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Watershed P Balances as a Tool for TMDL 
Planning 
Lawrence Baker and Heidi Peterson1 
1Now at the Minnesota Department of Agriculture 
Support: 
MPCA/EPA 319 Program
Goal: Develop a Watershed P Balance Tool 
To Inform Nutrient Reduction Plans 
1. Develop watershed-specific P balance with high level 
of detail 
2. Develop spreadsheet tool to support general use 
Albert Lea Lake Watershed 
- 164 square miles 
- 64% cropland 
- City of Albert Lea
Fertilizer 
Human food 
Sewage 
Animal 
products Crops Lake 
Atmospheric 
deposition 
Deliberate 
Exports 
Inputs 
Retention 
(soil P) 
Stream P 
Animal feed 
The Whole Watershed P Balance Concept
Relationship between watershed P 
balance and stream P 
P inputs > Deliberate P export: 
Soil test P (STP) increases 
Stream P increases 
P inputs < Deliberate P export: 
STP decreases 
Stream P decreases 
Is this true?
1. In lab studies, runoff P is predicted from STP 
(Vadas et a., 2005, J. Env. Qual.)
Stream P, ug/L 
Klatt et al., 2003. J. Env. Qual . 
2. For watersheds, stream P 
concentrations is related to average STP 
(Klatt et al., 2003, J. Env. Qual.)
How would we use a watershed P balance 
approach? 
50 
40 
30 
20 
10 
0 
Manure P 
0.31 0.39 0.47 
% dietary P 
Milk production, kg/day 
100 
80 
60 
40 
20 
0 
Manure P, g/day 
Milk P 
1. Move “upstream”: Study of P supplements in dairies 
showed overuse of P supplements (Wu et al. 2001, J. Dairy Sci.)
% to lake 
% exports 
% retention 
0 25 50 75 100 
Hubert 
Big Trout 
Sibley 
Long 
Belle Taine 
Gilbert 
Le Homme Dieu 
Fishook 
Darling 
Lobster 
Victoria 
% input P 
2. Understand fate 
of input P 
(Schussler et al., 2007, 
Ecological Eng.)
50 
40 
30 
20 
10 
0 
No yield reduction below 13 mg/kg 
1975 
1977 
1979 
1981 
1983 
1985 
1987 
1989 
1991 
1993 
Soil P, mg/kg 
40 lb P/acre No P fertilizer 
3. Understand temporal watershed P dynamics 
(Randall et al., 1997, J. Ag. Production)
Approach for Albert Lea Watershed P Balance 
Crop cover in 2010 
Soybeans (39%) 
Corn (56%) 
USDA Cropland Data Layer (2010)
Albert Lea Lake watershed crop data 
Fertilizer 
application 
per acre 
Land area 
fertilized 
Land 
area† 
Calculated 
total P crop 
uptake‡ 
Calculated 
total P 
applied 
lbs P2O5 lbs % (acre) (tons) (tons) 
Alfalfa 11 5 20 687 9 0.3 
Corn 66 29 89 33,123 543 426 
Corn- 
Sweet 62 27 62 1,256 28 10 
Soybeans 46 20 5 23,164 223 12 
†Area calculated using the USDA, 2010 Cropland data layer. 
‡Based on %P dry-matter values from Ketterings and Czymmek (2007). 
Crop data were determined from 88 on-farm interviews 
(Denton Bruening) + NASS data.
Adjusted Number of Animal Units 
(Denton Bruening and Colin Whitmer) 
Livestock 
System Permitted Actual 
% of 
Permitted 
Beef 2,223 829 37% 
Dairy 218 218 100% 
Horses 245 43 18% 
Sheep 398 95 24% 
Swine 12,824 6,157 48% 
Turkey 445 440 99% 
Multi-Animal 434 98 23% 
Watershed 
16,787 7,880 47% 
Total 
Visual inspection showed that actual animal counts were 
lower than permit values.
Swine P Balance 
(tons/yr) 
Meat = 48.4 
Rendered 
= 1.5 
Manure = 38.5 
Piglets = 5.2 
Feed = 85.0 
Input: 90.2 ton P / yr 
Output: 88.4 ton P / yr 
We developed P balances for each animal system.
Summary of Calculated Livestock Efficiencies 
System Input Manure 
Product 
Export Efficiency 
(tons/yr) 
Beef 18.1* 14.3 5.0 28% 
Pork 90.2 38.5 49.9 55% 
Dairy 3.6* 2.4 1.3 37% 
Turkey 22.7* 11 12.4 54% 
* Includes calves / piglets / poults imported into herd 
We developed a spreadsheet calculator for each major 
animal system.
Average Annual Agricultural Stream P Loads, 2009- 
2011 = 24 tons/yr 
6.0 tons 
High annual variability 
5.8 tons 
8.7 tons 
2.6 tons 
0.9 tons 
Includes winter adjustment 
Tons TP 
2009 14 
2010 29 
2011 26
Stream TP flux, 
kg/yr 
TP yield, 
kg/ha-yr 
Part. P, 
% 
Soluble 
P, % 
Water 
yield, 
cm/yr 
Bancroft Ct. 5411 0.62 26 74 30 
Wedge Cr. 7904 0.88 39 61 33 
Peter Lund Cr. 5250 0.69 36 64 24 
Watersheds are similar with respect to TP yields, dominance 
of soluble P, and water yields.
Atmospheric Deposition 
19 
Piglets 5 
Holstein 
Steer Calves 0.3 
Watershed P use efficiency = 824/487 = 1.7 
Fertilizer 
391 
Pork 50 
Milk 1.1 
Beef 5 
Crops 
754 
Dairy & 
beef feed 
21 
Manure 
38 
Hog feed 
82 
Deliberate 
exports = 824 
Manure 
17 
Inputs =487 
Stream export 
24.0 (5% of input) 
Units: Tons 
Poults 0.02 
Manure 
11 
Turkey Turkey 12 
feed 
12 
Feed Imports 
74 
Albert Lea Agricultural P balance 
Peterson et al., in prep.
Atmospheric Deposition 
10.5 
Fertilizer 
80.6 
Pork 8.3 
Milk 3.7 
Beef 3.1 
Crops 
121 
Dairy & 
beef feed 
25.5 
Manure/ 
Compost 
Feed 
18.4 
9.3 
Deliberate 
exports: 138 
Manure 
18.9 
Inputs =94 
Units: Gg 
Chicks 0.004 
Turkey 2.1 
Manure 
4.2 
Feed 
6.3 
Feed Imports 
2.9 
Manure Chicken 0.2 
0.6 
Feed 
0.9 
State-wide P use efficiency = 1.47 
Peterson in prep b State-wide Ag P balance
Urban P balance (City of Albert Lea) 
P x 1000 kg/yr 
Industrial effluent 22.7 
Household effluent 21.4 
Total effluent 43.8 
Biosolids P 15.9 
Effluent P 28.3 
P removal efficiency 36%
Part II. Dynamics of P flows through the watershed
3. Identify opportunities to shift current P flow through 
system toward a circular P economy (NSF proposal ongoing). 
Processing Waste 
Food 
Food Waste 
Sewage Biosolids 
Treated 
Water 
Irrigation 
or 
Biosolids 
Agricultural 
Products 
Composted/ 
Animal Feed 
Fertilizer

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Watershed P balances as a tool for TMDL planning

  • 1. Watershed P Balances as a Tool for TMDL Planning Lawrence Baker and Heidi Peterson1 1Now at the Minnesota Department of Agriculture Support: MPCA/EPA 319 Program
  • 2. Goal: Develop a Watershed P Balance Tool To Inform Nutrient Reduction Plans 1. Develop watershed-specific P balance with high level of detail 2. Develop spreadsheet tool to support general use Albert Lea Lake Watershed - 164 square miles - 64% cropland - City of Albert Lea
  • 3. Fertilizer Human food Sewage Animal products Crops Lake Atmospheric deposition Deliberate Exports Inputs Retention (soil P) Stream P Animal feed The Whole Watershed P Balance Concept
  • 4. Relationship between watershed P balance and stream P P inputs > Deliberate P export: Soil test P (STP) increases Stream P increases P inputs < Deliberate P export: STP decreases Stream P decreases Is this true?
  • 5. 1. In lab studies, runoff P is predicted from STP (Vadas et a., 2005, J. Env. Qual.)
  • 6. Stream P, ug/L Klatt et al., 2003. J. Env. Qual . 2. For watersheds, stream P concentrations is related to average STP (Klatt et al., 2003, J. Env. Qual.)
  • 7. How would we use a watershed P balance approach? 50 40 30 20 10 0 Manure P 0.31 0.39 0.47 % dietary P Milk production, kg/day 100 80 60 40 20 0 Manure P, g/day Milk P 1. Move “upstream”: Study of P supplements in dairies showed overuse of P supplements (Wu et al. 2001, J. Dairy Sci.)
  • 8. % to lake % exports % retention 0 25 50 75 100 Hubert Big Trout Sibley Long Belle Taine Gilbert Le Homme Dieu Fishook Darling Lobster Victoria % input P 2. Understand fate of input P (Schussler et al., 2007, Ecological Eng.)
  • 9. 50 40 30 20 10 0 No yield reduction below 13 mg/kg 1975 1977 1979 1981 1983 1985 1987 1989 1991 1993 Soil P, mg/kg 40 lb P/acre No P fertilizer 3. Understand temporal watershed P dynamics (Randall et al., 1997, J. Ag. Production)
  • 10. Approach for Albert Lea Watershed P Balance Crop cover in 2010 Soybeans (39%) Corn (56%) USDA Cropland Data Layer (2010)
  • 11. Albert Lea Lake watershed crop data Fertilizer application per acre Land area fertilized Land area† Calculated total P crop uptake‡ Calculated total P applied lbs P2O5 lbs % (acre) (tons) (tons) Alfalfa 11 5 20 687 9 0.3 Corn 66 29 89 33,123 543 426 Corn- Sweet 62 27 62 1,256 28 10 Soybeans 46 20 5 23,164 223 12 †Area calculated using the USDA, 2010 Cropland data layer. ‡Based on %P dry-matter values from Ketterings and Czymmek (2007). Crop data were determined from 88 on-farm interviews (Denton Bruening) + NASS data.
  • 12. Adjusted Number of Animal Units (Denton Bruening and Colin Whitmer) Livestock System Permitted Actual % of Permitted Beef 2,223 829 37% Dairy 218 218 100% Horses 245 43 18% Sheep 398 95 24% Swine 12,824 6,157 48% Turkey 445 440 99% Multi-Animal 434 98 23% Watershed 16,787 7,880 47% Total Visual inspection showed that actual animal counts were lower than permit values.
  • 13. Swine P Balance (tons/yr) Meat = 48.4 Rendered = 1.5 Manure = 38.5 Piglets = 5.2 Feed = 85.0 Input: 90.2 ton P / yr Output: 88.4 ton P / yr We developed P balances for each animal system.
  • 14. Summary of Calculated Livestock Efficiencies System Input Manure Product Export Efficiency (tons/yr) Beef 18.1* 14.3 5.0 28% Pork 90.2 38.5 49.9 55% Dairy 3.6* 2.4 1.3 37% Turkey 22.7* 11 12.4 54% * Includes calves / piglets / poults imported into herd We developed a spreadsheet calculator for each major animal system.
  • 15. Average Annual Agricultural Stream P Loads, 2009- 2011 = 24 tons/yr 6.0 tons High annual variability 5.8 tons 8.7 tons 2.6 tons 0.9 tons Includes winter adjustment Tons TP 2009 14 2010 29 2011 26
  • 16. Stream TP flux, kg/yr TP yield, kg/ha-yr Part. P, % Soluble P, % Water yield, cm/yr Bancroft Ct. 5411 0.62 26 74 30 Wedge Cr. 7904 0.88 39 61 33 Peter Lund Cr. 5250 0.69 36 64 24 Watersheds are similar with respect to TP yields, dominance of soluble P, and water yields.
  • 17. Atmospheric Deposition 19 Piglets 5 Holstein Steer Calves 0.3 Watershed P use efficiency = 824/487 = 1.7 Fertilizer 391 Pork 50 Milk 1.1 Beef 5 Crops 754 Dairy & beef feed 21 Manure 38 Hog feed 82 Deliberate exports = 824 Manure 17 Inputs =487 Stream export 24.0 (5% of input) Units: Tons Poults 0.02 Manure 11 Turkey Turkey 12 feed 12 Feed Imports 74 Albert Lea Agricultural P balance Peterson et al., in prep.
  • 18. Atmospheric Deposition 10.5 Fertilizer 80.6 Pork 8.3 Milk 3.7 Beef 3.1 Crops 121 Dairy & beef feed 25.5 Manure/ Compost Feed 18.4 9.3 Deliberate exports: 138 Manure 18.9 Inputs =94 Units: Gg Chicks 0.004 Turkey 2.1 Manure 4.2 Feed 6.3 Feed Imports 2.9 Manure Chicken 0.2 0.6 Feed 0.9 State-wide P use efficiency = 1.47 Peterson in prep b State-wide Ag P balance
  • 19. Urban P balance (City of Albert Lea) P x 1000 kg/yr Industrial effluent 22.7 Household effluent 21.4 Total effluent 43.8 Biosolids P 15.9 Effluent P 28.3 P removal efficiency 36%
  • 20.
  • 21. Part II. Dynamics of P flows through the watershed
  • 22. 3. Identify opportunities to shift current P flow through system toward a circular P economy (NSF proposal ongoing). Processing Waste Food Food Waste Sewage Biosolids Treated Water Irrigation or Biosolids Agricultural Products Composted/ Animal Feed Fertilizer

Editor's Notes

  1. The TMDL approach (legal framework) focuses on stream P loading only. The whole watershed concept looks at P entering the watershed (food, fertilizers, etc.), what is deliberately exported (meat, crops), what accumulates, and stream export. This allows watershed managers to think about how P is moving through their watershed, and to think about efficiency of use, novel types of controls, and equity of various actions.
  2. Six corn states (1998-2000): Dibb Fixen and Stauffer, 2003: 1.1-1.49 International Fertilizer Association Partial Puse for 113 crop fields (corn or soybean)
  3. Verification of permitted Animal Units within the Albert Lea Lake watershed. † Documented through personal communication or property observation.
  4. Error ranges from 2-7%; Beef is feed and dairy beef calves
  5. Accounts for >98% of the Animal Units in watersheds.
  6. Instead of looking at the Ag production independently, this flow diagram summarizes the entire Ag system within MN. Contrary to common beliefs that ag systems have very low efficiency, MN’s is driven by crops producing an efficient system where farmers are mining P from the soils. Consistent with research by the International plant nutrition institute.
  7. P enters the food system through ferti/manure application and results in commodity consumed by urban communities. Currently our system P flows look like this…… Read Goal and show circular P economy. In MN most biosludge from WWTP landfilled.