State wildlife conservation programs, Kenya No No n=201 from perimeter of 2 parks (157 locals, 44 park officials), 1 individual of a household (selection process not provided) 11 mos. De Boer and Baquete, 1998 Maputo Elephant Reserve, Mozambique No No n = 200, 50 randomly selected households in ea. of 4 villages 3 wks/ village Hill, 1998 Elephants, Uganda No No n = 116, from 3 villages, chosen upon encounter 1 person of any household 1 week/ village Gillingham and Lee, 1999 Wildlife and management institutions, Tanzania No No n = 202, 190 local people, local leaders from randomly selected households from 4 of 11 villages in district. Mostly men because of Muslim faith 4 mos.

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80 Table 3 2. Continued Citation Attitude object, Country Pretest Reliability and Validity Sampling Study Length Infield and Namara, 2001 1 Lake Mburo National Park, Uganda Yes No n=243, 2 phase sample: 1 st sampled enumeration areas, 2nd sampled households within areas within 6km of park (avg of 30 households per area) household heads or other senior members 3 mos. Holmes, 2003 Katavi National Park, Tanzania No No n=201, households randomly selected from generated lists of households in 3 villages 5 mos. Sitati, 2003 Elephant conservation, Kenya Yes No n=251, from areas experiencing elephant problems, 25 of 54 sublocations randomly sampled with a minimum of 10 households per sub location, any household member ? Weladji et al., 2003 Wildlife policy and Bnou Wildlife Conservation Area, Cameroon No No n=114 across 3 communities, 20% of households randomly selected in 2 larger settlements, all available households selected in small settlement 4 mos. Dickman, 2005 Wildlife in general, protected area, carnivores, Tanzania Yes No n=60, 15 villages/sub villages in three clusters, as many as possible households were visited, most senior member of household present was interviewed, mostly males Gadd, 2005 Wildlife/elephants, Kenya Yes No n=74, 34 herders selected via convenience sample (no census data available), 40 individuals at 2 other locations (every 10th household) 2 mos. (1999) 2 mos. (2002)

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81 Table 3 2. Continued. Citation Attitude object, Country Pretest Reliability and Validity Sampling Study Length Lindsey et al., 2005 Wild dogs and other carnivores, South Africa Yes No n=209 across 6 areas in South Africa and Zimbabwe, in each area as many ranchers as possible were interviewed, contact information obtained from telephone directory 7 mos. Kaltenborn et al., 2006 Wild and domestic animals, Tanzania Yes No n=590 from 6 villages across 3 districts, 3 villages near protected area and 3 further away ? 1Methods for this study were not included in this citation. We referred to Marquardt et al. 94 and Nam ara et al. 98 for details.

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82 CHAPTER 4 THE MAASAI ELEPHANT RELATIONSHI P: THE EVOLUTION AND INFLUE NCE OF CULT URE, LAND USE, AND ATTITUDES1 Introduction The African elephant evokes varied and deep emotion in people around the world (Adam s and McShane 1992; Dublin 1994; NaughtonTreves et al. 1999). It is characterized by the most extreme attitudes (Dublin 1994, p. 5). To some, it is the symbol of wisdom, strength, and good luck. For others who see the elephant only in zoos, in books, and on television, it is a gentle giant, intelligent and nurturing, maintaining close family bonds. For people who live alongside elephants and those who work to manage and conserve them, the story is more complex. One of the greatest challenges in conservation today is how to balance local concerns of security and development with international interests in conservation of threatened species (Treves et al. 2006). After the ban on ivory was implemented in 1990 and elephant populations a cross Africa began to recover, the incidence of human elephant conflict began to rise. With this change in circumstances, wildlife managers and conservationists started looking for new ways to manage and conserve elephant populations. Several approaches ha ve emerged to address this and other modern conservation challenges. These methods include community based conservation, integrated conservation and development programs, and collaborative management (Mburu et al. 2003; Wells et al. 1992; Western and Wrigh t 1994). Such programs are part of an effort to move away from the fences andfines approach, or fortress conservation, by involving local people in conservation (Adams and Hulme 2001; Bauer 2003; Gibson and Marks 1995; Holmes 1 This chapter is reprinted by permission of the publisher The University of Chicago Press. The origin al citation is: Browne Nuez, C. In press. The Maasai elephant relationship. In The Amboseli Elephants eds. C. Moss, H. Croze, and P. Lee. Chicago: The University of Chicago Press.

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83 2003; Songorwa 1999), with the goal of affecting the conservation attitudes and behaviors of local people (Abbot et al. 2001; Infield and Namara 2001). Amboseli is the setting for some of the earliest community conservation programs in Africa. As the Amboseli landscape has evolved over time, so has the relationship between elephants and the Maasai. Understanding the dynamics of their interactions is critical to conserving the Amboseli elephants and ensuring the well being of the human population with whom they coexist. This chapter considers the Maasai elephant relationship by examining the attitudes and behaviors of the Maasai toward elephants over time by reviewing historical accounts of early European travelers through Maasailand, discussing the results of r ecent attitudinal research in the Amboseli ecosystem, and evaluating the notion of the Maasai as conservationists and considering the importance of culture, livelihood activities, conservation interventions, and landuse change in determining the future of the Maasai elephant relationship in Amboseli. Attitudes, Behavior, and Wildlife Conservation T here have been a number of attitudinal studies done in Africa regarding wildlife conservation (Akama et al. 1995; Ali 2006; DeBoer and Baquete 1998; Gillingham and Lee 1999; Hill 1998; Infield 1988; Kangwana 1993; Kideghesho et al. 2007; Kioko 2004; Lindsey et al. 2005; Mordi 1987; Newmark et al. 1993; Omondi 1994; Parry and Campbell 1992; Pennington 1981; Sitati 2003). Four studies ( Browne Nuez 2010; Kangwana 1 993; Kioko 2004; Sitati 2003) specifically investigated attitudes toward elephants in Maasailand. Two of these studies were conducted around the Amboseli National Park (results discussed later). Many of these studies found that people hold positive attitudes toward wildlife and the concept of conservation but are more negative toward wildlife authorities and conservation policy (Gillingham and Lee 1999; Infield 1988; Kangwana 1993; Newmark et al. 1993; Parry and

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84 Campbell 1992). Where attitudes are found to be negative, it is often due to the costs local people incur as a result of conservation policy or wildlife damage such as loss of land or other constraints on livelihood activity (Anthony 2007; De Boer and Baquete 1998; Gadd 2005; Gillingham and Lee 1999; Kideghesho et al. 2007; Newmark et al. 1993; Parry and Campbell 1992) and loss of crops and livestock (De Boer and Baquete 1998; Infield 1988; Marquardt et al. 1994; Mugisha 2002; NaughtonTreves 1998; Newmark et al. 1993). Methods suggested for improving attitudes toward wildlife include education and outreach, increasing benefits to local people, and involving local communities in conservation (Hulme and Murphr ee 2001; Parry and Campbell 1992). Positive attitudes have been found in communities that recognize benefits related to wildlife such as having a household member employed in a wildlife re lated job (Anthony 2007; Infield 1988; Lewis et al. 1990), having access to game meat (Infield 1988 ; Kideghesho et al. 2007), and generation of foreign ex change from tourism (Gadd 2005; Newmark et al. 1993; Pennington 1983; Weber 1987), among others (Abbot et al. 2001; Bauer 2003). Programs that are successful in providing wildlife related benefits to local communities not only highlight the importance of providing benefits that are valued by the communities but also demonstrate a clear link between the benefits and the wildlife resources (Gadd 2005). Although there has been some success, a consistent link has not been demonstrated between improved or posit ive attitudes and conservation interventions (Kideghesho et al. 2007; Parry and Campbell 1992; Wells et al. 1992). Some reasons for the lack of success include the following: costs ex ceed benefits (Emerton 1998, Hulme and Infield 2001), broken promises (Ka ngwana and Browne Nuez, in press ), lack of awareness of s ource of benefits (Archabald and NaughtonTreves 2001; Kangwana 1993), unr ealized expectations (Gadd 2005; Songorwa

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85 1999), limited community involvement (Parry and Campbell 1992; Songorwa 1999), lac k of soci oeconomic information (Wells et al. 1992), and lack of understanding of the link between conservat ion and development (Barrett and Arcese 1995; Newmark and Hough 2000; Songorwa et al. 2000; Wells et al. 1992). The limited success of conservation may be attributed in part to a lack of understanding of the local context of conservation (e.g., the way local people value natural resources). Social science offers the tools for understanding these issues. Prior to developing new programs or modifying ex isting programs, there needs to be an understanding of the communitys history and current dynamics, particularly in relation to the authority structures which influence peoples behavior and the patterns of resource use which form the basis for both conf licts and opportunities in wildlife management (Kiss 1990, p. 25). The knowledge and experience derived from research and conservation programs in Amboseli can aid in the development of new conservation and development initiatives as we adapt our methods in this ever changing environment. The E lephant in T raditional Maasai C ulture The elephant appears in many Maasai stories and proverbs. Some stories demonstrate the cultural value of the elephant. Hollis (2003) retells the story of the elephants role in aiding the Maasai in acqui ring their highly valued cattle, where at the beginning of the Earth, the elephant, along with a member of the Dorobo tribe and a snake, was one of three things Enkai (God) found upon the land when he came to prepare the world. In this story, the Dorobo kills the snake for breathing on him and the elephant for muddying a waterhole that was to be used by his cow. The elephants baby leaves the Dorobo for another land where he finds a Maasai. The young elephant ta kes the Maasai to the home of the Dorobo. The Maasai overhears a conversation between

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86 Enkai and the Dorobo. The next day the Maasai goes to where the Dorobo had been instructed to go and, acting as the Dorobo, is given a herd of cattle. Other stories are n ot as exalting and often involve the elephant being deceived by the clever hare and other small, less powerful animals (Greaves 1996; Hollis 1905; Kipury 1983). Such stories, while portraying the elephant as an easy mark, also portray it as a creature who breeds no malice, but his mere size and little brain is a cause for constant ridicule (Kipury 1983, p. 24). The Maasai and the related Samburu people have a number of traditional beliefs and practices associated with elephants. Members of both groups have reported customs such as placing green branches or grass atop the remains of or in the orifices of the skull of a dead elephant ( pers. observ., Kangwana 1993; Ki oko 2004; Kuriyan 2002). The Maasai have explained this practice as a way of appeasing the spirit of the elephant the only other creature with a soul like a human (C. Moss, personal communication). Elephants are seen as having physical characteristics similar to those of humans, such as two breasts ( pers. observ., Kioko 2004; Kuriyan 2002), a t runk that operates like an arm, and comparable skin (Kuriyan 2002). Maasai believe it is good luck to find an elephant placenta ( pers. observ., Chadwick 1992; Kangwan a 1993; Kioko 2004; Sitati 2003). It is thought that if one finds an elephants afterbirth and then constructs a temporary boma and sleeps there overnight with his animals, he will becom e rich in cattle (Chadwick 1992; George Lupempe, personal communication; Sitati 2003). Early Maasai used products made of ivory such as tobacco and snuff conta iners, fly whisk handles, upper arm bands, rungus (clubs), earlobe stretchers, and clappers hung around the necks of domestic animals (Bernsten 1976; Blackburn 1982; Hollis 1905; Kasfir 1992; Merker 1910; Mol 1981; Thomson [1885] 2006). These items no longer seem to be in frequent

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87 use today ( pers. observ., Kasfir 1992). Plastic containers have replaced snuff containers and earlobe stretchers, although one can occasionally observe a Maasai man wearing an ivory ring or see a pendant hanging from the neck a do mestic animal (personal observation; George Lupempe, personal communication). Elephant products have reportedly been used by the Maasai for medicinal purposes (P. E. Glover in Mol 1981). When discussing the use of elephant products, two questions arise: (1) how did the Maasai acquire these items and (2) what does their use indicate, if anything, about Maasai attitudes toward elephants? With pastoralism being the primary mode of subsistence, the Maasai have rarely hunted wild animals, viewing them as their s econd cattle upon which they could rely in times of severe famine (Baumann 1894; Berger 1996; Deihl 1985; Homewood and Rodgers 1991; Smith 1907; Waller 1976; Western 1997). It is even claimed that they have contempt for those, such as the Dorobo, who regul arly hunt and consume wildlife (Kipur y 1983; Saitoti and Beckwith 1993; Thomson [1885] 2006). In Laikipia, Kenya, some Maasai report having cultural taboos against consuming the meat of elephants because of their similarities to humans (Gadd 2005), but the re are historical accounts of Maasai hunting wildlife, including elephants (Berger 1993; Hollis 1905; Huntingford 1953). For instance, in the early 20th century, Maasai boys reportedly killed elephants and would take only the tusks to exchange for cattle ( Hollis 1905). An exception to the rarity of hunting is the ilm ur ran, or Maasai warrior, tradition of hunting lions ( olamayio) to demonstrat e bravery and courage (Mol 1981; Saitoti and Beckwith 1993). The warriors also hunt elephants to retaliate against them when they injure or kill livestock or people. Elephants and other wildlife have also been targe ts of Maasai warriors (Mol 1981; Moss 1988; Simon 1963). The purposes of these hunts have been the same as for the lion hunt. Additionally, in more recent decades, spearing has been political in nature, with wildlife

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88 being targeted in order to demonstrate unhappiness with government policy (Lindsay 1987; Peluso 1993; Western 1982a,b ). Other Maasai methods for obtaining ivory included finding it in the bush (Mol 1981) and acquiring it from their hunting neighbors, including the Waboni of the coast (Beachey 1967) and the various groups that fall under the name Dorobo (Blackburn 1982; Huntingford 1953; Mol 1981). Ivory acquired from the Dorobo and Waboni enable d the Maasai to participate in the lucrative ivory trade during the 19th century (Beachey 1967; Bernsten 1976; Waller 1976). Waller (1976, 533) reports that after a period (188494) referred to as The Disaster when two disease epidemics severely depleted livestock herds, the Maasai of Loitokitok were kept alive by hunting, cultivating, and by selling ivory and rhino horn to traders. More recent discoveries of Maasai artifacts made of ivory and other materials are the source of debate. In his book, The Ar t of the Maasai, Turle (1992) claims that numerous ivory pieces are Maasai cultural artifacts. These include ivory pipes used by laibons (diviners or medicine men) to administer medicine, elephant vertebrae used for grinding bowls, elephant pelvic bones us ed for stools, and ivory rungus Critics of Turles collection point to the numerous inaccuracies written about Maasai culture; they point out that anthropologists, who have spent years studying Maasai culture, have never come across such artifacts, and th ey ask why Turle never describes seeing the artifacts in use in his encounters with Maasai (Pido 1994). Turle (1992, 131) himself states that these artifacts seem to have sprung into view from a past without clues. While experts debate these more recent discoveries (Bl ackburn 1996; Kasfir 1995; Kurtis 1994; Kratz 1996; Pido 1994, 1995; Schildkrout 1996), there is no doubt that elephant products were used by the Maasai in the past and to a lesser degree today. For whatever reason, ivory has been replaced by other materials.

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89 Sitati (2003) reports other traditional values and uses of elephants and elephant products in the Trans Mara District of Kenya, which include the following: Elephants locate salt licks and water for livestock use. Elephants thin fores ts. Elephant bones are used to treat trypanosomiasis. Elephant fat is used to treat skin disease and is mixed with herbs to increase growth in babies. Elephant dung is burned in order to smoke out bees for honey harvesting and to treat measles. Elephant ta ils have been used to make bangles. Ivory is a source of money. Elephants deter cattle rustlers. Elephant trails are used for ceremonies, as they are believed to be without obstacles. It is evident that wildlife, including the elephant, is a valued element of traditional Maasai culture. Values in nature have been categorized to include cultural, utilitarian, economic, aesthetic, and religious values among others (Kellert 1976, 1996; Rolston 1988). For the Maasai, these values vary by species. The influence of the ever present religiosity of the Maasai ( pers. observ.; Berger 1993; Goldman 2003; Mol 1981; Saitoti and Beckwith 1993 ) is illustrated by the terms used to describe some wildlife. For example, small plains animals are referred to as inkineji e En kai the goats of God, or inkishu e Enk ai the cattle of God (Mol 1981). Furthermore, there is a degree of fatalism present in Maasai culture. It is not uncommon for Maasai to state that because God put them on earth together with wildlife, they must live toge ther (pers. observ.). The oral literature and extensive use of elephant products provide examples of cultural and utilitarian values. Additionally, some cases of the spearing of elephants by the ilm ur ran demonstrate a value similar to what Rolston (1988) t ermed a character building value.

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90 The Maasai, P astoralism, and Wildlife C onservation Being Maasai Over time, there have been various characterizations of the Maasai, their culture, and their impact on wildlife. From guardians of wildlife to irresponsible, overgrazing herders, these descriptions contain various degrees of accuracy and have resulted in s everal stereotypes. Some of these false perceptions are the bases of the modern and often romanticized image of the Maasai (Ole Ndaskoi 2006). While a complete discussion of the Maasai identity is not within the scope of this chapter (see Spear and Waller 1993 for a more exhaustive treatment), a brief overview provides a foundation for understanding the relationship between Maasai and elephants. Defining what it is to be Maasai is complex, as there are a series of political, cultural, and ecological divis ions and subdivisions of the Maasai (Talbot 1972, p. 702). Maasai interactions with their environment have been dynamic over space and time, depending on environmental and social c onditions (see also Kangwana and Browne Nuez, in press ). For instance, the Maasai of Ngorongoro have dealt with different environmental and political forces from the Maasai of Amboseli. Also, in times of disease and famine, Maasai have turned to other ethnic groups and adopted other means of subsistence; when they have become im poverished, they have sought employment in order to purchase livestock and return to pastoralism; when political pressure has required it, they have made superficial or temporary changes with t heir culture intact (Knowles and Collett 1989). Europeans first became aware of the Maasai through the writings of Krapf (1854, 1860), who obtained his information from caravan leaders and a Wakwavi slave in Mombasa (Knowles and Collette 1989). He described the Maasai as hostile savages who were feared by their neighbors; subsisted strictly on milk, butter, honey, and meat (including hunted wildlife); and

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91 detested agricultural foods (Collett 1987). Others described the Maasai as warlike (Lugard 1893) and as pure pastoralists (Hinde and Hinde 1901; Hollis 1905). Thoms on (1885), who later traveled though Maasailand, provided a different, somewhat more accurate portrait. He noted that the Maasai were not hunters, and wildlife displayed little fear toward humans. Additionally, he reported that women, children, and married men consumed agricultural products that were acquired through trade from neighboring agriculturalists. Thomsons portrayal was not the one adopted by the British colonial administration, who concurred with Lugard and Krapf in viewing the Maasai as hostil e and purely pas toral (Collett 1987; Knowles and Collett 1989). Such inaccurate accounts along with the belief that the Maasai failed to use their land properly (Eliot 1905; Lugard 1893) led to a history of policies resulting in land alienation and the bre akdown of traditional Maasai culture ( Browne Nuez 2010; Kangwana and Browne Nuez, in press). Defining a Maasai identity is also dependent on how one views ethnicity. Galaty (1993, p. 174) states that the term Maasai marks two different cultural realities, the first being the gamut of Maaspeaking people and groups in East Africa, the second [being] the set of central and primarily pastoral Rift Valley Maa speaking sections for which the term marks their distinctiveness. This second reality the Maasai as people of cattle is the most widely adopted, but as Galaty (1993, p. 179) states . to speak Maa is increasingly equated with being Maasai, pastoral or not. Therefore, as one considers the values, attitudes, and behaviors of the Maasai, it is important to keep the complexity and fluid boundaries of the Maasai ethnic identity in mind. Maasai Pastoralism Pastoralists have received much of the blame for desertification, with critics pointing to the theory of the tragedy of the commons (Hardin 1968), citing overstocking and overgrazing

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92 as the primary if not the only causes of desertification (Lamprey 1983). Today, most who have studied and worked with the Maasai see this as a faulty contention, given that the Maasai have always had a system in place to control access to resources communally. Moreover, research shows that the ecological dynamics of savanna ecosystems have been misunderstood, and concepts such as equilibrium and carrying capacity used to describe temperate zones are not able to ex plain the functioning of savanna ecosystems (Behnke 1994; Homewood and Rodgers 1991; Little 1996). The complex relationships between humans and African savannas are better understood using theoretical concepts such as disequilibrium and disturbance, given that these ecosystems are inherently unstable (Little 1996). Although some studies have concluded that there is competition between wild ungulates, such as wildebeests and zebras, and domestic animals (Fritz et al. 1996; Lamprey and Reid 2004; Prins 1992; Voeten and Prins 1999; Young et al. 2005), the idea of the compatibility of pastoralism and wildlife is inc reasingly supported (Deihl 1895; Goldman 2003; Little 1996; Nelson 2000; Reid et al. 2003). There is substantial evidence that light to moderate liv estock grazing increases rangeland productivity (Mearns 1997) and that the customary pastoral approach to resource management constitutes an efficacious adaptation to ecological stress (Behnke 1994, p. 21). Other evidence of compatibility is offered by H omewood and Rodgers (1991), who found that pastoralist land use in the Ngorongoro Conservation Area was not a threat to wildlife populations or the environment. In fact, research has demonstrated that removal or decline of pastoralist populations can have negative eff ects on vegetation (Conant 1982; Lamprey and Waller 1990; Mearns 1997). Speaking at the 2003 World Parks Congress, wildlife veterinarian Richard Kock stated, Traditional pastoralism has very positive benefits to the environment and wildlife. You only

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93 have to look at distributions of wildlife to see that they are often associated with pastoral systems. So, should we be doing wildlife? Should we be doing livestock? Should we be doing both? I think its clear [researchers] have done good work on this over the years and have shown how the benefits economically, environmentally of mixed systems are there. Mearns (1997) qualifies this position stating, Under the right conditions, production systems relying on mobile livestock represent the most sus tainable way to utilize arid rangelands and ought to be supported and enhanced through policy intervention designed to give greater decision making power to local producer groups. Today, the nature of pastoralism is changing. Pastoralists of East Africa are diversifying their livelihood activities, depending less on their livestoc k than in the past (McCabe 2003; McCabe et al. 1992). This change is a result of several factors, including loss of grazing land resulting from conservation policy, subdivision of the group ranches, and immigration of people from farmi ng groups (Campbell et al. 2000; Kangwana and Browne Nuez, in press ). The ideal model of pastoralism is disappearing, if it ever existed at all (Hogg 1987, p. 293). As the Maasai of Amboseli div ersify their livelihood practices grow crops, rent land to cultivators who are members of other ethnic groups, develop small enterprises, and so onthe challenge for conservationists is to work with the Maasai to develop conservation strategies that will e nable wildlife to continue to utilize the land outside the park. An important question is whether there exists a conservation ethic or attitude among the Maasai that can serve as the foundation of local conservation efforts. The Maasai as Conservationists Many have described the relationship between the Maasai, wildlife, and the environment they share as one of peaceful or harmonious coexistence (Amin et al. 1987; Berger 1993, 1996; Homewood and Rodgers 1991; IUCN 1987; Kinyua et al. 2000; K W S 1990; Lovatt Smith 1986;

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94 Ole Dapash 2002; Orindi and Huggins 2005; Parkipuny 1997; Saitoti and Beckwith 1993). Further, the Maasai have been described as the custodians of Kenyas wildlife (Asiema and Situma 1994), the greatest preservationists in Africa (Simon 1963), historic vanguards of conservation (Parkipuny 1997), par excellence conservationists (Richard Leakey cited in Horgan 1989), and more valuable to the cause of conservation than a whole army of paid game scouts (Fosbrooke 1972). The notion of harm onious coexistence is not accepted by all. Prins (1992) questions the harmony theory, pointing out that many pastoralists across Africa, including the Maasai, have at some time hunted and that livestock competes with wildlife. Some simply view coexistence as a romantic notion that was made possible by the fact that the pastoralists lacked the resources for change and had low population levels and low production demand that allowed them simply to ignore wildlife (Adams and McShane 1992; Norton Griffiths 1998). Richard Leakey states, I dont know that people anywhere have ever lived in harmony with wild animals, despite our wishful belief that once this was so, but the Maasai came as close as anyone ever has (Leakey and Morell 2001, p. 146). Early accounts of harmonious coexistence might be explained, in part, by a series of disasters that occurred in East Africa in the late 19th century, when disease wiped out most of the regions cattle population and, together with colonial warfare and famine, drastically reduced pastoral populations (Enghoff 1990; Talbot 1972). This snapshot in time showed the land filled with wildlife and a sparse human population. If we reject the notion of harmonious coexistence, we are still left to consider the Maasai as conservation ists. Likely the most frequently offered evidence of Maasai conservation is the existence of large numbers of wildlife on their land (Asiema and Situma 1994; Bulte et al. 2006; Mol 1981; Organ and Fosbrooke 1963; Parkipuny 1989; Simon 1963). More than half of Kenya

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95 and Tanzanias wildlife is found in Maasailand (Ole Parkipuny and Berger 1993). Explanations of this phenomenon include the compatibility of pastoralism and wildlife conservation, Maasai attitudes toward wildlife that permitted coexistence, low p opulation densities that allowed enough space for coexistence (Mol 1981), and discouragement by the Maasai of the intrusion of others (Fosbrooke 1972), such as poachers (Beachey 1967; Homewood and Rodgers 1991; Western 1997) and agriculturalists (Organ and Fosbrooke 1963). A useful approach for considering conservation among the Maasai and other indigenous societies is to ask whether there is intention to conserve. Hunn (1982) distinguishes between deliberate or true conservation and unintentional or epiphenomenal conservation. Deliberate conservation occurs when people pay an enduring cost in the present so that some benefit will be realized in the future (Alvard 1993, p. 358). Conversely, epiphenomenal conservation can be an artifact of low human popula tion densities, high mobility, limited technology, abundance of or low demand for a resource, or security issues (Ruttan and Borgerhoff Mulder 1999; Smith and Wishnie 2000). Although it is clear that Maasailand is home to abundant and diverse wildlife, many would ague that this is indeed an artifact of traditional Maasai pastoralism and low population densities. While the livelihood strategies and cultural institutions of the Maasai aim to manage grasslands, when possible, there is no evidence that conse rvation of wildlife is a principal goal of the Maasai. Mol (1981, p. 27) supports the idea of the Maasai as preservationist rather by accident than by purpose. He states, From all this we can conclude that the Maasai did not interfere with the pos ition of the game on their land. On the other hand it is also clear that the Maasai did not take any positive steps to maintain and preserve the game. The game happened to

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96 exist peacefully alongside the Maasai before [human] population pressure began to interfere with the statu s of the game (Mol 1981, p. 26). From Early Attitudes toward Elephants to Modern Attitudes and Interactions Early A ttitudes The abundant wildlife found in Maasailand has also been offered as evidence of positive or at least to lerant attitudes toward wildlife (Mol 1981; Ole Dapash 2002; Parkipuny 1997; Simon 1963). Simon (1963, p. 93) states that it is entirely due to [the Maasai] that substantial herds of plains game still exist in southern Kenya and northern Tanganyika. We ow e an immense debt of gratitude to the Masai for being the only East African tribe to adopt an indulgent attitude towards wild animals. Many authors have anecdotally described a traditionally tolerant attitude (Campbell et al. 2000; Capone 1972; Darling 1960; Fosbrooke 1972; Kipury 1983; Ndaskoi 2006; Western 1997). One proposed explanation for Maasai tolerance of wildlife is their reliance on wildlife as their second cattle (Western 1994). Simon (1963) and Myers (1973) suggest indifference among the Maasai toward wildlife This descriptor corresponds with the view of the Maasai as accidental conservationists in that they did nothing to threaten wildlife, nor did they do anything to conserve it. An example of this laissez faire attitude is that the Maasai took no action when soldi ers in World War I killed large numbers of wildlife along the Kenya Tanganyika border (Lovatt Smith 1997). It could be that tolerance or apparent indifference is based on the fatalistic orientation of many Maasai. Not everyone agre es that the Maasai only tolerated or were simply uninterested in wildlife. Some who have studied and worked with the Maasai have argued that they have demonstrated positive feelings toward wildlife and recogn ize its intrinsic value (A WF 1999; Homewood and Rodgers 1991; Kipury 1983). When discussing the possible exclusion of the Maasai from the Ngorongoro Conservation Area, Homewood and Rodgers (1991, p. 248) state,

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97 The Maasai respect for wildlife and the strong aesthetic as well as practical sense of their environment are such a natural basis for local conservation support that it is counterproductive as well as hypocritical and unethical to exclude them. Further, some argue that the Maasai love of wildlife is evidenced in their childrens songs and chants and that because of this positive feeling, they dislike other people who kill wildlife and destroy what should be left to exist for its own aesthetic value (Kipury 1983, p. 4 ). Again, these claims could be supported, in part, by the earlier discussion of values of wildlife. A concern of conservationists working in Maasailand today is how much of the positive attitude toward, or at least tolerance of, wildlife remains. In the latter part of the 20th century, several authors noted the changing attitudes of the Maasai (Darling 1960 ; Mol 1981; Myers 1973; Simon 1963; Western 1994). Simon (1963) asserts that two beliefs held by the Maasai at the time were the basis for a change from tolerance to veiled hostility: (1) that wild animals consume resources tha t should be for cattle and (2) that Europeans were casting envious eyes in the direction of lands that were rich with wildlife. Others have attributed a change in attitudes to increased competition between the Maasai and wildlife brought about by rising human and live stock populations (Darling 1960; Mol 1981; Myers 1973). Western (1994) describes three phases of the Development Plans for Amboseli that influenced attitudes from the late 1970s through the early 1990s. Phase 1, the implementation phase, whi ch included the water pipeline and imposition of a wildlife utilization fee, had early success, including the generation of funding for the construction of the first school in the area and a decline in spearing and poaching of wildlife. After 1981, the pla n began to fail. The water pipeline stopped operating, the wildlife utilization fee was no longer being paid, relations between the Maasai and wildlife officials deteriorated, and spearing of wildlife, especially rhino,

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98 increased. The next phase saw the Ma asai of Olgulului take an active role in a number of wildlife related initiatives, such as assuming responsibility for the public campsite, constructing a fence at Namelok, and negotiating a tourist concession (Western 1994). There was a renewed tolerance for wildlife, and wildlife numbers, especially elephants, increased in Amboseli when poaching was rampant in other parts of the country. The third phase came with the creation of the Kenya Wildlife Service (KWS) in 1990. Western (1994) cites some early su ccesses of this phase that include the building of new schools and hiring of Maasai game scouts (paid for with monies from the revenue sharing program), Olgululuis resistance to subdivision in order to protect wildlife corridors, plans for electric fences to protect crops, improved relations between the KWS and the Maasai, low poaching levels, and fairly positive attitudes toward wildlife (Western 1994). This last outcome is substantiated by Kangwanas 1991 attitude survey. Measures of A ttitudes As part of her study of elephant Maasai interactions around Amboseli National Park, Kangwana (1993) conducted an exploratory survey of Maasai attitudes toward wildlife and the park. Most respondents were not in favor of removing wildlife from the area, indicating that the overall attitude towards wildlife is, if not p ositive, then at least tolerant (p. 95). Surprisingly, agriculturalists were found to be more positive toward wildlife and the park than pastoralists. One possible explanation offered by Kangwana (1993) is that agriculturalists were less marginalized, having diversified livelihood activities (i.e., crops and livestock) and more access to water, as most lived in the better watered Kimana Group Ranch. These individuals also tended to be more educated an d aware of the benefits of conservation. Elders were found to be more positive than ilm ur ran and women, with women being the most negative. Elders and

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99 agriculturalists were also more likely to be aware of benefits brought by wildlife, although respondents in general were more likely to believe that wildlife benefits the country of Kenya rather than the Maasai as a group or themselves as individuals. Additionally, some respondents who were receiving wildlife related benefits did not recognize them as such, highlighting the importance of increasing awareness of the link between wildlife and benefits through education. Overall attitudes toward elephants wer e found to be positive, with 58% of the people categorized as pastoralists and 47% categorized as agricult uralists saying that elephants should not be removed from the area. Those with a positive attitude believed that elephants were beneficial to the area, were gentle, and had always been there. Respondents with a negative attitude believed they should be rem oved because they were dangerous and destroyed crops. Elders had more positive attitudes than others who were surveyed. Kangwana posited that the elders were more aware of the benefits (e.g., opening up grazing land for cattle) of elephants than were young er individuals. This view is supported by the Maasai saying, Cows grow trees, elephants grow grasslands (Western 1997). Change, Conflict, and I ntervention Many changes have occurred in the Greater Amboseli Ecosystem since Kangwanas study. The most crit ical is that of land use change. In addition to the influence of colonialism, conservation, and agriculture, the human population is continuing to grow. With rapid population grow th resulting from immigration (Table 2 1) the rain fed areas have become set tled, which has reduced the area available for dry season grazing and access to water for livestock and wildlife (Campbell et al. 2000). Intensifying the land use problem is the more recent subdivision of the group ranches. As of 2006, of the 52 group ranc hes in the Kajiado District, 32 had completed subdivision and 15 were in the process and subdivision, leaving only 5 that had not

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100 sta rted the process (BurnSilver and Mwangi 2007). The two group ranches that immediately border Amboseli, Olgulului/Lolarashi, and Kimana, which were surveyed by Kangwana in 1991 and Browne Nuez in 2005, were among the last to begin subdivision. Kimana completed the process in 2005, and in 2007, the rainfed and irrigated agricultural areas of Olgulului were being subdivided. Ch anges in land use, along with the growing human and elephant populations, have significant implications for Amboselis elephants. Conversion from pastoralism to agriculture is a critical threat to elephants as it contributes to habitat loss and decreased t olerance (Gadd 2005). Human elephant conflict is a growing problemperceptual, political, and actual in Keny a and across Africa (Ngure 1992; Waithaka 1993; Hoare 1995; Tchamba 1995; Thouless and Sakwa 1995; Barnes 1996; Lee and Graham 2006) and threatens t he conservation of elephants. Most incidents of conflict involve crop raiding or competition for water and grazing resources. Deaths and injury to both humans and elephants occur as a result of the negative interaction. Mortality among Amboselis elephants caused by local people may be the result of retaliation for losses incurred directly from conflict but can also be a demonstration of unhappiness with a social or political situation. Historically, levels of spearing were associated with the circumstances of the ilmur ran age set. For instance, in 1984, when there was an initiation of new ilmur ran, there was an increase in the level of spearing (Lindsay 1987; Kangwana 1993). The opposite occurred in the six year period prior to the 1984 initiation. In 1978, ilmur ran were initiated into elderhood, and there was not another ilmur ran initiation until 1984. Western (1982) attributes this low spearing level to positive attitudes resulting from the receipt of benefits allocated to the Maasai by the development pla ns for Amboseli

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101 Conflict with wildlife can cause negative attitudes toward wildlife and reduce support for co nservation (Newmark et al. 1993; De Boer and Baquete 1998; Naughton Treves 2001) and can affect the long term success of conservation programs (We bber et al. 2007). Although the elephant is the species most often reported as being a problem by l ocal people (Gadd 2005; Parry and Campbell 1992), it is not always the proven cause of most damage. NaughtonTreves et al. (1999, p. 7) offer two case studie s that demonstrate that elephants create distinctive, highly localized crop damage patterns that are cataclysmic for the affected individual farmers, but insignificant to the regional farming economy. Although smaller animals tend to produce greater econ omic loss, they are better tolerate d than elephants (Gillingham and Lee 1999, 2003; Hoare 2000; NaughtonTreves et al. 1999; NaughtonTreves and Treves 2005). This attitude can be explained, at least in part, by the fact that elephants are a high profile s pecies, and they can be more dangerous to people than can other p est species (De Boer and Baquete 1998; NaughtonTreves et al. 1999; Sitati et al. 2003). In interviews conducted with Maasai around Amboseli in 2005, when asked which wild life species cause problems, 44% of individuals surveyed reported they had personally experienced problems with elephants and 21% said someone else in their boma had had a problem Later in the same interview, as survey questions became more focused on elephants, 65% of respondents stated that elephants had caused them problems. Part of the explanation for this increase is that some respondents consider other household members elephant problems to be their own problems. Another possible explanation is an awareness of t he value of the elephant to others (e.g., the Kenyan government, tourists, researchers, and conservation organizations). The elephant is the symbol of conservation found on uniforms and vehicles of government and nongovernmental organizations. Elephants re ceive a great deal of attention from these groups,

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102 and when one is killed, there is an instant reaction (killing other pest species does not elicit the same kind of reaction). Individuals suffering from wildlife damage, particularly from large species such as the elephant, are often hoping for compensation, which may lead to an increas e in damage reports (De Boer and Baquete 1998; Gesicho 1991; Mascarenhas 1971 [cited in NaughtonTreves et al. 1999]). While costs to agriculturalists are the chief complaint in many parts of the elephants range, the leading costs reported by people living around Amboseli National Park in 2005 were human and livestock injuries and death. Additionally, 42% of respondents who believed that local people incur costs related to pr oblems with elephants complaine d about damage to trees. Only 8% cited crop damage as a cost. Other costs included competition for water and grazing and damage to property such as water pipelines, fences, and houses. In addition to the direct costs of livin g alongside elephants, there are opportunity costs. These costs are difficult to quantify but may outweigh the direct costs of agricultural damage and be a major component of conflict as it is perceived by local people (Hoare 2000 p. 35 citing Dublin et al. 1997). Survey respondents reported such costs, including the inability to walk freely in the group ranches, interference with children attending school, and sleepless night s (guarding crops or property) There have been numerous interventions initiated around Amboseli to improve attitudes toward elephants and mitigate conflict. These have been implemented by several organizations, including the KWS, the Amboseli Elephant Research Project (AERP), and the African Wildlife Foundation (AWF). While these int erventions vary in their approaches and objectives, all have the long term goal of ensuring continued tolerance of elephants outside of the relatively small protected area of the park.

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103 In 1998, after a period of intensified conflict and long negotiations among community representatives and members of the KWS and the AERP, the elephant research project implemented a consolation scheme that pays for livestock killed by elephants outside the park. Twenty four percent of local people, mostly men, who were sur veyed in 2005, were aware that the AERP has a consolation progra m for livestock losses, with 73% of these individuals evaluating the AERP as being slightly good to very good. In order to address humanelephant conflict in the nearby agricultural areas, an electric fencing project was started by the KWS in two areas in 1996. The two solar powered fences, at Kimana and Namelok, were financed by the European Union and completed in 2000. The fences have had limited efficacy because they are often in disrepair due to vandalism and elephant damage. They have not solved the problem of humanwildlife conflict, as conflict has shifted to the LoitokitokOlchorro area and made wildlife more vulnerable to poaching in nearby Tanzania (Ntiati 2002). Additionally, there i s confusion among community members as to who owns the fence and who is responsible for its ma intenance. Despite these issues, most of the 2005 survey respondents (99% ) living within the fences be lieved the fences do a good job. Another significant change around Amboseli is the growing number of cultural bomas established in the Olgulului Group Ranch along the southern park boundary. These business entities have been established by Maasai who are interested in entering the cash economy. Here, tourists can tour a traditional Maasai homestead, buy beadwork from the women (and other handicrafts brought in by outside sellers), and observe demonstrations, including dancing, singing, the building of fires, and home maintenance. While t here are perceived and real benefits for the Maasai who participate, such as the provision of an alternative economic activity, these bomas are fraught with problems. A major issue that hinders their economic success is the

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104 problem of the tour drivers who pocket most of the money charged to the tourists for entrance into the bomas ( pers. observ., Onetu 1998; Ritsma and Ongaro 2002). Cultural boma members believe there is nothing that can be done about this situation, concluding that if they protest, drivers will take their groups to other bomas so a little money is better than none at all. A further criticism of the cultural bomas is their contribution to the erosion of Maasai culture (Onetu 1998; Ritsma and Ongaro 2002). While this claim is also directed at tourism in general, the cultural bomas are specifically blamed for splitting families, as women leave their homes to work in the bomas Related to this problem is the concern among community members that cultural bomas provide a setting for prostitutiona new occurrence in Maasai culture and a rise in the incidence of sexually transmitted diseases (Onetu 1998). Additionally, cultural bomas act as collection points for idle sitters who in turn participate in petty crimes and other unapproved social beha viors (Onetu 1998, p. 47). From a health and safety perspective, the cultural bomas have led to an increase in disease, as large numbers of people concent rate in small areas (Akama 2002; Onetu 1998). Finally, because they obstruct elephant corridors, the y actually increase, rather than d ecrease, conflict (Douglis 2001; Ritsma and Ongaro 2002). In 1999, the AWF proposed several activities aimed at ensuring that the Maasai areas surrounding Amboseli National Park are friendly to elephants (and other wil dlife) by reducing conflicts between humans and elephants (AWF 1999). Among these activities was an outreach program that would induce change favorable to wildlife conservation, including improving attitudes toward elephants through meetings, workshops, and educational tours. At the time of the 2005 survey, only 7 of 569 respondents identified the AWF as an organization that helps people who have problems with elephants, while 27 stated that the AWF helps elephants. When asked directly about the AWFs ac tivities in the area, many Maasai complained that they were

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105 unsure exactly what members of the organization do, only that they drive their cars around and hold meetings. Other activities and projects are in progress in the ecosystem that are designed to ensure that elephants and other wildlife are able to continue to share group ranch lands with the Maasai. Many of these involve providing alternative forms of income for local Maasai through employment in the conservation and tourism industries. For example the Selenkei Group Ranch has set aside an area for a private wildlife sanctuary and rents land to Porini Ecotourism for a luxury tented camp. In addition to rent, the community receives an entry fee for each visitor. The Kimana Group Ranch also has a wil dlife sanctuary and lodging, although local Maasai complain that not enough Maasai are employed in these establishments and that the jobs that are available are usually low level, degrading positions ( pers. observ.; Ole Dapas h 2002; Onetu 1998). This compl aint is a criticism of the positions held by most Kenyans working in the tourism industry (Sindinga 1994). Maasai are believed to be the least represented in the industry, even in the lowest level jobs (Akama 1999). Another serious problem is the equitable distribution of benefits from tourism generated revenues. Local authorities such as the county council often are the recipients of tourism money, with little going to the individual group ranch members. Resolutions to these issues are needed in order for tourism to be the viable alternative economic activity that government and conservation organizations promote. Current A ttitudes In the 2005 survey, several questions were asked concerning attitudes. First, respondents were asked to arrange cards with dr awings of wild animals into piles according to whether they liked or disliked the animals. Most respondents (57% ) placed the elephant card in the dislike pile, while 42% of respondents placed the elephant card in t he like pile (the remaining 1%

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106 were either neutral or said they liked all animals). When asked specifically if they liked seeing elephants in their group ranch, there was a 50/50 split. The most common reason for liking to see elephants in the group ranch is the belief that elephants at tract tourists and therefore generate revenue. This most likely explains why some who report not liking elephants say that they like to see them in their group ranch. The top reason for not wanting elephants in the group ranch is the danger they pose to pe ople. As in the survey conducted in 1991, where respondents were asked if elephants should be removed (Kangwana 1993), respondents in 2005 were asked about a hypothetical vote on whether to allow elephants to continue to enter their group ranch. A majorit y of pe ople (53% ) said they would vote to allow elephants to continue to be in the group ranch, the same percentage who were against removing elephants in 1991, while 46% said they would vote not to allow them access. In 1991, 45 % of respondents stated tha t elephants should be removed or confined to the park (Kangwana 1993). Again, the top reason for a positive response was tourism revenue, and the top reason for a negative response was the problems caused by elephants. Individuals with an awareness of org anizations that help people when they have a problem with elephants were more likely to say that they would vote to allow elephants in the group ranch. There was not a significant difference in voting intention between those who are primarily agricultural ists or pastoralists, between age groups, or between group ranches, but there was a significant difference between men and women, with more men being favorable to allowing elephants in the group ranches. As mentioned earlier, it is essential to understand the complexity of the attitude behavior relationship. Knowledge of attitudes alone is not sufficient for making policy decisions, as attitudes are not always straightforward. For example, 25 % of respondents who stated they do

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107 not like to see elephants in their group ranch stated they would vote to allow them in the group ranch. Of these individuals, 85% cited tourism revenue as their reason for toleration. Conversely, 18% of respondents who stated they do like elephants in their group ranch stated they would not vote to allow them in the group ranch. Seventy three percent of these respondents would vote against elephants because of the danger they pose. Here it is evident that attitude alone does not predict behavior or, in this case, behavioral intention. Other variables, such as economic benefits and fear of human elephant conflict, contribute to the level of tolerance of elephants. As the context of Maasai elephant interactions continues to evolve in the Greater Amboseli Ecosystem, it is important to und erstand to what degree Maasai behaviors toward elephants are a consequence of theoretically predicted attitudinal variables and the extent of influence of more dynamic situational variables such as socioeconomic status, prior experience, and land use. This understanding can contribute to the development of strategies to maintain the coexistence of the Maasai and elephants. The Future of the Maasai and Elephants of Amboseli Writing about the fate of Amboselis elephants, Chadwick (1992, p. 85) stated, The f uture of Amboselis giants clearly hinges upon the attitudes and land use practices of the people surrounding the reserve. The future of the people of Amboseli is also dependent upon the fate of the elephants. Maasai and wildlife have always competed to some degree but have also been very interdependent (Deihl 1985). Perhaps the best summary of the symbiotic relationship between the Maasai and wildlife was given over 30 years ago by a Maasai elder addressing a group of representatives from the World Bank (Western 1997): Yes, the Maasai do intend to accommodate wildlife as we always have. We protected wild animals from hunters, and wildlife protected us from drought, so we

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108 see it as fatal that we should not be allowed to move back into Amboseli. We wi ll leave the park to show our good intentions. We will allow wild animals onto our land, stop our young men from harassing them, and discourage poachers. But we expect that when it is seen that we cannot survive without Amboseli, we too shall be extended t he same treatment as the animals and that we will derive the benefits from the park. If such reciprocity is not shown, we cannot make assurances for the future of wildlife outside Amboseli National Park. And if wild animals are restricted to the park, thei r numbers will fall. If we are excluded, our livestock will die. Coexistence is the essence of survival for us both. This tone of cooperation and goodwill is still evident among the Maasai of Amboseli today. Although a large amount of modern tolerance of elephants appears to be explained by the perceived role of elephants in attracting tourists to the area (economic valu e), there is an element of cultural value present today. Traditional tales of the elephant are still told by the Amboseli Maasai. During survey follow up interviews conducted in May 2005, senior elders told many of the stories and proverbs of the elephant described earlier. The Maasai of Amboseli have indeed been people of cattle. Some have argued that Maasai throughout history have always made changes when necessary with the intention of returning to pastoralism (Knowles and Collett 1989). This notion is supported by research in northern Tanzania, where Maasai stated they began farming in order to save their livestock, that is, so that fewer animals would have to be sold in order to obtain food (McCabe 2003; OMalley 2000), but this view is not universa l among all Maasai. As one elder living near Tarangire National Park, Tanzania, stated, You cannot expect us to remain in history. Many projects come and recommend we remain pastoralists, but we have discovered the new foods. Now we want to grow crops and keep our cows (in Ka ngwana and Ole Mako 2001, p. 159). If modern Maasai do indeed diversify their livelihood activities with the intention of returning to transhumant pastoralism, would such a transition even be possible in the Greater Amboseli Ecosystem, given the many changes, namely subdivision, in group ranches? The answer is obviously no. While it is impossible to turn back the clock and return to the days when

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109 the Maasai, their livestock, and wildlife coexisted, unrestricted by boundaries created by outside policy, it may be feasible to nurture what remains in terms of traditional values and beliefs, develop sustainable opportunities for livelihood diversification, and encourage landuse planning that will minimize further loss of land available for wildlife and livestock. Understanding, respecting, and including local people in decision making are requirements for successful conservation. In Amboseli, where culture and land use have played significant roles in the conservation of diverse and abundant wildlife populations, this holds especially true. Aspects of Maasai communal social organization, their productions system, and their culture are valuable human resources that can be a foundation for a modern livelihood which integrates livestock keepin g with wildlife management and tourism (Berger 1996, 175). Although changes in land tenure communal property to private property have weakened these human resources, many conservationists recognize these resources and are working to include the local people as partners in conservation. Education can be an important part of conservation programs, although there are caveats as to how it should be done. The goal of environmental education programs is to influence behavior. M any variables influence behavio r; therefore, addressing these other variables must be a component of conservation programs. There is a large body of literature on the efficacy of environmental education that cannot be adequately reviewed here, but the following excerpt from Byers (1996, p86) provides insight into the best approach to environmental education: Modern environmental education recognizes that environmental behaviors are influenced not only by knowledge, but also by values, options, skills, and many other motivating factors (H ungerford and Volk 1990; Wood and Wood 1990). [It] attempts, therefore, to communicate more than just knowledge. It is a process that enables people to acquire knowledge, skills, and positive environmental experiences in order to analyze issues, assess benefits and risks, make informed decisions, and take responsible actions to achieve and sustain environmental quality (North American Association for Environmental Education 1993).[it] is

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110 concerned with communicating environmental values and ethics, not j ust knowledge and information (Caduto 1985). The results of the 2005 attitude survey show that while the cultural value of elephants does not appear to be highly prevalent among todays Amboseli Maasai, there is some degree of appreciation (e.g., beauty, r ole in ecosystem modification, etc.) and theistic value as demonstrated by the statement of an old woman in Kimana group ranch: God created elephants and they belong to this earth just like us An environmental education program in Amboseli area schools and the greater community based on traditional knowledge, beliefs, and values as well as on science would not only increase knowledge of and cultivate positive attitudes toward elephants but also perhaps aid in the preservation of the culture that has been credited with conserving the diverse wildlife of the Greater Amboseli Ecosystem. Economic O opportunities and O ther B enefits Improving knowledge and attitudes alone is not enough. As pastoralist families move closer to poverty, the need to diversify their livelihood activities increases. Many have turned their hopes to tourism as a source for alternative income. In the last few decades, there has been great emphasis on creating economic incentives for conservation in rural areas. This approach is based on a growing, but debated, effort to link conservation and development, but most of Africas protected areas do not and almost certainly will not contribute significantly to reducing poverty (Infield 2001, p. 800). While the Maasai recognize the benefits or potential benefits of tourism, many do not see it as benefiting them personally or their household. Although a relatively small perce ntage (16% ) mentioned selling handicrafts as the top personal benefit, many saw it as a benefit to the Maasai in general. A bout 10% mentioned school bursaries as a benefit to their household.

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111 These results have implications for elephants, given that the most cited reason for tolerating elephants is generation of tourism revenue. Amboseli is one of Kenyas top earners among pa rks in terms of annual gate fees (Bulte et al. 2006; Ole Dapash 2002), but benefits have been inconsistent, insufficient, and inequitably distributed (Mburu et al. 2003). These problems and others previously mentioned that are related to tourism in Ambosel i need to be rectified if tourism is to be promoted as a viable alternative livelihood activity. There are, however, examples of ecotourism enterprises in the Greater Amboseli Ecosystem that not only limit the impact on the natural environment but respect local culture and provide more equitable sharing of benefits. These include the Oldonyo Wuas Camp in the Mbirikani Group Ranch and the Porini Camp in the Eselenkei Group Ranch. Additionally, some organizations working in the ecosystem, such as the Amboseli Trust for Elephants and the Maasai Wilderness Conservation Trust, provide benefits to the local community such as scholarships for school age children and university students. There are also consolation and compensation schemes such as the one implemented by the trust and a scheme for lion damage operated by the Lion Guardians Project. Where benefits do exist, they should be promoted to increase awareness in the community. Land U se P lanning Recent research shows that pastoralists are unsure of the economic viability of individual land parcels after group ranch subdivision and are working to re aggregate their access to resources through pasture sharing and swapping mechanisms (BurnSilver and Mwangi 2007, p. 4). These arrangements are based on reciprocity or, less commonly, monetary exchange. These findings refute the inevitability suggested by earlier research that changes in land tenure and livelihood activities would weaken social and cultural relationships among pastoralists (Kituyi 1990; Ensminger and Rutten 1991 [cited in BurnSilver and Mwangi 2007]). It is still early in the process of transition from communal to individual ownership. Challenges to these new

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112 arrangements may become more evident. In the 2005 survey, 70% of respondents named pastoralis m and 25% named cultivation as their primary economic activity. When asked what they thought their primary livelihood activity would be in five years time, only 57% said pastoralism, while 35 % predicted they would primarily be farmers Conclusion The welf are of the Amboseli elephants has long been intertwined with the local human population. As noted here and by other authors (Campbell et al. 2003), the social context of Amboseli is changing. The human population is no longer a homogeneous society but rather comprises a diversified Maasai population with an ever increasing population of cultivators from other ethnic groups. As the human dimensions of conservation in the Greater Amboseli Ecosystem continue to evolve and become more complex, local, national, and international stakeholders need to collaborate in order to continually monitor and adapt conservation and development strategies to ensure the well being of both species.

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113 CHAPTER 5 PREDICTING INTENTION TO ALLOW ELEPHANTS ON PRIVATE LAND: AN INTEGRATED MODEL OF COGNITIVE AND CONTEXTUAL VARIABLES I ntroduction Conserving the African elephant ( Loxodonta africana) is a critical and complex task due to its role in the natural world, its conservation status, and its r elationship with people From an ecological perspective, the elephant is recognized as a keystone species (Balfour et al. 2007) and ecosystem engineer (Owen Smith 1988; Wright and Jones 2006; Pringle 2008), with complex effects on its habitat and species d iversity (Laws 1970; Balfour et al. 2007; Stephenson 2007). It modifies its environment through activities such as seed dispersal, tree felling, bark stripping, and the creation of waterholes. It is an intelligent, social animal that communicates with othe rs near and far, maintains strong family bonds throughout its life, and has life stages parallel to those of people Additionally, many elephant behaviors, such as those demonstrated in greeting ceremonies or when standing over and covering a dead body or bones, are interpreted as displays of emotion. Elephants also have economic value at the local and national level by attracting tourists for consumptive and nonconsumptive use. The elephant is admired by many people around the world, and is therefore used as a flagship and umbrella species in appeal s for support of conservation initiatives (Waithaka 1993), but not all people view elephants positively. M any people living in proximity to e lephants view them negatively, as elephants can be a threat safety and livelihood. Conserving Africas elephants is complex because of the variation in the elephants status and habitats across countries and because of the multifaceted social dimensions involved. Once occupying nearly the entire continent of Afr ica (Laws 1970; UNEP 1989; Cumming et al. 1990), today the elephants range is estimated to be 22% of Africas land area, with populations occurring in 37 subSaharan countries. Its distribu tion and abundance vary greatly f rom

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114 declining, fragmented popul ations in West Africa, to larger, more stable populations in central and southern Africa, to locally overabundant populations in areas where populations are confined to smaller areas with limited or no opportunity for dispersal (Balfour et al. 2007; Blanc et al. 2007; Stephenson 2007). Historically, declines in elephant numbers have been attributable to the ivory trade and habitat loss resulting from human population growth and expansion (Said et al. 1995). After the ban on trade in ivory was instituted by the Convention on the International Trade in Endangered Species of Wild Flora and Fauna (CITES) in 1990, elephant numbers began to recover in many areas (Blanc et al. 2005), but poaching for meat and ivory remains a significant threat and has been on the rise in recent years (Stephenson 2007; Wasser et al. 2008). The African elephant is currently l isted as vulnerable on the IUCN Red List of Threatened Species and remains on Appendix I of CITES in most range states1 (Blanc 2008) In addition to poaching, ot her critical threats to elephants include habitat loss and fragmentation (Blanc 2008). Of the remaining habitat, it is believed that 70% of elephant range lies outside protected areas (Blanc et al. 2007), highlighting the importance of maintaining private lands as viable elephant habitat land often occupied by people. Humans and Elephants Humans and elephants have coexisted for thousands of years with different levels and types of interaction, depending on variables such as human and elephant population densities and land use. Today, as the human population rises and more land is converted for agriculture and other human uses, recovering elephant populations are unable to occupy much of their former range (Omondi et al. 2004). The humanelephant interface is expanding along with the potential for conflict. Conflict with wildlife can cause ne gative attitudes to wildlife and reduce support f or 1 Elephant populations in four range states in southern Africa we transfer red back to Appendix II: Botswana, Namibia, and Zimbabwe in 1997, and South Africa in 2000 (Blanc 2008).

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115 conservation (Newmark et al. 1993; De Boer and Baquete, 1998; NaughtonTreves, 2001) and can affect the long term success of conservation programs (Webber et al. 2007). Therefore, it is critical for wildlife managers and conservationists to have a n understanding of the human dimensions of wildlife issues. Although conflict between humans and elephants has a long history, humanelephant conflict (HEC) is perceived to be on the rise. This is especially appar ent where agriculture is practiced (Naughton et al. 1999). There is extensive research on conflict between elephants and farmers (e.g., Brown 1968; Kinloch 1972; Barnes et al. 1995; Tchamba 1995; De Boer and Baquet 1998; NaughtonTreves 1998, 1999; Hoare a nd Du Toit 1999; Lahm 1996, OConnell Rodwell et al. 2000; Osborn and Parker 2002; Wunder 1996). Research has found that elephants can cause devastating damage at the level of the individual farmer, but elephant damage is typically negligible compared to the widespread damage caused by smaller pest species ( Adjewodah et al. 2005; Bell 1984; DeBoer and Baquete 1998; Gillingham and Lee 1999; Lahm 1996; Naughton et al. 1999; Parker et al. 2007; Wunder 1996). Despite this fact, there is a great deal of animosit y among farmers toward elephants (Barnes 1996; Gadd 2005; Naughton Treves 1997; Wunder 1997). This may be due to the size and potential danger posed by the elephant (DeBoer and Baquete 1998; Hoare 2000; Naughton et al. 1999; Sitati et al. 2003), dread and increased perceptions of risk that occur where there are low probability high consequence events (Slovic 1987), and resentment of local people related to the importance of the elephant to governments and conservationists (Matzke and Nabane 1996; Naughton e t al. 1999; NaughtonTreves 1997; OConnell Rodwell et al. 2000). Until recently, little attention has focused on the attitudes and behaviors of pastoralists regarding elephants and other wildlife Historically, pastoralists have not been perceived as

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116 hav ing a positive influence on the environment and wildlife. They have received much of the blame for desertification, with critics for example, pointing to the theory of the tragedy of the commons (Hardin 1968), citing overstocking and overgrazing as the primary, if not the only, causes of desertification (Lamprey 1983), but these ideas have been challenged in the last few decades (see Ostrom et al. 1999) with increased recognition and understanding of the pastoralist institutions that regulate access to communal resources. The compatibility of pastoralism and wildlife is increasingly supported (Barrow et al. 2007; Boone and Coughenour 2001; Gadd 2005; Goldman 2003; Ho mewood and Rodgers 1991; Little 1996; N elson 2000; Reid et al. 2003), especially relative to agriculture. An oft cited example of the compatibility of pastoralism with wildlife co nservation is the long term coexistence of East African pastoralists and some of the largest and most diverse concen trations of wildlife on the planet (Lindsay 1987; Little 1996) Research has found that with low to moderate use of grasslands, pa storalism is a sustainable land use option in dryland savannas ( Mearns 1997 ; Reid et al. 2003). Ironically, the shift in thin king about pastoralism and wildlife conservation comes at a time when the nature of pastoralism is changing. Across Africa, there is a widespread and irreversible shift from nomadic and seminomadic pastoralism to sedentary agropastoralism (Young and Sol brig 1993), where traditional pastoralists are modifying their livelihood strategies to include other economic activities, such as agriculture and wage labor, and/or intensifying livestock production (Barrett et al. 2000; Du Toit and Cumming 1999; Little e t al. 2001). In the midst of these changes, the incidence of humanwildlife conflict, including conflict with elephants, is on the rise (Kasiki 1998; Low 2000; Sitati 2003). A prime example of this is occurring in East Africa, where Maasai pastoralists ar e diversifying their livelihood activities, depending less on livestock (McCabe 2003; McCabe et al.

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117 1992) and increasingly on agriculture. This is the result of several factors, including population growth, loss of grazing land to wildlife conservation and agriculture, and subdivision and privatization of communal lands (Campbell et al. 2000; Kangwana and Browne Nuez, in press). Potential implications (for wildlife conservation) of shifting livelihood strategies were highlighted by research in Laikipia, Kenya. Individuals from two pastoralists groups, the Maasai and Turkana, were found to be more tolerant of elephants than agricul turalists (Gadd 2005). Former pastoralists, who had converted to agriculture, were more similar in attitude to individuals from traditional agricultural groups such as the Kikuyu. These results provide evidence of the increasing threat posed to elephants and other wildlife that formerly coexisted with humans on pastoral lands. Not only did the shift in livelihood strategy result in habitat loss, it also led to decreased tolerance of elephants (Gadd 2005). Similar to the situation in Laikipia, the human con text around Amboseli National Park, Kenya, is changing. The traditionally pastoral Maasai are shifting livelihood strategies, people from farming groups are increasingly immigrating to the area, and less land is available for elephants and other wildlife outside the park. As a result of these changes, there is a mounting focus on HEC (Chapter 2). Several organizations are working to ensure that elephants have continued access to the private lands surrounding the park, which include critical seasonal dispers al areas. There are a number of interventions aimed at reducing negative interactions and improving attitudes toward elephants, with the ultimate goal of increasing tolerance of elephants on private land. Given the dependence of the Amboseli elephants on t he tolerance of local people and the substantial efforts of wildlife authorities and conservationists to increase this tolerance, an empirical measure of tolerance and an analysis of the factors that influence tolerance is needed.

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118 In 1993, Kangwana provided a preliminary assessment of the attitudes of the Maasai of Amboseli toward wildlife in general and elephants specifically. She found that the overall attitude towards wildlife in general was if not positive, then at least tolerant (p. 95). A gricultura lists were slightly more positive than pastoralists possibly because they were less marginalized, having diversified livelihood activities (i.e., crops and livestock) and more access to water (Kangwana 1993) The y also tended to be more educated and aware of the benefits of conservation. A ttitudes towards elephants specifically were interpreted as positive with 58% of pastoralists and 47% of agriculturalists stat ing that elephants should not be removed from the area. My study builds on this work, providing a current assessment of attitudes toward elephants that is grounded in social psychological theory, allowing for an analysis of other variables that predict tolerance of elephants. In this chapter, I provide a n assessment of attitudes toward elephants around Amboseli. The overall goal is to identify variables, including attitudes, that predict Maasai willingness to allow elephants on private land, measured by intention to vote to allow or not allow elephants in group ranches immediately bordering the par k. A secondary goal is to test the transfer of s ocial science theory and methods commonly used in human dimensions research in North America to a rural African setting. Based on theory and previous research, I test an integrated predictive model of cogniti ve and contextual variables to explain variation in local peoples willingness to accept elephants on the private lands around Amboseli National Park. This study has practical, theoretical, and methodological implications. The practical value lies in identifying variables that predict willingness to tolerate elephants to provide stakeholders with a means for evaluating current, and planning future, interventions. This study demonstrates that it is possible to extend social psychological theory and research methods developed in the West to a rural African

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119 setting to survey of a representative sample of a widely dispersed, partially mobile population that parallels complex surveys carried out in industrialized countries. It also contributes to advancing a standardized framework for cross cultural attitudinal research, especially in situations of humanwildlife conflict. Conceptual and Theoretical Framework The Cognitive Hierarchy Studies of attitudes are the most common line of research in human dimensions of natural resource management (Manfredo et al. 2004) Implicit in these studies is the goal of understanding behavior. A proven theoretical framework in this realm of study in North America is the cognitive hie rarchy. The cognitive hierarchy posits that an individuals view of the environment can be organized into a n inverted pyramid that consist s of values, value orientations, attitudes, norms, and behaviors ( Figure 51). At the foundation of this pyramid lie values, enduring beliefs about the world which tend to be shared by a culture. The influence of values on attitudes and norms occurs indirectly via value orientations, which are patterns of basic beliefs toward an object that provide meaning to fundamental values. Attitudes and norms then influence behavioral intentions, the most direct predictor of actual behavior Support for the validity of attitudes and norms in predicting behavior has been provided by a large body of research based on Fishbein and Ajzens ( 1975) Theory of Reasoned Action (TRA). However, researchers have suggested that expanding this theoretical framework to include additional variables may help improve understanding and prediction of behaviors and other constructs in the hierarchy (Eagly and Chaiken 1993; Fazio 1990; Vaske and Donnelly 1999). My proposed model of predictors of willingness to allow elephants in Maasai group ranches, while largely based on the cognitive hierarchy, tests the inclusion of additional variables that have been used to predict behaviors, including demographic variables, prior experience,

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120 knowledge, and perceived risk. In addition, I examine the influence of HEC mitigation interventions on attitudes, norms, and behaviors. The model is visually represented in Figur e 5 2, with arrows representing the hypothesized relationships between variables. The following is a brief overview of each concept within the model and includes my corresponding hypotheses. Value Orientations Values tend to be widely shared by all member s of a culture and, therefore, are unlikely to account for much of the variability in specific attitudes and behaviors. Rather, the influence of values on attitudes and behavior occurs indirectly via patterns of basic beliefs Research conducted in the U.S has found that the basic beliefs that give meaning to values can be organized into patterns of beliefs, which can in turn form value orientations These value orientations can be represented on a continuum such as protection / use and existence / benefits (Fulton et al. 1996), and biocentric / anthropocentric (Vaske and Donnelly 1999). Procedures to measure these orientations have not translated to developing countries, where r esearch has found that individuals can hold more than one value orientat ion concurrently, possibly suggesting that as societies become more complex and removed from the natural world, such as in the U.S., their values concerning wildlife become less complex (Finchum 2002; Manfredo and Fulton 1997). Hence, where societies maint ain a closer link to the natural environment, such as in rural Africa, a framework for capturing more complex value orientations may be required. Kellerts (1980) typology of attitudes toward animals (Table 5.1) has been repeatedly adapted for use in var ying settings around the world, such as Botswana (Mordi 1987), Costa Rica (Drews 2002), the Dominican Republic, Trinidad and Tobago (Rauwald and Moore 2002), Germany (Kellert 1993), Japan (Kellert 1993), Norway (Bjerke and Kaltenborn 1999), and Peru (Frost 2000), with researchers including Kellert himself, using various terms to describe the categories, including wildlife values, value orientations, and attitudes (Kellert 1980, 1985, 1993,

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121 1996; Manfredo et al. 2004; Rauwald and Moore 2002). Mordi (1987, p. 52), discussing his study in Botswana, stated that the categories of Kellerts typology are both mutually exclusive and collectively exhaustive of the universe of attitudes toward wild animals in Africa, although he added an eleventh type that he terme d theistic to capture the fatalism that is present in most African cultures. Even though the attitude types collapsed into eight new factors, Mordi felt the abstractness and mutually exclusive nature of the attitude types made them valid measures for cro sscultural research. I adapted the items used by Mordi to measure wildlife value orientations Based on previous research and the proposed predictive model (Figure 52), t he following hypotheses were examined: H1: Maasai basic beliefs about wildlife can b e organized into distinct wildlife value orientation s. H2: Wildlife value orientati ons will predict attitudes towards elephants and allowing elephant s in group ranches. H3: Wildlife value orientati ons will predict norms for allowing elephant s in group ranches Attitudes A general definition of the a ttitude concept is the tendency to respond favorably or unfavorably to an object where an attitude object can be any abstract or concrete object of thought ( Eagly and Chaiken 1993). In the present study, ther e are two attitude measures: (1) general attitudes toward elephants (targets) and (2) specific attitudes toward allowing elephants in group ranches (behavior). Fishbein and Manfredo (1992) provide a behavior oriented definition of the attitude concept, bas ed on the TRA, which defines an attitude as the product of an individuals salient beliefs about the potential outcomes that result from a behavior and the corresponding evaluations of those outcomes. Research based on the TRA has repeatedly

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122 demonstrated t hat specific attitude s toward behavior s can be strong predictors of specific behaviors (Eagly and Chaiken 1993, Fishbein and Manfredo 1992). General attitudes toward targets are not explicitly considered in the TRA. Ajzen and Fishbein (1980) view attitudes toward targets, along with personal characteristics, as variables external to their model, only influencing behaviors as they relate to the variables within the TRA. However, other researchers continue to examine the predictive ability of more general attitudes toward targets with regard to specific behaviors directed at the target ( Fazio 1986; Fazio et al. 1989; Fazio and Towles Schwen 1999) According to Fazio (1986, 1990), in situations where motivation and opportunity for deliberative (MODE) processi ng are lacking, behaviors are spontaneous and attitude accessibility and attitude strength become important in determining to what degree behavior is based on attitude. Therefore, where an attitude is strong, it is more accessible and likely to be automati cally activated and direct behavior. In addition to affecting behavior, strongly held general attitudes may influence attitudes and norms for a behavior toward a target (Ajzen and Fishbein 2005; Eagly and Chaiken 1993). In short, the Fazio model describes automatic, spontaneous processes, and the TRA is concerned with deliberative processes. Both deliberative and spontaneous processing may occur in situations of humanwildlife conflict. Where there is a high degree of salience and volatility among stakeholders, one would expect strong general attitudes toward the wildlife species of concern. These attitudes would be more accessible and more likely to influence attitudes toward a behavior and guide performance of the behavior concerning the attitude object (Ajzen and Fishbein 2005). On the other hand, the complexity of managing such conflict may invoke thoughtful consideration of possible behavior outcomes among certain individuals. The predictive model (Figure 52) tests the following hypotheses:

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123 H4: General attitude s toward elephants will predict attitudes and norms for allowing elephants in group ranches. H5: Specific attitude s toward allowing elephants will directly predict intention to allow elephants in group ranches. Norms Researchers define norms (e.g., social vs. personal) and measure norms in different ways (Vaske 2008). Under the TRA, which focuses on social norms, a subjective norm is a set of beliefs about the normative expectations of certain referents (an individual s most important others) and ones motivation to comply with those referents (Ajzen and Fishbein 1980). It is an injunctive social norm concerned with perceived social pressure for whether one should or should not engage in a behavior. It has been suggeste d that some individuals may be primarily influenced by attitudes while others are more strongly influenced by injunctive norms (Hui 1988; Trafimow and Finlay 1996). Terry et al. (2000) demonstrated that norms have a stronger influence when people identify strongly with their groups. The influence of such norms is an important consideration in the present study, as it is a common assertion that African cultures, with variation between ethnic groups and exceptions throughout, are more collectivist than indivi dualist ( Brislin 1993; Gannon and Pillai 2010; Myers 2002), and, in such cultures, subjective norm should play a stronger role ( Aar et al. 2007; Giles et al. 2005). Empirical support was provided by a study on individualism and collectivism in Kenya (Ma and Schoeneman 1997), where Maasai and Samburu pastoralists conceptions of self were found to be more collective and less individualized than the self concepts of Westerners. A critical component of Maasai culture is a system of social organization, which creates groups such as clans, sections, and age sets. Each of these groups provides common bonds among all Maasai, with the age system providing the deepest sense of unity (Spencer 2003, p. 3). There are two terms for age set : ol poror refers to th e f riendships of the peer group, and ol aji

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124 denotes the sterner expectations of the age set with the ultimate threat of a curse following any breach (Spencer 2003). This latter term underscores the potential significance of normative expectations. Further e vidence of the importance of norms in Maasai society lies in the many Maasai proverbs that teach the value of group membership and altruism (see Rainy 1989). Given the collectivist elements of Maasai culture which support cooperation and reciprocity, which in turn have facilitated transhumant pastoralism and a communal landtenure system, it is expected that subjective norm will be a significant predictor of intention to allow elephants. The model tests the following hypothesis: H6: Norms for allowing elep hants will predict intention to vote to allow elephants in group ranches. External Variables Ajzen and Fishbein (2005) while maintaining that the influence of external or background variables on behaviors occurs indirectly via attitudes and norms rather t han directly on behavior, recognize that there are a multitude of variables that could potentially influence other variables in models such as the TRA They also note that no theory exists to guide selection of potential background or external variables T herefore, the selection of additional variables to include in my predictive model was based on the findings of previous research, including research on human wildlife conflict. Demographic variables It is common practice in attitude studies to examine the relationship between demographic variables and attitudes, and, more recently, with other variables within the cognitive hierarchy. For example, research in North America has often demonstrated that g ender influence s attitudes and other variables in the hierarchy (Bright et al. 2000; Czech et al. 2001; Dougherty et al. 2003; Kellert and Berry 1987; Lauber et al. 2001; Vaske et al. 2001; Zinn and

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125 Peirce 2002). Studies of wildlife conservation attitudes in rural Africa have found correlations between attitudes and gender (Gillingham and Lee 1999), affluence/wealth (Infield 1988, Kideghesho et al. 2007; Mordi 1987), education (Akama et al. 1995; Infield 1988; Mordi 1987), ethnic group (Akama et al. 1995), level of westernization (Infield 1988), and livelihood/landuse activity (Infield and Namara 2001). Studies specific to attitudes toward elephants in Africa have found that gender (Hill 1998; Kangwana 1993; Kioko 2004), age (Kangwana 1993; Kioko 2004), an d livelihood/land use activity ( Gadd 2005; Kangwana 1993; Kioko 2004 ) explained some of the variance in attitudes. Age and gender are important organizing principles within Maasai society (H odgson 2001, 2005; Spencer 1993) and have been found to be relate d to attitudes toward wildlife (Kangwana 1993). In Amboseli, Kangwana (1993) found that older men were more positive than ilmurran (commonly referred to as warriors) and women toward wildlife in general and elephants specifically. Spencer (1993) provides a gerontocratic model that represents major groupings by sex and age grade among the Maasai ( Figure 5.3). It illustrates the important divisions between the young and old, and men and women. These divisions represent the partitioning of traditional righ ts, responsibilities, and activities of daily life in Maasai pastoralism. For example, i lmurran are traditionally responsible for protecting the homestead, middle age sets are responsible for managing resources for herding, and members of the retired agesets are responsible for broad decision making through the council of elders. Women are responsible for the operation of the household, including house construction, caring for children, preparing meals (including collecting water and firewood), and milki ng cows.

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126 Although there is ongoing change in the traditional age and gender rights and roles,2 divisions between young and old, and men and women, remain strong. These divisions are hypothesized to affect how individuals perceive, understand, and evaluate things, given that they determine access to knowledge, experience, and so on. As described earlier, Kangwana (1993) and Gadd (2005) found differences in attitudes between pastoralists als and agriculturalists with pastoralists more likely to have favorab le attitudes toward elephants than agriculturalists. The present research identifies current livelihood strategies in the study area and, given the shift toward livelihood diversification, inquires into future livelihood plans. It examines the influence of primary livelihood activity on variables of the cognitive hierarchy and considers the implications of future livelihood intentions. Traditionally, community decisions in Maasailand were decided by councils of elders. When the group ranch system was created by the Land Adjudication Act of 1968, elected group ranch committees became responsible for the management of group ranch affairs, including encouraging sound land use practices, allocating funds for new projects, and registering new members (Mwang i 2005). The group ranch is also the local institution that receives and disburses wildlife benefits to the community (Kangwana 1993). Following Kangwana (1993), I examine the potential influence of group ranch residence on variables in the cognitive hiera rchy. 2 Examples of change for men include an extremely limited security role for modern ilmurran and the transfer of decision making from senior elders to elected officials. For women, who prior to the 20th century, enjoyed shared rights and benefits associated with livestock production, today, while maintaining many of the same responsibilities for livestock production, have been disenfranchised and margina lized by men, and are excluded from political and economic affairs (Hodgson 1999, 2005).

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127 Based on previous research and given the importance of age and gender stratification in Maasai culture, it is expected that age and gender, along with livelihood activity and group ranch of residence will influence the constructs of the cognitive h ierarchy. H7: Age, sex, primary livelihood strategy, and group ranch will predict value orientation s, attitudes, and norms. Prior experience Research has demonstrated that in individuals with prior (direct) experience with an attitude object, attitude b ehavior correlations tend to be higher than for individuals who lack such experience (Bentler and Speckart 1979; Borgida and Campbell 1982; Bright and Manfredo 1995; Fazio and Zanna 1978). Fazio and his colleagues have attributed this to increased attitude strength and accessibility to higher levels of direct experience (see Eagly and Chaiken 1993 for review). Another explanation is related to attitude stability. Individuals who have had direct experience with an attitude object are more likely to have stab le, difficultto change attitudes (Doll and Ajzen 1992). Conversely, individuals who have no, or only, indirect experience might be more likely to change their attitudes upon directly experiencing an attitude object (Ajzen and Fishbein 1980). It is expecte d, given the context of the current study, where most respondents have lived alongside elephants for their entire lives, that there will be a strong attitude behavior relationship due in part to a high level of experience with elephants. The type of experi ences (positive or negative) is expected to differentiate those who are positive toward elephants and those who are negative. H8: Type of prior experience with elephants will predict attitudes toward elephants and allowing elephants in the group ranches. Knowledge of elephants Knowledge is a common variable in attitude research regarding wildlife and the environment (Aipanjiguly et al. 2003; Barney et al. 2005; Brooks et al. 1999; Casey et al. 2005;

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128 Drews 2002; Kellert 1993 ; Kellert and Berry 1987; McDuff et al. 2008; Papageorgiou 2001; Reading and Kellert 1993). Several studies have found low correlations between knowledge and attitudes (see Tarrant et al. 1997 for review), with exceptions. For instance, Thompson and Mintzes (2002), using Kellerts typolog y, found relationships between knowledge and attitude types. Aipanjiguly et al. ( 2003) found a positive correlation between boaters knowledge of manatees and their support for manatee conservation. Knowledge has been shown to have a moderating effect on t he relationship between values and wildlife attitudes, with variation between constituent groups (Tarrant et al. 1997). This could be explained in part by differing levels of reliance on factual information by different types of individuals in the formation of attitudes. Individuals with more information about an attitude object may have more stable and more accessible attitudes (Eagly and Chaiken 1993). Environmental education and communication programs seek to increase knowledge, influence attitudes, and ultimately influence environmental behaviors (Byers 1996; Jacobson 2009; Monroe 2003). Studies have demonstrated that increasing environmental knowledge can improve environmental attitudes (Bradley et al. 1999; Mangas and Martinez 1997; Petrzella and Korsc hing 1996), but several studies also have shown that education alone does not change behavior (see McKenzieMohr and Smith 1999; Schultz 2002). This discrepancy highlights the need to understand the range of factors that may influence behavior in a given context, including knowledge normative beliefs, and factors (barriers to behavior) that may moderate the relationship between knowledge, attitudes, and behavior (McKenzie Mohr and Smith 1999; Schultz 2002). When discussing knowledge of wildlife and conser vation in traditional cultures it is important to consider the distinction between traditional ecological knowledge, also referred to

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129 as local or indigenous knowledge, and modern, scientific or Western knowledge (Gadgil et al. 1993; Hunn et al. 2003; S emali and Stambach 1997). Traditional knowledge is generally defined as local knowledge regarding the natural world that has been developed over time through close interaction with, and observation of the natural world and passed down through generations, while modern knowledge is obtained through empirical methods and formal, Westernstyle education. Many community based conservation programs promote the integration of local and modern knowledge, but have been criticized for their lack of success in meeti ng this goal (Goldman 2003; Kellert et al. 2000). I examined knowledge of elephants using items deemed to represent a mix of local and modern knowledge. It is expected that the Maasai, in general, will exhibit a high level of knowledge of elephants given their level of experience with the natural environment and a history of extension and educational outreach interventions in the region. Maasai traditional environmental knowledge is evident in the understanding of seasonal wildlife movements, the use of me dicinal plants, the use of a communal land management system, and, as evidenced here, their understanding of wildlife ecology. This is especially true for males who are out in the bush as young herd boys and ilmurran learning the layout of Maasailand (Kipuri1983). While the duties and responsibilities of females in Maasai society require them to spend most of their time in the homestead, they too experience the bush when gathering water, firewood, and building materials, or when called on to assist with her ding. Given the variation between men and women to have opportunities to be in contact with elephants, it is expected that women will demonstrate less knowledge of elephants than men (similar to Gillingham and Lee 1999). The following hypotheses are advanced: H9: Men will have a higher level of knowledge of elephants than women.

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130 H10: Knowledge will predict attitudes toward elephants (targets). Risk perception s Risk perceptions regarding wildlife are important to understand, as they can influence attitudes and behaviors toward wildlife and receptivity to educational communications ( Gore et al. 2006; Knuth et al. 1992; Lohr et al. 1996; Riley and Decker 2000 ; Saberwal et al. 1994). Slovic (1987) suggests that when attempting to understand and address public r isk perceptions, researchers should attend to a broader conception of risk, one that would require a more comprehensive measure (as opposed to the technical measurements of experts, e.g., fatalities). Furthermore, Sjberg (1998) points to the need to diffe rentiate between emotional and cognitive dimensions of risk perceptions, where c ognitive risk perceptions are judgments about the probabilit y of experiencing a risk and emotional perceptions involve a preoccupation with thoughts about uncertain and unplea sant events hereafter descr ibed as worry (Sjberg 1998). Additional constructs have been related to risk perception, including voluntariness, dread, knowledge, and controllability (Slovic 1987). Research on risk perception has been limited by difficulties in conceptualization and measurement (Baird et al. 2009), but there have been several efforts to advance this area in studies of humanwildlife conflict (Gore et al. 2006; Riley and Decker 2000; Stout et al. 1993; Zinn and Pierce 2002). My study contri butes to this effort by examining the influence of constructs previously related to risk perception on attitudes and behavioral intention toward elephants. Drawing on the earlier discussion of HEC, the probability of experiencing conflict with elephants, compared to other species, tends to be low Viewed in a broader perspective, the risk of dying from disease, especially HIV/AIDS, and road accidents in Kenya is far greater (WHO 2006), but the impact of a single encounter with an elephant can be catastroph ic. In such

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131 situations where there is a low probability, but the potential for severe consequences exists risk perceptions tend to increase (Decker et al. 2002). Additionally, perceptions of risk are higher when the threat is perceived to be uncontrollabl e and involuntary (Slovic 1987) In such situations, self efficacy beliefs in dealing with a situation may be affected, thereby influencing how an individual behaves.3 The perceived controllability of HEC could be a significant issue for local people give n that the elephant is such a large and potentially dangerous animal. This, considered together with the high level of fatalism present in many African cultures (Gannon and Pillai 2010 ; May 2003; Mordi 1987), may influence attitudes and behaviors toward el ephants. Kangwana (1993, p. 81) suggests that the Maasai are indeed fatalistic in their attitudes toward conflict with wildlife, stating that the Maasai seem to view conflict and its outcomes as their lot as people that live with wildlife. Similar to Go re et al. (2006) and following the recommendation of Slovic (1987), I examine multiple constructs to gain a more comprehensive understanding of perceptions of risk related to HEC. I explore the influence of perceived incidence of HEC, perceived level of ri sk to personal safety and economic livelihood, level of worry, and beliefs about general and personal controllability of HEC. H11: Construct s associated with risk perception will predict attitudes toward elephants and allowing elephants in the group ranc hes. HEC mitigation interventions The disproportionate costs, including costs resulting from humanwildlife conflict, borne by local people living alongside protected areas are well recognized (Archabald and Naughton3 There are numerous approaches for defining and measuring concepts related to self efficacy, locus of control, and perceived behavioral control (a concept of the TPB ) (see Rhodes and Courneya 2003 for a review). Formal conceptualization and measurement of these concepts is beyond the scope and purpose of this paper, but a preliminary exploration is provided.

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132 Treves 2001; Nyhus et al. 2005). For pa storalists and agropastoralists such as the Maasai, these costs may include competition for grazing and water, personal safety, crop damage, and livestock losses from depredation and disease (Campbell et al 2002). When elephants are involved an intellige nt, potentially dangerous and costly species of conservation concern (Osborn and Hill 2005) the situation is especially complex. Interventions are needed that address the needs and concerns of local people and the conservation requirements of elephants ( Parker et al. 2007, Tchamba 1995). Several strategies for mitigating humanelephant conflict have been tested throughout the elephants range, including methods aimed at reducing damage (e.g., lethal and nonlethal deterrents such as noise, fences, control led shooting) and increasing tolerance (e.g., compensation, environmental education, tourism revenue). There have been various levels of success, but, in general, research has demonstrated that a variety of methods, both long and short term, should be use d in combination (Omondi et al. 2004; Osborn and Parker 2003; Parker et al. 2007) The methods selected should be site specific and be based on interdisciplinary research so that there is an understanding of the true nature of conflict, perceptions of conf lict, and the acceptability of proposed mitigation interventions. Amboseli National Park has been the site of many conservation schemes. Cited as one of the earliest examples of an integrate d conservation and development program (ICDP), Amboseli was initially touted as a model for local participation (Western 1982b, 1994) but, as time has passed, it has proven to be an example of limited successes (Adams 1998; Kangwana and Browne Nuez, in press; Lindsay 1987; Wells et al. 1992) Today, a number of organizations are working in the ecosystem to conserve wildlife by gaining the support of the local people, largely by increasing wildlife conservation benefits (through tourism) and reducing costs. Several of these efforts are specific to elephants, with the goal of improving attitudes toward and tolerance

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133 of elephants (see Study Area and Chapter 2). I provide a preliminary assessment of these interventions in the present analysis by first identifying the perceived costs and benefits of living with elephants. I then explore the impact of awareness of conflict interventions on attitudes and behavioral intentions. H12: Awareness of conflict mitigation interventions will predict attitudes toward elephants and allowing elephants in the gr oup ranches. Methods Results presented in this chapter are based on a survey of local attitudes and behaviors toward elephants which took place from August 2004 to June 2005. A more detailed description of the study area and methods is provided in Chapter 2. Study Area The Greater Amboseli Ecosystem is located in southern Kenya at the north foot of Mt. Kilimanjaro on the Kenya Tanzania border (a more detailed description of the study area is provided in Chapter 2). At the heart of th e ecosystem is Ambosel i National Park (Figure 5.4), encompassing 390 km2 area of the approximately 8 ,000 km2 ecosystem (see Chapter 2 for more detailed description ). Several species of the parks wildlife including elephants, migrate seasonally along with Maasai livestock, be tween the basin and the surrounding rangelands, which are divided into Maasai group ranches. The Amboseli elephants are a key component of this ecosystem. They are emblematic of the critical and complex role of elephants at the local, national, and international level coexisting with pastoral people for thousands of years, increasingly in conflict with transitioning human neighbors, and drawing attention and revenue from abroad. At the time of my survey, there were approximately 1,500 elephants in the population, with over 1,000 primarily using the private lands outside the park (C. Moss, pers. comm.).

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134 Pastoralists have occupied present day Maasailand for thousands of years (Ehret 1971; Foley 1981; Jacobs 1975; Kesby 1977). It is believed that the M aasai, as they are known today, moved into the Amboseli ecosystem several hundred years ago ( Jacobs 1975; Kituyi 1990 ). The Maasai have been credited for the abundant wildlife present in Maasailand (Chapter 4). Explanations for coexistence range from toler ant attitudes (Mol 1981; Ole Dapash 2002; Parkipuny 1997; Simon 1963) to the compatibility of pastoralism with wildlife conservation (Chapter 4). While tolerant and indifferen t are the m ost common anecdotal descriptors of Maasai attitudes toward wildlife ( Campbell et al. 2000; Capone 1972; Darling 1960; Fosbrooke 1972; Kipury 1983; Myers 1973; Ndaskoi 2006; Western 1994, 1997), some maintain that the Maasai hold positive attitudes toward wildlife ( AWF 1999; Homewood and Rodgers 1991; Kipury 1983) Kangwana (1993) provided the first empirical findings on attitudes of the Maasai of Amboseli, stating the overall attitude towards wildlife is, if not p ositive, then at least tolerant (p. 95). As mentioned, m any changes have occurred in the Greater Amboseli Ecosystem since Kangwana conducted the first assessment of Maasai attitudes toward elephants around Amboseli in 1991. The most critical is that of land use change. As described in Chapter 2, the Maasai have a long history of land alienation resulting from colonial and post independence government policy that has led to land ownership, cultivation, and the development of protected areas (see Chapter 2; Lindsay 1987; Western 1994 for a review). Today, former communally owned group ranches, which were created, in part, to keep land under Maasai ownership (Ntiati 2002), are largely subdivided. As of 2006, of the 52 group ranches in the Kajiado District, 32 had completed subdivision and 15 were in the process of subdivision, leaving only 5 that had not sta rted th e process (BurnSilver and Mwangi 2007). Olgulului Lolarashi and Kimana Tikondo,

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135 the two group ranches that immediately border the park, hereafter referred to as Olgulului and Kimana, were among the last to begin subdivision. Kimana completed the process in 2005, and in 2007, the agricultural areas of Olgulului were being subdivided. With a growing human population, largely from immigration of nonMaasai (Chapters 2), and decreasing land availability, many Maasai are shifting from livestock based livelihoods to more diversified livelihood strategies, including agriculture. T he settle ment of the rain fed areas has reduced the area available for dry season grazing and access to water for livestock and wildlife (Campbell et al. 2000). In addition to the long st anding effort to increase conservationrelated benefits to local Maasai, s everal organizations, such as the Kenya Wildlife Service (KWS), the Amboseli Elephant Research Project (AERP), and the African Wildlife Foundation (AWF) have implemented intervention s to reduce human elephant conflict around Amboseli and maintain or increase tolerance of elephants in the group ranches (Chapter 2) KWS has used several strategies to conserve elephants and manage conflict, including revenue sharing through a school burs ary program, chasing and scaring problem elephants, and erecting fences around agricultural areas at Kimana and Namelok The Kimana fence is located on the east side of Kimana Group Ranch and the fence at Namelok straddles the KimanaOlgulului border (Figu re 5 4). AERP implemented a consolation scheme in 1998 that pays for livestock (cattle, goats, and sheep) killed by elephants outside of the park in an effort to end th e retaliatory spearing of elephants (AERP made retro active payments for 1997, when negotiations for the consolation program began). At the beginning of the study reported here, AERP had paid out 1,684,000 KSh (approximately 22,000 USD) over the course of eight years (see Chapter 2 for a breakdown across years ) and the director of AERP belie ved that the program was positively influencing

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136 Maasai attitudes and helping to reduce the number of elephants being speared (C. Moss, pers. comm.). Although the spearing of elephants has not completely stopped ( ilmurran spear elephants for other reasons see Chapter 4), retaliatory spearing of elephants due to HEC came to an end in the three group ranches participating in the program (both group ranches in the present study participate in the consolation scheme). Finally AWF developed an outreach program in 1999, where the goal was to promote awareness and communication through meetings, workshops and educational tours. Another goal was to promote benefit sharing. O ne planned activity was to assist the Maasai in improvin g the planning and operation of c ultural bomas (Chapter 2). In light of the many changes in Amboseli, a current assessment of attitudes and the factors influencing them, along with plans for future livelihood activity, is critical to informing successful conservation and conflict mitigation policy and interventions. The present study, following Kangwana (1993), was conducted in Olgulului and Kimana group ranches (Figure 54). Sampling P rocedure A current sampling frame did not exist, so a census was conducted of all the households in the study area by collecting GPS waypoints for each residential site4. Two local field assistants, equipped with Garmin GPS receivers and census worksheets, collected 519 waypoints that were integrated into the Amboseli Eleph ant Research Projects GIS database. A map of the study area, including residences, was produced (Figure 5.4). From the census sheets, I 4 A waypoint could represent a traditional enkang, comprise d of single or multiple households, a manyat ta or a nontraditional, modern residence (Chapter 2).

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137 determined that there were 2,444 households in the study area, 1,606 (66%) in Olgulului and 838 (34%) in Kimana. A mul tistage area sample (Weisburg et al. 1996) was selected to capture the increasing heterogeneity of the widely scattered, sometimes hard to reach, members of the population. Every effort was made to obtain a random, representative sample. I selected the largest sample size possible, g iven the limits in resources and time, to increase the possibilities of analysis and decrease the sampling error (Piel et al. 1982). A sample of 293 households (12% of total) was selected, with the goal of interviewing two adul ts (one male, one female) in each household (n = 586). This was first stratified by group ranch, following Kangwana (1993). Therefore, 193 households (66%) were selected in Olgulului and 100 (34%) in Kimana While many studies seek to interview the household head, this limitation can cause serious bias, as the sample will likely be over represented by elderly men, who differ significantly from other adults living in the household (Piel et al. 1982). Therefore, in addition to targeting both male and female r espondents, all adults in a household were eligible for interviews. Questionnaire D esign Nine focus groups were conducted in the study area t o elicit salient beliefs about wildlife elephants in particular, and related issues in Amboseli, and to acquire appropriate culturally relevant, local vocabulary for the survey instrument. Questionnaire items were developed using the knowledge gained from the focus group discussions, the review of the records and documents of various organizations involved in elephant conservation in Amboseli, and key informant interviews. Cognitive items were based on hypotheses grounded in social psychological theory. The questionnaire started with general questions regarding wildlife, progressed to questions specific to elephants and concluded with sociodemographic questions (Appendix C). Questions were a combination of openand fixed response (yes/no, true/false, agree/disagree, etc.)

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138 questions. Openended questions were either field coded, where enumerators selected response from pre coded lists, or were coded during data analysis (for longhand responses). Picture cards were used to elicit responses to questions regarding identification of wildlife that occurs in the group ranches, wildlife that is liked/disliked (card sorting ), problematic wildlife (ranking), and current and future livelihood activities. Every effort was made to minimize measurement error, including asking two practice questions at the beginning of the interview to ensure understanding of the Likert scale resp onse format (see Chapter 2 for further details). All Likert scale items included a neutral midpoint, with an additional dont know response option where applicable. Variables of the C ognitive H ierarchy Wildlife value orientation s. Following Mordi (1987) the measure of value orientat ions was modeled after Kellerts work. Forty four agree disagree belief statements, many adapted from Mordi, were used to develop eleven possible scales, with four belief statements per scale (Appendix C questionnaire). Res ponse choices ranged on a seven point scale from strongly disagree (1 ) to strongly agree (7). General a ttitude s toward elephants. Two measures were used to assess attitudes toward elephants. The purpose of the first measure, which was obtained early in the interview, was to obtain a preliminary indicator of attitudes toward elephants. Respondents first identified wildlife species found in their group ranch using animal picture cards, then sorted the cards to create like and dislike piles. This was done before questions specific to elephants were asked. The second measure was developed from 25 agreedisagree belief statements that were used to develop an attitude index. The belief statements were designed to capture cognitive, affective, and behavi oral components of attitudes toward elephants. Response choices ranged on a seven point scale from strongly disagree ( 3) to strongly agree (+3). The belief statements

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139 were based on information obtained from the preliminary research and focus group dis cussions. The attitude index was the measure used in the model. Specific a ttitude s toward allowing elephants. Following procedures put for th by Ajzen and Fishbein (1980) and tested by Whittaker (2000) belief evaluation (BE) scores regard ing possible outcomes of allow ing elephant s in group ranches were created by asking two se ts of questions regarding eight possible outcomes of tolerating elephants (e.g., cause more tourists to visit group ranches ). The first series asked respondents to indicate their beliefs regarding the outcomes on a seven point scale from extremely unlikely ( 3) to extremely likely to (+3). In the second series, respondents were asked to evaluate each outcome on a scale from extremely bad ( 3) to extremely good (+3) An atti tude score was generated for each respondent by multiplying each belief score by the corresponding evaluation and then summing the products. Subjective norms for tolerating elephants. Procedures for creating norm scores for allowing elephants in the group ranches were adapted from Ajzen and Fishbein (1980). First, respondents were asked to identify five important referents in a free response format5. They were then asked to what degree their referents would approve or disapprove of the respondent allowing elephants to come into the group ranch without harm. Responses could range from strongly disapprove ( 3) to strongly approve (+3). Respondents were then asked how motivated they were to comply with each referent. Motivation could range from not at all (1) to very much (4) with a dont know option. The norm score was created by multiplying the 5 Each respondent was allowed to identify referents freely rather than identifying referents from a pretested list of modal salient referents to avoid a p ossibly incorrect assumption that all individuals in the sample had the same set of referents (Terry et al. 2000).

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140 normative belief score by the motivation to comply, summing the product scores for each referent, and calculating the average.6 Intention to tolerate elepha nts. Following Whittaker (2000), the behavior of interest (allowing elephants in group ranches) was signified by the reported intention to vote to allow or not allow elephants in the group ranches. Respondents were asked how they would vote if there was a vote on whether or not elephants should be allowed or not allowed inside the group ranch. Responses were coded as allow (1), not allow (2), or dont know (99). A hypothetical vote was used to measure intentions to make willingness to allow elephants as concrete and action oriented as possible (Whittaker 2000, p. 48). Variables External to the H ierarchy Demographic Variables. Four sociodemographic variables were examined: gender, group ranch, livelihood activity, and age. Gender was measured as male (0 ) or female (1 ). Group ranch was coded as Olgulului (0) and Kimana (1). For livelihood, respondents were asked in depth questions regarding the herding and cultivation activities of their households. They were then asked if they, or any other m ember of the household, were involved in any other livelihood activities using picture cards representing the various economic opportunities available in the region. After listing all forms of household livelihood activities, respondents ranked the importa nce of each activity by sorting the cards. Primary livelihood activities are listed in the demographic summary in Table 5.2. It was anticipated that a large number of individuals would not know their ages. Therefore, three approaches were used to measure age. First, res pondents were asked to provide their age in years. Second, men were asked their age grade. Third, enumerators assigned a 6 Diverging from Ajzen and Fishbein (1980), an average score was obtained, rather than just a sum of the product scores, because of the vari ation in the number of referents per respondent.

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141 person type classification to each individual based on age provided, age set, or subjectively7. The categories for men were elder (1) or young man (2). For women, the categories were old woman (3), middle woman (4), or young woman (5). These categories were cross checked responses to the first two age measures where provided. Based on the three measures, the sam ple was divided into two groups for analysis: younger and older. Prior Experience. There were multiple measures of experience. Two broad measures were used in the causal model. First, respondents who reported seeing elephants in the group ranch during the card sorting activity were asked if they enjoyed seeing elephants in their group ranch (a measure of positive experience). Seco nd, respondents were asked if they had problems with elephants (a measure of negative experience). This second measure was assessed at two points during the interview to examine the possible effects of question order. On the first occasion, following the w ild animal card sorting activity, respondents were asked if they had problems with any of the wild animals that they see in the group ranch, no (0) or yes (1) these codes were used for all yes/no questions on the questionnaire. If they stated they di d have problems, they were instructed to select the cards of problem animals. Enumerators ticked the selected animals on a pre coded list. After a series of questions regarding interactions with elephants (e.g., where have you seen elephants near the enkang, in the bush, etc.), respondents were asked, would you say that it is true that elephants cause you problems? To understand possible effects of location, respondents were asked about the specific locations where they see elephants and if they liked/di sliked seeing elephants at each location. 7 It was assumed that this would be a reasonable approximation given that women know that age sets of the young men ( ilmurran) they dated when they were young girls. The female enumerators were aware of th is and, as all Maasai do, knew the age grades for the men of their age, their mothers ages, and their grandmothers ages.

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142 Knowledge. There were ten truefalse statements measuring knowledge of general elephant ecology. Responses were coded as true (1), false (2), and dont know (99). Risk perceptions. There were six questions re garding risk associated with living alongside elephants. One question asked about the rate of HEC in the last 5 years (1 = increased, 2 = the same, 3 = decreased, 99 = dont know). Two questions asked about perceived personal risk physical and economic associated with HEC (1 = great risk, 2 = little risk, 3 = no risk, 99 = dont know). One question asked how much the respondent worries about HEC (1 = a great deal, 2 = a little, 3 = not at all, 99 = dont know). Finally, two questions asked about the co ntrollability of HEC, one about general controllability (1 = very, 2 = somewhat, 3 = not at all, 99 = dont know) and one regarding self efficacy (yes/no/dont know). HEC mitigation interventions There were five questions regarding the costs and benefits of living with elephants. They were: do elephants bring costs to people in this group ranch (yes/no/dont know); if yes, what are the costs; do elephants bring benefits to people in this group ranch (yes/no/dont know); and, if yes, what are the benefits (open response). Respondents were asked if their household receives benefits from tourism (yes/no/dont know). Ten questions measured awareness and evaluations of interventions. Respondents were a sked if they were aware of any organizations that help people who have problems with elephants (yes/no/dont know); if yes, which organizations and what actions the organizations take (there were a precoded lists of organizations and interventions see q uestionnaire, Appendix C); if they had ever asked for help from any of the organizations (yes/no/dont know); and, if yes, were they satisfied with the organizations action. Responses could range from very unsatisfied ( 3) to very satisfied (+3). A se ries of questions specific to interventions (electric fences, cultural bomas, and compensation and consolation payments) was asked to assess

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143 awareness of specific interventions and general evaluations of the interventions. The questions were: does your gro up ranch have an electric fence (yes/no/dont know); if yes, does the fence do a good job (yes/no/dont know); does your group ranch have any cultural bomas (yes/no/dont know); and are there benefits to having cultural bomas (1 = money, 2 = teaches touris ts Maasai culture, 3 = other, 99 = dont know). Finally, respondents were asked if receiving money for elephant damage makes people in their group ranch more tolerant of elephants in the group ranch (yes/no/ dont know). Future L and U se Following the livelihood ranking activity, respondents were asked which livelihood activity they thought would be most important to their household in five years. Validity and R eliability As discussed in Chapter 3, it is important to address the issues of validity and re liability when conducting scientific inquiry. The validity of the present survey was evaluated based on three types of validity: content, criterion, and construct validity. Content validity is concerned with the degree to which a measurement instrument cap tures the full meanings of concepts it is intended to measure (Bernard 2001; Vaske 2008). The content validity of my survey was evaluated by a panel of experts, which included individuals with expertise in human dimensions research, elephant ecology, and M aasai culture. Adjustments were made to the survey instrument based on reviewer feedback. Criterion validity in the present study has to do with ability to predict a criterion. Therefore, an estimate of criterion validity is provided by the predictive abil ity of the proposed model. Construct validity is concerned with concepts and relationships supported by theory. Two forms of construct validity addressed in my survey are convergent validity, supported by correlations between concepts, and factorial validi ty, demonstrated by meaningful groupings of items (see Vaske 2008 for discussion of various forms of validity).

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144 Finally, to determine the reliability of multiple item indicators, measures of internal consistency are examined using Cronbachs alpha reliabil ity coefficients. Alpha is influenced by the number of items in a scale, with a higher alpha for scales with more variables. In human dimensions research, an alpha of 0.65 can be considered adequate, although some researchers accept a cut off of 0.60 (Va ske 2008, p. 518). Analysis Data were analyzed using SPSS Grad Pack v. 14 for Windows (2006). Frequencies and descriptive statistics were obtained to check for errors in the data, to understand the distributions of the study variables, and for discussion purposes. Exploratory factor analysis (EFA) with varimax rotation was conducted to assess the underlying structure for the 44 Kellert type items. EFA is recommended when the goal is to identify latent constructs underlying measured variables and when the assumption of normality is violated, as was the case for several of the belief variables (Costello and Osborne 2005; Fabrigar et al. 1999). Cronbachs alpha was calculated for each factor suggested by the EFA to assess internal consistency. Based on these analyses, responses for items within each factor that was found to have a satisfactory level of reliability ( 0) were averaged and the resulting score s were used as indicator s of respondents general wildlife values. EFA was also used to examine the s tructure of general attitudes toward elephants based on responses to 25 belief statements regarding elephants. The internal consistency of the resulting factors was examined using Cronbachs alpha reliability coefficients. Following the methods suggested by Fishbein and Ajzen (1980) and described above, attitudes and norms for allowing elephants in the group ranches were measured for each respondent Comparisons of beliefs and evaluations for each potential outcome of allowing elephants were made by charti ng means scores for those who vote to allow and not allow

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145 elephants. Average belief evaluation scores were also graphed to visually summarize differences between voting groups. T tests were used to compare mean scores of voting intention groups (allow or not allow elephants in group ranch) for attitudinal and normative variables. A path analysis was conducted to test the hypothesized model of predictors of intention to vote to allow elephants in the group ranches (Figure 52). A series of regression anal yses were performed to obtain path coefficients. All independent variables were entered into the regressions simultaneously, as all variables, based on theory and previous research, were expected to be important. To examine predictors of wildlife value ori entation s, dummy variable regression was conducted using three dichotomous demographic variables (age: young/old, gender: male/female, and livelihood: pastoralism/cultivation). Multiple regression analysis was used to show the effect of predictor variables on the dependent attitude and norm variables. Finally, logistic regression analysis was used to predict voting intention (dichotomous) using the attitude and norm variables (continuous). The first model tested the TRA by examining the effects of attitude toward the behavior (specific attitude) and norm on behavior intention. The second model included the additional predictor variable, attitude toward elephants (general attitude). Results W e interviewed individuals at the desired number of households (n=293). There was a 2.7% (n = 8 households) nonresponse rate.8 These households were replaced w ith alternate households that were randomly selected at the time the original sample was drawn. In seventeen households, we were only abl e to interview one adult t hree males and four teen females The reasons for single interviews per household were: 1) eight individuals were away at a job or 8 One household head was intoxicated and members of two households were absent during two attempts to schedule interviews. Five households had relocated.

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146 herding, 2) three were deceased, and 3) the remaining six either were not home or declined to be i nterviewed. A total of 569 interviews were conducted. Table 5 2 shows the demographic characteristics of the sample. The number of respondents from each group ranch was proportionate to the number of households counted in the census. The level of education was low, with 76% of respondents having less than a primary school education. The sample was predominantly Maasai (98%) with a nearly equal representation of males (49%) and females (51%), and young and older adults. Only 34% of respondents provided the ir age, with 66% stating they did not know their age. Of these, ages ranged from 18 to 67, with 30.73 as the mean. Table 53a shows the age grades present in Amboseli in 20042005 and their representation in the study sample Most male respondents (92%) fa ll into one of the younger three age sets, which are considered the active groups, with ilmurran comprising the Ilkiponi age set and the men responsible for decision making (e.g., for herding) comprising the Ilkishimu and Ilkishuri/Ilkidotu age sets (Tab le 5 3a). Most men in the sample are below the age of 50, which is expected, given that Kenyas average life expectancy for men is 51 (WHO 2006), with estimates for the Maasai being even lower. Table 5 3b shows the results of the person type measure. Whe n this measure was cross tabulated with the age set variable, results showed that the division between young and elder occurred among the Ilkishuri/Ilkidotu age set (age range = 20 35). For women who provided their ages, which only included middle and young women, the divide occurred at age 30. Based on these findings, and given the mean age of 30.74 (n = 193), respondents were grouped into two groups, older and young, with an approximate cutoff of age 30 (Table 5 3c). Voting Intention and D emograph ics If a vote were held at the time of the survey on whether to allow elephants in the group ranches, results indicate that a slight majority of respondents (53%) would have vote d to allow

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147 elephants while 47% would have voted again st allow ing elephants i n the group ranches. There were two cases of item non response; therefore, the total sample size for analysis was 567. Table 52 shows that gender ( p < 0.001) and school attendance ( p = 0.04) were statistically related to voting intention. Most men (72%) i ndicated they would vote to allow elephants in the group ranch, while most women (65%) stated they would vote to not allow elephants. The effect size of gender on voting intentions was medium or typical ( = 0.36)9. Although school attendance was statistically significant ( p = 0.04), it had a minimal effect on voting intention. ( = 0.09). No statistical differences were observed between other demographic variables (group ranch, age, and livelihood activity) and voting intention (Table 52). Wildli fe V alue Orientation s The exploratory factor analysis of the 44 Kellert type items produced a 13factor solution accounting for 42% of the variance, with elements of Kellerts typology collapsing together. Examination of the scree plots indicated a maximu m of four factors. Reliability analysis of the four factors revealed good to moderate internal consistency for the first three factors as indicated by Cronbachs alpha reliability coefficients greater than 0.60 (Table 54), and low for the fourth factor, which was excluded from further analysis. Table 5 4 displays the items and factor loadings for the three factors, with loadings of less than 0.40 omitted to improve clarity. The three remaining factors explain 20% of the variance, with Factor 1 explaining the largest pe rcentage of the variance (12%). These resul ts provide limited support for h ypothesis 1, in that there is preliminary evidence (as provided by exploratory factor analysis) that at least three orientation s of wildlife values may exist among the study population, but they fall short of demonstrating the suggested eleven orientati ons. The three wildlife belief orientation s and their 9 See Vaske et al. (2002) for discussion of modifications to Cohens (1988) suggested labels for effect sizes in behavioral studies (small = minimal, medium = typical, large = substantial).

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148 relationship to other variables in the model should be interpreted with caution, as they have not undergone further analysis (e.g., confirmatory factor analysis) and they are based on variables with nonnormal distributions. The three composite basic belief scales were interpreted, based on item content, and labeled as new wildlife value orientations to be included in the predictive model. The first scale (Factor 1) was comprised predominantly of items originally operationalized as neutralistic and naturalistic (Table 5 4) An apt label for this new category is indifference. Factor 2 is dominated by negativistic items, although the statements are species specific, necessitating additional caution in interpretation. Factor 3 is fully comprised of dominionistic statements but based on the content of the items used to measure this orientation and knowledge of Maasai culture, it was renamed skills/bravery. A statistical comparison of voting intention groups on each value orientat ion is presented in Table 5 5. The groups differed significantly ( p < 0.001) on each orientati on, with the indifference orientation having much larger than typical effects ( d = 1.32), the skills/bravery orientat ion having larger than typical effects ( d = 0.79), and the negativistic orientation having typical effects ( d = 0.59). Scores could range from one to seven, with higher scores i ndicating a high level of indifference and low scores indicating lack of indifference. The allow group had lower indifference scores ( M = 3.41, SD = 1.42) than the not allow group ( M = 5.27, SD = 1.39). On the negativistic orientation both voting int ention groups scored high, with an overall mean of 6.13 ( SD = 1.40). The allow group was less negativistic ( M = 5.77, SD = 1.55) than the not allow group ( M = 6.55, SD = 1.07). The mean for skills/bravery orientation occurs at the neutral point ( M = 4.09, SD = 2.13) with the allow group having lower scores ( M = 3.36, SD = 2.07) than the not allow group ( M = 4. 92, SD = 1.88)

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149 Gender and age were statistically related to the indifference value orientation ( t = 19.46, p < 0.001, d = 1.62 and t = 4.30, p < 0.001, d = 0.36, respectively). Females ( M = 5.32, SD = 1.38) and older respondents ( M = 4.59, SD = 1.67) were more indifferent than males ( M = 3.20, SD = 1.23) and younger respondents ( M = 3.99, SD = 1.65). Gender, age, and group ranch were re lated to the negativistic orientation ( t = 12.11, p < 0.001, d = 1.02; t = 3.51, p < 0.001, d = 0.30; t = 3.87, p < 0.001, d = 0.36, respectively). Females ( M = 6.76, SD = 0.67), older respondents ( M = 6.35, SD = 1.27), and Olgulului residents ( M = 6.32, SD = 1.15) were more negativistic than males ( M = 5.48, SD = 1.65), younger respondents ( M = 5.94, SD = 1.50), and Kimana residents ( M = 5.79, SD = 1.73). On the skills/bravery orientation gender and group ranch were significant, suggesting that females ( M = 4.95, SD = 1.86) and Kimana residents ( M = 4.39, SD = 2.18) valued demonstrations of skills and bravery with wildlife more than males ( M = 3.20, SD = 2.02) and Olgulului residents ( M = 3.93, SD = 2.08) ( t = 10.70, p < 0.001, d = 0.90 and t = 2.46, p = 0.02, d = 0.22). Primary livelihood was not statistically related to any of the wildlife value orientation s. These results provide partial support for hypothesis 7. General A ttitudes t oward Elephants In the animal card sorting activity, 99.8% (all but one) of respondents reported seeing elephants in their group ranch. Of these respondents, 56% (n = 321) placed the elephant card in the dont like pile, 43% (n = 242) placed the card in the like pile, and 1% (n = 5) stated they neither liked nor disliked the elephant. Most respondents who reported liking elephants (80%) stated they would vote to allow elephants in the group ranch, while most who indicated they didnt like elephants (67%) stated they would vote to not allow elephants. The relationship is significant ( 2 = 119.58, p < 0.001), and this preliminary measure of attitudes toward elephants had a substantial effect on voting intention ( = 0.46)

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150 Exploratory factor analysis of the 25 belief statements regarding elephants produced a seven factor solution accounting for 37% of the variance. Examination of the scree plots indicated a maximum of two factors. Fourteen of the 25 belief statements compris ed the two factors, which are shown in Table 5 6, along with the factor loadings for the two rotated factors (loadings of less than .40 are omitted to improve clarity). The two factors explained 22% of the variance, with Factor 1 explaining the largest per centage of the variance (14%). Two elephant belief scales were computed to create elephant attitude dimensions. Reliability analysis revealed good to moderate internal consistency as indicated by Cronbachs alpha reliability coefficients greater that 0.65 (Table 5 6). The scales were interpreted, based on item content, and labeled negative (factor 1) and positive (factor 2). With attitude scores ranging from 1 to 7, the mean of the negative ( M = 4.39, SD = 1.64) and positive ( M = 4.41, SD = 1.49) dimens ions was close to the midpoint. However, the negative attitude scores formed a bimodal distribution, with large percentages of respondents on either side of the neutral point. This suggests that the mean has little value in interpretation of the results. A nother approach is to examine the percentages of respondents who scored above and below the mean. Using this method demonstrates that a majority (52%) of respondents scored higher on the negative dimension, with the remaining respondents scoring low (36%), or near the neutral point (12%). In comparison, 50% of respondents scored high on the positive dimension, 31% scored low, and 19% were neutral. A statistical comparison of the two voting intention groups on each attitude dimension is presented in Table 55. The groups differed significantly ( p = 0.001) on each dimension, with the negative dimension demonstrating much larger than typical effects ( d = 1.85) and the positive dimension having larger than typical effects ( d = 0.81). The not allow group scored higher on the negative attitude dimension ( M = 5.56, SD = 1.06) than the allow group ( M = 3.34, SD

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151 = 1.33) while the allow group scored higher on the positive dimension ( M = 4.94, SD = 1.30 ) than the not allow group ( M = 3.82, SD = 1.46) Each elephant attitud e dimension was included in the causal model to predict specific attitudes, norms, and behavioral intentions for allowing elephants in the group ranches (Figure 57) Age and gender were statistically related to the negative dimension of attitude toward elephants (hypothesis 7). Females ( M = 5.35, SD = 1.17) and older respondents ( M = 4.56, SD = 1.56) were more negative than males ( M = 3.38, SD = 1.44) and younger respondents ( M = 4.21, SD = 1.69; t = 17.86, p < 0.001, d = 1.50 and t = 2.54, p = 0.01, d = 0.22 respectively). For the positive dimension of attitudes toward elephants, males ( M = 4.56, SD = 1.34) and Kimana residents ( M = 4.93, SD = 1.58) were more positive than females ( M = 4.26, SD = 1.60) and Olgulului residents ( M = 4 .13, SD = 1.35) ( t = 2.41, p = 0.02, d = 1.00 and t = 6.08, p < 0.001, d = 0.54, respectively). Age was not significantly related to the positive dimension and livelihood was not related to either dimension. Specific Attitude toward Allowing Elephants i n Group Ranches Respondents could score between 9 and 9 on the measure of attitude toward elephants in the group ranches. The actual range was 8 to 9, with the overall mean occurring near the midpoint ( M = 0.38, SD = 3.26). Examination of the distribut ion revealed that those with an unfavorable attitude (42%) were generally less extreme in their attitude than respondents with a favorable attitude (45%). The mean scores for the voting intention groups for the beliefs and evaluations regarding allowing e lephants in the group ranches are graphically displayed in Figure 55. The charted scores generally indicate if the groups believe an outcome is likely or unlikely, and if the outcome is good or bad. The figure also provides a visual depiction of differenc es between groups. Table 57 shows significant differences in mean belief and evaluation scores between the

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152 vote groups. The groups differed significantly ( p < 0.05) on five of the eight outcome beliefs. For the other three outcome beliefs, mean scores sug gest that both vote groups believe that allowing elephants in the group ranches will increase potentially dangerous encounters with elephants, cause more tourists to visit the group ranches, and increase the number of elephant speared by Maasai ( Figure 5 5). Measures of effect size show larger effects for the beliefs that allowing elephants will increase peoplepeople conflict ( d = 0.64) and increase costs to local people ( d = 0.52). The groups differed significantly ( p < 0.05) on all but one of the evaluat ions of outcomes (increasing the number of elephants speared by Maasai) (Table 5 7). Effect sizes were minimal for six of the eight evaluations. The largest difference between the vote groups was for allow elephants to increase in number ( d = 1.42). The re was a substantial effect for increase opportunities to see elephants ( d = 0.71). The mean scores for the summed belief evaluation product scores for each group are visually represented in Figure 5 6, with statistical comparisons in Table 5 7. The gr oup means for the belief evaluation product scores differed significantly ( p < 0.05) for all but one outcome (increase the number of elephants speared by Maasai). Effect sizes ranged from minimal ( d = 0.14) to much larger than typical ( d = 1.20), with a llow elephants to increase in number having the largest effect. The average of the belief evaluation scores for each respondent was used to create individual attitude scores. Attitude scores could range from 9 to +9. The overall mean for attitude toward allowing elephants in the group ranches was 0.38 ( SD = 3.26). The mean attitude score for the allow group ( M = 1.74, SD = 3.07) was significantly more positive than the mean attitude of the not allow group ( M = 1.18, SD = 2.71; t = 12.05, p = 0.001 equal va riances not assumed) (Table 5 5). Outcomes most strongly associated with support for allowing elephants in the group ranches included: cause more tourists to visit group ranch,

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153 increase opportunities to see elephants, and allow elep hants to increase in number. While those opposed to allowing elephants in the group ranches also thought these outcomes were likely, they were less positive in evaluating these outcomes, especially allow elephants to increase in number. Although males ( M = 0.72, SD = 3.05) were significantly more positive toward allowing elephants in the group ranches than females ( M = 0.06, SD = 3.42), the effect size was minimal ( t = 2.40, p = 0.02, d = 0.20). Age, l ivelihood, and group ranch were not statistically re lated to attitude toward allowing elephants. Subjective N orm A total of 568 respondents named at least one referent, with 95% naming at least four and 87% naming five. The referents most frequently identified by respondents were immediate family members. Most respondents (78%) named their fathers and/or mothers, and many named brothers (44%) and husbands (75% of women). Other individuals frequently mentioned included elders and local leaders (n = 163), friends and age set members (n = 152) children (n = 151), brothers in law (n = 123), fathers in law (n = 116), and mothers in law (n = 106). There were several other person types named as important referents, highlighting the variation that could have been lost with a fixed list of potential referents. Norm scores could range from 12 to +12, with negative scores indicating a norm against allowing elephants in the group ranches and positive scores indicating a norm of support. The overall mean was 4.29 ( SD = 8.05). There was a significant difference ( p = 0.001) between voting groups, with those who would vote to allow elephants having a substantially higher norm score than those who would vote against allowing elephants (Table 55). Voting groups also differed significantly (p < 0.05) on the two components of the norm measure: the normative belief, where scores could range from 3 to +3, and the motivation to comply, where scores could

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154 range from 1 to 4 (Table 55). Respondents in favor of allowing elephants believed that their referents would more strongly approve of him/her allowing elephants in the group ranch than those who were against allowing elephants. Although there was a significant difference ( p = 0.04) between voting intention groups in motivation to comply, both groups indicated a high level of mot ivation to comply (Table 55). Gender and group ranch were the only significant demographic predictors of the norm for allowing elephants ( t = 6.31, p < 0.001, d = 0.53 and t = 3.73, p < 0.001, d = 0.32). Men ( M = 6.42, SD = 7.38) and Kimana residents ( M = 5.93, SD = 7.19) were more likely than women ( M = 2.27, SD = 8.16) and Olgulului residents ( M = 3.41, SD = 8.36) to have a stronger norm for allowing elephants in the group ranches. Prior E xperience Table 5 8 shows differences between vote groups for each measure of prior experience with elephants. Respondents were evenly divided when asked if they liked seeing elephants in the group ranches, with 284 individuals stating they liked to see elephants and 284 stating they did not like to see elephants. Those who liked seeing elephants in their group ranch were significantly ( p = 0.001) more likely to vote to allow elephants in the group ranch than those who did not like seeing elephants. Gender was the only demographic variable associated with this positiv e experience measure. Men were more likely than women to report that they enjoyed seeing elephants ( 2 = 84.66, p < 0.001, = 0.39). The most frequently cited reasons for liking to see elephants included: elephants draw tourists (n = 168), elephants are a ttractive (n = 34), they have always been here/God put them here (n = 16). The primary reasons for not liking to see elephants were: elephants are dangerous to people (n = 188), elephants injure/kill livestock (n = 103), elephants destroy crops (n = 26) and elephants break trees (n = 21).

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155 Most respondents (93%) indicated they had problems with wildlife in general during the animal card sorting activity. Of these respondents, less than half (47%) identified the elephant as one of the problem species, but la ter in the interview, when questions were specific to interactions with elephants, this number increased significantly ( 2 = 192.60, p < 0.001, = 0.58), with 65% of all respondents stating that elephants had caused them problems. Men were more likely tha n women to report having problems with elephants ( 2 = 36.28, p < 0.001, = 0.25), with 77% of men and 53% of women reporting direct negative experience. Respondents in Kimana (82%) were more likely than respondents in Olgulului (57%) to report that elephants cause them problems ( 2 = 40.53, p < 0.001, = 0.27). Other demographic variables were not associated with prior negative experience with elephants. There was not a statistical relationship between the second negative experience measure and voting intention (Table 5 8). Table 5 9 shows the locations where respondents reported seeing elephants and, if they see them in a location, if they liked or disliked seeing them there. Most respondents (91%) reported seeing elephants in the bush, about half see them near their home, and about one fifth (21%) see them near waterholes. Few respondents (5%) reported seeing elephants near their shamba. A majority (62%) of those who see elephants in the bush stated that they like to see them in this location. Most respo ndents who reported seeing elephants near their home, at waterholes, or near their shamba, stated they did not like to see them in these locations. Knowledge of E lephants The mean score for responses to the ten general knowledge statements regarding eleph ants (Table 5.10) was 7.37 ( SD = 1.51), with males having significantly higher scores ( M = 7.85, SD = 1.55) than females ( M = 6.92, SD = 1.32) ( t = 7.65, p < 0.001, d = 0.65). Other demographics were not statistically related to knowledge. There was a significant difference

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156 between the knowledge scores of voting intention groups ( t = 7.44, p < 0.001, d = 0.62). Individuals who would vote to allow elephants had higher knowledge scores ( M = 7.8, SD = 1.41) than those who vote to not allow elephants ( M = 6.9, SD = 1.47). Table 510 shows that respondents, in general, had a good understanding of the elephants dietary requirements and its role as an ecosystem engineer, but less understanding of their social behavior Risk P erceptions Table 5 11 displays the results of the series of questions regarding risk beliefs associated with elephants. About half (51%) of respondents believed that HEC had increased in the previous five years, while 26% believed it had stayed at the same level and 23% believed it had decreased. The relationship between voting intention and ones belief regarding the level of HEC in the previous five years was significant, but the effect size was minimal ( 2 = 14.64, p = 0.002, = 0.16). The not allow group was more likely to believe that HEC had increased than the allow group. Men, older respondents, and Olgulului residents were more likely to believe there was an increase in problems with elephants than women, younger respondents, and Kimana residents ( 2 = 8.49, p = 0.04, = 0.13; 2 = 9.06, p = 0.03, = 0.13; 2 = 14.79, p = 0.002, = 0.16, respectively). Less than half (45%) of respondents felt their personal safety was at great risk, while 28% believed there was a small amount of risk to their personal safety and 27% believed they were at no risk at all. Results were similar when respondents were asked about the risk to their livelihoods, with 49% stating their livelihood was at great risk, 27% stating there was a small risk, and 23% stating their livelihood was not at risk. There was a significant relationship between voting intention and beliefs about risks to personal safety and livelihood, with minimal effect sizes ( 2 = 16.76, p = 0.001, = 0.17 and 2 = 18.56, p = 0.001, = 0.18, respectively). A

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157 higher percentage of not allow respondents believed their personal safety and livelihood were at great risk. Kimana residents (58%) were more likely than Olgulului residents (38%) to feel the ir personal safety was at risk, while Olgulului residents (30%, 32%) were more likely than Kimana residents (24%, 17%) to feel their personal safety was at little or no risk ( 2 = 25.54, p < 0.001, V = 0.21). There were no statistical differences between gender, age, or livelihood and personal and livelihood risk beliefs. About half of respondents stated that they worry about problems with elephants a great deal, while 26% stated they only worried a little and 24% s tated they did not worry at all. There was a significant relationship between voting intention and level of worry regarding HEC among respondents ( 2 = 26.13, p = 0.001, = 0.22), with the not allow group reporting a higher level of worry. Women (52%, 28%) were more likely than men (49%, 23%) to report worrying about problems with elephants a great deal or a little, while men (29%) were more likely than women to state they did not worry at all ( 2 = 7.41, p =0.03, V = 0.11). Kimana residents (63%) we re more likely than Olgulului residents (44%) to state that they worry about elephant problems a great deal, while Olgulului residents (29%) were more likely than Kimana residents (15%) to state that they did not worry at all ( 2 = 22.11, p < 0.001, V = 0.20). Age and livelihood were not statistically related to worry. When asked about the general controllability of problems with elephants, 39% of respondents stated that problems were very controllable, 19% believed they were somewhat controllable, 39% s tated they were not at all controllable, and 4% stated that they did not know if they were controllable. There was not a statistical relationship between voting intention and ones belief regarding the general controllability of HEC ( 2 = 3.29, p = 0.35, = 0.08). Women and men had significantly different beliefs regarding the level of controllability of elephant

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158 problems ( 2 = 7.41, p = .03, = .11), with women more likely to believe that elephant problems were controllable. Kimana residents (48%, 26%) w ere more likely than Olgulului residents (33%, 14%) to believe problems were very or somewhat controllable, while Olgulului residents were more likely to believe elephant problems were not at all controllable ( 2 = 40.59, p < 0.001, V = 0.27). There w as not a statistical relationship between controllability and age or livelihood. Most respondents (95%) did not feel they were personally able to reduce problems with elephants. There was not a relationship between voting intention and ones belief regardi ng their personal ability to control problems with elephants ( 2 = 0.02, p = 0.88, = 0.01). Gender was the only demographic variable with a statistical relationship to belief regarding personal ability ( 2 = 5.11, p = 0.02, = 0.10), with men (6%) slightly more likely than women (2%) to believe they were personally able to reduce elephant problems. HEC Mitigation I nterventions Most respondents (94%) believed that elephants bring costs to people in their group ranch (Table 5 12). The most often cited cost was the injury or death of a person (n = 409), followed by injury or death of livestock (n = 387), damage to trees (n = 226), and crop losses (n = 155). Other costs included competition for water (n = 54), damage to fences ( n = 38), damage to other property (n = 36), chasing people (n = 34), interference with travel on foot (n = 33), and competition for grazing (n = 29). While only a small number of individuals (n = 26) believed that elephants do not bring costs to people in the group ranch, those who held this view were more likely to vote to allow elephants than those who did not (Table 512). There was no statistical relationship between perceived costs and gender, age, livelihood, or group ranch.

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159 A majority (62%) of respondents believed that elephants brought benefits to people in their group ranch. The most frequently mentioned benefit was attraction of tourists (n = 235), followed by school bursaries (n = 117), and the creation of jobs (n = 87). There was a substantial relationship ( = 0.59) between perception of benefits from elephants and intention to vote for elephants, with those believing there were benefits being more likely to vote to allow elephants than those who did not believe there were benefits brought by elephants. Men (85%) were more likely than women (44%) to believe that there were benefits to having elephants in the group ranch ( 2 = 99.43, p < 0.001, = 0.43). Only 36% of respondents believed their household directly received tourism benefits, wi th those who believed they received benefits being more likely to vote to allow elephants than those who did not believe they received benefits. Men (n = 130) were more likely than women (n = 75) to believe their household received tourism benefits ( 2 = 1 9.89, p < 0.001, = 0.19). Age, livelihood, and group ranch were not related. Results indicate that 56% of respondents (n = 318) were aware of organizations in Amboseli that assist people who experience problems with elephants, while 31% (n = 173) were not aware and 13% (n = 75) stated they did not know. The primary groups named were the Government of Kenya (GOK), KWS, and AERP (Table 513). Other groups mentioned included AWF (n = 7) and the Game Scouts Association (n = 6). For the purposes of this analys is, the GOK and KWS were combined, as KWS is a government parastatal, or stateowned enterprise, and many respondents viewed them as one in the same (pers. observ.). Based on this, the GOK/KWS was the organization most often named by respondents as helping people with HEC, followed closely by AERP (Table 5 13). Respondents who were aware of these organizations were more likely to vote to allow elephants in the group ranches than those who lacked such awareness (Table 5 12). There was a substantial and signi ficant difference between men and

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160 women ( 2 = 79.47, p = 0.001, = 0.37), with 75% of men and 38% of women stating there were organizations helping people with elephant problems. Younger respondents (64%) were more likely than older respondents (47%) to be aware of organizations with interventions ( 2 = 15.83, p = 0.001, = 0.17). Livelihood and group ranch were not related to awareness of organizations. There was a considerable amount of confusion regarding the actions or interventions taken by each org anization. Table 513 shows that several people erroneously believed that the GOK and KWS pay for livestock losses. The only action the government takes in relation to HEC is to pay compensation for loss of human life. Other misconceptions include the beli ef that organizations other than the GOK pay compensation for loss of human life and that AERP shoots problem elephants. The only organization with a mandate to shoot wildlife is KWS. Of the respondents who were aware of these organizations, only 20% (n = 65) reported ever asking for help with elephants. Most of these individuals had requested help from either KWS (n = 30) or AERP (n = 28). Eighteen people who requested assistance from KWS reported feeling unsatisfied with the organizations actions, while one individual felt neutral, and 10 reported feeling satisfied. Fourteen people were satisfied with AERPs actions and 12 were unsatisfied. Approximately 50% of respondents (n = 282) were aware of the electric fences. Most of these respondents (87%, n = 245) believed the primary purpose of the fence was to keep wildlife out, with 37% (n = 91) of these respondents specifically mentioning elephants. Almost all (99%, n = 280) believed that the fences did a good job, even though a majority of people listed pro blems with the fences (e.g., no electricity). Respondents with awareness of the fences were more likely to vote to allow elephants in the group ranches (Table 5 12). Gender and livelihood were significantly related to awareness of the electric fences ( 2 = 10.62, p = 0.01, = 0.14 and

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161 2 = 27.96, p < 0.001, = 0.23, respectively). More men (56%) and cultivators (68%) knew of the fences than women (44%) and pastoralists (42%). Kimana residents (94%) were more likely than Olgulului residents to be aware of the fences ( 2 = 232.39, p < 0.001, = 0.64). Age was not related to awareness of the fences. A large majority of respondents (90%, n = 511) correctly stated that their group ranch had at least one cultural boma, with 9% (n = 51) stating their group ranch did not have any cultural bomas and 1% (n = 6) stating they did not know. Of those who knew of the cultural bomas, 96% (n = 493) perceived benefits associated with the bomas, with the most frequently named benefit being generation of revenue/employm ent (n = 477). Some respondents (n = 56) believed there were costs associated with having cultural bomas, including exploitation of the Maasai, changes in Maasai culture, and transmission of sexually transmitted diseases. Respondents who were aware of the cultural bomas were more likely to vote to allow elephants in the group ranches (Table 5 12). Men (97%) were more likely than women (83%) to be aware of the cultural bomas ( 2 = 38.33, p = 0.001, = 0.26). Age, livelihood, and group ranch were not related to awareness of the bomas. Finally, a majority of respondents (61%, n = 344) felt that receiving money for elephant damage made people more tolerant of elephants in the group ranches, while 36% (n = 203) did not believe it increased tolerance, and 4% (n = 20) stated that they didnt know. Respondents who believed money for elephant damage increased tolerance were significantly more likely to vote to allow elephants in the group ranches than those who did not agree (Table 512). Men (80%) were more likely than women (42%) to believe elephant damage compensation increases tolerance of elephants ( 2 = 86.33, p < 0.001, = 0.39). Age, livelihood, and group ranch were

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162 not statistically related to ones belief regarding the influence of damage compensation on tolerance of elephants. The Model Results of the path analysis are visually represented in Figure 5 7. The path coefficients shown in the figure are limited to the paths between cognitive variables, and the R2 values indicate the variance explained by all of the independent variables represented in the figure. Results of the dummy variable regression analyses indicated that gender was the only variable that significantly predicted the indifference value orientation ( = 0.63, t = 19.42, p = 0.001) and expl ained 40% of the variance. The negativist ic and the skills/bravery orientations were predicted by gender ( = 0.46, t = 12.60, p < 0.001 and = 0.41, t = 10.74, p < 0.001, respectively) and group ranch of residence ( = 0.19, t = 5.07, p < 0.001 and = 0.10, t = 2.57, p = 0.01, respectively), partially supporting hypothesis 7. These results suggest that women had a higher level of indifference toward wildlife, were more negativistic, and had a higher value for demonstrations of skills and bravery with wildlife, while residents of Kimana were less negativistic and had a higher value for skills and bravery. Results of the multiple regression analyses for the attitude and norm variables are shown in Table 5 14 and Figure 57. The negative dimension for general attitude toward elephants was predicted by the indifference wildlife orientation, the skills/bravery wildlife value orientat ion, gender, prior negative experience, worry, knowledge, and awareness of organizations with HEC interventions. This combina tion of variables significantly predicted the negative attitude dimension, with 62% of the variance explained. The beta weights presented in Figure 57 and Table 5 14 suggest that the indifference wildlife value orientation contributed the most to predicti ng the negative dimension of attitude towards elephants, with respondents who had a

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163 higher level of indifference toward wildlife being more negative toward elephants. Respondents who were more indifferent toward wildlife, female, had a higher value for ski lls and bravery related to wildlife, had negative experience with elephants, were not aware of organizations with HEC interventions, had less knowledge of elephants, and had a higher level of worry were more likely to have a negative attitude toward elepha nts. The positive dimension of attitude toward elephants was predicted by group ranch of residence, worry about elephant problems, gender, prior negative experience, awareness of organizations with HEC interventions, and the indifference value orientation (Table 5 14, Figure 57). These variables explained 22% of the variance, with group ranch demonstrating the most predictive ability (Table 5 14). Respondents who lived in Kimana, had a lower level of worry, were female (unexpected result see below), had a wareness of organizations with HEC interventions, did not have negative experience with elephants, and who were less indifferent toward wildlife scored higher on the positive dimension of attitudes toward elephants. Attitude toward allowing elephants in t he group ranch was predicted by gender, the positive dimension of attitude toward elephants group ranch, the belief that compensation for elephant damage increases tolerance, awareness of the electric fences, prior negative experience, the skills/bravery value dimension, worry, the negativistic wildlife value orientation, and the negative dimension of attitude toward elephants (Table 514, Figure 57). These variables explained 37% of the variance in attitude, with the negative dimension of attitudes towar d elephants contributing the most to this prediction. The negative coefficient for gender suggests that females were more likely to have a positive attitude toward allowing elephants in the group ranch, contradicting earlier t test results showing men were more likely to be in favor of allowing elephants than women. This is most likely attributable to response distributions, with the

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164 distribution for females being moderately) skewed to the left (skewness = 0.60). More specifically, a larger number of women had negative attitude scores than positive scores, but negative scores were less extreme than positive scores. With this caveat in mind, the regression results suggest respondents who were female, had higher scores on the positive dimension of attitudes toward elephants, were residents of Kimana group ranch, believed that compensation increases tolerance, were not aware of the fences, did not have negative experience with elephants, were low on the skills bravery orientation, had less worry about elephant s, were low on the negativistic dimension and the negative dimension of attitude toward elephants were more positive toward allowing elephants in the group ranch. The norm for allowing elephants in group ranches was predicted by the positive elephant attitude dimension, the negative elephant attitude dimension, and group ranch of residence, explaining 30% of the variance (Table 5 14, Figure 57). The negative dimension of attitudes toward elephants was the strongest predictor of norm, with those with a more negative attitude having a lower norm for allowing elephants in their group ranch. Individuals who were residents of Kimana and were higher on the positive dimension of attitudes toward elephants were more likely to have a higher norm for allowing elephants. None of the wildlife value orientation s were predictors of the norm variable. Logistic regression was used to test two models of the relationships between intention to vote to allow elephants, and attitudes toward elephants, attitudes toward allowing elephants, and norms regarding allowing elephants. The first model generated in the logistic regression analysis tested the TRA, i.e. it did not include the general attitude variables. It revealed that attitude toward allowing elephants in the group ranch (specific) and norm significantly predicted intention to vote to allow elephants in the group ranches ( 2 = 180.82, p < .001), explaining 37%

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165 of the variance. Table 5 15 presents the odds ratios, which suggest that the odds of voting to allow elephants in crease as attitude toward allowing elephants and norm for allowing elephants increase. The model was able to correctly classify 79% of respondents who would vote to allow and 71% who would vote to not allow elephants in the group ranches, with an overa ll success rate of 75%. The second model produced by logistic regression, which included the addition of attitude toward elephants (general), revealed that both the positive and the negative dimensions of attitude toward elephants, attitude toward allowing elephants, and norm for allowing elephants, significantly predicted intention to vote to allow elephants in the group ranches ( 2 = 348.35, p < .001). Table 515 shows that in addition to the previously described effects of specific attitude and norm, t he odds of voting to allow elephants are increasingly greater as the positive dimension of attitude toward elephants increases. Overall, 82% of respondents were correctly classified by voting intention. Figure 5 7 depicts the relationships in this second m odel and shows that 62% of the variance in voting intention is explained by the four predictor variables. Future L ivelihood A ctivity A considerable percentage (16%) of respondents who identified pastoralism as their primary livelihood activity indicated that they planned to shift to agriculture within five years. Table 5 16 shows the current and future livelihood activities reported by respondents. More than half (57%) of respondents stated that pastoralism would be their households primary livelihood activity in five years, with 35% identifying cultivation as their primary future livelihood activity. The remaining respondents identifi ed other activities (7%), such as working in a cultural boma or wage labor, or stated that they did not know (1%). There was a significant difference between

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166 current and future primary livelihood activity ( 2 = 301.14, p < .001, V = .52), with a decrease i n those planning to depend primarily on pastoralism and an increase in those planning to be primarily dependent on cultivation. Discussion The overall purpose of this chapter was to examine the antecedents of willingness to allow elephants on private la nd by using an integrated predictive model of behavior. A second goal was to test the transferability of theory and methods developed in the West to a rural African setting. The cognitive hierarchy provided a theoretical framework of cognitive variables in which to integrate additional variables found to be related to attitudes and behavior in previous human dimensions research. The model was tested using data from a survey of 569 people, of which a slight majority stated that they would vote to allow eleph ants in the group ranches. Overall, the survey results support the conceptual relationships posited by the cognitive hierarchy and t he addition of several external variables, such as demographics, worry, and awareness of HEC mitigation which were found to be important in explaining variation in value orientation s, attitudes, and norms regarding willingness to tolerate elephants on private land. Wildlife Value Orientat ions Kellerts (1980) typology of attitudes toward animals was used as the conceptual framework for measuring wildlife value orientations. A concern with the typology has been whether the measurement items are reliable and valid. Similar to other studies ( Drews 2002; Frost 2000; Mordi 1987; Rauwald and Moore 2002), the theorized attitude ty pes collapsed together in factor analysis, producing only three reliable factors and only partially supporting hypothesis 1. While all of the value types proposed by Kellert (1980) and Mordi (1987) did not prove to be distinct orientation s among the Maasai of Amboseli, three meaningful orientations were identified and contributed to the prediction of attitudes toward elephants and allowing

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167 elephants in the group ranch, partially supporting hypothesis 2. However, norms were not predicted by the value orienta tion s as postulated in hypothesis 3. The orientation explaining the most variance, the indifference value orientation (neutralistic/naturalistic), provides empirical support for anecdotal descriptions of Maasai indifference toward wildlife (Myers 1973, We stern 1994) Although it could also be interpreted as representing a spectrum from highly indifferent (Going outdoors just to see wild animals is a waste of time) to not at all indifferent (When I am walking in the bush, I enjoy seeing wildlife around) or, in other words, appreciative. This orientation was the strongest predictor of the negative dimension of attitude toward elephants. The second wildlife value orientation identified by factor analysis suggests a degree of negativity toward, at least, certain species of wildlife. Although a positive orientation was not identified, there is evidence in Maasai culture of species preferences. According to Berger (1993), species such as the hedgehog and the mole are bringers of good luck and species such as the jackal and the cape hare bring bad luck. During focus groups, several individuals described positive and negative characteristics of certain animals, such as the greedy hyena that kills more livestock than it can eat or the polite giraffe that b rings no harm. The third orientation was based on three items intended to measure Kellerts dominionistic orientation but based on the content of the items used to measure this orientation and the traditional view of wildlife belonging to God (Berger 1993) and, today, the government (pers. observ.), dominionistic may not be the most appropriate label for this orientation For example, the time honored tradition of the olamayio, the lion hunt of the ilmurran to test bravery is more representative of Rolst ons (1985; 1988a,b) recreational and character building values, where an individual is interested demonstrating skills and finding ones place under the

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168 sun. Two of the dominionistic meas urement items in the survey refer to lion hunting. Therefore, this orientation was labeled skills/bravery. The existence of the skills/bravery wildlife value orientation has potential implications for Amboselis elephants, as elephants are also speared by ilmurran for the purpose of demonstrating skills and bravery (Kangwana 1993; Bates et al. 2007). The Amboseli elephants have demonstrated avoidance behavior in experiments using playback sounds of Maasai cow bells, the presence of ilmurran, olfactory cu es (worn Maasai clothes), and visual cues (typical bright red Maasai clothing) (Kangwana 1993; Bates et al. 2007). Kangwana (1993) suggested that spearing may influence elephant avoidance of the Maasai, although individual elephants with experience with sp earing have demonstrated a variety of responses (Bates et al. 2007). The value of the elephant to the Maasai for demonstrating skills and bravery combined with the avoidance response of elephants when encountering signs of Maasai presence point to the pote ntial of maintaining fear of the Maasai among elephants as a way to reduce HEC. Further research into this area may provide additional, site specific tools for mitigating HEC. The failure of the Kellert type items to capture a positive dimension, or the other Kellert categories, could be attributable to conceptual or measurement issues, or both. Further pretesting may have clarified this issue. It is possible that some of the Kellert value types simply do not exist among the Maasai, although some of the ot her value types conceptualized by Kellert were evident. Factor analysis produced two additional factors that were wholly comprised of the intended measurement items, the moralistic and theistic value types. Each of these scales had low reliability ( = 0.49 and 0.43, respectively), but they each contained only three measurement items. When added to the model, they explained a minimal, but statistically significant, amount of variance in attitudes and norms. It is noteworthy that the theistic value, in particular, did not

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169 prove to be a significant factor, given the deep religiosity among the Maasai. This result perhaps supports suggested problems with measurement. Future research using the Kellert value types, or other approaches currently under exploration (e.g., see Teel et al. 2007), should improve the reliability and validity of measurement items and, in turn, our understanding of value orientations among cultur es in the developing world. General Attitudes Toward Elephants Two dimensions of attitudes toward elephants, based on beliefs regarding elephants, were indentified a negative dimension and a positive dimension. The two general attitude dimensions predi cted specific attitudes, norms, and behavioral intentions regarding allowing elephants in group ranches, fully supporting hypothesis 4. The negative dimension was the strongest predictor of attitudes and norms for allowing elephants in the group ranches. K nowledge of the underlying belief structures of the attitude dimensions provides managers and conservationists with information for developing interventions. That is, addressing potential misconceptions regarding elephants may help improve attitudes and influence subsequent variables in the cognitive hierarchy. For example, respondents with a high score in this dimension tended to believe that the only reason elephants come out of the park is to disturb people and that elephants are always angry toward p eople. They did not believe that elephants have an important role in the environment. The inclusion of the general attitude variable in the model demonstrated that, in the current research setting, general attitudes toward elephants greatly improved the prediction of intention to allow elephants in the group ranches, with the positive dimensions serving as the strongest predictor of behavioral intention. There are a number of possible explanations for the strong influence of general attitudes, as the rel ationship between general attitudes and specific

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170 behaviors is influenced by several variables (Eagly and Chaiken 1993). Consistent with previous research, two of these variables, direct experience with and knowledge of the target (which may be increased wi th direct experience), were found to be significant predictors of attitudes toward elephants. The Maasai of Amboseli have a high level of experience with and knowledge of elephants, allowing for highly accessible, easily activated attitudes. In such situat ions, research has found that individuals may rely on spontaneous rather than deliberative processing (see Fazio 1995; Fazio and Towles Schwen 1999). This finding supports the continued examination of the role of general attitudes, or attitudes toward targ ets, in predicting behavior, including the effects of potential mediators and moderators of the attitude behavior relationship (Eagly and Chaiken 1993). It also suggests direction for conservationists and managers in planning interventions. Given that the positive dimension of attitude toward elephants was the strongest predictor of intention to vote to allow elephants and the negative dimension was the strongest predictor of attitudes and norms for allowing elephants interventions aimed at improving attitudes toward elephants may increase overall tolerance. Additionally, understanding the processes (e.g., spontaneous vs. deliberate) which guide the attitude behavior relationship may inform the design of interventions For example, program planners could target individuals with negative attitudes toward elephants for persuasive communications that provide the motivation and opportunites for more careful thought about potential positive outcomes of tolerating elephants Specific Attitudes toward Allowing Elephants in Group Ranches Respondents were fairly evenly divided in their attitudes toward allowing elephants in the group ranches, with a significant percentage of individuals falling into the neutral category. This attitude measure was the second strongest predictor of intention to vote to allow elephants (hypothesis 5). It was based on beliefs and evaluations of potential outcomes of having elephants in the group ranches. For instance, respondents against tolerating elephants believed that

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171 allowing elephants would increase people people conflict and costs to local people, suggesting that efforts to foster favorable attitudes should address these and other beliefs that underlie negative attitudes. There were several i ndependent variables that predicted respondents attitudes toward allowing elephants, with the negative dimension of attitude toward elephants having the most substantial relationship, followed by gender and the positive dimension of attitude toward elephants. Several external variables (discussed below) were less strongly associated with attitude toward allowing elephants, but demonstrate the complexity of, and opportunities for, increasing tolerance. Subjective N orm Human dimensions research (Campbell and Mackay 2003; Hrubes et al. 2001) and research in other fields of study (Ajzen 1991; Armitage and Conner 2001; Farley et al. 1981) have found that subjective norm is a weaker predictor of behavior than attitudes Suggested explanations include concerns of conceptualization and measurement (Manfredo 2008; Terry and Hogg 1996), and different person types (Trafimow and Finlay 1996). Conceptualization was not anticipated to be an issue in the current study, given the collectivist nature of Maasai culture. Two measurement concerns cited in the literature, the use of modal salient referents (Terry et al. 2000) and the use of a global measure of subjective norm (Armitage and Conner 2001), were addressed in my study by allowing each respondent to free list their re ferents and by creating an index measure of norms. Results suggested that subjective norm was a strong predictor among the Maasai of intention to vote to allow elephants in their group ranches (hypothesis 6). This finding provides support for the assertion that norms can play a stronger role in influencing behaviors in collectivist cultures, such as the Maasai culture, than in individualistic cultures, and that the measurement procedure suggested by Ajzen and Fishbein (1980) is a valid one.

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172 Norms for toler ating elephants were based on beliefs regarding respondents perceived social pressure to tolerate or not tolerate elephants. Family members were most often identified as referents, and there was a strong motivation to comply with referents among both voti ng intention groups. These results suggest that interventions, including education and communication programs, may be improved by targeting social networks, including families, agesets, and group ranches associations. The negative dimension of attitude toward elephants was the strongest predictor of norm; therefore, efforts aimed at improving attitudes toward elephants may increase the norm for allowing elephants in the group ranch. Demographics This analysis examined the influence of four demographic var iables: gender, age, primary livelihood activity, and group ranch of residence. Similar to other studies (Vaske et al. 2001), including demographic variables in the model provided an understanding of who holds which beliefs regarding wildlife, elephants in particular, and tolerance of elephants in the group ranches (hypothesis 7). As expected, gender proved to be an important variable across analyses as the only demographic variable with a significant relationship with each dependent variable in the model, including wildlife value orientation s. A few studies have examined the determinants of environmental value orientations (Bright et al. 2000; Manfredo and Zinn 1996; Mohai 1992; Steel et al. 1994; Vaske et al. 2001). Of these, causal models have identified gender, education, income, and length of residence as influences on value orientations (Vaske et al. 2001; Steel et al 1994). In the present analysis, gender was the strongest of two predictors of value orientations, with women scoring higher than men on all three scales, indicating that they were more indifferent (less appreciative), more negativistic, and had a higher value for demonstrations of skills and bravery. Women also had more negative attitudes toward elephants. This is contrary to findings in N orth America, where women tend to be more environmentally oriented (Mohai

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173 1992; Vaske et al. 2001; Steger and Witt 1989), but consistent with other research in Africa (Gillingham and Lee 1999). This could be attributable to several factors including gender ed differences in resource use, interactions with wildlife, and access to knowledge and conservation benefits (Hunter et al. 1990; Nabane and Matzke 1997; Ogra 2008). Maasai women had a lower level of knowledge of elephants, were less likely to perceive benefits associated with elephants, had a higher level of worry about HEC, and had less awareness of HEC interventions, pointing to the need for increased efforts to address the concerns of women, include them in outreach and planning processes, and increase their perceived and actual benefits. Group ranch of residence was a significant predictor of several variables, including two of the value orientations, attitudes toward elephants and allowing elephants, norm, and several risk beliefs. Interestingly, Kima na residents were more positive toward elephants and had a stronger norm for allowing elephants in the group ranch, even though they were more likely to report problems with elephants, perceived a higher personal safety risk, and had a higher level of worr y. This may be partially explained by the belief that elephant problems are controllable, the belief that elephants bring benefits (not statistically different from Olgulului residents), and awareness and a positive evaluation of the two electric fences in the group ranch. Age and livelihood were predictors of a more limited set of variables. For instance, older respondents were more negative toward wildlife in general and to elephants specifically. This is contrary to the earlier findings of Kangwana (19 93), who found older respondents to be more positive. A possible explanation for this difference is that older respondents in my survey were more likely to believe that HEC had increased in recent years and were less aware of organizations providing HEC mi tigation interventions.

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174 I nformation on differences between demographic groups can be used by conservation professionals to more effectively develop conservation and conflict mitigation interventions. It can be used to target specific segments of the popul ation and better predict responses of members of these groups to potential management policies (Bright et al. 2000). The present analysis, although limited to only four demographic variables, suggests communication and education needs for different segment s of the population. Examination of additional demographic variables (e.g., wealth) may improve the ability of planners to target interventions. Future research should also sample a larger portion of the nonMaasai population to consider differences between ethnic groups. Prior E xperience Respondents were evenly divided in whether or not they liked to see elephants (positive experience) in the group ranch. The primary reason for liking to see elephants was that elephants draw tourists, and the most oft ci ted reason for not liking to see elephants was the danger they pose to people. Positive experience did not predict attitudes, but negative experience, having problems with elephants, did (hypothesis 8). Respondents were asked about problems with elephants at two points in the interviews. On the first occasion, when questions were concerned with wildlife in general, 47% of respondents categorized the elephant as a problem animal. Later, when questions became more specific to elephants and humanelephant interactions, 65% of respondents stated that elephants caused them problems. It is unclear why this variation in responses occurred, but potential explanations may be related to questionorder effects (Schuman and Presser 1981). For instance, questions prior to the second negative experience question may have activated memories that were not immediately accessible at the t ime the first question was asked. Another possibility may be that when some respondents realized that the survey was

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175 becoming more focused on elephants, they were more likely to complain about elephants, given the local, national, and international attention focused on the Amboseli elephant population. While it is not possible to explain the variation in responses, it is important to be cognizant of it when interpreting related results. It was presumed that question order simply increased the salience of b eliefs regarding elephants and that bias was kept to a minimum with careful attention to question wording. The second measure of negative experience with elephants was used in the causal model, as this question was posed later in the interview, in closer proximity to the voting intention question, and it was based on a larger number of responses. Knowledge of E lephants The relatively high level of knowledge of elephants among the study sample provides support for the assertion that the Maasai are na tural ecologists (Berger 1993), possessing a high degree of ecological knowledge. Survey results demonstrated that men had a higher level of knowledge than women (hypothesis 9). Knowledge was a significant, albeit weaker, predictor of the negative dimensi on of attitude toward elephants (hypothesis 10). Education and communication are often the s uggested approach for influencing attitudes and behaviors (Gardner and Stern 1996; Jacobson 1999; Manfredo et al. 1995). Based on the current findings, efforts to i mprove knowledge of elephants would likely have a minimal impact on attitudes and behaviors toward elephants. Instead, such efforts would be better directed at improving knowledge of strategies for mitigating HEC (see below) which may, in turn, affect mot ivation, confidence, and locus of control (Boerschig and DeYo ung 1993; Hwang et al. 2000). Risk P erceptions The influence of several constructs related to risk perception associated with living alongside elephants was explored. The voting intention groups differed in their beliefs regarding the incidence of HEC, risks to personal safety and livelihood, and worry. They did not differ in

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176 their beliefs regarding the general controllability of HEC and their personal ability to control elephant problems, with nearly all respondents stating that they were not personally able to control elephant problems. Worry was the only riskrelated construct to remain in the predictive model, explaining a portion of the variance in each of the attitude variables, partially s upporting hypothesis 11. Although there is lack of perceived personal ability to manage elephant problems, most respondents indicated that problems with elephants are controllable to some degree, implying a belief that only others, most likely KWS, can manage elephant problems. Wildlife managers and conservationists are faced with the challenge of reducing actual and perceived risks of living alongside elephants. As previously mentioned, where there is low probability of an incident occurring, but potent ial for severe consequence, risk perceptions may increase (Decker et al. 2002). Such is the case with HEC, where elephants cause less damage to crops than other pest species, but a single raid can be catastrophic for some individuals (Naughton et al. 1999) Additionally, elephants are not the most dangerous animals in Africa, in terms of human mortality (Croze et al. 2007), but an encounter with an elephant can be fatal. Several approaches, past and present, have been utilized to reduce HEC in Amboseli, wit h most interventions aimed at physically reducing negative humanelephant interactions (e.g., fences) and offsetting the costs of HEC (compensation, promoting wildlife based tourism). While these approaches demonstrate some efficacy in reducing HEC, this e xamination of risk beliefs suggests that additional interventions aimed at reducing risk perceptions and increasing perceived controllability (general and personal) may improve attitudes and tolerance of elephants. These could include educating local peopl e on the actual risk level associated with elephants and current and potential methods for reducing negative humanelephant encounters.

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177 HEC Mitigation I nterventions Consistent with hypothesis 12, three HEC mitigation variables predicted attitudes. Awareness of organizations with HEC mitigation interventions was a significant predictor of the two dimensions of attitude toward elephants, but it did not directly predict attitude toward allowing elephants in the group ranches. Awareness of the fence s and the b elief that damage compensation increases tolerance contributed to the prediction of attitude toward allowing elephants in the group ranches. Overall, there was a considerable lack of awareness and understanding of HEC interventions. For example, just under half of the respondents surveyed were not aware of any of the organizations working to mitigate HEC, and, among those who were aware of these organizations, there was a significant amount of confusion regarding the specific interventions of each organizat ion. The fact that very few individuals named AWF was unexpected, given the organizations long history in the region and the amount of resources it directs toward its Kilimanjaro Heartlands Program. There is an overall need to improve the implementation of current strategies for reducing HEC and maintaining elephant habitat outside the park boundaries. First, program staff need to improve awareness and knowledge of interventions. The lack of awareness of organizations with HEC interventions underscores thi s need. The most frequently cited costs associated with elephants were injury and death to people and livestock, but only 26 respondents knew of the government compensation program for human injury and death, and only 88 correctly knew that AERP makes cons olation payments for livestock losses. Obviously, compensation for loss of a human life provides little solace, but it can, at least, alleviate some of the increased financial burden brought by funeral costs and loss of a source of income. While it is well known that rural Kenyans who suffer such losses are generally dissatisfied with the government compensation program, critical of both the claims process and the payment amount (KWS 2000; Sindiga 1995),

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178 improvement of this program may at least offset the c ommonly voiced belief that the government cares more about its wildlife than its people. Maasai pastoralists are becoming increasingly poor (BurnSilver et al. 2008) and are seeking ways to diversify their livelihoods. Wildlife authorities and conservationists have promoted wildlife based tourism as a way to address this need, but, as demonstrated here, a limited number of households perceive any direct benefits from tourism (nor do they actually receive such benefits Akama 1999, Bulte et al. 2008). It is evident that conservationists have been effective in communicating the tourism value of elephants in Amboseli by the large percentage of respondents offering this as their reason for being positive toward elephants and/or tolerating elephants. The question then is, if the tourism value of elephants is critical for toleration, how long will tolerance last if this benefit is never realized by the individual? Amboseli generates a substantial amount of revenue, especially in comparison to most othe r protected areas in Kenya. While tourism revenue may not be substantial enough to offset all costs (Barrett and Arcese 1995), increasing wildlife (and cultural) tourism benefits to the people who suffer the costs of tolerating wildlife and ensuring that they understand the link between benefits and wildlife conservation is imperative if wildlife based tourism is to be a viable tool in maintaining tolerance. The challenge is in determining who should receive these benefits and how should they be disbursed ( Archabald and NaughtonTreves 2001). Almost all of the respondents who were aware of the fences offered a positive evaluation of the fences. As recommended elsewhere (Kioko et al. 2008), improved maintenance of the electric fences is needed. A limitation in meeting this need is the uncertainty among respondents, including those who live in the fenced areas, as to who owns the fences and who is responsible for fence maintenance. The position of KWS is that the organization assisted the community in

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179 building the fence and, upon its completion, it became the property and responsibility of the community (P. Omondi, KWS, pers. commun). While most people who were aware of the fences had a positive evaluation of the fences, a limited number perceived personal owner ship or responsibility. The fences were effective in reducing crop damage up to the time of this study (Kioko 2004), but if problems with fence repair and maintenance are not addressed, the fences and their efficacy will likely decline, especially as more elephants become aware that the fences do not pose any harm to them (Hoare 2001). Further research is needed to address questions on this issue. For example, does the community have the knowledge and resources to maintain the fences? If not, what are the o ptions for funding fence maintenance (e.g., government or donor support) and providing training to community members? In addition to improving existing interventions, new approaches are needed that address the needs identified in this study, including addressing both perceived and actual risks, costs, and benefits associated with elephants, and changing erroneous beliefs regarding elephants upon which attitudes are based. Additional consideration should be given to gendered differences in the cognitive and contextual variables that influence tolerance of elephants. New measures should be developed in collaboration with local people (bottom up) rather than being imposed by outsiders (topdown), so there is a higher likelihood for increased tolerance and successful interventions (Gillingham and Lee 2003; Osborn and Parker 2003; Taylor 1993; Thouless 1999; Treves et al. 2006). This includes developing elephant and conflict management actions that are acceptable to local people.10 Finally, in order to regain the trust and confidence of the local people, managers, conservationists, and researchers must make every effort to avoid raising false expectations and 10 Acceptable elephant and conflict management actions were examined in the survey and will be reported separately.

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180 to follow through on promises (e.g., providing water sources outside of the park). This may seem obvious, but given the local history of land alienation, broken promises, and failed interventions, and the resulting lack of access for water and grazing resources in the park and costs from wildlife damages, the tolerance and goodwill of the Maasai may reach i ts limit. The Maasai do indeed exhibit a great deal of tolerance of wildlife with a hint of appreciation, especially for specific species. Interventions that take this into account are likely to be more successful. The M odel The integrated model demonstr ated that the addition of other variables to the cognitive hierarchy was useful in understanding and predicting intention to tolerate elephants, with a substantial amount of variance in behavioral intention explained. Intention to allow elephants in group ranches was strongly determined by the positive dimension of general attitude towards elephants, specific attitude s toward allowing elephants in group ranche s subjective norm for allowing elephants, and, to a lesser degree, by the negative dimension of attitude towards elephants relationships supported by the Theory of Reasoned Action ( Fishbein and Ajzen 1975) and Fazios spontaneous processing model (Fazio 1986, 1990). These results suggest that the inclusion of a general attitude variable may be a st ronger predictor of behaviors than specific attitudes in certain contexts. They also demonstrate that interventions aimed at maintaining or increasing tolerance of elephants should target attitudes and norms, and their underlying constructs. Further support for the model was demonstrated by the ability of the value orientation s to predict general and specific attitudes. The strongest relationship was between the indifference value orientation and the negative dimension of attitude toward elephants, which, in turn, was the strongest predictor of attitude and norm for allowing elephants. While the negative attitude

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181 dimension was the weakest of the four predictors of behavioral intention, its effects may be partially mediated through the attitude and norm for allowing elephants variables. Several external variables were identified as predictors of value orientation s, attitudes and norms, including gender, group ranch, knowledge of elephants, prior negative experience, worry, awareness of organizations, and belief that damage compensation increases tolerance. While they were weaker predictors they are useful in assisting wildlife officials and conservationists with managing elephants and HEC by indentifying areas of concern for local people and the content re quirements and targets for education and communication. Future Livelihood A ctivity Results indicate that fewer people believed that pastoralism would be their primary livelihood activity in five years, with a significant number of respondents stating that they planned to shift to agriculture or another economic activity. This is consistent with the general trend of livelihood diversification among African pastoralists (McCabe 2003). Some argue, based on historical evidence, that the Maasai have always made superficial change when necessary (e.g., in times of disease and drought) with the intention of returning to pastoralism (Knowles and Collett 1989). This is supported by research among Maasai in Tanzania, where Maasai agropastoralists expressed the goal o f adopting agriculture to avoid selling livestock (McCabe 2003) and livestock remained the priority for all but the poorest and commercially oriented farmers (OMalley 2000, p. 245). No matter what intentions are, the continued adoption of agriculture, c ombined with subdivision and privatization of land, has serious implications for wildlife and pastoralists as competition for land and water increases. The feasibility of the historical strategy of temporary shifts in livelihood with the intention of retur ning to pastoralism is highly questionable given modernday circumstances (e.g., increasing human population, increasing poverty, and changing land tenure).

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182 Several strategies are in discussion or development to address the social and ecological needs of t he Amboseli ecosystem. A priority issue is the development of a landuse plan. The Government of Kenya currently does not have a national landuse policy, although discussions of a plan have been on going for several years (P. Omondi pers. commun., 2002). In the meantime, a local level plan, developed collaboratively by all stakeholders and based on social and ecological research, is needed to protect both wildlife and people. Without a landuse plan and viable, alternative economic activities that are comp atible with wildlife conservation, local attitudes toward wildlife may become irrelevant. A Note on Gender In 1987, in discussing the results of their study on the influence of gender on American attitudes toward wildlife, Kellert and Berry (p. 370) stated that gender is among the most important demographic factors in determining attitudes about animals in our society. They recommended that major efforts to broaden the scope and effectiveness of wildlife management should thus consider and understand t he influence of gender. Since this early study, gender is increasingly recognized as an important consideration in wildlife and protected area management (Badola and Hussain 2003; Biermayr Jenzano 2003; Czech et al. 2001; Dougherty et al. 2003; Hunter et al. 1990; Nabane and Matzke 1997; Ogra 2008; Zinn and Pierce 2002). In the present study, gender was significantly related to multiple variables, including voting intention, with a majority of women (65%) stating they would vote against allowing elephants in the group ranches. Gender was the only predictor across all three of the wildlife value orientations. Women were more negative toward wildlife in general, and elephants specifically, had lower knowledge scores, a higher level of worry, less awareness of HEC interventions, and were less likely to believe elephants bring benefits to people. In Uttarakhand, India, Ogra (2008) found that women bear the disproportionate burden of hidden costs associated

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183 with conflict with wildlife, such as fear and increased workload. For example, when elephants break water pipes, women are forced to fetch water from an alternate site. Research in southern Africa, found that gendered differences in humanwildlife conflict were related to ownership of resources, with men prima rily concerned with livestock and women with crops (Muruthi 2005). These results highlight the need for a gendered perspective in developing policy and interventions. Nabane and Matzke (1997, p. 521) state that as a social construct, gender roles are mal leable and potentially responsive to changes in natural resource management activities. This is supported by research on the impact of development interventions in Maasailand, where Wangui (2008) found that development interventions in Loitokitok Division of Kajiado District, Kenya (just to the east of the study area) had altered livelihood activities and contributed to unforeseen shifts in gender roles, with women increasingly responsible for small stock. Future research and i nterventions should focus on women to understand their roles and perceptions related to the environment and to ensure that they are also beneficiaries of conservation. Limitations and Future Research This study has a number of significant strengths, such as the test of an integrated model, the transfer of theory to a new setting, and implications for conservation practice, but it also has several limitations. As a test of an integrated theoretical model, there were numerous measures and constructs, which limited the parsimony of the model. Further work is needed to refine the constructs of the model and the sets of items that measure each construct. This was particularly evident with the value orientations scales. Additionally, the influence of the riskrelated concepts was examined i ndividually, with a single indicator for each concept. While this contributes to the understanding of the various dimensions of risk perception in settings of humanwildlife conflict, additional research is needed to develop a comprehensive measure that ca ptures the full scope of

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184 risk perception, which may, in turn, increase its explanation of attitudes and behaviors to potentially dangerous or costly wildlife. Results provide support for the model tested here, but it could be improved through refinement of the measurement items and the addition of other variables suggested by research and other theories (e.g., past behavior). Researchers have called for an expansion of the cognitive hierarchy and related theories, such as the Theory of Reasoned Action, in order to improve understanding and prediction. This study tested only a small set of additional variables, while there are a multitude of variables that can influence values, attitudes and behaviors. Of particular note was inclusion of the general attitude toward elephants variable, which proved to be significant in explaining attitude toward allowing elephants on private land and the intention to allow elephants, possibly indicating a more spontaneous or automatic response to tolerance of elephants. Further examination of factors influencing the dual processes between attitudes and behaviors is needed. Another limitation of measurement is that this study predicted behavioral intentions, rather than actual behaviors. Although intentionbehavior correlations have varied, with some being quite high (e.g., r = 0.85; Ajzen and Fishbein 1980), there is not a perfect correlation between behavioral intention and actual behavior (Vaske and Donnelly 1999). Additionally, a hypothetical vote, a single item indicator, wa s used as a proxy for willingness to allow elephants in the group ranches. An index of tolerance behaviors may provide a better measure of willingness to tolerate elephants. Another limitation of this study is the length of the questionnaire. While the qu estionnaire items were thoughtfully included to measure the variables in the theoretical model, the survey was a little too ambitious and taxing on the ever patient and cooperative respondents. The

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185 survey length, combined with the fact that the Maasai are a highly researched group, and therefore at increased risk for survey fatigue, may have affected responses, especially in the latter portion of the interviews. There are limitations inherent to survey research itself, such as lack of flexibility (e.g., in asking questions) and being subject to multiple sources of error and bias. Face to face interviews present additional opportunities for bias attributable to the behavior of the enumerator. While I attempted to address this by providing enumerator traini ng, maintaining close supervision, and using male and female enumerators for the corresponding respondents, there was, no doubt, some degree of interviewer bias introduced. Another source of bias in the present study was response bias. I tried to minimize this source of bias by differentiating my project from other researchers and organizations working in the area by using local enumerators, communicating my role as a university student, and by using a human dimensions logo on my teams t shirts and on my vehicle. Despite these efforts, 15% of respondents stated that they believed the government sent us to interview them. Finally, the random sampling procedure only resulted in the selection of 13 nonMaasai respondents. This is an important limitation beca use, while the study area was formerly comprised of a generally homogenous Maasai population, since independence, this area has become increasingly heterogeneous. This change is due mainly to the immigration of Kikuyu and Kamba farmers, who have settled pr imarily in areas of high agricultural potential and urban centers (Ntiati 2002) and rent land from predominantly Maasai owners (Campbell et al. 2003). Campbell et al. (2003) point out that organizations that implement community based wildlife management schemes in the Amboseli area have continued to focus on the Maasai, ignoring the increasing heterogeneity of culture and livelihoods. While it was not my intention to exclude

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186 nonMaasai from this survey, the sampling procedure did not result in the selection of the only urban center, Kimana town, in the study area. It is unclear how many nonMaasai live in Kimana town, but future research should address this shortcoming by purposefully sampling nonMaasai residents in Kimana and nearby Loitokitok town. Concl usions The integrated model, based on the cognitive hierarchy, provides a sound foundation for understanding tolerance of potentially dangerous and costly wildlife on private lands. By adding demographics, risk perceptions, prior experience, and beliefs and awar eness about conflict mitigation interventions, I was able to assess the relative influence of some of the determinants of tolerance of elephants. However, modification of the model may improve its theoretical value and practical utility. This may include the addition of other variables proposed by theory, such as perceived behavioral control and actual behavior. The findings presented here should help managers and program staff with improving current and planning future interventions aimed at reducing conf licts and conserving Amboselis elephants. The extension of this model to other settings of HEC will provide further evaluation of its reliability and validity.

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187 Figure 5 1. The cognitive hierarchy model of human behavior (a dapted from Fulton et al. 1996, Vaske and Donnelly 1999). Table 5 1. Kellerts typology of attitudes toward animals Attitude Description Naturalistic Primary interest and affection for wildlife and the outdoors Ecologistic Primary concern for the environment as a system Humanistic Primary interest and strong affection for individual animals, principally pets Moralistic Primary concern for the right and wrong treatment of animals Scientistic Primary interest in physical attributes and biological functioning of animals Aesthetic Primary interest in the artistic and symbolic characteristics of animals Utilitarian Primary concern for practical and material value of animals or its habitat Dominionistic Primary interest in mastery and control of animals Negativistic Prim ary orientation an active avoidance of animals due to dislike or fear Neutralistic Primary orientation a passive avoidance of animals due to indifference Source: Kellert (1980) Behaviors Behavioral Intentions Attitudes and Norms Value Orientations (Basic Belief Patterns) Values Few in number Slow to change Central to beliefs Transcend situations Numerous Faster to Change Peripheral Specific to situations

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188 Figure 5 2. Hypothesized model of predictors of willingness to allow elephants in group ranches.

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189 Figure 53. The Gerontocratic Model: Distribution of Status by Age and Gender ( adapted from Spencer 1993) married elders bachelor murran herdboys wives and widows unmarried girls MALES FEMALES A G E

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190 Figure 5 4. Map of study area Amboseli National Park and surrounding group ranches, with Maasai enkangs in darkened circles.

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191 Table 5 2. Demographic characteristics by voting intention groups Voting Intention Allow Not allow 2 p Demographic characteristic n % a n % b n % b Ethnicity Maasai 555 (98) 296 (53) 258 (47) 3.50 0 .18 Kamba 10 (2) 5 (50) 5 (50) Kikuyu 3 (1) 0 (0) 3 (100) Group Ranch Olgulului 370 (65) 188 (51) 180 (49) 1.68 0 .20 Kimana 199 (35) 113 (57) 86 (43) Gender Male 279 (49) 199 (72) 79 (28) 74.92 0 .001 Female 290 (51) 102 (35) 187 (65) Age Mean c = 30.73 Young <30 293 (52) 161 (55) 131 (45) 1.10 0 .29 Older >30 275 (48) 139 (51) 135 (49) Attended school No 430 (76) 218 (51) 212 (49) 4.08 0 .04 Yes 137 (24) 83 (61) 54 (39) Level completed Primary 104 (77) Secondary 22 (16) A level 4 (3) Technical college 4 (3) Other 2 (1) Livelihood (primary) Pastoralism 399 (70) 210 (53) 189 (47) 4.04 0 .13 Cultivation 139 (24) 70 (50) 69 (50) Other 25 (5) 18 (72) 7 (28) a Column percentages. b Row percentages. c Based on 193 responses.

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192 Table 5 3a. Age set representation in the study sample Age set Approx. age range Number in sample Retired a Ilterito 80+ 0 Inyangusi 65 80 5 Iseuri 50 65 16 Active b,c Ilkishimu 35 50 59 Ilkishuri/Ilkidotu 20 35 102 Ilkiponi <20 97 a Members of the council of elders come from these agesets. b The Ilkishumu and Ilkishuri/Ilkidotu age sets control resources. c The Ilkiponi age set is comprised of ilmurran Table 5 3b. Person type Person type n Elder 97 Young man 182 Old woman 34 Middle woman 145 Young woman 111 Table 53c. Young and older a ge groups for analysis Gender Age set Age Groups a Total n n Young (ages 18 30) 293 Women 111 Men 182 Ilkiponi 97 Ilkishuri/Ilkidotu b 85 Older (ages 30 67) 276 Women 179 Men 97 Ilkishuri/Ilkidotu b 17 Ilkishimu 59 Iseuri 16 Inyangusi 5 a Age 30 is the approximate cut off. This estimation is based on the limited number of women who provided their ages and the age range of the Ilkishuri/ Ilkidotu age set b This group was divided based on the subjective measure person type.

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193 Table 5 4. Factor a nalysis of basic beliefs about w ildlife Variable Factor loadings Factor 1 Indifference Factor 2 Negativistic Factor 3 Skills/bravery Standardized item alpha reliability 0.82 0.62 0.73 Going outdoors just to see wild animals is a waste of time Naturalistic 0.753 I would rather be in a place without wildlife than one with wildlife Negativistic 0.727 Watching wild animals during my free time strikes me as a waste of time Naturalistic 0.694 When I am walking in the bush, I enjoy seeing wildlife around Naturalistic a 0.624 It is not important to me whether elephants are many or few in number Neutralistic 0.503 I do not care if we have many or few rhinoceros in Kenya Neutralistic 0.487 Having fewer wild animals around in the future is nothing to worry about Neutralistic 0.484 I do not agree with the person who says he dislikes the hyena. Negativistica 0.446 I think poisonous snakes are wicked by nature Negativistic 0.635 I dislike places where wild animals like hyenas are abundant Negativistic 0.611 Termites serve no useful purpose in the environment Ecologistic 0.486 I admire the hunter who is able to kill a lion Dominionistic 0.683 A man who can kill a lion with a spear or arrow deserves praise. Dominionisti c 0.641 I would like to watch hunters as they hunt large animals like the buffalo Dominionistic 0.505 a Reverse coded items.

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194 Table 55. Wildlife values orientations attitudes, and norms by voting intention groups Variable Overall m ean Allow Not Allow M SD M SD t df p d a Wildlife value orientation sb ,c Indifference 4.28 3.41 1.42 5.27 1.39 15.72 565 0.001 1.32 Negativistic 6.13 5.77 1.55 6.55 1.07 7.05 b 534 0.001 0.59 Skills/bravery 4.09 3.36 2.07 4.92 1.88 9.37b 564 0.001 0.79 Attitudes Toward elephantsc Negative dimension 4.39 3.34 1.33 5.56 1.06 22.07 b 560 0.001 1.85 P ositive dimension 4.41 4.94 1.30 3.82 1.46 9.67b 535 0.001 0.81 Toward allowing elephants in group ranchd 0.38 1.74 3.07 1.18 2.71 12.05b 564 0.001 1.01 Norm for allowing elephants in group ranche 4.29 7.60 6.53 0.49 7.96 11.45b 502 0.001 0.98 Belieff 1.11 2.00 1.72 0.11 2.13 11.48b 505 0.001 0.98 Motivation to comply g 3.62 3.67 0.62 3.55 0.66 2.12 536 0.04 0.19 a Effect sizes d computed indirectly from the t test. b Levenes test for equality of variances indicated that the variances of the two groups were significantly different. The reported values are the result of t tests with equal variances not assumed. c Range = 1 to 7. d Range = 9 to +9. e Range = 12 to +12. f Range = 3 to +3. g Range = 1 to 4.

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195 Table 5 6. Factor analysis of basic beliefs regarding elephants Factor loadings Factor 1 Negative Factor 2 Positive Standardized item alpha reliability 0.85 0.66 People in my group ranch would be better off if there were no elephants. 0 .7 12 Moving elephants somewhere else is the best way to stop problems caused by elephants. 0 .7 04 This would be a better place without elephants. 0 673 Killing elephants is a good way to stop problems caused by elephants. 0 .6 22 It is not possible for people and elephants to stay together. 0.584 The only reason elephants come out of the park is to disturb people. 0 556 Elephants and livestock owners can live together. (reverse coded) 0 .5 54 Elephants have an important role in the environment. (reverse coded) 0 472 Elephants are always angry toward people. 0.400 Elephants are gentle unless they are provoked. 0.565 Elephants chase people because they have been treated badly by people. 0 537 No elephant around Amboseli should be killed. 0.513 If people did not grow crops, there would not be problems with elephants. 0.493 Elephants have a right to exist around Amboseli just as people do. 0.401

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196 Figure 5 5. Mean belief expectancy and evaluation scores for voting groups regarding potential outcomes of allowing elephants in group ranches

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197 Figure 5 6. Mean belief evaluation products for voting groups regarding potential outcomes of allowing elephants in the group ranches.

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198 Table 57. Comparisons of mean expectancy, evaluation, and belief evaluation product scores between respondents for and against allowing elephants in G roup R anches Outcome Item Belief Scores Evaluation Scores BE Product Scores t p d t p d t p d Allowing elephants would increase/cause number of elephants shot by KWS 2.31 0.02 0.20 2.61 0.009 0.22 5.70 0.001 0.48 number of elephants speared by Maasai 1.43 0.16 0.12 0.65a 0.52 0.06 1.64 0.10 0.14 conflict between people who favor/oppose elephants 7.67a 0.001 0.64 2.26a 0.02 0.19 7.52a 0.001 0.63 potentially dangerous people elephant interactions 1.75 0.08 0.15 3.37a 0.001 0.26 2.23 0.03 0.19 increase costs to local people 6.15a 0.001 0.52 3.01a 0.003 0.24 6.51a 0.001 0.55 opportunities to see elephants 3.43a 0.001 0.29 8.30a 0.001 0.71 7.10a 0.001 0.61 elephants to increase in number 2.44a 0.02 0.21 16.77a 0.001 1.42 14.16a 0.001 1.20 more tourists to visit group ranch 1.41a 0.16 0.12 2.90a 0.004 0.26 2.07a 0.04 0.18 a Levenes test for equality of variances indicated that the variances of the two groups were significantly different. The reported values are the result of t tests with equal variances not assumed.

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199 Table 5 8. Prior experience with elephants and voting intention groups Voting intention Allow Not allow Experience variable n % a n % b n % b 2 p Like to see elephant (n = 568) Yes 284 (50) 232 (82) 51 (18) 188.53 0 .001 0 .58 No 284 (50) 69 (24) 214 (75) Problems with elephants Card sort (n = 531) Yes 250 (47) 115 (46) 135 (54) 10.10 0 .001 0 .14 No 281 (53) 168 (60) 113 (40) Direct questions (n = 566) Yes 368 (65) 199 (54) 169 (46) 0 .34 0 .56 0 .02 No 198 (35) 102 (52) 96 (48) a Column percentages. b Row percentages. Table 5 9. Locations where respondents see and like to see elephants Like to see in location a No Yes Lo cation of experience n % b n % c n % c Near home No 283 (50) Yes 285 (50) 243 (85) 42 (15) Near shamba No 539 (95) Yes 29 (5) 28 (97) 1 (3) At waterhole No 447 (79) Yes 119 (21) 66 (55) 53 (45) In the bush No 53 (9) Yes 515 (91) 195 (38) 320 (62) a Based on yes responses to location question. b Column percentages. c Row percentages.

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200 Table 5 10. Correct responses to ten knowledge statements regarding elephants Knowledge statements % correct a Male elephants live alone most of the time. 64 Elephants can live to be more than 65 years old. 72 Male elephants le a d the elephant family group. 28 Elephants only eat grass. 75 Elephants open up the bush for other animals. 92 Sometimes elephants must get water outside the park to survive. 86 Elephants have long memories. 48 The Amboseli elephants need water inside and outside the park. 94 Elephants have to spend most of their time eating to survive. 96 Adult elephants need about 100 liters of water each day. 82 a Based on n = 568.

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201 Table 5 11. HEC risk beliefs by voting intention groups Voting intention Allow Not allow Belief a n % b n % c n % c 2 p d Problems in last 5 years have increased 287 (51) 137 (46) 150 (56) 14.64 0.002 0.16 stayed the same 146 (26) 79 (26) 67 (25) decreased 128 (23) 84 (28) 44 (17) dont know 6 (<1) 1 (<1) 5 (2) Personal safety at great risk 256 (45) 113 (38) 143 (56) 16.76 0.001 0.17 little risk 158 (28) 100 (33) 58 (22) no risk 150 (26) 87 (29) 63 (24) dont know 3 (<1) 1 (<1) 2 (<1) Livelihood at great risk 279 (49) 123 (41) 156 (59) 18.56 0.001 0.18 little risk 155 (27) 97 (32) 58 (22) no risk 132 (23) 80 (27) 52 (19) dont know 1 (<1) 1 (<1) Worry a great deal 286 (50) 122 (40) 164 (62) 26.13 0.001 0.22 a little 145 (26) 90 (30) 55 (21) not at all 135 (24) 89 (30) 46 (17) Controllability of elephant problems very 218 (38) 124 (41) 94 (35) 3.29 0.35 0.08 somewhat 105 (19) 58 (19) 47 (18) not at all 219 (39) 107 (36) 112 (42) dont know 25 (4) 12 (4) 13 (5) Personally able to control yes 22 (4) 12 (4) 10 (4) 0.02 0.88 0.01 no 542 (96) 287 (96) 255 (96) a N = 567 for each risk belief variable except worry and personally able to control, where N = 566 and 564, respectively. b Column percentages. c Row percentages. d The values for Phi and Cramers V were equal.

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202 Table 5 12. Knowledge and beliefs regarding HEC mitigation by voting intention groups Voting intention Allow Not allow Variable n % a n % b n % b 2 p Elephants bring costs Yes 532 (94) 279 (52) 253 (48) 9.46 0.01 0.13 No 26 (4) 20 (77) 6 (23) Dont know 9 (2) 2 (22) 7 (78) Elephants bring benefits Yes 351 (62) 267 (76) 84 (24) 195.50 <0.001 0.59 No 189 (33) 29 (15) 160 (85) Dont know 27 (5) 5 (18) 22 (82) Household receives tourism benefits Yes 208 (39) 144 (69) 64 (31) 26.24 <0.001 0.22 No 322 (61) 150 (47) 172 (53) O rganizations helping people Yes 318 (56) 210 (66) 108 (34) 49.50 <0 .001 0 .30 No 248 (44) 90 (36) 158 (64) Electric fence(s) Yes 282 (50) 164 (58) 118 (42) 6.19 0 .01 0 .11 No/dont know c 283 (50) 135 (48) 148 (52) C ultural bomas Yes 510 (90) 278 (55) 232 (45) 4.13 0 .04 0 .04 No/dont know c 57 (10) 23 (40) 34 (60) Compensation increases tolerance Yes 344 (61) 231 (67) 113 (33) 73.63 <0.001 0.36 No 202 (36) 59 (29) 143 (71) Dont know 20 (3) 10 (50) 10 (50) a Column percentages. b Row percentages. c Dont know responses were provided by two respondents on the electric fence question and by six respondents on the cultural bomas question.

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203 Table 513. Frequencies for awareness organizations with HEC interventions Organization GOK KWS AERP AWF Organizations that help people with HEC 27 143 152 7 Interventions Nothing 2 1 Make a report 6 6 2 Chase/scare elephant(s) 6 47 19 1 Shoot elephant 1 14 7 Erect fence 5 Take injured to hospital 2 13 11 1 Pay compensation (for people) 8 26 19 1 Pay consolation (for livestock) 8 25 88 1 Have meetings/workshops 2 1 Other 1 Dont know 2 2 1

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204 Figure 5 7. R elationships between wildlife value orientations, attitudes, norms, and behavioral intentions, with external variables shown in gray

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205 Table 5 14. Multiple regression analysis results for attitude and norm variables Independent variable B SE B a Adj. R 2 F df p Attitude toward elephants negative dimension 0.62 130.85 7, 555 <0.001 Indifference wildlife value orientation 0.40 0.04 0.41*** Gender 0.78 0.12 0.24*** Skills/bravery value orientation 0.15 0.02 0.20*** Prior negative experience 0.32 0.10 0.09*** Awareness of organizations with HEC interventions 0.21 0.10 0.06* Knowledge of elephants 0.08 0.03 0.08** Worry about elephants (reversed) 0.17 0.05 0.08** Attitude toward elephants positive dimension 0.22 26.74 6, 558 <0.001 Group ranch 1.00 0.12 0.32*** Worry about elephants (reversed) 0.40 0.07 0.22*** Gender 0.31 0.15 0.10* Awareness of organizations with HEC interventions 0.27 0.12 0.09* Prior negative experience 0.31 0.13 0.10* Indifference wildlife value orientation 0.25 0.04 0.28*** a *p < .05, **p < .01, ***p < .001

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206 Table 5 14. Continued Independent variable B SE B a Adj. R 2 F df p Attitude toward allowing elephants in group ranches 0.37 32.97 10, 551 < 0.001 Gender 1.66 0.31 0.26*** Attitude toward elephants positive dimension 0.46 0.09 0.21*** Group ranch 0.67 0.26 0.10*** Belief elephant damage compensation increases tolerance 0.01 0.01 0.08* A wareness of electric fences 0.05 0.02 0.09** Prior negative experience 0.61 0.26 0.10* Skills/bravery wildlife value orientation 0.18 0.06 0.11** Worry about elephants (reversed) 0.47 0.15 0.12*** Negativistic wildlife value orientat ion 0.27 0.09 0.12** Attitude toward elephants negative dimension 0.83 0.10 0.41*** Norm for allowing elephants in group ranches 0.30 81.28 3, 555 <0.001 Attitude toward elephants positive dimension 0.84 0.21 0.16*** Group ranch 2.32 0.63 0.14*** Attitude toward elephants negative dimension 2.25 0.19 0.46*** a *p < .05, **p < .01, ***p < .001

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207 Table 5 15. Logistic regression predicting voting intention Variable B SE Walds 2 df p Odds ratio Model 1 a Attitude toward allowing elephants 0.29 .04 53.71 1 <0.001 1.33 Norm for allowing elephants 0.10 .01 49.79 1 <0.001 1.10 Model 2 b Attitude toward elephants positive dimension 0.24 0.09 7.13 1 0.01 1.28 Attitude toward elephants negative dimension 1.08 0.11 104.49 1 0.001 0.34 Attitude toward allowing elephants 0.15 0.05 10.40 1 0.001 1.16 Norm for allowing elephants 0.03 0.02 3.74 1 0.05 1.03 a Nagelkerke R2 = 0.37 b Nagelkerke R2 = 0.62

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208 Table 5 16. Current and future primary livelihood activity Current a Future Livelihood activity n % n % 2 p V Pastoralism 391 (70) 322 (57) 301.14 <0.001 0.52 Cultivation 138 (24) 197 (35) Other 25 (5) 35 (8) a The total does not equal 100% due to rounding.

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209 CHAPTER 6 CONCLUSIONS This study examined Maasai tolerance of elephants in group ranches adjacent to Amboseli National Park, Kenya. The overall goal was to provide stakeholders with critical human dimensions information for conserving elephants and reducing humanelephant confl ict. A cultural and his torical context for this study wa s provided to allow a broader perspective for considering tolerance in a changing landscape. A questionnaire survey was conducted among the predominantly pastoral and agropastoral Maasai population in the two group ranches bordering the park to identify predictors of intention to allow elephants in the group ranches. The results of the survey provide a snapshot view of the current level of tolerance and a baseline on which to compare future assessments They also provide a means for evaluating the impact of interventions on attitudes and behaviors. A secondary goal of this study was to test the transferability of theory and methods often used in North American human dimensions research to a rural African setting. A review of wildlife conservation attitude research in Africa provided an assessment of methods used in this area of study on which to build the present study. The cognitive hierarchy provided a theoretical framework in which to add other variables suggested by previous research. The results of the survey have implications for conservation pr actice and for research theory and methods. While results, conclusions, and recommendations are presented throughout the dissertation, the following summarizes the overall results and implications of the study. General R esults and I mplications for E lephant C onservation Predicting T olerance of E lephants A slight majority (53%) of respondents indicated that they would vote to allow elephants in the group ranch, leaving a substantial minority against allowing elephants outside of the park.

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210 My theoretical mod el, based on the cognitive hierarchy, provided a valid framework for understanding tolerance of elephants, as indicated by the predictive ability of the model. Intention to allow elephants in the group ranches was predicted by the variables of the cognitive hierarchy and the related Theory of Reasoned Action. That is, attitudes toward elephants, attitudes toward tolerating elephants, and the norm for allowing elephants explained a substantial portion of the variance in voting intention. Wildlife value orien tation s, along with external variables, predicted attitudes. This study provides empirical evidence of indifference toward wildlife among the Maasai. It identified an indifference wildlife value orientation which represents a spectrum from not at all in different to very indifferent (and perhaps even appreciative). The indifference orientation was the strongest predictor of attitudes toward elephants, which in turn predicted attitudes, norms, and behavioral intention to tolerate elephants. While gender ex plained a significant amount of variance in this value orientation, the basis for indifference is not clear. While the specialized pastoralism of the Maasai is often offered as an explanation for indifference toward, and coexistence with, wildlife, livelih ood strategy was not a predictor of indifference in my analysis. This may be attributable to a lack of congruency in the way I measured livelihood and the way in which the Maasai view themselves. That is, if most Maasai continue to view themselves as tradi tional pastoralists or have the intention of returning to pastoralism, even when their livelihood is derived primarily through other means, a measure of primary livelihood would fail to explain variance. Perhaps a measure based on culture would serve as a better predictor of value orientations. A comparative study with a larger subsample of nonMaasai would allow for the examination of the predictive ability of culture.

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211 Two other wildlife value orientation s were identified, negativistic and skills/bravery and there were indications that additional orientation s, such as moralistic and theistic were present. There is further evidence in Maasai culture of other values such as aesthetic value. This was expressed on several occasions in the survey, such as whe n describing the attractiveness of the elephant and when agreeing with the Kellert type statements regarding the beauty of gazelles (97% of respondents) and leopards (80% of respondents). U tilitarian value has been demonstrated in the past when wildlife wa s used as second cattle in times of disease and drought and today in viewing wildlife as a source of revenue. More research is needed to identify other orientation s that were not captured in this study and to understand the basis for wildlife value orien tation s. This information may help wildlife managers and conservationists develop policy and interventions that are in line with and can preserve traditional wildlife value orientation s. Attitudes toward elephants proved to be important in predicting subsequent variables in my theoretical model, including willingness to tolerate elephants. Therefore, they have important implications for the future of elephants on private lands around Amboseli. A slight majority of respondents were negative toward elephant s. Negative attitudes were based on certain beliefs, such as people in my group ranch would be better off if there were no elephants, and were related to external variables such as gender, worry, knowledge, and awareness of organizations with HEC interve ntions. This information suggests targets and content for interventions, which can be incorporated into current interventions and used to develop new interventions. For example, AERP had been operating its consolation scheme for livestock losses for seven years (at the time of the survey), yet only 15% of respondents had accurate knowledge of this program. Given that awareness of organizations with HEC interventions was related to more positive

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212 attitudes and that livestock loss was one of the primary concer ns of those against allowing elephants in the group ranches, it would be expected that increasing awareness and knowledge of this intervention would positively influence attitudes and behaviors toward elephants. M y findings regarding the level of support for elephants in the group ranches are similar to those of Kangwana (1993). In 1991, 53% of Kangwanas respondents stated that elephants should not be removed from the area, the same percentage of respondents in favor of allowing elephants in the group ranches in the 2005 survey. The most commonly voiced reason for being positive toward elephants in both studies was the perception of benefits (largely to others) associated with elephants, but only 36% of respondents in the 2005 survey stating that their household received such benefits. If the tourism value of elephants is going to continue to be a selling point for tolerating elephants, there needs to be an increase in actual and perceived benefits. This has proven to be a challenging endeavor for community based conservation in general (Parry and Campbell 1992, Songorwa 1999, Wells et al. 1992), but research supports the notion that increasing benefits can increase support for conservation (Archabald and NaughtonTreves 2001; Gillingham and Lee 1999; Holmes 2003; Kideghesho et al. 2007). While most protected areas do not generate enough sur plus income to reduce local poverty (Barrett and Arcese 1995; Infield 2001), increased and equitable revenue sharing should be directed, at a minimum, at offsetting costs incurred from tolerating wildlife on private land and forgoing access to resources in protected areas. However, given the limitations of benefits based approaches, it would be unwise to limit the value of elephants, and other wildlife, to purely economic value. In addition to evidence of general wildlife values, results suggest certain val ues specific to elephants. As discussed in Chapter 4, there is some degree of appreciation (e.g., beauty, role in ecosystem modification, etc.) and theistic value For example, an old woman in

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213 Kimana group ranch stated, God created elephants and they belo ng to this earth just like us An education program based on traditional knowledge, beliefs, and values as well as on science could increase knowledge of and cultivate positive attitudes toward elephants and could also work to preserv e the culture that h as been credited with conserving the diverse wildlife of the Greater Amboseli Ecosystem. Mitigating H uman E lephant C onflict While benefits were cited as the principal reason for tolerating elephants, the costs associated with elephants were the primary reason given for being against elephants in the group ranches. Respondents were concerned about the dangers posed to both humans and livestock. Negative attitudes toward elephants and allowing elephants in the group ranches were related to prior negative ex perience with elephants and worry about problems with elephants. These results demonstrate that more effort is needed to reduce actual and perceived levels of HEC. Current interventions are either insufficient or are not well known or understood by the com munity. The electric fences are not fully operational (and they have deflected problem elephants to other locations), compensation for human injury and death is meager, the consolation program for livestock losses is not wellknown or understood, and proje cts related to tourism benefits have a history of failures, which include corruption, inequitable distribution of benefits, and short term implementation. Additionally, interventions have generally been developed and implemented through a topdown approa ch, with little ownership and responsibility held by local people. This may perhaps explain the belief among almost all of the survey respondents (95%) that they were not personally able to control problems with elephants (this is also probably related to the nature of conflict with such a large animal), even though more than half of respondents felt that elephant problems were at least somewhat controllable.

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214 If tolerance is to be maintained and improved, problems with interventions need to be addressed. B arriers (electric fencing) and deterrents in cultivated areas need to be better managed and adapted as elephants learn new ways of bypassing them. This can help reduce human mortalities that occur in guarding crops during a raid, in addition to reducing cr op losses. At the time of this study, other strategies, which included community involvement, were being tested in cultivated areas in nearby Loitokitok (Kiiru, in progress). These may prove to be promising methods to be used alongside the electric fences at Kimana and Namelok. While it is not clear where most conflicts occur, a fairly accurate assessment can be obtained from the KWS occurrence books and AERP records. This information can be used to develop additional measures for reducing conflict. For instance, if most livestock losses occur at waterholes, then alternate, wildlife only waterholes may be feasible. This management action was found to be highly acceptable among 78% of survey respondents, with another 10% stating that it was slightly to moderately acceptable. Education and communications related to HEC can provide local residents with knowledge of ways to avoid encounters with elephants and increase awareness of HEC mitigation interventions. Such a program is currently being implemented in schools around the Maasai Mara to the west of Amboseli. If local people have accurate information on the incidence of HEC ( i.e., it is a rare occurrence), feel empowered by knowledge and tools for reducing and coping with HEC, and obtain primary responsibility for mitigating problems, not only would the level of HEC be expected to decrease, but so too might the level of anxiety. In Amboseli and elsewhere, if HEC or the perception of HEC continues to increase, it is highly likely that attitudes toward elephants will become increasingly negative and result in reduced tolerance of elephants outside of protected areas. HEC will escalate if land conversion

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215 (i.e., communal to private, pastoral to cultivation) continues unchecked. L anduse is a critical issu e for elephant conservation in Amboseli and across the elephants range. As human and elephant populations increase, land use policy that limits land use practices in critical elephant habitat, including corridors, is key to mitigating HEC and ensuring the longterm survival of elephants. The survey results reported in Chapter 5, along with historical and cultural evidence presented in earlier chapters, supports the notion that Maasai indifference, facilitated by specialized pastoralism, has allowed the coexistence of pastoral Maasai and wildlife. If land continues to be converted for private use, including cultivation, Maasai specialized pastoralism will become increasingly unfeasible, HEC will continue to increase, and elephants will have reduced access to private land. As stated in Chapter 4, it is impossible to return to the days when the Maasai, their livestock, and wildlife coexisted, unrestricted by boundaries created by outside policy but i t may be feasible to nurture what remains in terms of traditional values and beliefs and to encourage land use that will minimize further loss of land available for wildlife and livestock. This includes encouraging the continuation of transhumant pastoralism, where possible, and supporting the development of wildlif e based enterprise. The implications of these findings are likely generalizable to other settings of human elephant conflict and demonstrate that, with potentially dangerous and costly animals such as elephants, reducing risk and implementing effective co nflict mitigation interventions will influence attitudes and, potentially, behaviors toward wildlife. While these results may be generalizable for broad scale planning, each setting of HEC need s to be examined at the local level because of great variation in circumstances across the elephant s range. Theory and M ethods in A ttitude R esearch in Africa Human dimensions research aimed at understanding attitudes and predicting behaviors provides important and complex information for wildlife managers and conserv ation program

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216 staff. Data from attitude surveys can guide management decisions and serve as a baseline to test the effects of policy and interventions. Key to the successful application of survey data is ensuring the rigor of the methodology. Attitudes and behaviors vary between individuals and between situations, with a multitude of other variables influencing the beliefs upon which attitudes and behaviors are based. Theory guides the selection of concepts to be examined. This study tested a model for unde rstanding attitudes and behaviors in situations involving humanwildlife conflict in a rural African setting by transferring theory and methods often employed in North American human dimensions research. Chapter 3 provided a review of conservation attitude research in Africa and highlighted the many challenges of conducting surveys in rural African settings. These include, but are not limited to, lack of census information, widely distributed study populations, transportation limitations, and lack of exper ience in surveys among study populations. The chapter also included several recommendations for future research, with the main point being that this growing body of research should be guided by the central tenets of scientific inquiry, which include considerations of validity, reliability, representativeness, and generalizability. Other important issues discussed included use of theory and issues of survey quality. The results presented in Chapter 5 demonstrated that my theoretical model based on the cogni tive hierarchy provided a valid framework for understanding tolerance of elephants on private land. The proximal variables, attitudes and norms, predicted voting intention, while more distal variables, such as value orientation s and external variables, helped explain it. The model provides a good starting point for understanding behavior toward wildlife in the context of humanwildlife conflict. As discussed in Chapter 5, further development and testing of measurement items is needed. Additionally, other variables proposed by theory and previous

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217 research may improve its theoretical value Extension of the model to other settings will provide further assessment of the models utility and the reliability, validity, and generalizab ility of the study results Overall, this study demonstrated that the challenges of survey research in rural Africa can be overcome and rigorous methods can be employed. However, it should be noted that adequate funding and time were key to surmounting som e issues. First, I was able to produce a sampling frame for selecting a representative, random sample by mapping each home in the study area and collecting census information. This required hiring two experienced local Maasai who were familiar with the entire study area and equipping them with GPS units and bicycles (and more than a few spare tire tubes). Second, I was fortunate to be able to rent a 4wheel drive vehicle to transport my team around the study area (and to serve as a local taxi). Without a ve hicle, it would have been impossible to cover the entire area, which would have resulted in significant coverage error. Third, I was able to offer a one week enumerator training course for local Maasai, which included room and board, as necessitated by log istical circumstances. This training, along with other measures, should have limited interviewer bias. Finally, adequate funding allowed me to hire four enumerators and my assistant, allowing me to collect an adequate sample size, thereby reducing sampling error. Feedback from R espo n dents Most respondents (81%) had a positive evaluation of the research, with 14% expressing a neutral evaluation and 1% a negative evaluation. Even though each respondent was informed that this was a University of Florida student research project at the beginning of each interview (as required by the IRB), responses to the question who do you think sent us for this interview? were mixed and included the white person/researcher (n = 232), the government (n = 66), God (n

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218 = 21), K WS (n = 19), among others. A large number of respondents (n = 178) stated they did not know who sent us. The fact that a total of 85 people thought we represented the government, even with all of our efforts to distinguish ourselves as an independent proje ct, may indicate a high level of mistrust and could have had an impact on the data. This highlights the importance of being aware of the history of a region when conducting research. A considerable number of individuals (n = 103) stated that they had been interviewed by another researcher. A common complaint among these individuals was that nothing ever resulted from the research. They complained that they were promised a report, but never received one. This complaint was also voiced by the park warden. A preliminary report of the present research was provided to the park warden, AERP, and the group ranch committees in June 2008. At the completion of this dissertation, a final report is being provided to all stakeholders, with plans for presentations for com munity members in both group ranches.

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219 APPENDIX A PRELIMINARY RESEARCH REPORT OCTOBER 1, 2002 For my dissertation, I am planning to conduct and attitudinal survey of people living adjacent to Amboseli National Park toward elephant conservation, and possibly use a second site as a comparison. In preparation for this research, I traveled to my propos ed research sites in Kenya to conduct preliminary research. My objectives were to identify stakeholders through stakeholder analyses, identify salient issues and critical locations of humanelephant conflict, and to test survey questions. In addition to these objectives, I planned to investigate logistical requirements for fieldwork in Kenya. I spent six weeks in Kenya (April 29June 11). During the first two weeks, I conducted interviews with key informants in Nairobi, including the head scientist of the Amboseli Elephant Research Project, the program director of the African Wildlife Foundation, and the director of the International Fund for Animal Welfare Kenya. These interviews were part of the stakeholder analysis and led to the identification of othe r stakeholders. It was during this period that I was invited to attend a meeting of decision makers in elephant policy and management at the Kenya Wildlife Service Headquarters. They were meeting to discuss a crisis with crop raiding elephants outside Amboseli National Park. Here, I met the Elephant Programme Coordinator for the Kenya Wildlife Service (KWS). This was a key contact as the coordinator is involved in all aspects of elephant management in Kenya and he is the individual from whom I would need to request affiliation it is a requirement of the Kenya government that all foreign researchers have an affiliation with an approved Kenyan institution. I interviewed the coordinator a few days after the meeting. At this time, I explained my objectives and provided him a copy of my draft research proposal. He was keen to have the proposed research carried out, but his support came with a warning not to stir up any trouble, meaning, do not make people

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220 who are not complaining about elephants start complaining He provided me a letter granting me permission to enter the national parks and conduct interviews with local people. The third week was spent in the TsavoKasigau Corridor in southern Kenya a potential research site for a comparative study. This area l ies between Tsavo East and Tsavo West National Parks and is occupied by elephants moving between the parks and by people in several villages in the central and northern section of the corridor. I stayed at the Taita Discovery Center (TDC), which is located on a private ranch. The Center typically hosts university student groups from Europe and the U.S. who do volunteer work in the local villages and participate in the Centers wildlife research activities. A portion of the Centers income goes to the local villages in hopes of creating positive attitudes toward conservation, making the Centers owner a stakeholder in elephant conservation in this area. While in TsavoKasigau, I conducted stakeholder interviews with the owner of TDC, the chairman of Kasigau Ranch, and the district officer who serves the Office of the President. The interview with the owner of TDC represented business enterprise in the area, the chairman of the ranch represented the local people, and the district officer offered the position of the government. Each of the interviewees perceived the elephant as a problem and all were supportive of my research. I also did a mapping activity with residents of two communities to identify sites of humanelephant conflict and to promote discussion of the issue. Two assistants from the village were hired to help with communication. one male and one female. Both had recently completed their final year of school before university. I did a brief interview with them and explained my project and told them that, if they were available, I would be interested in hiring them when I returned for my fieldwork. There was not time for extensive training, but I did explain the purpose of the mapping activity and demonstrated how it was to be conducted. There

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221 were s ome problems. One tried to lead some of the mapping participants and the other was very shy and did not speak often. This, of course, made glaringly evident the need for thorough training when I return to conduct my survey. Another critical lesson learne d was that, as an outsider, I would need to spend time at the research site gaining the trust of the local people before conducting a survey. At the commencement of the activity, I found the people to be guarded, but as it progressed, participants became m ore relaxed and more open in their responses. The mapping activity was not only useful in gathering information about elephant conflict, key resources, and settlement areas, but because the participants seemed to enjoy the activity, it aided the progressio n of discussions. I returned to Nairobi for a week of meetings. I met again with the Elephant Programme Coordinator to discuss my proposal and he gave me some reports to review. He also agreed to grant me affiliation with KWS for my fieldwork given he approves the final draft of my research proposal. I did a stakeholder interview with the program coordinator for the East African Wildlife Society. Finally, I interviewed a Maasai graduate student, Leonard Onetu, from the University of Nairobi for the job of assisting me on my trip to Amboseli. He is from the Amboseli region and was recommended by one of the researchers with the Amboseli Elephant Research Project. The next week was spent in Amboseli National Park. Leonard and I traveled around the settlement areas bordering the park. Leonard introduced me to community leaders and assisted with the mapping activity. Without his assistance, it would have been extremely difficult, if not impossible, to gain entrance into the Maasai community. This trip was invalu able in preparing me for my fieldwork. I was able to establish working relationships with government officials, representatives of conservation NGOs, and

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222 community leaders critical to the success of my project. I will be better able to plan for the logistical and methodological details such as sampling design, hiring research assistants, establishing a camp, transportation, powering a computer, and obtaining a research permit. The groundwork has been laid and I will be able to hit the ground running upon my return to Kenya. I gratefully acknowledge the financial support provided by three programs at the University of Florida: a Jennings Scholarship from the Department of Wildlife Ecology and Conservation, a TCD field research grant from Tropical Conservation and Development Program, and the Niddrie Award from the Center for African Studies.

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223 APPENDIX B GPS DATA COLLECTION WORKSHEET

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283 BIOGRAPHICAL SKETCH Christine Browne Nuez is origninally from the Greater Kansas City area of Missouri She graduat ed from Blue Springs High School in 1986 and earned a B.A. in e lementary e ducation from the University of Missouri Kansas City in 1990. The next five years were spent teaching at a science/math magnet school in the Kansas City, Missouri School District. In 1995, Christine was selected to serve as a volunteer in Nairobi, Kenya, with the International Foundation for Education and Self Help Teachers for Africa Program (IFESH TFA). She spent her first year in Nairobi working at Makini Primary School, where she taught English and math, and led two school clubs, the Environmental Action Club and the Wildlife Club. During this year, she also volunteered at the David Sheldrick Wildlife Trusts elephant orphanage in Nairobi National Park. She was later re assigne d to the Trust for her second year of tenure with IFESH TFA, during which time she managed the volunteer program and assisted with general operations of the Trust. Christine returned to the U.S. to pursue graduate studies in natural resource management In 1998 she joined the masters program in Human Dimensions of Natural Resources at Colorado State University, where she earned her M.Sc. in 2001. That same year, she began her doctoral studies in the Department of Wildlife Ecology and Conservation at the University of Florida, continuing her focus on Human Dimensions. During her studies at the University of Florida, Christine was hired as a temporary instructor and developed and taught a course in Human Dimensions of Wildlife Management. Upon completion of her Ph.D. program, Christine will seek employment in the broad field of Human Dimensions. Christine has been married to her husband, Richard Nuez, for 11 years. They have two children: Mara, age 4, and Kai, age 1.