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Biogeochemistry

, Volume 54, Issue 1, pp 85–114 | Cite as

Dissolved and particulate nutrient flux from three adjacent agricultural watersheds: A five-year study

  • Michael J. Vanni
  • William H. Renwick
  • Jenifer L. Headworth
  • Jeffery D. Auch
  • Maynard H. Schaus
Article

Abstract

Fluxes of dissolved and particulate nitrogen (N) and phosphorus(P) from three adjacent watersheds were quantified with ahigh-resolution sampling program over a five-year period. The watershedsvary by an order of magnitude in area (12,875, 7968 and 1206 ha), and inall three watersheds intensive agriculture comprises > 90% ofland. Annual fluxes of dissolved N and P per unit watershed area (exportcoefficients) varied ∼2X among watersheds, and patterns were notdirectly related to watershed size. Over the five-year period, meanannual flux of soluble reactive P (SRP) was 0.583 kg P ·ha−1 · yr−1 from the smallestwatershed and 0.295 kg P · ha−1 ·yr−1 from the intermediate-sized watershed, which hadthe lowest SRP flux. Mean annual flux of nitrate was 20.53 kg N ·ha−1 · yr−1 in the smallestwatershed and 44.77 kg N · ha−1 ·yr−1 in the intermediate-sized watershed, which had thehighest nitrate flux. As a consequence, the export ratio of dissolvedinorganic N to SRP varied from 80 (molar) in the smallest watershed to335 in the intermediate-sized watershed. Because most N was exported asnitrate, differences among watersheds in total N flux were similar tothose for nitrate. Hence, the total N:P export ratio was 42(molar) for the smallest watershed and 109 for the intermediate-sizedwatershed. In contrast, there were no clear differences among watershedsin the export coefficients of particulate N, P, or carbon, even though> 50% of total P was exported as particulate P in allwatersheds. All nutrient fractions were exported at higher rates in wetyears than in dry years, but precipitation-driven variability in exportcoefficients was greater for particulate fractions than for dissolvedfractions.

Examination of hydrological regimes showed that, for all nutrientfractions, most export occurred during stormflow. However, theproportion of nitrate flux exported as baseflow was much greater thanthe proportion of SRP flux exported as baseflow, for all threewatersheds (25–37% of nitrate exported as baseflow vs.3–13% of SRP exported as baseflow). In addition, baseflowcomprised a greater proportion of total discharge in theintermediate-sized watershed (43.7% of total discharge) than theother two watersheds (29.3 and 30.1%). Thus, higher nitrateexport coefficients in the intermediate-sized watershed may haveresulted from the greater contribution of baseflow in this watershed.Other factors potentially contributing to higher nitrate exportcoefficients in this watershed may be a thicker layer of loess soils anda lower proportion of riparian forest than the other watersheds. Theamong-watershed variability in SRP concentrations and exportcoefficients remains largely unexplained, and might represent theminimum expected variation among similar agriculturalwatersheds.

agricultural watershed nitrogen non-point sources nutrients nutrient flux phosphorus watershed 

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References

  1. Allan JD, Erickson DL & Fay J (1997) The influence of catchment land use on stream integrity across multiple spatial scales. Freshwater Biol. 37: 149-161Google Scholar
  2. Baker DB (1993) The Lake Erie Agroecosystem Program: Water quality assessments. Agricult. Ecosyst. Environ. 46: 197-215Google Scholar
  3. Beaulac MN & Reckhow KH (1982) An examination of land use-nutrient export relationships. Water Resources Bull. 18: 1013-1024Google Scholar
  4. Boggess CF, Flaig EG & Fluck RC (1995) Phosphorus budget-basin relationships for Lake Okeechobee tributary basins. Ecol. Eng. 5: 143-162Google Scholar
  5. Brenner FJ & Mondok JJ (1995) Nonpoint source pollution potential in an agricultural watershed in northwestern Pennsylvania. Water Resources Bulletin 31: 1101-1112Google Scholar
  6. Caraco NF & JJ Cole (1999) Human impact on nitrate export: An analysis using major world rivers. Ambio 28: 167-170Google Scholar
  7. Carpenter SR, Caraco NF, Correll DL, Howarth RW, Sharpley AN & Smith VH (1998) Nonpoint pollution of surface waters with phosphorus and nitrogen. Ecol. Appl. 8: 559-568Google Scholar
  8. Cleresci NL, Curran SJ & Sedlak RI (1986) Nutrient loads toWisconsin lakes: Part 1. Nitrogen and phosphorus export coefficients. Water Resources Bull. 22: 983-990Google Scholar
  9. Cohn TA (1995) Recent advances in statistical methods for the estimation of sediment and nutrient transport in rivers. Rev. Geophys. 33 (Suppl): 1117-1123Google Scholar
  10. Cohn TA, DeLong EE, Gilroy EJ, Hirsch RM & Wells DK (1989) Estimating constituent loads. Water Resources Res. 25: 937-945Google Scholar
  11. Cooke SE & Prepas EE (1998) Stream phosphorus and nitrogen export from agricultural and forested watersheds on the Boreal Plain. Can. J. Fish. Aquat. Sci. 55: 2292-2299Google Scholar
  12. Correll DL (1998) The role of phosphorus in the eutrophication of receiving waters: A review. J. Environ. Qual. 27: 261-267Google Scholar
  13. Correll DL, Jordan TE & Weller DE (1999) Effects of precipitation and air temperature on phosphorus fluxes from Rhode River watersheds. J. Environ. Qual. 28: 144-154Google Scholar
  14. Creed IF & Band LE (1998) Export of nitrogen from catchments within a temperate forest: Evidence for a unifying mechanism regulated by variable source area dynamics. Water Resources Res. 34: 3105-3120Google Scholar
  15. Crumpton WG, Isenhart TM & Mitchell PD (1992) Nitrate and organic N analyses with second derivative spectroscopy. Limnol. Oceanogr. 37: 907-913Google Scholar
  16. Daniel TC, Sharpley AN & Lemunyon JL (1998) Agricultural phosphorus and eutrophication: A symposium overview. J. Environ. Qual. 27: 251-257Google Scholar
  17. DeVantier BA & Feldman AD (1993) Review of GIS applications in hydrologic modeling. J. Water Resources Planning and Management. 119: 246-261Google Scholar
  18. Dillon PJ & Kirchner WB (1975) The effects of geology and land use on the export of phosphorus from watersheds. Water Research 9: 135-148Google Scholar
  19. Downing JA, McClain M, Twilley R, Melack JM, Elser J, Rabalais NN, Lewis Jr. WM, Turner RE, Corredor J, Soto D, Yanez-Arancibia A, Kopaska JA & Howarth RW (1999) The impact of accelerating land-use change on the N-cycle of tropical aquatic ecosystems: Current conditions and projected changes. Biogeochemistry 46: 109-148Google Scholar
  20. Gambrell RP, Gilliam JW & Weed SB (1975) Nitrogen losses from soils of the North Carolina Coastal Plain. J. Environ. Qual. 4: 317-322Google Scholar
  21. Gburek WJ & Sharpley AN (1998) Hydrologic controls on phosphorus loss from upland agricultural watersheds. J. Environ. Qual. 27: 267-277Google Scholar
  22. Grayson RB, Moore ID & McMahon TA (1992) Physically based hydrologic modeling 2. Is the concept realistic? Water Resources Res. 26: 2659-2666Google Scholar
  23. Groffman PM, Simmons RC & Gold AJ (1992) Nitrate dynamics in riparian forests: Microbial studies. J. Environ. Qual. 21: 666-671Google Scholar
  24. Gustard A, Bullock A & Dixon JM (1992) Low flow estimation in the United Kingdom. Report 108 (pp 19-25). Institute of Hydrology, Wallingford, EnglandGoogle Scholar
  25. Heckrath G, Brookes PC, Poulton PR & Goulding KWT (1995) Phosphorus leaching from soils containing different phosphorus concentrations in the Broadbalk experiment. J. Environ. Qual. 24: 904-910Google Scholar
  26. Hessen DO, Hindar A & Holtan G (1997) The significance of nitrogen runoff for eutrophication of freshwater and marine recipients. Ambio 26: 312-320Google Scholar
  27. Hill AR (1996) Nitrate removal in stream riparian zones. J. Environ. Qual. 25: 743-755Google Scholar
  28. Howarth RW (1988) Nutrient limitation of net primary production in marine ecosystems. Ann. Rev. Ecol. Syst. 19: 89-110Google Scholar
  29. Howarth RW, Billen G, Swaney D, Townsend A, Jaworski N, Lajtha K, Downing JA, Elmgren R, Caraco N, Jordan T, Berendse F, Freney J, Kudeyarov V, Murdoch P & Zhu ZL (1996) Regional nitrogen budgets and riverine N& P fluxes for the drainages to the North Atlantic Ocean: natural and human influences. Biogeochemistry 35: 75-139Google Scholar
  30. Hunsaker CT & DA Levine DA (1995) Hierarchical approaches to the study of water quality in rivers. BioScience 45: 193-203Google Scholar
  31. Jansson M (1985) A comparison of detransformed logarithmic regressions and power function regressions. Geografiska Annaler 67A: 61-70Google Scholar
  32. Jordan TE, Correll DL & Weller DE (1993) Nutrient interception by a riparian forest receiving inputs from adjacent cropland. J. Environ. Qual. 22: 467-473Google Scholar
  33. Jordan TE, Correll DL & Weller DE (1997a) Relating nutrient discharges from watersheds to land use and streamflow variability. Water Resources Res. 33: 2579-2590Google Scholar
  34. Jordan TE, Correll DL & Weller DE (1997b) Nonpoint source discharges of nutrients from piedmont watersheds of Chesapeake Bay. J. Amer. Water Resources Assoc. 33: 631-645Google Scholar
  35. Kalkhoff SJ (1995) Relation between stream-water quality and geohydrology during base-flow conditions, Roberts Creek watershed, Clayton County, Iowa. Water Resources Res. 31: 593-604Google Scholar
  36. Kennedy EJ (1983) Computation of continuous records of streamflow. Techniques of Water-Resources Investigations of the United States Geological Survey, Book 3. U.S. Geological SurveyGoogle Scholar
  37. Lewis WM Jr, Melack JM, McDowell WH, McClain M & Richey JE. 1999. Nitrogen yields from undisturbed watersheds in the Americas. Biogeochemistry 46: 149-162Google Scholar
  38. Likens GE & FH Bormann (1995) Biogeochemistry of a forested ecosystem. Second edition. Springer-VerlagGoogle Scholar
  39. Logan TJ (1990) Sustainable agriculture and water quality. In: Edwards CA, Lal R, Madden P, Miller RH & House G (Eds) Sustainable Agricultural Systems (pp 582-613). Soil and Water Conservation Society, Ankeny, Iowa, USA.Google Scholar
  40. Medley KE, Okey BW, Barrett GW, Lucas MF & Renwick WH (1995) Landscape change with agricultural intensification in a rural watershed, southwestern Ohio, USA. Landscape Ecol 10: 161-176Google Scholar
  41. Miltner RJ & Rankin ET (1998) Primary nutrients and the biotic integrity of rivers and streams. Freshwater Biol. 40: 145-158Google Scholar
  42. Mueller DK, Hamilton PA, Helsel DR, Hitt KJ & Ruddy BC (1995) Nutrients in ground water and surface water of the United States-An analysis of data through 1992. United States Geological Survey Water-Resources Investigations Report 95-4031Google Scholar
  43. Murphy J & Riley JP (1962) A modified single solution method for the determination of phosphate in natural waters. Anal. Chim. Acta. 27: 31-36CrossRefGoogle Scholar
  44. Naiman RJ, Ed (1992) Watershed management: Balancing Sustainability and Environmental Change. Springer, New YorkGoogle Scholar
  45. Naiman RJ, Magnuson JJ, McKnight DM & Stanford JA, Eds (1995) The Freshwater Imperative: A Research Agenda. Island Press, Washington DC.Google Scholar
  46. Nathan RJ & McMahon TA (1990) Evaluation of automated techniques for base flow and recession analyses. Water Resources Research 26: 1465-1473Google Scholar
  47. Omernik JM (1976) The influence of land use on stream nutrient levels. United States Environmental Protection Agency Report EPA 600/3-76-014, Corvallis, OregonGoogle Scholar
  48. Osborne LL & Kovacic DA (1993) Riparian vegetated buffer strips in water quality restoration and stream management. Freshwater Biol. 29: 243-258Google Scholar
  49. Porterfield G (1972) Computation of fluvial-sediment discharge. Techniques of Water-Resources Investigations of the United States Geological Survey, Book 3. U.S. Geological SurveyGoogle Scholar
  50. Prairie YT & Kalff J (1986) Effect of catchment size on phosphorus export. Water Resources Bull. 22: 465-470Google Scholar
  51. Puckett LJ (1995) Identifying the major sources of nutrient water pollution. Environ. Sci. Tech. 29: 408-414Google Scholar
  52. Richards RP & Baker DB (1993) Trends in nutrient and suspended sediment concentrations in Lake Erie tributaries, 1975-1990. J. Great Lakes Res. 19: 200-211Google Scholar
  53. Richards RP & Holloway J (1987) Monte Carlo studies of sampling strategies for estimating tributary loads. Water Resources Res. 23: 1939-1948Google Scholar
  54. Schaus MH, Vanni MJ, Wissing TE, Bremigan MT, Garvey JA & Stein RA (1997) Nitrogen and phosphorus excretion by detritivorous fish (the gizzard shad, Dorosoma cepedianum) in a reservoir ecosystem. Limnol. Oceanogr. 42: 1386-1397Google Scholar
  55. Sharpley AN (1995) Identifying sites vulnerable to phosphorus loss in agricultural runoff. J. Environ. Qual. 24: 947-951Google Scholar
  56. Sims JT, Simard RR & Joern BC (1998) Phosphorus loss in agricultrual drainage: Historical perspective and current research. J. Environ. Qual. 27: 277-293Google Scholar
  57. Smith RA, Alexander RB & Wolman MG (1987) Water-quality trends in the nation's rivers. Science 235: 1607-1615Google Scholar
  58. Smith VH (1998) Cultural eutrophication of inland, estuarine, and coastal waters. In: Pace ML & Groffman PM (Eds) Successes, Limitations, and Frontiers in Ecosystem Science (pp 7-49). Springer, New YorkGoogle Scholar
  59. Sokal RR & Rohlf FJ (1981) Biometry. Second edition. Freeman, New YorkGoogle Scholar
  60. Solorzano L (1969) Determination of ammonia in natural waters by the phenolhypochlorite method. Limnol. Oceanogr. 14: 799-801Google Scholar
  61. Soranno PA, Hubler SL, Carpenter SR & Lathrop RC (1996) Phosphorus loads to surface waters: A simple model to account for spatial pattern of land use. Ecol. Appl. 6: 865-878Google Scholar
  62. Stainton MP, Capel MJ & Armstrong FAJ (1977) The chemical analysis of fresh-water. Miscellaneous Special Publication 25. Freshwater Institute, WinnipegGoogle Scholar
  63. Steinheimer TR, Scoggin KD & Kramer LA (1998) Agricultural chemical movement through a field-size watershed in Iowa: Surface hydrology and nitrate loss in discharge. Environ. Sci. Tech. 32: 1048-1052Google Scholar
  64. USDA (United States Department of Agriculture) (1992) Watershed plan and environmental assessment for Four Mile Creek Watershed, Ohio and IndianaGoogle Scholar
  65. Vitousek PM, Gosz JR, Grier CC, Melillo JM, Reiners WA & Todd RL (1979) Nitrate loss from disturbed ecosystems. Science 204: 469-474Google Scholar
  66. Winner RW, Strecker RL & Ingersoll EM (1962) Some physical and chemical characteristics of Acton Lake, Ohio. Ohio J. Sci. 62: 55-61Google Scholar

Copyright information

© Kluwer Academic Publishers 2001

Authors and Affiliations

  • Michael J. Vanni
    • 1
  • William H. Renwick
    • 2
  • Jenifer L. Headworth
    • 3
  • Jeffery D. Auch
    • 4
  • Maynard H. Schaus
    • 5
  1. 1.Department of ZoologyMiami UniversityOxfordUSA (Author for correspondence; e-mail:
  2. 2.Department of GeographyMiami UniversityOxfordUSA
  3. 3.Department of ZoologyMiami UniversityOxfordUSA
  4. 4.Department of ZoologyMiami UniversityOxfordUSA;
  5. 5.Department of ZoologyMiami UniversityOxfordUSA;

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