Implementation and Monitoring to Reduce Agricultural ...

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Implementation and Monitoring to. Reduce Agricultural Impacts on ... Develop soil P thresholds. Incorporate into site assessment tools for P-based management ...
Implementation and Monitoring to Reduce Agricultural Impacts on Water Quality: US Experience Curtis Dell, Peter Kleinman, and Tamie Veith U.S. Department of Agriculture-Agricultural Research Service Pasture Systems and Watershed Management Research Unit University Park, PA, USA Rory Maguire Crop, Soil, and Environmental Science Department Virginia Tech Blacksburg, VA, USA

Recent water quality issues in the US  P primary national focus in last 15 yr Concern over increasing eutrophication of water bodies such as the Chesapeake Bay

Recent water quality issues in the US  Contributing factors

Concentration of animal production  Fewer, but larger animal feeding operations

N to P imbalance in manure  Applying manure to meet crop N requirement

can result in excess soil P

Farming System and P Balance Crop

Dairy

Pig

Poultry

- - - - - - kg P/ha/yr - - - - - -

Input Fertilizer

18

11

--

--

Feed

--

30

104

1690

Output

16

12

20

515

Balance

2

29

84

1175

Pennsylvania farms Cash crop 65 Holsteins 1280 hogs 75,000 birds 30 ha

40 ha

30 ha

12 ha

Recent water quality issues in the US  Ongoing N issues, but less national focus than P  Grassland/grazing land impacts on water quality receiving limited attention Perceived as a low impact land use Manure application to grasslands addressed in regions where P in runoff is an issue

US water quality regulations  Clean Water Act (1972)  Confined Animal Feeding Operation Rule (2002)  Permits required if: 1. ≥ 200 animal units 2. Animals confined ≥ 45 days in 12 mo 3. Waste discharge to a water body  Permit requirements: 1. No discharge for less than 25-yr storm

2. Comprehensive nutrient management plan

 Voluntary compliance for non-CAFO’s, but cost-

share incentives

Cooperative Projects

National Phosphorus Project Locations

USDA AL AR CO FL GA IA ID

IN IL OH OK OR MD MS

NE PA SC TX WA WI WV

University AL AR DE FL GA IN

KS VA MD VT NC WA NY WI OR WV TN PR

The National P Project Objectives Develop soil P thresholds

Getting from here

Incorporate into site assessment tools for P-based management 2 1.5

The simulator is mobile

Runoff P (mg/L)

1 0.5 0

To here

0

To here !

200

400

Soil test P (mg/kg)

600

Standardized protocols Nozzle to simulate rainfall

Runoff boxes

Critical Source Areas (CSAs) High P source areas Runoff source areas CSAs

X Outlet

The P Index - a tool for improved farm nutrient management Transport

Source

 Climate

 Soil P content

 Surface runoff class

 Fertilizer P application

 Erosion potential  Proximity to stream channel  Leaching potential

Rate, method, timing

 Manure P application Rate, method, timing

The P Index P Index Rating Low (clear) Medium High

~90% of P export comes from 200 farmers surveyed  Local vs. New York City benefit and responsibility large factors  Additional obligations for landowners, such as  Build and maintain fences  Install watering equipment  Differences in attitudes between long-time farmers and newer “hobby” farmers

Optimization of BMP Selection and Placement Expected outputs

Components/sources Baseline (preBMP) P losses SWAT model

Average annual baseline P loads Extent of P-loss (high / low)

-Multiple scenarios -Associated scenario costs -Associated scenario loads

BMP effectiveness estimates - BMP database/tool

Site specific BMP effectiveness estimates

BMP costs – Delaware county records

Annualized BMP costs

-Cost-effectiveness based on load reductions and scenario costs

Genetic algorithm Optimization

BMP Placement Results in Town Brook

Basic

Optimal

Nutrient management plans

Crop rotations & nutrient management plans

Crop rotations & contour strip crop

Contour strip crop & nutrient management plans

Riparian forest buffers

None

Same effectiveness - 30% Cost Reduction

Scenario

Total P load (kg)

Fitness score

Scenario cost, $/yr

Cost effectiveness $/kg P removed/yr

Basic

1585 kg

0.99

$78,000

$34

Optimal

1563 kg

1.67

$55,000

$24

Assessment Projects

National USDA project with two major efforts Watershed monitoring and simulation modeling Nov/Dec Journal of Soil and Water Conservation features findings from participating watersheds National assessments for 4 components Cropland, Wetland, Wildlife, and Grazing Land

Conclusions, Recommendations, and Cautions  National P Project showed that multi-state collaborative research programs are effective for the development of decision-making tools that help achieve a balance between environmental quality and farm productivity

Conclusions, Recommendations, and Cautions  New York City Watershed Agriculture Project showed that voluntary programs can work, but..  Careful coordination among participating government agencies critical  Farmer/land owner involvement in process critical  Cost-share assistance critical  Local benefit must be evident

Conclusions, Recommendations, and Cautions  Assessment is challenging  Monitoring is expensive and time consuming  Attributing inputs or reductions to individual

sources within a watershed is very difficult

 Validation of models limited by availability of

measured data  Accurate scaling of estimates from plot to field to farm to watershed levels is an evolving science  Monitoring should be continued to the extent of

available funding to support and improve modeling efforts

Conclusions, Recommendations, and Cautions  Researcher and policy makers should consider the broadest possible range of pollutants and land uses in order to consider trade-offs and all potential impacts when developing and recommending management practices