Strengthening Agriculture's Commitment to Water Quality: The Iowa Nutrient Reduction Strategy - Dr. John Lawrence, from the 2014 Iowa Pork Congress, January 22-23, Des Moines, IA, USA.
More presentations at http://www.swinecast.com/2014-iowa-pork-congress
3. Iowa Nutrient Research Center
•
•
•
•
Established by 2013 Legislature
Funded at $1.5 million for 2013-2014
Regents Center administered by CALS Dean
The purpose of the center shall be to pursue
a science based approach to nutrient
management research…
• http://www.nutrientstrategy.iastate.edu/
4. 10 Projects year 1: $1,425,770
• Iowa Institute of Hydraulic Research ‐ Hydroscience and
Engineering Work Plan
• Distribution, transport, and biogeochemical transformations of
agriculturally derived nitrogen and phosphorus in Cedar River
• Establishing pragmatically dynamic program for extending
water quality BMP financial information: Farmer tools for
Iowa Nutrient Reduction Strategy
• Social-economic research work plan
• Phosphorus transport in Iowa streams: Importance of stream
bed and bank erosion
5. 10 Projects year 1: $1,425,770
• Establishment and monitoring of saturated buffers within
priority watersheds
• Investigating causes of corn yield decreases following
cereal rye winter cover crop
• Impacts of cover crops on phosphorus and nitrogen loss with
surface runoff
• Nonpoint source nitrogen and phosphorous loads at
implementation scale: Direct agricultural nutrient loads to
surface waters in relation to land use and mgt.
• Bioreactor Research & Assessment of Woodchip Tile
Denitrification Bioreactors: Optimal Design/ Performance and
Experimental Bioreactor Installation and Study
6. Manure Research
• Evaluating Instinct with fall applied liquid swine
manure. Finish likely this summer
Northeast Iowa Research Farm,
• Impact of Liquid Swine Manure Application and Cover
Crops on Ground Water Quality
– http://www.ag.iastate.edu/farms/11reports/Northeast/I
mpactManure.pdf
• Fertilizer and Swine Manure Management Systems
Impacts on phosphorus in Soil and Subsurface Tile
Drainage
– http://www.ag.iastate.edu/farms/11reports/Northeast/F
ertilizerSwine.pdf
• Drainage Water Quality Impacts of Current and Future
Agricultural Management Practices
7. Manure Research
Northwest Iowa Research Farm
• Effects of Tillage and Phosphorus Source on Long-term
Phosphorus Runoff Loss and Crop Yield
– http://www.ag.iastate.edu/farms/2012%20Farm%20Rep
orts/Northwest/EffectsTillage.pdf
1. Corn-soybean rotation managed with chisel/disk tillage and
fertilizer P.
2. Corn-soybean rotation managed with no-tillage and fertilizer P.
3. Corn-soybean managed with chisel/disk tillage and P-based
liquid swine manure.
4. Corn-soybean managed with no-tillage and P-based manure.
5. Continuous corn managed with chisel/disk tillage, N-based
manure, and baled stover.
8. Measures of success
committee
• WRCC committee on how to measure if
we are making progress toward the goal
• Met 3 times: Sep, Nov, Jan
• Report to WRCC on January 22
9. Measures of success
committee
Measurable indicators of desirable change
Specific indicators in attached text
Inputs
Human
People
Partner Organizations
Funding
Partner Agribusinesses
Agency resources
Farmer knowledge and
attitude
Private sector resources
Point source communities
and management
knowledge and attitude
Land
Water
Land use changes
Calculated load reduction
Net acres cover crops
Net acres perennials
Etc.
Practice adoption
Measured loads in priority
watersheds
Acres of practice X
Acres of practice Y
Etc.
Point source implementation
Feasibility studies
Permit applications
Construction
Measured loads at existing
monitoring stations
Organized watersheds
reported load changes
10. Example Combination Scenarios that
Achieve N and P Goal From NPS
Total EAC* Statewide
Initial
Cost
Average
% Reduction Investment (million
EAC Costs
from baseline (million $)
$/year)
($/acre)
N
P
MRTN Rate, 60% Acreage with Cover Crop,
NCS1 27% of ag land treated with wetland and 60%
of drained land has bioreactor
42
30
3,218
756
36
MRTN Rate, 95% of acreage in all MLRAs with
Cover Crops, 34% of ag land in MLRA 103 and
NCS3
104 treated with wetland, and 5% land
retirement in all MLRAs
42
50
1,222
1,214
58
Name Combined Scenario
11. Example Combination Scenarios that
Achieve N and P Goal From NPS
N
Name Combined Scenario
MRTN Rate, Inhibitor with all Fall
Commercial N, Sidedress All Spring N, 70% of
all tile drained acres treated with bioreactor,
70% of all applicable land has controlled
drainage, 31.5% of ag land treated with a
wetland, and 70% of all agricultural streams
NCS8
have a buffer) - Phosphorus reduction
practices (phosphorus rate reduction on all
ag land, Convert 90% of Conventional Tillage
CS & CC acres to Conservation Till and
Convert 10% of Non-No-till CS & CC ground
to No-Till
P
Total EAC* Statewide
Initial
Cost
Average
% Reduction Investment (million EAC Costs
from baseline (million $)
$/year)
($/acre)
42
29
4,041
77
4
12. Next Steps
•
•
•
•
•
•
Successful management of cover crops
Launch priority watershed projects
Continued education and demonstration
Establish measurements and baseline
Make changes, show progress
Innovate and implement new methods
Notas del editor
Examples for illustration only, not for recommendation. It shows that to achieve the 41% N and 29% P targets for nonpoint source, it will require a high adoption rate of several practices.Remember that Equal Annualized Costs (EAC) includes the annualized initial investment, so you cannot add initial investment and EAC.
Examples for illustration only, not for recommendation. It shows that to achieve the 41% N and 29% P targets for nonpoint source, it will require a high adoption rate of several practices.Remember that Equal Annualized Costs (EAC) includes the annualized initial investment, so you cannot add initial investment and EAC.The low EAC for this example is due to no P application on soils that have high or very high soil test phosphorous. That savings helps pay the costs of the other practices in this statewide example. The farmer then makes a large initial investment, may not have high STP and thus will not get the P cost savings.If high STP is due to manure application, the livestock farmer may have higher cost to move manure to additional fields.