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2021 | OriginalPaper | Buchkapitel

4. Decision Making at the Farm Level

verfasst von : James Shortle, Markku Ollikainen, Antti Iho

Erschienen in: Water Quality and Agriculture

Verlag: Springer International Publishing

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Abstract

A key theme of this book is that producers’ economic choices are the key determinants of water quality problems. Designing and implementing policies that are effective in managing water pollution from agriculture and do so without imposing undue social costs require an understanding of farm decisions making. This chapter introduces economic concepts and tools for analyzing farm decision making affecting key choices determining water quality outcomes. It begins with a brief introduction to key choices and objectives in farm decision making. The chapter then introduces standard economic models used to explain producers’ choice of crops, production inputs, and the spatial distribution of agricultural activity. These models are used to illustrate how various choices affecting water quality outcomes differ between market driven agricultural landscapes in which the costs of water pollution are external to producers, and agricultural landscapes in which choices balance the social benefits and costs of agricultural production. Subsequent sections introduce additional concepts and tools relevant to farm decision making on polluting inputs, crops, the spatial structure of production, and the use of best management practices. Concepts and models are illustrated by simple numerical examples and by empirical applications to significant water quality problems in the Gulf of Mexico and Chesapeake Bay.

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Fußnoten
1
Field boundaries are defined by various factors including physical features, legal boundaries, and historical practice. We say a field is mostly operated as a single unit as the area of the field will be planted to the same crop, or crop rotation, and subjected to the same field operations (tillage, planning, fertilization, harvesting) at more or less the same time. But advances in information technology enable “precision farming” that allows for spatial fine-tuning of certain farming practices like fertilizer applications within fields that would be otherwise managed as homogenous units. Within-field variations can result from variations in soils and other factors.
 
2
Water quality protection measures undertaken by producers motivated by their own environmental preferences entails private provision of a public good. Were producers the sole cause of a problem and their private benefits sufficiently great, private provision could achieve the Pareto Optimum. While there may be localized instances where this is the case, it is clearly not the general condition.
 
3
Maximizing short-term profits takes the farm capital as given. Farm capital comprises items like machinery, drainage of fields, and buildings. In the long run, producers also choose farm capital.
 
4
Climate and soils, for example, impose large constraints on economically viable crops. Some climates and soils are suitable to fruits or vegetable or wine grapes and some are not. Fixed inputs (farm labor, machinery, structures) also impose constraints on economically viable crops in the short run.
 
5
In the general economic theory of production, the technical relationship between input levels, both fixed and variable, and output is referred to as a production function.
 
6
In the general economic theory of production, yield response functions are total product functions for crop production inputs.
 
7
The Law of the Minimum implies at the plant level that yield responds linearly to fertilizer inputs up to a maximum at which some other input becomes limiting. Producers, however, do not manage individual plants but populations of plants in fields. Research demonstrates that when aggregating many plants over heterogeneous land areas, empirical response functions for land management units (i.e., fields) are nonlinear and display diminishing marginal returns (Berck and Helfand 1990).
 
8
As a caveat we note that land allocation and land use change is a considerably more complex topic than we have represented. The basic messages regarding the amount and pattern hold true, but a comprehensive analysis of market-driven and socially optimal landscapes requires consideration of many additional issues. There are many externalities in land use other than water quality that affect optimal patterns of use. There can be significant adjustment costs in land use change that affect market and Pareto Efficient allocations. Some land use changes are economically or ecologically irreversible so that the history of land use constrains subsequent use.
 
9
The models we have presented are bare bones versions to introduce key concepts and messages with minimal complexity. Models used in economic research are considerably more complex in the variables and relationships they include.
 
10
Even with ample manure producers may use some purchased fertilizer as a starter to initiate plant growth. Fertilizer management can use split applications. A starter is applied early in the season. Additional fertilizer may be applied after planting based on soil test indicating need.
 
11
Limits on manure application to fields may exist for reasons other than diseconomies of fertilizer application. For example, large manure application volumes may interfere with some field operations.
 
12
In some locations there may be a demand for manure sufficient to support markets in which excess manure can be sold as a fertilizer, soil conditioner, animal bedding (after treatment), or for other purposes (Parker 2004). The ability to sell manure can reduce the cost of excess manure when available.
 
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Metadaten
Titel
Decision Making at the Farm Level
verfasst von
James Shortle
Markku Ollikainen
Antti Iho
Copyright-Jahr
2021
DOI
https://doi.org/10.1007/978-3-030-47087-6_4

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