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2021 | OriginalPaper | Chapter

5. Environmental Policy Instruments for Agriculture

Authors : James Shortle, Markku Ollikainen, Antti Iho

Published in: Water Quality and Agriculture

Publisher: Springer International Publishing

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Abstract

Agriculture poses a unique set of challenges for water pollution control policy that emerge from the large spatial scope of agricultural production, the small-scale spatial heterogeneity and complexity of agricultural operations, the complex and diffuse pathways by which pollutants move from agricultural land to water resources, and the importance of weather to pollution events. This chapter explores the implications of these characteristics for the choice of water quality goals and policy instruments for agriculture. The chapter presents a framework for characterizing policy instruments based on property rights, policy targets, and regulatory mechanisms; discusses essential features of policies that are effective and efficient; and presents and illustrates concepts and methods for policy optimization using simple numerical examples and empirical case studies. The chapter evaluates contemporary agricultural nonpoint pollution controls given the criteria and the principles for efficient policy. These policies are dominated by voluntary compliance approaches that rely on information programs to encourage producers to adopt pollution control practices and participate in programs that provide subsidies in various forms to facilitate adoption. The effectiveness and efficiency of the voluntary compliance approaches are generally limited by a variety of factors. These include the reliance on farmer self-selection into pollution control programs, a reliance on public spending to purchase pollution controls, suboptimal targeting of locations for public expenditures on pollution control, muddled policy objectives, and unproductive economic spillovers. Policy reforms that can improve the voluntary approach are suggested but the fundamental limitations of the approach suggest a need for innovative alternatives. The chapter presents examples that are in the Pigouvian tradition of internalizing externalities through policies requiring mandatory compliance. The chapter provides overall guidelines for better policies but concludes that no single option stands out for all circumstances. Identifying the best choice for a particular problem requires place-based evaluation of options.

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Appendix
Available only for authorised users
Footnotes
1
Metering pollution for scientific research can be done in small, instrumented plots. Metering for regulatory purposes requires routine accurate measurements for regulated sources.
 
2
The figure is a representation of the concept of managing pollution probabilistically and is not based on a specific location BMP.
 
3
Our discussion of managing water quality risk with nonpoint sources is focused on managing the probability distribution of the total pollution load at a targeted receptor (or receptors). At the farm and field scales some kinds of risk can be controlled effectively. For example, designing manure storage facilities to manage the risk of breaching from extreme rain events is a routine engineering problem given data on the severity and frequency of rainfall events is routine engineering design.
 
4
What we refer to as pay-the-polluter is sometimes referred to as the “beneficiary-pays” principle. Those who benefit from pollution reductions compensate polluters for their costs.
 
5
The model is based on Lankoski and Ollikainen (2003).
 
6
Though information rents are an unproductive use of resources, the additional farm income that comes when payment exceed costs is considered by some to be a positive feature of voluntary incentive programs (Segerson 2013).
 
7
The overall efficiency of multi-objective programs like the CRP and EQIP would consider the overall benefits provided versus their costs. Biases in favor of non-water quality objectives might compensate to some degree for inefficiencies in water quality protection if large benefits were obtained from the non-water quality objectives. Water quality is, however, likely the most significant environmental market failure associated with agriculture. Underweighting water quality protection in multi-objective programs likely decreases the overall efficiency of the spending.
 
8
The terms leakage and slippage are sometimes used synonymously. For example, Wu (2000, 2005) describes as slippage what we are describing as leakage. Following Fleming, Lichtenberg, and Newburn (2018), we find it useful to distinguish between spillovers that are internal to the farm as slippage and the analogous external spillovers from price changes as leakage.
 
9
Phase 5 CBWM has been superseded by Phase 6, which includes a new segmentation (Easton et al. 2017).
 
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Metadata
Title
Environmental Policy Instruments for Agriculture
Authors
James Shortle
Markku Ollikainen
Antti Iho
Copyright Year
2021
DOI
https://doi.org/10.1007/978-3-030-47087-6_5