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Nutrient Management Strategy for
Falls Lake
Ariel Atkinson
James Kribs
James Mattice
Outline
• Background
• Costs and Benefits
– New development
– Existing development
– Point Sources
– Agriculture
– Drinking Water
– Recreational and Other Benefits
• Cost/Benefit Analysis Results
• Sensitivity Analysis
• Conclusions
Goals of the NMS
• Decrease Nitrogen levels by 40% and
Phosphorus by 77%.
• Improve Water Quality Designation (Impaired
to Normal)
• Protect recreational and ecological value;
reduce drinking water treatment costs
Background
• Other nutrient management project have
been started successfully in the area
• Rules consist of two rule amendments and
nine new rules
• Rules apply to six counties and eight
municipalities
• Rules were adopted on November 19th, 2010
Background
• Rules focus on sources of nutrient pollution
including: new development, existing
development, agriculture, and point sources
Analysis
• Assess Costs
– Planning and Water Quality Monitoring
– New development
– Existing Development
– Point Sources
– Agriculture
• Assess Benefits
– Reduced/Avoided Drinking Water Treatment Costs
– Recreational
– Other Benefits
New Development
• As part of the Falls Lake
Nutrient Management
Strategy, new
development must:
– Institute nutrient control
on-site
– Purchase credits to offset
their production
– Only applicable to
properties larger than
5000 sq. ft.
New Development
TN (lbs/year)
Cost of removal of
TN per year TP (lbs/year)
Cost of removal of
TP per year Total cost per year
For the Eight
Municipalites 20337 $150,410 1419 $141,024 $142,442
For 3 Rural
Counties (Person,
Franklin, Granville) 134197 $992,523 9523 $946,732 $956,255
For 3 Urban
Counties (Wake,
Durham, Orange) 415548 $3,073,395 29505 $2,933,233 $2,962,738
Total 570082 40447 $4,061,435
Amt of reduction 342049 24268
Goal Level 228033 16179
Total Cost of TN
and TP removal $121,843,062
Existing Development
• Each county or municipality must institute a plan for
regulating nitrogen and phosphorus in stormwater
runoff
– Also, they must monitor their pollutant levels
• Any existing plan must attempt to reach the
recommended levels according to what is
“economically and technically feasible”
Existing Development
TN (lbs/yr) TP(lbs/yr)
Current level 1141667 152174
Percentage from
Development 13% 5%
Current load from
Development 148417 7609
Percentage Reduction Goal 40% 77%
Reduction Amount 59367 5859
TN TP Total
Cost of Reduction per year $1,097,690 $832,052 $1,929,742
Cost of Reduction for 30
year plan $29,637,621 $22,465,403 $52,103,024
Point Sources
Dischargers TN allocation(lbs/yr) TP allocation (lbs/yr)
Large 95858 5228
Small 1052 175
Total 96910 5403
Total Reduction per year 64607 18088
Cost of Reduction per year $1,194,577 $2,568,901
Total Cost of Reduction $35,837,318 $77,067,030
Total Cost of TN and TP Reduction $112,904,348
Agriculture
• Fertilizers and animal waste contribute
heavily to a farms total pollution.
• Runoff leads to streams and rivers which
lead into the lake.
• A riparian buffer 10 meters wide will filter
much of this waste before it reaches water.
Agriculture
Removal
Efficiency(lbs/acre/yr)
Stage 1 Reduction
(lbs/yr)
Amt of Buffers Needed
to Reach Stage 1
Reduction(acres)
TN 21 66217 3153
TP 4 28000 7000
Stage 2 Reduction
(lbs/yr)
Amt of Buffer Needed
to Reach Stage 2
Reduction(acres)
TN 21 132433 6306
TP 4 53900 13475
Stage 1 Stage 2 Both Stages
Cost of Buffer
Construction $2,555,000 $2,363,375 $4,918,375
Maintenance Cost $766,500 $472,675 $1,239,175
Opportunity Cost of
Land $28,672,000 $26,521,600 $55,193,600
Total Cost $31,993,500 $29,357,650 $61,351,150
Drinking Water Benefits
• The levels of nitrogen and phosphorus in
Raleigh’s drinking water will not change as a
result of this study, but will reduce cost of
treatment
• The amount of treatment required to achieve the
1mg/l of N and 1µg/l (1/1000 mg) of P
Drinking Water Benefits
Year of the
Program
Consumption
(gallons)
Cost of Removing
TN and TP
w/NMS
Cost of Removing
TN and TP @
Current Levels of
Pollution Benefit of NMS
Discounted
Benefit of NMS
0 17646008160 $277,384 $3,673,336 $3,395,952 $3,395,952
1 18950606928 $277,362 $3,673,313 $3,395,952 $3,173,787
2 20255205696 $277,340 $3,673,291 $3,395,952 $2,966,156
3 21559804464 $277,317 $3,673,269 $3,395,952 $2,772,108
⁞ ⁞ ⁞ ⁞ ⁞ ⁞
28 54174773664 $276,763 $3,672,714 $3,395,952 $510,759
29 55479372432 $276,741 $3,672,692 $3,395,952 $477,345
30 56783971200 $276,718 $3,672,670 $3,395,952 $446,116
Total Benefit over
30 yrs $105,274,499 $45,536,455
Recreational Benefits
• Travel Cost Study
done
• Evaluate how
changes in water
quality correlated
with changes in
the amount of
trips made and
the WTP per trip
to Falls Lake for
recreation
Other Benefits
• Decrease in Other
Types of Pollution
• Improved Aesthetics
• Impact on Public
Health
• Ecological Benefits
• Increased Property
Values
Results of Cost/Benefit Analysis
Costs of NMS Cost
Planning and Monitoring $854,700
New Dev'p Stormwater Management $293,131,625
Existing Dev'p Stormwater Management $52,103,024
Point Source Loading Reductions $112,904,348
Agricultural Loading Reductions $61,351,150
Total Cost $520,344,847
Benefits of NMS Benefit
Recreational Benefits $241,000,000
Reduced Drinking Water Treatment $45,536,455
Avoided Upgrade in Treatment (only avoided construction costs) $120,000,000
Others(Aesthetic, Ecological, Property Values, Public Health) ---
Total Benefit $406,536,455
Net Benefit -$113,808,392
Sensitivity Analysis
• Changing the discount rate effects the results,
but never results in the costs outweighing the
benefits
• All population growth was assumed to be
linear
• Property values were assumed to be constant
• Cost of reducing nutrient pollution was
assumed to be at a constant rate ($/lb) for
development and point sources
• Technological Advances
Conclusions
• While the costs exceed the benefits, due to
uncertainty and sensitivity of the analysis, it is
not recommended to accept or reject these
rule changes
– Economic Analysis of other Nutrient Management
Plans have shown benefits outweigh costs
– Future efforts should focus on detailing the
methodology and timeframe
References
• Army Corps of Engineers- Wilmington District. (2008, January 18). Falls Lake. Retrieved from Army Corps of Engineers- Wilmington District:
http://www.saw.usace.army.mil/falls/index.htm
• Barnes, S. (2010, September 10). Project Description. Retrieved from Falls Lake Restoration Project: http://www.fallslakestakeholder.org/
• Bellinger, W. K. (2007). The Economic Analysis of Public Policy. New York, New York: Routledge.
• Bird, S. L., & Exum, L. R. (2010, March 4). Estimating Impervious Cover from Regionally Available Data. Retrieved October 31, 2010, from U.S. Environmental
Protection Agency: http://www.epa.gov/athens/highlights/le1335.pdf
• Brown, D., & Wilbur, S. (2008, September 11). Stormwater 201-Development Standards. Retrieved November 5, 2010, from City of Durham Stormwater Services:
http://www.ci.durham.nc.us/departments/works/pdf/sw201-5_development.pdf
• Capitol Broadcasting Company. (2010, January 5). Falls Lake pollution could require new treatment plant. Retrieved from WRAL.com:
http://www.wral.com/news/local/story/6746623/
• Energy Information Administration. (2006, November 27). Summary Table for All Buildings. Retrieved November 5, 2010, from U.S. Energy Information
Administration: http://www.eia.doe.gov/emeu/cbecs/cbecs2003/detailed_tables_2003/2003set1/2003pdf/a1.pdf
• Herrera Environmental Consultants. (2003). Green Lake Alum Treatment Study. Seattle. Wa: Seattle Department of Parks and Recreation.
• Huisman, J. (2010, March). 15A NCAC 02B.275-283. Retrieved November 5, 2010, from Falls Lake Stakeholder Project Online Wiki:
http://fallslakestakeholder.wikispaces.com/Draft+Rules
• Huisman, J. (2010). Overview of Falls Lake Nutrient Strategy. NC Division of Water Quality, Planning Section, Raleigh.
• Lynch, L., & Tjaden, R. (2000). When a Landowner Adopts a Riparian Buffer-Benefits and Costs. College Park, Maryland: University of Maryland.
• Municipal Support Division, Municipal Technology Branch. (2008). Municipal Nutrient Removal Technologies Reference Document. Office of Wastewater
Management. US EPA.
• NC Division of Parks and Recreation. (2010, September). Falls Lake State Recreation Area. Retrieved 10 2010, September, from North Carolina State Parks:
http://www.ncparks.gov/Visit/parks/fala/main.php
• NC Divison of Water Quality, Planning Section. (2010, June 14). Fiscal Analysis for Proposed Nutrient Management Strategy. Retrieved November 5, 2010, from
NCDENR: NC Divison of Water Quality: http://portal.ncdenr.org/c/document_library/get_file?uuid=2a29f5a4-3db1-4c63-bd63-cad51a5ac385&groupId=38364
• NC Ecosystem Enhancement Program. (2010, September 1). EEP's Nutrient Offset Program. Retrieved November 7, 2010, from NC Ecosystem Enhancement Program
Website: http://www.nceep.net/services/stratplan/Nutrient_Offset_Program.htm
• Rowe, R. (2001, May 22). Implementation of Neuse River Basin Model . Retrieved November 5, 2010, from Wake County Environmental Services:
http://www.wakegov.com/NR/rdonlyres/85E5620C-87E2-4D6B-AF88-46E6E644DB2E/0/StormwaterRules.pdf
• Schlegel, M. (2010). Project Description. Retrieved 2010, from Falls Lake Stakeholder Project.
• U.S. Census Bureau: State & County Quick Facts: North Carolinas. (2010, November 5). Retrieved November 5, 2010, from
http://quickfacts.census.gov/qfd/states/37000.html
• USDA National Agricultural Statistics Service. (2007). Table 40. Farms by Concentration of Market Value of Agricultural Products Sold: 2007. North Carolina.
• von Haefen, R. H. (2010, April 6). Preliminary Recreational Benefits Esitmates for the Falls Lake Nutrient Management Strategy. Raleigh, North Carolina: North
Carolina State University.

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Cost-Benefit Analysis of Nutrient Management for Falls Lake

  • 1. Nutrient Management Strategy for Falls Lake Ariel Atkinson James Kribs James Mattice
  • 2. Outline • Background • Costs and Benefits – New development – Existing development – Point Sources – Agriculture – Drinking Water – Recreational and Other Benefits • Cost/Benefit Analysis Results • Sensitivity Analysis • Conclusions
  • 3. Goals of the NMS • Decrease Nitrogen levels by 40% and Phosphorus by 77%. • Improve Water Quality Designation (Impaired to Normal) • Protect recreational and ecological value; reduce drinking water treatment costs
  • 4. Background • Other nutrient management project have been started successfully in the area • Rules consist of two rule amendments and nine new rules • Rules apply to six counties and eight municipalities • Rules were adopted on November 19th, 2010
  • 5. Background • Rules focus on sources of nutrient pollution including: new development, existing development, agriculture, and point sources
  • 6. Analysis • Assess Costs – Planning and Water Quality Monitoring – New development – Existing Development – Point Sources – Agriculture • Assess Benefits – Reduced/Avoided Drinking Water Treatment Costs – Recreational – Other Benefits
  • 7. New Development • As part of the Falls Lake Nutrient Management Strategy, new development must: – Institute nutrient control on-site – Purchase credits to offset their production – Only applicable to properties larger than 5000 sq. ft.
  • 8. New Development TN (lbs/year) Cost of removal of TN per year TP (lbs/year) Cost of removal of TP per year Total cost per year For the Eight Municipalites 20337 $150,410 1419 $141,024 $142,442 For 3 Rural Counties (Person, Franklin, Granville) 134197 $992,523 9523 $946,732 $956,255 For 3 Urban Counties (Wake, Durham, Orange) 415548 $3,073,395 29505 $2,933,233 $2,962,738 Total 570082 40447 $4,061,435 Amt of reduction 342049 24268 Goal Level 228033 16179 Total Cost of TN and TP removal $121,843,062
  • 9. Existing Development • Each county or municipality must institute a plan for regulating nitrogen and phosphorus in stormwater runoff – Also, they must monitor their pollutant levels • Any existing plan must attempt to reach the recommended levels according to what is “economically and technically feasible”
  • 10. Existing Development TN (lbs/yr) TP(lbs/yr) Current level 1141667 152174 Percentage from Development 13% 5% Current load from Development 148417 7609 Percentage Reduction Goal 40% 77% Reduction Amount 59367 5859 TN TP Total Cost of Reduction per year $1,097,690 $832,052 $1,929,742 Cost of Reduction for 30 year plan $29,637,621 $22,465,403 $52,103,024
  • 11. Point Sources Dischargers TN allocation(lbs/yr) TP allocation (lbs/yr) Large 95858 5228 Small 1052 175 Total 96910 5403 Total Reduction per year 64607 18088 Cost of Reduction per year $1,194,577 $2,568,901 Total Cost of Reduction $35,837,318 $77,067,030 Total Cost of TN and TP Reduction $112,904,348
  • 12. Agriculture • Fertilizers and animal waste contribute heavily to a farms total pollution. • Runoff leads to streams and rivers which lead into the lake. • A riparian buffer 10 meters wide will filter much of this waste before it reaches water.
  • 13. Agriculture Removal Efficiency(lbs/acre/yr) Stage 1 Reduction (lbs/yr) Amt of Buffers Needed to Reach Stage 1 Reduction(acres) TN 21 66217 3153 TP 4 28000 7000 Stage 2 Reduction (lbs/yr) Amt of Buffer Needed to Reach Stage 2 Reduction(acres) TN 21 132433 6306 TP 4 53900 13475 Stage 1 Stage 2 Both Stages Cost of Buffer Construction $2,555,000 $2,363,375 $4,918,375 Maintenance Cost $766,500 $472,675 $1,239,175 Opportunity Cost of Land $28,672,000 $26,521,600 $55,193,600 Total Cost $31,993,500 $29,357,650 $61,351,150
  • 14. Drinking Water Benefits • The levels of nitrogen and phosphorus in Raleigh’s drinking water will not change as a result of this study, but will reduce cost of treatment • The amount of treatment required to achieve the 1mg/l of N and 1µg/l (1/1000 mg) of P
  • 15. Drinking Water Benefits Year of the Program Consumption (gallons) Cost of Removing TN and TP w/NMS Cost of Removing TN and TP @ Current Levels of Pollution Benefit of NMS Discounted Benefit of NMS 0 17646008160 $277,384 $3,673,336 $3,395,952 $3,395,952 1 18950606928 $277,362 $3,673,313 $3,395,952 $3,173,787 2 20255205696 $277,340 $3,673,291 $3,395,952 $2,966,156 3 21559804464 $277,317 $3,673,269 $3,395,952 $2,772,108 ⁞ ⁞ ⁞ ⁞ ⁞ ⁞ 28 54174773664 $276,763 $3,672,714 $3,395,952 $510,759 29 55479372432 $276,741 $3,672,692 $3,395,952 $477,345 30 56783971200 $276,718 $3,672,670 $3,395,952 $446,116 Total Benefit over 30 yrs $105,274,499 $45,536,455
  • 16. Recreational Benefits • Travel Cost Study done • Evaluate how changes in water quality correlated with changes in the amount of trips made and the WTP per trip to Falls Lake for recreation
  • 17. Other Benefits • Decrease in Other Types of Pollution • Improved Aesthetics • Impact on Public Health • Ecological Benefits • Increased Property Values
  • 18. Results of Cost/Benefit Analysis Costs of NMS Cost Planning and Monitoring $854,700 New Dev'p Stormwater Management $293,131,625 Existing Dev'p Stormwater Management $52,103,024 Point Source Loading Reductions $112,904,348 Agricultural Loading Reductions $61,351,150 Total Cost $520,344,847 Benefits of NMS Benefit Recreational Benefits $241,000,000 Reduced Drinking Water Treatment $45,536,455 Avoided Upgrade in Treatment (only avoided construction costs) $120,000,000 Others(Aesthetic, Ecological, Property Values, Public Health) --- Total Benefit $406,536,455 Net Benefit -$113,808,392
  • 19. Sensitivity Analysis • Changing the discount rate effects the results, but never results in the costs outweighing the benefits • All population growth was assumed to be linear • Property values were assumed to be constant • Cost of reducing nutrient pollution was assumed to be at a constant rate ($/lb) for development and point sources • Technological Advances
  • 20. Conclusions • While the costs exceed the benefits, due to uncertainty and sensitivity of the analysis, it is not recommended to accept or reject these rule changes – Economic Analysis of other Nutrient Management Plans have shown benefits outweigh costs – Future efforts should focus on detailing the methodology and timeframe
  • 21. References • Army Corps of Engineers- Wilmington District. (2008, January 18). Falls Lake. Retrieved from Army Corps of Engineers- Wilmington District: http://www.saw.usace.army.mil/falls/index.htm • Barnes, S. (2010, September 10). Project Description. Retrieved from Falls Lake Restoration Project: http://www.fallslakestakeholder.org/ • Bellinger, W. K. (2007). The Economic Analysis of Public Policy. New York, New York: Routledge. • Bird, S. L., & Exum, L. R. (2010, March 4). Estimating Impervious Cover from Regionally Available Data. Retrieved October 31, 2010, from U.S. Environmental Protection Agency: http://www.epa.gov/athens/highlights/le1335.pdf • Brown, D., & Wilbur, S. (2008, September 11). Stormwater 201-Development Standards. Retrieved November 5, 2010, from City of Durham Stormwater Services: http://www.ci.durham.nc.us/departments/works/pdf/sw201-5_development.pdf • Capitol Broadcasting Company. (2010, January 5). Falls Lake pollution could require new treatment plant. Retrieved from WRAL.com: http://www.wral.com/news/local/story/6746623/ • Energy Information Administration. (2006, November 27). Summary Table for All Buildings. Retrieved November 5, 2010, from U.S. Energy Information Administration: http://www.eia.doe.gov/emeu/cbecs/cbecs2003/detailed_tables_2003/2003set1/2003pdf/a1.pdf • Herrera Environmental Consultants. (2003). Green Lake Alum Treatment Study. Seattle. Wa: Seattle Department of Parks and Recreation. • Huisman, J. (2010, March). 15A NCAC 02B.275-283. Retrieved November 5, 2010, from Falls Lake Stakeholder Project Online Wiki: http://fallslakestakeholder.wikispaces.com/Draft+Rules • Huisman, J. (2010). Overview of Falls Lake Nutrient Strategy. NC Division of Water Quality, Planning Section, Raleigh. • Lynch, L., & Tjaden, R. (2000). When a Landowner Adopts a Riparian Buffer-Benefits and Costs. College Park, Maryland: University of Maryland. • Municipal Support Division, Municipal Technology Branch. (2008). Municipal Nutrient Removal Technologies Reference Document. Office of Wastewater Management. US EPA. • NC Division of Parks and Recreation. (2010, September). Falls Lake State Recreation Area. Retrieved 10 2010, September, from North Carolina State Parks: http://www.ncparks.gov/Visit/parks/fala/main.php • NC Divison of Water Quality, Planning Section. (2010, June 14). Fiscal Analysis for Proposed Nutrient Management Strategy. Retrieved November 5, 2010, from NCDENR: NC Divison of Water Quality: http://portal.ncdenr.org/c/document_library/get_file?uuid=2a29f5a4-3db1-4c63-bd63-cad51a5ac385&groupId=38364 • NC Ecosystem Enhancement Program. (2010, September 1). EEP's Nutrient Offset Program. Retrieved November 7, 2010, from NC Ecosystem Enhancement Program Website: http://www.nceep.net/services/stratplan/Nutrient_Offset_Program.htm • Rowe, R. (2001, May 22). Implementation of Neuse River Basin Model . Retrieved November 5, 2010, from Wake County Environmental Services: http://www.wakegov.com/NR/rdonlyres/85E5620C-87E2-4D6B-AF88-46E6E644DB2E/0/StormwaterRules.pdf • Schlegel, M. (2010). Project Description. Retrieved 2010, from Falls Lake Stakeholder Project. • U.S. Census Bureau: State & County Quick Facts: North Carolinas. (2010, November 5). Retrieved November 5, 2010, from http://quickfacts.census.gov/qfd/states/37000.html • USDA National Agricultural Statistics Service. (2007). Table 40. Farms by Concentration of Market Value of Agricultural Products Sold: 2007. North Carolina. • von Haefen, R. H. (2010, April 6). Preliminary Recreational Benefits Esitmates for the Falls Lake Nutrient Management Strategy. Raleigh, North Carolina: North Carolina State University.