http://www.extension.org/67629 To meet Chesapeake Bay Total Maximum Daily Load requirements for agricultural pollution, conservation districts and farmers are tasked with implementing best management practices (BMPs) that reduce farm losses of nutrients and sediment. The importance of the agricultural industry to the regional economy highlights the need for determining cost-effective BMP solutions given the geographical and operational characteristics of these farms. This study evaluated both the environmental risk and farm profitability of common farm-level management practices for three major farm types in the region: crop, tractor-based ("English") dairy, and horse-drawn ("Amish") dairy.
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Farm System Modeling to Evaluate Environmental Losses, Profitability, and BMP Cost-Effectiveness
1. Farm-System Modeling to Evaluate
Environmental Losses and Management
Practice Cost-Effectiveness
Andy McLean, Tamie Veith, Al Rotz,
Jim Hamlett, Jim Shortle
USDA-ARS Pasture Systems and Watershed
Management Research Unit & The
Pennsylvania State University
2. Loadings to the Chesapeake Bay
Agriculture dominates all
other sectors for nutrient and
sediment contributions
57%
45%
70%Legend
Agriculture
Point Source
Forest
Developed
4. Most Beneficial Practices as
Determined by Regional Studies
Rank Lancaster County
Informal Study (2004)
CBC (2004) Cost-effective
strategies for the Bay
1 Nutrient management plan Wastewater Treatment Plant Upgrades
2 Cover crops Diet and Feed Adjustments
3 Management advice Traditional Nutrient Management
4 Structural field practices Enhanced Nutrient Management
5 Conservation tillage Conservation Tillage
6 Implement farm conservation
plan
Cover Crops
7 Cultural field practices (crop rotation, etc.)
8 Develop farm conservation plan
9 Grass buffers, 15-ft
10 Animal waste system
6. Baseline Descriptions
Crop Farm
Old Order Amish
Dairy
Contemporary
Dairy
400 ha (1000 ac)
4 yr rotation
C-SB-C-SB/WW
Primarily no-till
Import poultry manure
& some starter fertilizer
100 cows
120 ha (300 ac)
8 yr rotation
2(Cg)-2(Cs/WW)-4(Hay)
Primarily no-till
Low grain to forage
50% rented fields
50 cows
24 ha (60 ac)
8 yr rotation
4(Cs/WW)-4(Alfalfa)
Conventional-till
High grain to forage
Horse-drawn methods
7. Practices Investigated
Farm Management Cropping Strategies
Nutrient Management
Treatment Strategies
Tillage (conv., mulch, no)
Strip cropping
Manure storage (4, 6, 12 month)
Manure reallocation among crops
Manure application
(broadcast, immediate incorp.) Field-edge grass buffer
Crop conversion
(50% silage to grazed pasture)
Cover Crop
(mulch winter grain)
Double Crop
(harvest winter grain)
Dietary P (100%, 120% of NRC)
Dietary N (100%, 110% of NRC)
Tests against prior methods
8. Integrated Farm System Model
(IFSM)
Soil
Establish
Crop Harvest
Storage
AnimalManure
Grazing
Volatile loss
Exported manure
Purchased feed,
bedding, etc.
Feed sold
Volatile
loss
Fixed
nutrients
Volatile loss
Purchased
fertilizer
Runoff &
Leaching loss
Milk and
animals
Engine exhaust
9. Challenges of Modeling an Amish
Dairy Farm
Machinery Differences
Machine specifications
Operational efficiency
Power requirements
Costs
Horses vs. Tractors
Corn Harvest
10. Challenges of Modeling an Amish
Dairy Farm
Operational Differences
Labor requirements
Timing of operations
Representing horses
29. Conclusions
Most management practices have a nutrient
tradeoff - at least as they are modeled in this study
Farm operation/strategy/location may have a
significant impact on which practices are best
Double cropping shows great potential
Cost-effective reductions from ―low-hanging
fruit‖
Corn appears to be water limited, not nutrient
limited, therefore we may be over-applying nutrients to
corn
Profitability and the environment benefited from
transferring manure nutrients from corn to small grain
30. Application of Results
Provide a basis for recommendations by
conservation district officials and policymakers
Hopefully encourages farmers to experiment with
these practices
31. USDA
Pasture Systems and Watershed
Management Research Unit
University Park, Pennsylvania
Agricultural Research Service
Editor's Notes
Mike Hubler and Larry Baum from the Dauphin County Conservation District and officials at the Lancaster and Lebanon County Conservation Districts helped categorize and characterize farms.
Source of PA nutrient loadings, as calculated by the Chesapeake Bay Model
Study region is 3 counties on East side of Susquehanna River. Loadings drain to river and straight down into Bay.~2500 farmsThe larger farms are feed crop farms (corn/soybean). Average farm size = 40 ha But median = 20 haThe green (good) N area is mountain top forest.
Need to properly characterize current and suggested management impacts at the FARM level.If practice changes aren’t economically feasible, or practical with available labor, then they aren’t going to be implemented well and the anticipated pollution reduction will be overstated.
Define and characterize categories of farms for Dauphin, Lancaster, and Lebanon Counties of Southeastern PA, so that farms typical of theregion may be represented in IFSM.Simulate current farm conditions as baseline models
Apply BMP scenarios to the baseline farm models to evaluate BMP impact on nutrient/sediment losses and farm profitability.4 categories of BMPs investigated, based (roughly) on EPA’s “core four” BMP list. (i.e., the types that EPA has identified as necessary to meet goals)
Process-based, farm-scale Outputs are annualaverages over 25 years varying weather Simulates the economics of farm operations- costs, revenues, profit (return)Simulates flow of nutrients in and out of farm boundaries
Yields compared well with NASS and local conservation officialsTable 1. Yield comparison (tDM ha-1) based on USDA-NASS (2012) reports, conservation district estimates, and IFSM simulations*. * USDA-NASS (2012): 10-yr averages; Conservation District (personal communication): estimates of recent past; IFSM 25-yr mean (SD).# USDA-NASS = hay; IFSM = 2 cuts hay, 2 cuts silage.
Also evaluated operational performance of farms (timing of operations, labor requirements)
And
Graphs show percentage change from baseline for select scenariosHighlighted scenarios seemed to be the most cost-effective overall for each farm typeCC = Corn (200 ha) and soybeans (200 ha) are only cash crops. A cover crop of winter rye is grown on 100% of the corn land (200 ha) after corn harvest and killed in the spring before soybean planting.100% CC = (100% soybean land has a winter rye cover crop. 100% of corn land is cover cropped with grass. Cover crops are killed in the spring.)
Nitrogen:Contemporary Dairy seems to be more consistent but less precise (wider ranges, all centered around roughly the same median) than the crop farm. BUT the crop farm y-axis has a 20t range and the dairy y-axis range is only 10t
Distribution and density of agricultural land, elevation, and physiographic regions within a representative subregion of the study area (PennDOT 2012, USDA 2002).
A variety of sources were used to gather data and to evaluate model output, to make sure that we were accurately representing these specific farm types in southeastern PA.
Output parameters evaluated for determining the impact of the change in management practice
SPARROW estimated loadings from agricultural sources delivered to streams and rivers in the Bay watershed (1997 conditions)Total N: red category = 6 to 33 kg/ha/yrP: red = 0.2 to 0.85 kg/ha/yrSed: red = 30 to 238 Mg/km = 3,000 to 23,800 t/ha (or 300 to 2,380 kg/ha)http://stat.chesapeakebay.net/?q=node/130&quicktabs_10=1&quicktabs_15=1