1 Farmers as Producers of Clean Water: Providing Economic Incentives for Reducing Agricultural Non- Point Source Pollution USDA, CSREES National Water.

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Presentation transcript:

1 Farmers as Producers of Clean Water: Providing Economic Incentives for Reducing Agricultural Non- Point Source Pollution USDA, CSREES National Water Conference Savannah, GA January 30, 2007

2 Authors Alan Collins, Associate Professor, Agricultural and Resource Economics West Virginia University Peter Maille, PhD student in Natural Resource Economics West Virginia University

3 Funding Provided by: USDA, National Research Initiative, Award No Research partner: Neil Gillies at the Cacapon Institute

4 Outline The problem in general A new approach? Objectives Research methods –Behavioral model –Payment formula –Institutional framework –Simulation Current progress and proposed next steps

5 The Problem in General 1.Current approaches to water quality are more expensive than they need to be Non point source pollution problems have persisted despite billions of dollars spent on conservation cost-share programs by the federal government over the last 20 years (See US GAO, 1992 and US GAO, 2005). Cost-share programs are not least-cost strategies for pollution abatement. 2. Water quality protection can raise equity concerns Should rural areas with historically lower per capita incomes be expected to provide clean surface water supplies for higher income urban areas?

6 Unresolved Issues 3.Who owns the property right to clean water? 4. Are farmers’ land management goals properly aligned with water quality concerns of society?

7 So we ask Can economic incentives provided by performance-based payments motivate farmers to address water quality problems and make conservation efforts ultimately more successful for both farmers and society as a whole?

8 Objectives For non-point source pollution at the watershed level: 1) Derive and assess the incentives created by water quality and quantity based payment formula. 2) Assess changes in farmer attitudes and behavior towards water quality protection in response to a performance-based payment program. 3) Compare water quality changes under this program to water quality changes in other watersheds. 4) Compare cost effectiveness of this program to that of traditional cost-share programs.

9 What is needed to accomplish these objectives?  A theoretical model of farmer behavior  A payment formula to create incentives for conservation  An institutional framework from which to make payments and provide appropriate incentives  Simulation of the payment formula for budgetary information

10 Preliminary Theoretical Model

11 Requirements of a Payment Formula  Provide an incentive to participate and pursue desired behaviors.  Deal sensibly with environmental conditions.  Transmit budget information to landowners and the Project Investigators.  Be seen as fair and likely to enhance participant well-being.  Simulate interest among participants in non- point pollution issues.

12 Payment Formula Need a per-unit price Price was based on the lowest price that would induce BMP installation by farmers. Need a unit quantity We choose volume as measured in acre-feet per month (1.23 x 10 6 liters). Need to measure quality The quality measure needs to make payment an increasing function of improved water quality, Must deal with uncontrollable weather-related fluctuations in a fair and intuitive manner. (Volume Water) x ($ per unit volume) x (quality-based adjustment)

13 Using the Payment Formula: we took these steps… Step 1: Estimate prices for water Developed a GAMS program in which assumed net revenue maximizing farmers who faced a land tradeoff between agricultural production and higher watershed payments from water quality protection. Solved model for BMP-inducing prices as a function of rainfall and season. Step 2: Developed a quality adjustment Used an index watershed approach and Nitrate-N as a quality indicator. Step 3: Test the payment formula Simulated monthly payments using field data and evaluated the results. (Volume Water) x ($ per unit volume) x (quality-based adjustment)

14 Our assumption is that using the index watershed approach provides the desired incentive in a way that is “fair.” Quality Adjustment via an “Index Watershed” Approach

15 Table 1. Price and Payment Summary Information Rainfall Price per Acre-Foot Monthly Payments Growing Season $ per kg. of N removed SummerWinterWith BMPsWithout BMPs Low$18$8$2,552$678$11 Medium$8$5$2,584$636$9 High$5 $2,837$638$8 Water Prices and Payments We substituted the computed prices back into (Volume Water) x ($ per unit volume) x (quality-based adjustment), and used actual flow and nitrate-N concentration data from Waites Run and Cullers Run, to get…

16 Institutional Framework  Determine who can participate within Cullers Run watershed.  Payments will be made to participating farmers a monthly basis for the entire watershed measured by nitrate-N quality changes and quantity of water flowing from their watershed over two, one year periods.  Farmer participants decide on sharing rules for watershed payments among themselves.  Farmers select their own best management practices management to impact water quality.  A unilateral contract defines roles and responsibilities, and lays out guidelines.  The project provides facilitator and water quality experts.

17 Simulated Payment Levels Payments were estimated under current conditions, i.e. without best management practices Payments were estimated under implementation of best management practices on all agricultural land in Cullers Run watershed Best management practices are assumed to be 75% effective in removing nitrate-N. We simulated payments using rainfall amounts from 1998 to The average annual payment amount over 12 months without best management practices is $8,318. With best management practices, the average is $23,051.

18 Rainfall Year Annual Totals “without” Annual Totals “with” 1998 $10,861$29, $10,208$26, $7,165$21, $5,041$14,179 Payment Simulations The average annual payment amount over 12 months “without” best management practices is $8,318. “With” best management practices, the average is $23,051.

19 Current Progress Water quality data has been collected for the past four months. The local community and state agency personnel have been kept informed of the project. A list of agricultural landowners and renters in the watershed has been developed and invitations have been sent to attend an initial informational meeting (scheduled for February 5 th ).

20 Proposed Next Steps Beginning in 2007 and continuing for 2 years: Data Collection Surveys and periodic farm visits to document actions taken and attitudes Weather/Water Quality Monitoring Payment Levels Data Analysis Logit/Probit regression of two-period panel data from household surveys, incorporating weather/payment/water quality monitoring information. OLS regression of water quality data. Cost/Benefit Analysis of conservation result.

21 Questions or comments? Contact information: x

22

23 REFERENCES Chapin, Mark. A Challenge to Conservationists. World Watch, November/December Worldwatch Institute. Dowie, Mark. Conservation Refugees: When Protecting Nature Means Kicking People Out. Orion Great Barrington, MD, The Orion Society. Ferraro, P.J. and Kiss, A., Direct Payments to Conserve Biodiversity. Science, 298: pp. Ferraro, P.J. and Simpson, R.D., Cost-Effective Conservation: A Review of What Works to Preserve Biodiversity. Resources, Spring: GAO. Chesapeake Bay Program: Improved Strategies Are Needed to Better Assess, Report, and Manage Restoration Progress Washington D.C., GOA. Leathers, H.D. and Smale, M., A Bayesian Approach to Explaining Sequential Adoption of Components of a Technological Package. American Journal of Agricultural Economics 73: Maille, P. and Collins, A., 2006 Converting Conservation from a Threat into an Opportunity: A Demonstration of a Performance-Based Payment Approach, ISEE Conference, New Delhi, India. Norton-Griffiths, M. and Southey, C., The Opportunity Costs of Biodiversity Conservation in Kenya. Ecological Economics, 12: pp. Peters, J., Transforming the Integrated Conservation and Development Project (ICDP) Approach: Observations from the Ranomafana National Park Project, Madagascar. Journal of Agricultural and Environmental Ethics, 11: Peterson, J.M. and Boisvert, R.N., Incentive- Compatible Pollution Control Policies Under Asymmetric Information on Both Risk Preferences and Technology. American Journal of Agricultural Economics, 86: Poe, G.L., Schulze, W.D., Segerson, K., Suter, J.F., and Vossler, C.A., Exploring the Performance of Ambient-Based Policy Instruments when Nonpoint Source Polluters Can Cooperate. American Journal of Agricultural Economics, 86: Ribaudo, M.O., Water Quality Impacts of Agriculture. In: R. Heimlich (Editor), Agricultural Resources and Environmental Indicators. USDA Economic Research Service, Washington, DC, pp. 31. Ribaudo, M.O. and Shortle, J.S., Estimating Benefits and Costs of Pollution Control Policies. Environmental Policies for Agricultural Pollution Control. CAB International, pp Sen, A., Commodities and Capabilities. Oxford University Press, New Delhi. Sen, A., Development as Freedom. Anchor Books, New York. Shortle, J.S., Horan, R.D., and Abler, D.A., Research Issues in Nonpoint Pollution Control. Environmental and Resource Economics, 11: pp. USGAO. Conservation Reserve Program Cost Effectiveness is Uncertain Washington D.C. USEPA. Rivers and Streams. National Water Quality Inventory: 1998 Report to Congress Washington D.C., U.S. EPA. Wells, M. and Brandon, K., People and Parks: Linking Protected Area Management with Local Communities. The World Bank, Washington DC.