Economic Analysis of Avoiding a Potential Health Hazard on an Individual Farm
Source: American Society of Farm Managers and Rural Appraisers, by Robert O. Burton, Jr., Ross M. Key, Bryan W. Schurle, and David L. Regehr
Research indicates that farmers are more likely than the general population to experience certain types of cancer (e.g.,
Frey; Burmeister; Schuman, Mandel, and Blackard; Blair and Zahm). An ongoing study by the National Cancer Institute
(NCI) is addressing links between types of cancer and possible causes such as use of specific agricultural pesticides
(Alavanja, et al.). Moreover, chlorinated pesticides are suspected (but not proven) to be endocrine disruptors (Tilson, Keith).
The Endocrine Disruptor Research Initiative is analyzing chemicals suspected of being disruptors (EPA July 2003).
Atrazine: An Example Pesticide
This study will analyze the economic impacts of ceasing to use atrazine on a representative Kansas farm. Atrazine is
selected because it is widely used and because it has received scrutiny from the U.S. Environmental Protection Agency
(EPA) and from regulatory agencies in other countries. Atrazine is a triazine molecule that has chlorinated components.
National Agricultural Statistics Service (NASS 2006) data indicate that the average annual percentages of acres treated with
atrazine in their 29 program states were 68 percent of all corn and 69 percent of all sorghum. The EPA recognizes atrazine
as “one of the most widely used agricultural pesticides” with approximately 76.5 million pounds of active ingredient applied in
the U.S. annually (EPA January 2003a).
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Abstract
A ten-year linear programming model of a representative dryland crop farm in North Central Kansas is used to develop and
illustrate procedures for analyzing economic impacts of the elimination of one or more pesticides on an individual
farm. Atrazine is used as an example pesticide because of its widespread use and because concerns about atrazine have
been expressed in the United States and in other countries. An important outcome is that impacts on grain sorghum
would likely be greater than impacts on corn because more alternative and effective herbicides are available for
corn.
Robert O. Burton, Jr. is professor, Ross M. Key is former graduate research assistant, and Bryan W. Schurle is professor
and Head, Department of Agricultural Economics, Kansas State University; David L. Regehr is Professor, Department of
Agronomy, Kansas State University. Key currently works as an Agricultural Loan Officer, Elberfeld State Bank, Elberfeld, IN.
Concerns addressed in EPA’s recent review of atrazine included dietary, residential, and occupational risks (EPA January
2003b) and associations between atrazine exposure and cancer, effects of atrazine on amphibians, and atrazine in
watersheds (EPA October 2003). EPA noted that it “will continue its review of all new data submissions,” including results
from the NCI study mentioned above (EPA October 2003). Concerns about atrazine have been addressed in several other
countries. Australian National Registration Authority for Agricultural and Veterinary Chemicals (NRA) concluded that
agriculture needs atrazine, but recommended its removal from non-agricultural/home garden use (NRA 2002, Australian
Pesticides & Veterinary Medicines Authority). NRA noted that some members of the European Union have discontinued
atrazine use (NRA 1997).
Problem Statement
If links between illnesses and causes become more firmly established, there will be a need for economic analysis of
impacts of avoiding those causes on individual farms. The purpose of this study is to develop and illustrate procedures for
analyzing economic impacts of the elimination of one or more chemicals on an individual farm. Atrazine use on a
representative farm in Kansas will be used as an example. The following questions will be addressed:
1) What is the representative farm’s return over variable costs with and without atrazine?
2) What is the representative farm’s capital carried forward with and without atrazine?
3) What is the representative farm’s cost of production with and without atrazine?
4) What is the representative farm’s number of acres of corn and grain sorghum farmed with and without atrazine?
5) What level of usage tax might cause producers to cease use of atrazine?
6) What effect does yield reduction have on a producer’s decision to eliminate atrazine?
Representative Farm
The representative farm was based on the 2003 average of crop farms in the North Central Kansas Farm Management
Association (KFMA). The farm owned 392 acres of land and rented 844 acres. All land was non-irrigated. Representative
proportions of crops produced were 40 percent hard red winter wheat, 24 percent grain sorghum, 20 percent soybeans, and
16 percent corn. Average non-farm income was $26,732 and average family living expenses were $39,652, including $4,133
for income taxes and self-employment taxes. Input costs for seed, fertilizer, and other expenses were based
on 2003 Kansas farm management guides (Kansas State University Agricultural Experiment Station and Cooperative
Extension Service). Cash rent of $39 per acre was based on 2003 data for North Central Kansas (Dhuyvetter and Kastens).
Machinery costs were based on 2003 custom rates for Kansas (KASS).
Herbicide programs and prices were suggested by Dave Regehr, Weed Science Extension Specialist. Dr. Regehr routinely
interacts with farmers, crop consultants, and other agricultural professionals. Therefore, he is an excellent source of
information about weed management and yield changes associated with alternative weed control programs. Herbicides
for wheat and soybeans did not include atrazine. Herbicide programs for corn and grain sorghum with and without atrazine
use trade names to identify products. No endorsement is intended, nor is any criticism implied of similar products not
mentioned.
Our analyses used the following per acre herbicide programs: for corn, 1 quart of Glyphomax Plus as a burndown application
followed by 2.4 quarts of Lumax (s-metolachlor, atrazine and mesotrione) in a pre-emergence application, and 1 ounce of
Spirit as a post-emergence herbicide. For sorghum, 1 quart of Glyphomax Plus as a burndown followed by 2.1 quarts of
Bicep II Magnum in a pre-emergence application, and 2 pints of Buctril+Atrazine (1 pt. Buctril and 1 pt. atrazine) as a
postemergence herbicide. Herbicide programs per acre without atrazine were as follows: for corn, 1 quart of Glyphomax Plus
as a burndown followed by 12 ounces of Epic (Balance and Define) as a pre-emergence application, and 6 ounces of Distinct
as a post-emergence herbicide. Costs of these herbicides for use in corn were $50.37 with atrazine and $53.33 without
atrazine. Thus, corn herbicide costs without atrazine were $2.96 (5.88%) higher than corn herbicide costs with atrazine. For
sorghum, 1 quart of Glyphomax Plus as a burndown followed by 1.6 pints of Dual Magnum as a pre-emergence application
and 1.5 pints of Buctril as a post-emergence herbicide. Costs for weed control on sorghum were $41.37 with atrazine and
$44.72 without atrazine. Thus, sorghum herbicide costs without atrazine were $3.35 (8.10%) higher that sorghum herbicide
costs with atrazine. These costs represent a 2003 price level and include appropriate adjuvants. Herbicide application costs
were the same for corn and grain sorghum with and without atrazine. Weed scientist Regehr stated that a 10-20 percent
yield reduction in sorghum can occur when the program changes from using atrazine to not using atrazine. No yield
reduction is expected when the corn program changes from using atrazine to not using atrazine. This study accounts for
sorghum yield reductions by analyzing reductions of 5, 10, and 20 percent. Revenue from the crop activities included crop
sales and government payments. The average yield for 1992-2003 for Mitchell County Kansas was used. A twelve-year
average was used because the data were readily available (NASS 2004). The county average for 1998-2001 established the
government program yields for this analysis. Government payment data were obtained from the Farm Service
Agency (FSA). Target prices and loan rates for each commodity were established through 2007. Direct, counter-cyclical
(CCP), and loan deficiency payments (LDP) were calculated in accordance with FSA guidelines. We assumed that the
government program will not change over the 10-year time period modeled. We know that farm programs change more
frequently than this. However, at the time this study was prepared, details of future farm programs were unknown and we
wanted to use a ten-year time period to model how capital carried forward might be affected over time. Prices were based on
historical data and price estimates from the Food and Agricultural Policy Research Institute (FAPRI).
The FAPRI 2003 price level estimates for 2004-2013 were used as national price levels for the analysis. For the calculation of
the loan deficiency payment portion of the government program, it is necessary to have county-level price information.
County prices were established by calculating the 12-year average price basis (1992-2003) between national and county
prices obtained from NASS for each commodity and subtracting this basis from the FAPRI prices.
Capital Carried Forward
Capital carried forward was investigated to determine how the amount of capital available at the end of each year was
affected by elimination of atrazine. Capital carried forward was calculated by subtracting fixed costs of land and buildings,
adding non-farm income and subtracting the cost of living from return over variable costs.
Fixed Costs
For machinery costs, this analysis used custom rates which include variable and fixed costs for machinery and labor.
However, to calculate capital carried forward, fixed costs of land and buildings are needed. Initially fixed costs for land and
buildings were calculated by multiplying the total value of land and buildings by a rent-to-value percentage of 5.1 percent,
established by Dhuyvetter and Kastens, plus 0.5 percent for building depreciation (based on KFMA data) and another 0.4
percent for insurance and any miscellaneous expense. In preliminary model runs, when fixed costs for land and buildings
were estimated as 6 percent of value, capital carried forward was negative in all 10 years. For most operations, not all fixed
costs are cash costs and not all farmers consider all economic cost when evaluating their operations. Therefore, for this
study, fixed costs of land and buildings were estimated as three percent of value.
Linear Programming Model
The linear programming (LP) model of the representative farm maximizes return over variable cost for a ten-year period. Crop
production activities included corn, grain sorghum, soybeans, and wheat. Constraints included owned and rented land and
rotation restrictions. In order to measure the economic impacts associated with ceasing to use atrazine, the amount of
capital available without borrowing was set at a high level to ensure that acres farmed in all model runs would be the same
as total acres for the representative farm. Labor and machinery constraints are not included because all machinery
operations are custom hired. The LP model was run in Excel using the simplex solver. The model included corn and grain
sorghum production activities with atrazine and with the alternative weed control program.
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