13.2 Environmental externalities and agricultural production
5 min read•july 30, 2024
Agricultural production generates both positive and negative environmental externalities. These impacts, like and , affect third parties and the environment. Understanding these externalities is crucial for .
Economic analysis reveals how externalities lead to market inefficiencies. Policy approaches, such as and , aim to internalize these costs and benefits. Valuing agricultural externalities presents challenges in measurement, attribution, and nonmarket valuation.
Environmental Externalities in Agriculture
Types of Externalities
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Agricultural production generates both positive and negative environmental externalities
Positive externalities provide benefits to third parties (carbon sequestration, )
Negative externalities impose costs on others not directly involved in the production process (water pollution, )
Major negative externalities from agriculture:
Water pollution from nutrient runoff (nitrogen, phosphorus)
Excessive nutrient runoff from fertilizer application leads to and hypoxic "dead zones" in water bodies (Gulf of Mexico)
and
Soil erosion reduces future land productivity and causes sedimentation in waterways, impacting aquatic habitats (reduced fish populations)
Air pollution from livestock operations
Concentrated animal feeding operations (CAFOs) emit ammonia, hydrogen sulfide, and particulate matter, affecting local air quality (respiratory issues in nearby communities)
Loss of biodiversity
Conversion of natural habitats to cropland and excessive pesticide use contribute to (decline in pollinator populations)
Positive Externalities
Positive externalities from agriculture encompass :
Carbon sequestration in soils
Agricultural practices like no-till farming and cover cropping can increase soil organic carbon, mitigating greenhouse gas emissions (climate change mitigation)
Groundwater recharge
Certain agricultural landscapes, such as wetlands and riparian buffers, facilitate groundwater recharge, replenishing aquifers (improved water security)
Preservation of rural landscapes and open space
Agricultural lands provide scenic amenities and recreational opportunities, contributing to rural tourism and quality of life (agritourism, hunting, fishing)
Economic Analysis of Agricultural Externalities
Causes and Consequences
Environmental externalities arise when the actions of agricultural producers have unintended and uncompensated impacts on third parties or the environment
Occur due to incomplete property rights and missing markets for environmental goods and services (lack of prices for clean air, water)
(PMC) of agricultural production only includes direct costs borne by the producer
In the presence of negative externalities, (SMC) exceeds PMC, as it incorporates additional external costs imposed on society
When producers only consider PMC and ignore external costs, they tend to overproduce the good generating the compared to the socially optimal level
Leads to and inefficient allocation of resources (overuse of fertilizers, pesticides)
Positive externalities from agriculture lead to underprovision of the beneficial activity, as producers do not fully capture the social benefits
(SMB) exceeds (PMB) (underprovision of ecosystem services)
Coase Theorem and Transaction Costs
suggests that in the absence of , private bargaining between affected parties can lead to an efficient outcome, regardless of the initial allocation of property rights
Example: if a downstream water user has the right to clean water, they could pay an upstream farmer to reduce nutrient runoff
However, high transaction costs often preclude such solutions for environmental externalities
Large number of affected parties, information asymmetries, and free-rider problems make private bargaining infeasible (diffuse pollution from multiple agricultural sources)
Policy Approaches to Internalizing Externalities
Pigouvian Taxes and Subsidies
Pigouvian taxes can be imposed on activities generating negative externalities
Tax on fertilizer or pesticide use
Optimal tax rate equals marginal external cost at the socially efficient level of output, forcing producers to internalize the externality
Pigouvian taxes are efficient as they incentivize producers to reduce the externality-generating activity to the socially optimal level
However, they place the cost burden on producers and may have regressive distributional effects (small farmers disproportionately affected)
Subsidies can be provided for activities generating positive externalities
Payments for ecosystem services or conservation practices (USDA Conservation Reserve Program)
Optimal subsidy rate equals marginal external benefit at the socially efficient level of provision
Subsidies encourage the provision of positive externalities but involve a transfer from taxpayers to producers
May lead to inefficiencies if not properly targeted or calibrated (overcompensation, lack of additionality)
Command-and-Control Regulations and Market-Based Instruments
, such as technology standards or emission limits, can directly mandate the abatement of negative externalities
Effective in achieving specific environmental targets but may not be cost-efficient and provide little flexibility to heterogeneous producers
Cap-and-trade systems establish a total limit on the externality-generating activity and allocate tradable permits among producers
Creates a market for the right to generate the externality, leading to an efficient allocation of abatement efforts (least-cost abatement)
Cost-effective as it allows flexibility in achieving the overall emissions target
Initial allocation of permits has distributional implications, with grandfathering favoring incumbent producers and auctioning generating revenue for the regulator
Challenges in Valuing Agricultural Externalities
Measurement and Attribution
Quantifying the physical magnitude of environmental externalities is complex due to the diffuse and often nonpoint nature of agricultural pollution
Tracing the fate and transport of pollutants from multiple sources to receptors is challenging (watershed-scale modeling)
Establishing the causal link between agricultural practices and environmental impacts requires detailed data and sophisticated modeling approaches
Data and resource-intensive (field-level monitoring, remote sensing)
Nonmarket Valuation Techniques
Valuing environmental externalities is complicated by the lack of market prices for many environmental goods and services
, such as stated and , are used to estimate the monetary value of these impacts
, like contingent valuation and choice experiments, rely on surveys to elicit individuals' willingness to pay for environmental improvements or willingness to accept compensation for environmental degradation
Subject to hypothetical bias and strategic responses
Revealed preference methods, such as and , infer the value of environmental amenities from observed market transactions or behavior
Limited by omitted variable bias and the need for sufficient variation in environmental quality
Aggregation and Discounting
Aggregating and comparing diverse environmental impacts, potentially occurring over different spatial and temporal scales, requires normalization and discounting
Choice of discount rate for future environmental costs and benefits is contentious (intergenerational equity concerns)
Uncertainty surrounding the magnitude, valuation, and irreversibility of environmental impacts complicates the assessment and internalization of externalities in decision-making