Biofuels and Water Quality in the Midwest: Corn vs. Switchgrass Silvia Secchi, Philip W. Gassman, Manoj Jha, Lyubov Kurkalova, and Catherine L. Kling Center.

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Presentation transcript:

Biofuels and Water Quality in the Midwest: Corn vs. Switchgrass Silvia Secchi, Philip W. Gassman, Manoj Jha, Lyubov Kurkalova, and Catherine L. Kling Center for Agricultural and Rural Development Iowa State University March 2008 Funding for this work has been provided by the U.S. Environmental Protection Agency, the U.S. Department of Agriculture, and the U.S. Department of Energy.

Rapid Expansion of Ethanol  U.S. production:7 billion gallons of ethanol today, 2 billion gallons in 2002  Corn:Acreage, 78 mil acres in 2006, 90 mil in 2007 (NASS) Prices, historically $2.5-$3/bushel, Prices, historically $2.5-$3/bushel, over $5 now over $5 now  Biorefineries:139 in production, 62 under construction (RFA, Jan. 2008)  Energy Bill:mandates 36 gallons from biofuels by 2022, 20 billion from advanced biofuels (EISA) biofuels (EISA)

Some Key Policy Drivers of Economics Behind Ethanol Expansion 1975 Lead phase-out begins Ethanol becomes attractive as octane booster 1978 Energy Tax Act A $0.40 subsidy per gallon of ethanol blended into gasoline introduced Energy Security Act, Crude Windfall Tax Act, Surface Transportation Act, Tax Reform Act Insured loans for small ethanol producers, tariffs on foreign produced ethanol, ethanol subsidy increased to $0.50 and then $ Clean Air Act Amendments Mandated oxygenates in many locations, MTBEs major oxygenate in use Various Acts Subsidy reduced gradually to $0.52/gallon Various states banned MTBE’s 2005 Energy Policy Act Phased out MTBEs as oxygenate thereby increasing demand for ethanol 2007 Energy Bill Biofuels mandate for 36 billion gallons by 2022

U.S. Ethanol Biorefinery Locations

The Upper Mississippi River Basin

Debate Concerning Benefits Continues  Energy independence  Carbon/GHG gains?  Water quality/ environmental effects  how and where it is produced  Feedstock, corn? switchgrass?

Our Focus  Water quality consequences of corn ethanol vs ethanol from switchgrass  Policy scenarios: If economic incentives were right to induce adoption of SG in the Upper Miss. River Basin: Where might switchgrass be produced? Where might switchgrass be produced? How much higher would returns to producing SG need to be to induce these changes? How much higher would returns to producing SG need to be to induce these changes? What would the water quality consequences be? What would the water quality consequences be?

Our Approach  Combine: Economic decision making models (highest profit opportunities) with, Economic decision making models (highest profit opportunities) with, Watershed based water quality model (SWAT). Watershed based water quality model (SWAT).  To: Project how changes in economic drivers affect land use, Project how changes in economic drivers affect land use, Water quality. Water quality.  Examine: Sensitivity to switchgrass profitability (subsidy) assumptions Sensitivity to switchgrass profitability (subsidy) assumptions Sensitivity to targetting (place only highly erodible lands) Sensitivity to targetting (place only highly erodible lands) Sensitivity to baseline land use. Sensitivity to baseline land use.

Watershed Schematic # of NRI points# HRUs Area km 2 % cropped , , , , , , , , , , , , , , Total2,730488,

Some Specifics  Baseline land use data we have is 1997 NRI, but fundamentally different price regime exists now  Use current prices and revised tillage assumptions to predict crop placement to represent “current baseline”  Switch grass scenarios: Place switchgrass on landscape where it is most profitable (assuming various SG payments)  Examine sensitivity to fertilization rates for commercially growing switch grass: “low” vs. “high”

Switchgrass Data and Assumptions  Cost of SG per metric ton - given a yield of tons/ha is $34.6 (based on M. Duffy’s budgets- ISU)  Average SG yields for UMRB = 9.74 tons/ha, of land chosen in most profitable scenario = tons/ha  Assume, no storage or transportation costs for farmers  Alamo variety (parameters adjusted for Iowa performance) used everywhere with same management  Two fertilization rates = 157 kg/ha and 100 kg/ha (Heggenstaller, (ISU Agronomy))

Switchgrass Fertilization

Acreage Responses to Switchgrass Prices/Metric Ton

Land Use Projected Current Baseline** Switchgrass Scenario ($100/ton) Continuous Corn 20,00020,000 Corn, Soybean 158,000119,000 Corn, Corn, Soybean 29,00026,000 Corn, Alfalfa 60,00055,000 Switchgrass46,000 *Other cropland and CRP total about 29,000 in the 1997 baseline, this land is allocated to cropland in the current baseline and/or switchgrass in the scenario **Baseline projected using current corn prices and N fertilizer prices and current information on tillage (CTIC)

Switchgrass Locations Predicted at Payment of $100/ton

Implications for EISA 2007  At $100/ ton UMRB could supply 70 million tons of switchgrass  Assuming an ethanol conversion efficiency of 0.3 liters/kg, 26% of the 21 billion gallon cellulosic ethanol Energy Bill goal could be accomplished.  The 25x25 (U Tenn.) study estimated switchgrass prices in the range of $ 44-88/metric ton; therefore to produce the switchgrass levels in our scenarios, subsidies would have to range from almost $800 million to over $4 billion.

Water Quality Predicted by SWAT at Grafton (exit of UMRB) Current Baseline Switchgrass Scenario Sediment(mmt) Total N (million kgs) Nitrate Total Phosphorous (million kgs)

Can we have our cake and eat it too?  Could we target conservation spending programs so that we place switchgrass in locations that are less profitable, but yield greater water quality benefits?  Undertook scenarios that yielded the same SG acreage, but targeted Highly erodible land (HEL) Highly erodible land (HEL) Most profitable HEL, and Most profitable HEL, and Highest yielding SG land Highest yielding SG land

19 Most profitable HEL land

20 Highest yield acreage

21 Water Quality Predicted by SWAT at Grafton (exit of UMRB) SG Scenario SG Scenario - yield Sediment(mmt) Total N (million kgs) Nitrate Total Phos. (million kgs) Water quality improves (at base of UMRB) Water quality improves (at base of UMRB) Switchgrass yield rises by ~2.6 million tons Switchgrass yield rises by ~2.6 million tons Additional subsidies of about $1 billion requiredAdditional subsidies of about $1 billion required Water quality upstream may change more dramatically Water quality upstream may change more dramatically

Take home messages? 22  Much is unknown regarding development of markets for cellulosic feedstocks Different feedstocks in different locations; woody biomass in northern UMRB, miscanthus and switchgrass elsewhere? Different feedstocks in different locations; woody biomass in northern UMRB, miscanthus and switchgrass elsewhere? Transportation, technological progress huge unknowns Transportation, technological progress huge unknowns  Scenarios based on landscape scale modeling systems can help us understand consequences of alternative policies  SG appears promising for biomass production, but needs subsidies and/or tech. advance to be large scale viable

Caveats (assumptions that might be particularly important in results)  Analysis includes cropland in production in 1997 only (no CRP)  Model under predicts corn yields ( ) Corn under estimated on average by 12% Corn under estimated on average by 12% Beans by 4.4% Beans by 4.4%  No yield drag for rotations  Ignores risk premia farmers might require to plant new crop, if so understates costs  Provides for no tech. advance, picture could change completely  Climate change?... Etc.