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Group Title: Water Quality Initiative Series circular - UF Soil Science Dept. ; no. 964
Title: Beans & southern peas
CITATION THUMBNAILS PAGE IMAGE ZOOMABLE
Full Citation
STANDARD VIEW MARC VIEW
Permanent Link: http://ufdc.ufl.edu/UF00067145/00001
 Material Information
Title: Beans & southern peas managing pesticides for crop production and water quality protection : a supplement to the IFAS pest control guides
Series Title: Water quality initiative series Soil Science Dept
Alternate Title: Beans and southern peas
Managing pesticides for crop production and water quality protection
IFAS pest control guides
Physical Description: 11 p. : ; 28 cm.
Language: English
Creator: Buttler, T. M
University of Florida -- Soil Science Dept
Publisher: Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of Florida
Place of Publication: Gainesville Fla
Publication Date: 1991
 Subjects
Subject: Beans -- Diseases and pests -- Control -- Environmental aspects -- Florida   ( lcsh )
Cowpea -- Diseases and pests -- Control -- Environmental aspects -- Florida   ( lcsh )
Pesticides -- Environmental aspects -- Florida   ( lcsh )
Soil surveys -- Florida   ( lcsh )
Genre: government publication (state, provincial, terriorial, dependent)   ( marcgt )
non-fiction   ( marcgt )
 Notes
Statement of Responsibility: T.M. Buttler ... et al..
General Note: Cover title.
General Note: "May 1991."
Funding: Circular (Florida Cooperative Extension Service) ;
 Record Information
Bibliographic ID: UF00067145
Volume ID: VID00001
Source Institution: University of Florida
Rights Management: All rights reserved by the source institution and holding location.
Resource Identifier: oclc - 24703901

Table of Contents
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        Page 2
        Page 3
        Page 4
        Page 5
        Page 6
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        Page 8
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        Page 10
        Page 11
        Page 12
Full Text





HISTORIC NOTE


The publications in this collection do
not reflect current scientific knowledge
or recommendations. These texts
represent the historic publishing
record of the Institute for Food and
Agricultural Sciences and should be
used only to trace the historic work of
the Institute and its staff. Current IFAS
research may be found on the
Electronic Data Information Source
(EDIS)

site maintained by the Florida
Cooperative Extension Service.






Copyright 2005, Board of Trustees, University
of Florida









Soil Science Department
Water Quality Initiative Series


Circular 964
May 1991


BEANS & SOUTHERN PEAS


C>
C.-..
N,


MANAGING PESTICIDES FOR CROP PRODUCTION

AND WATER QUALITY PROTECTION


Ni

C-J'
~2 'N


A Supplement to the IFAS Pest Control Guides


T. M. BUTLER
and
A. G. HORNSBY
Soil Science Department

W. M. STALL
Vegetable Crops Department

F. A. JOHNSON
Entomology and Nematology Department

J. W. NOLING
CREC, Lake Alfred, FL

T. A. KUCHAREK
Plant Pathology Department
Institute of Food and Agricultural Sciences
University of Florida
Gainesville, FL 32611





Florida Cooperative Extension Service
Institute of Food and Agricultural Sciences
University of Florida, Gainesville
John T. Woeste, Dean for Extension









WATER QUALITY CONSIDERATIONS IN
BEAN PRODUCTION

Concern about the harmful effects of pesticides on
surface water and groundwater quality should
motivate bean growers to select pesticides with the
least potential to cause water quality problems.
Many bean growers live in rural areas near where
they and other growers raise beans, therefore, their
personal water supply is susceptible to
contamination. Unfortunately, information that
allows growers to select pesticides less likely to
affect water quality has not previously been readily
available.

Our purpose is to provide information that can help
growers select pesticides that will have a minimum
adverse impact on water quality. The procedure
considers the soil properties of the application site,
the mobility of pesticides in these soils, and the
toxicity of the pesticides in water to humans and
aquatic species. A proper selection will decrease
chances of adversely affecting surface water and
groundwater quality. Certain combinations of soil
and pesticide properties (along with weather
conditions) can pose a significant potential hazard
to water quality. Our goal is to identify and avoid
these circumstances. Information contained in this
report can help bean growers make better decisions
about the pesticides that they use. This document
in no way endorses any particular pest control
product. All products must be used in accordance
with the label.


MATERIALS NEEDED TO USE THIS
PROCEDURE

To effectively use this procedure you will need the
following source materials:

1. A copy of the current IFAS Pest Control Guides
or other appropriate information sources that
identify pesticides that control specific pests.

2. A copy of your county soil survey report to
identify the soil types found in your fields.

3. A copy of the Soil Science Fact Sheet entitled
"[Name of your countv]:Soil Ratings for Selecting
Pesticides" for your county, available from your
county Cooperative Extension Office. The basis of
these ratings are given in the IFAS Extension


Circular 959 entitled "Soil Ratings for Selecting
Pesticides for Water Quality Goals," which is also
available from your county Cooperative Extension
Office.

Note: If your county has not yet been mapped by
the Soil Conservation Service, you will need to
contact the local SCS office for a site evaluation and
determination of soil types and ratings for leaching
and runoff of pesticides.


IMPORTANT FACTORS
PESTICIDE SELECTION


THAT AFFECT


How pesticides behave in the soil is determined by
many factors including properties of the pesticides
and of the soil at the application site. Some of the
factors that should be considered when selecting
pesticides with minimal potential for water quality
impacts are:

Pesticide properties 1) The organic carbon
adsorption coefficient, KI describes the relative
affinity or attraction of the pesticide to soil
materials and therefore its mobility in the soil. 2)
The biological degradation half-life, T, is a
measure of persistence of the pesticide in soil. 3)
The lifetime health advisory level or equivalent,
HALEQ, is a measure of health risk to humans of
pesticide contaminated drinking water. 4) Aquatic
toxicity, LCso is a measure of the ability of the
pesticide to cause 50% mortality in aquatic test
species.

Soil properties 1) Hydraulic permeability is a
measure of the soils ability to allow water to
percolate through it. 2) Organic matter is
important for providing binding sites for pesticides,
thus reducing their mobility and increasing their
opportunity to be degraded by soil microorganisms.
3) Slope affects the potential for water to run off
the land surface.

Management practices 1) Pesticide application
frequencies and rates determine the total amount
applied. Lower frequencies and rates reduce the
potential for contamination. 2) Application
methods affect the amount of pesticide subject to
transport by water. For example, if applied directly
to the soil, there is a greater probability that more
of the product will be available for leaching or
runoff than if applied to the foliage. If the product









is incorporated into the soil, leaching may be the
most important loss pathway. Pesticides applied to
the foliage may be lost to the atmosphere,
decomposed by sunlight, or absorbed by the foliage,
thereby reducing the amount available for wash-off
and transport to water bodies. Irrigation practices
can also determine the loss pathways of pesticides.
Pesticides often move with water, so the less excess
water that is applied the less potential there is for
a pesticide to move past the crop root zone or to
run off in surface water. Rainfall or overhead
irrigation can wash off significant quantities of
pesticides from foliage immediately after
application.


INDICES USED TO SELECT PESTICIDES

Table 1 contains two important indices, the
pesticide leaching potential (RLPI) and the
pesticide runoff potential (RRPI). Both indices are
relative. For a given soil, these indices rank the
pesticides by their potential to move from the
application site by the indicated pathway (leaching
or runoff). The indices are based on the organic
carbon sorption coefficient and degradation half-life
values of each pesticide. Values for these
parameters have been taken from scientific
literature, technical manuals, and company product
literature.

The Relative Leaching Potential Index (RLPI)
defines the relative attenuation (reduction in mass
as it moves through the soil) of each pesticide in
soil, and therefore its potential to leach to
groundwater. Pesticides that are very mobile, for
example, those that have Ko values less than 100 in
sandy soils, or 50 or less in fine-textured soils
should be used with caution. There is some
uncertainty in the data used to calculate this index.
However, since the values are relative they can still
be used. It is important to realize that the smaller
the RLPI value of a pesticide the greater is its
potential to leach.


The Relative Runoff Potential Index (RRPI)
defines the relative immobility and availability of
each pesticide in soil, and therefore its potential to
remain near the soil surface and be subject to loss
in the aqueous phase or sediment phase of runoff.
There is some uncertainty in the data used to
calculate this index. However, since the values are


relative they can still be used. The smaller the
RRPI value of a pesticide the greater is its potential
to be lost in runoff.

Table 1 also contains information on the toxicity of
pesticides to humans and aquatic species. This
information can be used as a secondary
consideration in the pesticide selection procedure.


The Lifetime Health Advisory Level or Equivalent
(HALEQ) provides a measure of pesticide toxicity
to humans. The lifetime health advisory level as
defined by the USEPA is the concentration of a
chemical in drinking water that is not expected to
cause any adverse health effects over a lifetime of
exposure (70 years), with a margin of safety. The
values in Table 1 are the USEPA lifetime health
advisory level, HAL, or an equivalent value,
HALEQ (denoted by a superscripted asterisk),
calculated using the same formula used by the
USEPA (HALEQ = RfD x 7000), where RfD is
the reference dose determined by the USEPA. For
non-carcinogenic pesticides the calculated HALEQ
should not differ by more than a factor of 10 from
the values forthcoming from the USEPA. The
HAL or HALEQ has units of micrograms per liter
(lg/l, or ppb). The smaller the value the greater is
the toxicity to humans.

The Aquatic Toxicity provides a measure of
pesticide toxicity to aquatic species. The values
given in Table 1 are the lethal concentrations at
which 50% of the test species die (LC, ). Unless
otherwise noted by a lower case letter following the
value, the test species was rainbow trout. The
smaller the value the greater is the toxicity to
aquatic species.

Data for K,, RLPI, RRPI, HALEQ, and aquatic
toxicity are given for the active ingredient (common
name) of a product. When using a product that is
a mixture of two or more active ingredients use the
RLPI, RRPI, HALEQ, and Aquatic Toxicity value
for the most restrictive active ingredient in the
mixture.

Important Note: The information presented in
Table 1 DOES NOT supersede or replace the
information on the pesticide container label or
product literature.









CRITERIA FOR MATCHING SOIL RATINGS WITH PESTICIDE INDICES


Pesticides with less potential to adversely affect water quality can be selected by matching the soil ratings and
pesticides using the following criteria:


PESTICIDE SELECTION CRITERIA


IF SOIL RATINGS
ARE:


RUNOFF


LEACH

HIGH


MEDIUM

LOW


HIGH


MEDIUM


LOW


HIGH


MEDIUM


LOW


LOW

LOW

LOW


MEDIUM


MEDIUM


MEDIUM


HIGH


HIGH


HIGH


THEN
SELECT PESTICIDE WITH:


Larger RLPI value,

Larger RLPI value,

Larger RLPI and
RRPI values,

Larger RLPI and
RRPI values,

Larger RLPI and
RRPI values,

Larger RRPI value,


Larger RLPI and
RRPI values,

Larger RRPI and
RLPI values,

Larger RRPI value,


AND Larger HALEQ value.

AND Larger HALEQ value.

AND Larger HALEQ and
Aquatic Toxicity values.

AND Larger HALEQ and
Aquatic Toxicity values.

AND Larger HALEQ and
Aquatic Toxicity values.

AND Larger Aquatic Toxicity
value.

AND Larger HALEQ and
Aquatic Toxicity values.

AND Larger Aquatic Toxicity
and HALEQ values.

AND Larger Aquatic Toxicity
value.


PROCEDURE FOR SELECTING PESTICIDES
TO REDUCE ADVERSE WATER QUALITY
IMPACTS

A "Pesticide Selection Worksheet" is provided as a
convenient way to organize the information needed
to select pesticides to avoid water pollution by
pesticides in a particular production or management
unit. Instructions for using the worksheet are
outlined below. The function of the worksheet is to
match the soil leach and runoff ratings at the
application site with the pesticide RLPI (leaching)
and RRPI (runoff) indices and toxicity values given
in Table 1.


This will indicate the relative potential for pesticides
to leach or run off from a particular site and
consider the toxicity of the pesticides to humans or
aquatic life if the pesticides leach into groundwater
or if runoff enters surface impoundments or
streams. The last two columns are for recording the
bean grower's choices and reasons for selecting
particular products.

Our intent is to provide a decision support tool for
the bean grower. The grower is responsible for
making the final choice. The completed worksheet
can serve as a permanent record of the selection
process used and decision made by the grower.









USING THE WORKSHEET


1. TARGET PEST: Correct identification of the
pests that need to be controlled is essential! Check
with knowledgeable experts and utilize competent
diagnostic laboratories so that a proper diagnosis
can be made. Misdiagnosis results in the wasteful
use of unnecessary pesticides and needless increases
in production costs. List confirmed pests in column
1 of the Pesticide Selection Worksheet.


2. RECOMMENDED PESTICIDES: Use the
current IFAS Pest Control Guides, or other
appropriate information sources to identify the
pesticides that control the pests of concern. List
these pesticides in column 2 of the Pesticide
Selection Worksheet.


3. PESTICIDE PROPERTIES: For each pesticide
listed in column 2 on the Pesticide Selection
Worksheet, copy the numeric value for K, RLPI,
RRPI, HALEQ, and Aquatic Toxicity from Table 1
into columns 3, 4, 5, 6, and 7 of the Pesticide
Selection Worksheet.


4. SOIL PROPERTIES: Consult the County Soil
Survey Report soil map sheets to locate your
production fields and to identify the soils that occur
in these fields. Use the Soil Science Fact Sheet
entitled "[Your County]:Soil Ratings for Selecting
Pesticides" (available from your county Cooperative
Extension Office) to determine the leaching and
surface runoff rating of the soils in your fields. As
you determine the soil leach rating and the soil
runoff rating for each soil in each field, list the soil
name, soil leach rating, and soil runoff rating in
columns 8, 9, and 10, respectively, of the Pesticide
Selection Worksheet.


5. SELECTION OF PESTICIDES: Using infor-
mation that you have compiled on the Pesticide
Selection Worksheet, select appropriate pesticides
using the selection criteria on page 4 to match soil
and pesticide properties. The selection made can
be recorded in column 11 and notes relating to the
selection can be recorded in column 12.


Notes:
1. If the pesticide product selected is a formulated
mixture or a tank mix, each active ingredient must
be considered. The most restrictive pesticide in the
mixture will determine the choice. Trade names in
Table 1 followed by (M) are formulated mixtures.

2. Sometimes there may not be a clear choice from
among the alternative chemicals available to control
a particular pest. In these cases, first order
screening using the RLPI or RRPI only can suffice.

3. Depth to groundwater and local geohydrology
may influence your final selection. Shallow
groundwater is more vulnerable to contamination.
Deep water tables with intervening impermeable
geologic layers are much less vulnerable.

4. Distance to surface water bodies may also
influence your final selection. Surface waters
adjacent to or near the pesticide application site are
more vulnerable to contamination than those further
away. If surface runoff from the application site
usually infiltrates into the soil off site before
reaching a surface water body, then the HALEQ
should be considered as the secondary screening
index.












IAnLC I. neM nu a IumKiane reas rcn~l.u ra laMenc nat< 1A. iU jCrtc tlr restm luI-a Lto mnimin e wader luuarly rrooteMi. U0/U1/1

Sorption Relative Losses Toxicity
Application Type2 Coefficient3 Leaching Runoff HAL or HALEQ6 Aquatic LC,
Trade Name' Common Name Soil Foliar Ko (mL/g) RLPI4 RRPI5 (ppb) (ppm)


Herbicide


Amiben
Basagran
Dacthal
Dual
Eptam
Eradicane
Gramoxone Extra
Prowl
Roundup
Treflan


chloramben
bentazon
DCPA
metolachlor
EPTC
EPTC
paraquat
pendimethalin
glyphosate
trifluralin


Insecticide/Miticide


parathion
esfenvalerate
Bacillus thuringiensis
Bacillus thuringiensis
parathion
dimethoate
malathion
dimethoate
disulfoton
nailed
Bacillus thuringiensis
fonofos
trichlorfon
azinphos-methyl
Bacillus thuringiensis
dicofol
cryolite


5,000
5,300
nd
nd
5,000
20
1,800
20
600
180
nd
870
10
1,000
nd
18,000
nd


E >2,000
1,510
nd
nd
E >2,000
29
>2,000
29
E 200
1,800
nd
318
10
1,000
nd
E >2,000
nd


HAL or HALEQ": Lifetime Health Advisory Level or Lifetime Health Advisory Level Equivalent.

Continued---


15
34
5,000
200
200
200
1,000,000
5,000
24,000
8,000


11
17
500
22
333
333
>2,000
556
>2,000
1,330


100
20
4,000
100
200
200
30
300
700
5


non toxic
635
lOOa
2
17
17
15
0.199b
8.3
0.041


Atkran
Asana
Bactospeine
Bactur
Bladan
Cygon
Cythion
Defend
Di-Syston
Dibrom
Dipel
Dyfonate
Dylox
Guthion
Javelin
Kelthane
Kryocide


14
5
nd
nd
14
29
556
29
56
>1,000
nd
29
10
100
nd
1
nd


1.43
0.00069j
95b
95b
1.43
6.2
0.2
6.2
1.85
0.195
95b
0.02
0.4
0.0043
95b
0.52b
47


-rrr o---- -~ CUIL--- n,,, o,,--;~ ~~- ~II Y-~-;r +~- CLIU~;Y OUC-^-~U C^ Y---------- Il-L-- C___I-L__ ~_~II


~rLll










TABLE 1. Beans and Southern Peas Pesticide Parameter Natrix--- Continued:


Sorption Relative Losses Toxicity
Application Type2 Coefficient3 Leaching Runoff HAL or HALEQ6 Aquatic LC,7
Trade Name1 Common Name Soil Foliar Ko (ml/g) RLPI4 RRPI5 (ppb) (ppm)


Insecticide/Miticide


methomyl
methoxychlor
oxydemeton-methyl
methomyl
acephate
parathion
methyl-parathion
mevinphos
trichlorfon
piperonyl butoxide
pyrethrins
insecticidal soap
carbaryl
Bacillus thuringiensis
diazinon
sulfur
phorate
endosulfan
Bacillus thuringiensis
carbophenothion
methyl-parathion


72
80,000
10
72
2
5,000
5,100
44
10
nd
nd
nd
300
nd
1,000
nd
1,000
12,400
nd
46,000
5,100


ethoprop


metalaxyl
benomyl


50
1,900


24
>2,000
10
24
7
E >2,000
E >2,000
147
10
nd
nd
nd
300
nd
E 250
nd
E 167
>2,000
nd
>2,000
E >2,000


7 400 >100
2 400 0.17


HAL or HALEQb: Lifetime Health Advisory Level or Lifetime Health Advisory Level Equivalent.

Continued---


Lannate
Marlate
Metasystox-R
Nudrin
Orthene
Para Mar
Penncap M
Phosdrin
Proxol
Pyronone(M)
Pyronone(M)
Safer Soap
Sevin
Sok
Spectracide
Sul-Cide
Thimet
Thiodan
Thuricide
Trithion
Wofatox


Nematicide


Mocap


3.4
0.062
6.4
3.4
730
1.43
3.7
0.0119
0.4
0.0034
114a
nd
114
95b
0.09
non toxic
0.013
0.0014
95b
nd
3.7


Fungicide


Apron
Benlate


28 0.1 *










TABLE 1. Beans and Southern Peas Pesticide Parameter Natrix--- Continued:


Sorption Relative Losses Toxicity
Application Type2 Coefficient3 Leaching Runoff HAL or HALEQ6 Aquatic LC 7
Trade Name Comon Name Soil Foliar Kc (ml/g) RLPI4 RRPI5 (ppb) (ppm)

Fungicide

Blue Shield cupric hydroxide x nd nd nd nd 0.08
Botran DCNA x 1,000 E 167 17 200 7
Bravo chlorothaloni x 1,380 460 24 2 0.049
Champion cupric hydroxide x nd nd nd nd 0.08
Chloroneb chloroneb x 1,650 127 5 90 >4,200b
Copper-Count-N copper ammonium carbonate x nd nd nd nd 0.0204
Dusting Sulfur sulfur x nd nd nd nd non toxic
K-Cop copper ammonium carbonate x nd nd nd nd 0.0204
Kocide cupric hydroxide x nd nd nd nd 0.08
Kolodust sulfur x nd nd nd nd non toxic
Kolospray sulfur x nd nd nd nd non toxic
Oxycop copper ammonium carbonate x nd nd nd nd 0.0204
Ridomil metataxyl x 50 7 7 400 >100
Rovral iprodione x 700 500 102 300 6.7
Super-six sulfur x nd nd nd nd non toxic
Tenn-Cop copper salts rosin acids x nd nd nd nd toxic
Terraclor PCNB x 5,000 E >2,000 10 20 low toxicity
Topsin M thiophanate-methyl x 1,830 E 1,830 55 600 11d
Tri-Basic copper sulfate basic x nd nd nd nd nd


Fumigants for Control of Soil Fungi and Nematodes

Telone II 1,3-dichloropropene INJ 32 32 32 0.2 5.5
Vorlex(M) M.I.T. INJ 6 9 9 nd 0.37
Vortex(M) 1,3-dichloropropene INJ 32 32 32 0.2 5.5


HAL or HALEQU: Lifetime Health Advisory Level or Lifetime Health Advisory Level Equivalent.

Continued---








TABLE 1. Beans and Southern Peas Pesticide Parameter Matrix--- Continued:

1Trade Name: (M) indicates that the product is a mixture of two or more active ingredients.
2Application Type: INC: incorporated INJ: injected x: applied to soil surface or foliage
3Sorption Coefficient: E: estimated G: educated guess
4Relative Leaching Potential Index (RLPI):Smaller number indicates greater leaching hazard.
5Relative Runoff Potential Index (RRPI): Smatter number indicates greater runoff hazard.
6HAL or HALEQ: Lifetime Health Advisory Level or Lifetime Health Advisory Level Equivalent.
*: Lifetime Health Advisory Equivalent
7Aquatic Toxicity LCo,: value is for rainbow trout 48 or 96 hr exposure time, unless otherwise specified
a=channel catfish b=bluegill d=goldfish j=fat head minnow
nd: no data available.








PESTICIDE SELECTION WORKSHEET


Landowner/Operator


County:


Farm ID:


Date:


Field ID Sheet of


IFAS Relative Losses Toxicity Soil Soil
Target Pest Recommended K. Leaching Runoff Lifetime Aquatic Soil Leaching Runoff Selected Comments
Pesticides Value RLPI RRPI HALEQ* Toxicity Type Rating Rating Pesticide
(1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12)


If the K. value is 100 or less or if the RLPI value is 10 or less and the soil leach rating is high, then
be used with extreme caution. Alternative pesticides and reduced rates should be considered if possible.
if possible.


the pesticide has a high potential for leaching and should
Apply pesticide during periods with low potential for rainfall


Crop:


U-.


w


.





PESTICIDE SELECTION WORKSHEET


Landowner/Operator Name:


Farm ID:


Countv:


Date:


Field ID Sheet of


IFAS Relative Losses Toxicity Soil Soil
Target Pest Recommended K, Leaching Runoff Lifetime Aquatic Soil Leaching Runoff Selected Comments
Pesticides Value RLPI RRPI HALEQ* Toxicity Type Rating Rating Pesticide
(1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12)














































If the Ko value is 100 or less or if the RLPI value is 10 or less and the soil teach rating is high, then the pesticide has a high potential for leaching and should
be used with extreme caution. Alternative pesticides and reduced rates should be considered if possible. Apply pesticide during periods with Low potential for rainfall
if possible.


Croo:


-I-


---'









Acknowledgements:


The development of this document was supported by the USDA/ES Water Quality Initiative Project
#89EWQI-1-9134 and the IFAS Center for Natural Resources, University of Florida, Gainesville, FL.
Printing supported by the U.S. Department of Agriculture, Extension Service under special project
#90EWQI-1-9214.





















































COOPERATIVE EXTENSION SERVICE,UNIVERSITYOFFLORIDA,INSTITUTEOF FOODANDAGRICULTURALSCIENCESJohnT.Woes:e.'
Director, in cooperation with the United States Department of Agriculture, publishes this information to further the purpose of the May 8 and June
30,1914 Acts of Congress; and is authorized to provide research, educational information and other services only to individual's and insttutons tha
function without regard to race, color, sex, age, handicap or national origin. Single copies of extension publications (excluding 4-H and youth
publications) are available free to Florida residents from county extension offices. Information on bulk rates or copies for out-of-state purchasers
is availablefrom C.M. Hinton, Publications Distribution Center, IFAS Building 664, Universityof Florida,Gainesville, Florida32611.Before pub'iczing
this publication, editors should contact this address to determine availability. Printed 10/91.




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