Skip to main content
Log in

Transport of phosphorus, nitrogen, and carbon by the Apure River, Venezuela

  • Published:
Biogeochemistry Aims and scope Submit manuscript

Abstract

The concentrations and transport of carbon, nitrogen, and phosphorus were studied in the Apure River, Venezuela, over a period of 21 months. The drainage basin, which is in western Venezuela, encompasses 167,000 kM2, most of which has low relief and supports tropical savanna vegetation. Average runoff for the period of study was 361 mm/year. Discharge-weighted mean concentrations were 188 ug/l for total P, 957 ug/l for total N, and 9.8 mg/l for organic C. Annual transport was 0.68 kg· ha-1· year-1 for total P, 3.45 kg · ha-1· year-1 for total N, and 35.4 kg · ha-1 · year-1 for organic C. Particulate matter accounted for 68% of P, 54% of N, and 37% of C transport. The yield of carbon from the Apure watershed agrees well with empirical predictions, based mostly on the temperate zone, for watersheds of similar size and water yield.

Seasonal patterns in chemistry are tied strongly to the hydrologic cycle. When the wet season begins, rising water flushes organic matter from side channels and produces a sharp increase in particulate C and N. Particulate P, which is associated more with mineral material, also increases during rising water. All dissolved constituents except inorganic C also increase over the rising-water phase. As the river inundates the floodplain, the concentration of nitrate declines, whereas the concentrations of dissolved organic C and N continue to rise. At high water the floodplain appears to store sediments that are later remobilized. During low water, all fractions except dissolved inorganic C tend to be at minimum concentration.

Soluble reactive P, total dissolved P, dissolved inorganic C, and dissolved organic C were successfully modelled as hyperbolic functions of discharge. No significant relationships were found between concentration and discharge for any particulate fraction because the flushing and storage mechanisms affecting these fractions occurred within specific hydrologic phases, rather than as a smooth function of discharge. No significant relationships were found for any nitrogen fraction. For nitrate, and thus for total dissolved N, of which nitrate is a major component, poor conformance to standard models is explained by association of key mechanisms (e.g. uptake) with specific hydrologic phases. Particulate components and nitrate in this sense violate the continuity assumptions implicit in the standard models.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Similar content being viewed by others

References

  • Bendschneider, K. & R.J. Robinson (1952) A new spectrophotometric method for the determination of nitrate in sea water. J. Mar. Res. 11: 87–96

    Google Scholar 

  • Cuevas, E. & E. Medina (1986) Nutrient dynamics within amazonian forest ecosystems. I. Nutrient flux in the litter fall and efficiency of nutrient utilization. Oecol. 68: 466–472

    Google Scholar 

  • Ewel, J.J., A. Madriz & J.A. Tosi, Jr. (1976) Zonas de Vida de Venezuela. Sucre, Caracas

  • Grasshoff, K. 1976. Methods of Sea Water Analysis. Verlag Chemie, Weinheim

    Google Scholar 

  • Hall, F.R. (1970) Dissolved solids-discharge relationships. 1. Mixing Models. Water Resources Res. 6: 845–850

    Google Scholar 

  • Hamilton, S.K. & W.M. Lewis, Jr. (1987) Chemistry and nutrient mass balance of a floodplain lake on the Orinoco River floodplain, Venezuela. Limnol. Oceanogr. 32: 1277–1290

    Google Scholar 

  • Hase, H. & H. Folster (1982) Bioelement inventory of a tropical (semi-) evergreen seasonal forest on eutrophic alluvial soils, western Llanos, Venezuela. Acta Oecol./Oecol. Plant. 3: 331–346

    Google Scholar 

  • Hedges, J.I., W.A. Clark, P.D. Quay, J.E. Richey, A.H. Devol & U. de M. Santos (1986) Compositions and fluxes of particulate organic material in the Amazon River. Limnol. Oceanogr. 31: 717–738

    Google Scholar 

  • Howard-Williams, C. & W.J. Junk (1977) The chemical composition of Central Amazonian aquatic macrophytes with special reference to their role in the ecosystem. Arch. Hydrobiol. 79: 446–464

    Google Scholar 

  • Johnson, N.M., G.E. Likens, F.H. Bormann, D.W. Fisher & R.S. Pierce (1969) A working model for the variation in streamwater chemistry at the Hubbard Brook Experimental Forest, New Hampshire. Water Resources Res. 5: 1353–1363

    Google Scholar 

  • Jordan, C.F. (1985) Nutrient Cycling in Tropical Forest Ecosystems. Wiley, New York

    Google Scholar 

  • Lesack, L.R., R.E. Hecky & J.M. Melack (1984) Transport of carbon, nitrogen, phosphorus, and major solutes in the Gambia River, West Africa. Limnol. Oceanogr. 29: 816–830

    Google Scholar 

  • Levine, S.N. & D.W. Schindler (1980) Radiochemical analysis of orthophosphate concentration and seasonal changes in the flux of orthophosphate to seston in Canadian Shield lakes. Can. J. Fish. Aquat. Sci. 37: 479–487

    Google Scholar 

  • Lewis, W.M., Jr. (1986) Nitrogen and phosphorus runoff losses from a nutrient-poor tropical moist forest. Ecol. 67: 1275–1282

    Google Scholar 

  • Lewis, W.M., Jr. (1987) Tropical Limnology. Ann. Rev. Ecol. Syst. 18: 159–184

    Google Scholar 

  • Lewis, W.M. Jr., J.F. Saunders III, F.H. Weibezahn, & S.N. Levine (1986) Organic carbon in the Caura River, Venezuela. Limnol. Oceanogr. 31: 653–656

    Google Scholar 

  • Likens, G.E., F.H. Bormann & N.M. Johnson (1981) Interactions between major biogeochemical cycles in terrestrial ecosystems. In: G.E. Likens (Ed) Some Perspectives of the Major Biogeochemical Cycles, Scope pp 93–112. Scope 17. Wiley, New York

    Google Scholar 

  • MARNR. (1983) Venezuela en Mapas. Ministerio del Ambiente y de los Recursos Naturales Renovables. Caracas

    Google Scholar 

  • Martins, O. (1982) Geochemistry of the Niger River. In: E.T. Degens (Ed) Transport of Carbon and Minerals in Major World Rivers. Part I. Mitt. Geol.-Palaont. Inst. Univ. Hamburg, SCOPE/UNEP Sonderbd. 52: 397–418

  • Meade, R.H., C.F. Nordin, Jr., D. Perez Hernandez, A. Mejia & J.M. Perez Godoy (1983) Sediment and water discharge in Rio Orinoco, Venezuela and Colombia. In: Proc. Second Internat. Symposium on River Sedimentation, 11–16 October, 1983, Nanjing, China (pp. 1134–1144). Water Resources and Electric Power Press, Beijing

    Google Scholar 

  • Meybeck, M. (1982) Carbon, nitrogen, and phosphorus transport by world rivers. Amer. Jour. Sci. 282: 401–450

    Google Scholar 

  • Murphy, J. & J.P. Riley (1962) A modified single solution method for the determination of phosphate in natural waters. Anal. Chim. Acta 27: 31–36

    Google Scholar 

  • Nordin, C. F., Jr. & J.V. Skinner (1977) Sediment sampling equipment for deep fast currents. Proc. Internat. Assoc. Hydraul. Res. 6: 606–609

    Google Scholar 

  • Nordin, C.F., Jr., C.C. Cranston & A. Mejia. (1983) New technology for measuring water and suspended-sediment discharge of large rivers. In: Proc. Second Internat. Symposium on River Sedimentation, 11–16 October, 1983, Nanjing, China (pp. 1145–1158). Water Resources and Electric Power Press, Beijing

  • Ramia, M. (1967) Tipos de sabanas en los Llanos de Venezuela. Bol. Soc. Venezolana Cien. Nat. 112: 262–288

    Google Scholar 

  • Redfield, A.C. (1958) The biological control of chemical factors in the environment. Am. Scientist 46: 205–221

    Google Scholar 

  • Richey, J.E., E. Salati & V. Dos Santos (1985) Biochemistry of the Amazon River: an update. In: E.T. Degens & S. Kempe (Eds), Transport of Carbon and Minerals in Major World Rivers. Part 3. Mitt. Geol. Palaont. Inst. Univ. Hamburg, SCOPE/UNEP Sonderbd. 58: 245–257

  • Rigler, F.H. (1968) Further observations inconsistent with the hypothesis that the molybdenum blue method measures orthophosphate in lake water. Limnol. Oceanogr. 13: 7–13

    Google Scholar 

  • San Jose, J.J., R. Montes, J. Garcia-Miragaya & B.E. Orihuela (1985) Bioproduction of trachypogon savannas in a latitudinal cross-section of the Orinoco Llanos, Venezuela. Acta Oecol./Oecol. Gener. 67: 25–43

    Google Scholar 

  • Schlesinger, W.H. & J.M. Melack (1981) Transport of organic carbon in world's rivers. Tellus 33: 172–187

    Google Scholar 

  • Sheldon, R.W. (1972) Size separations of marine seston by membrane and glass-fiber filters. Limnol. Oceanogr. 17: 494–498

    Google Scholar 

  • Sokal, R.R. & R.J. Rohlf (1981) Biometry, second ed. Freeman, San Francisco

    Google Scholar 

  • Solorzano, L. & J. Sharp (1980a) Determination of total dissolved phosphorus and particulate phosphorus in natural waters. Limnol. Oceanogr. 25: 754–758

    Google Scholar 

  • Solorzano, L. & J. Sharp (1980b) Determination of total dissolved nitrogen in natural waters. Limnol. Oceanogr. 25: 751–754

    Google Scholar 

  • Stevens, H.H., Jr., G.A. Lutz & D.W. Hubbell (1980) Collapsible-bag suspended-sediment sampler. American Society of Civil Engineers Proceedings 106: 611–616

    Google Scholar 

  • Stumm, W. & J.J. Morgan (1981) Aquatic Chemistry, second ed. Wiley, New York

    Google Scholar 

  • Welcomme, R. (1979) Fisheries Ecology of Floodplain Rivers. Longman, London

    Google Scholar 

  • Wood, E.D., F.A.J. Armstrong & F.A. Richards (1967) Determination of nitrate in sea water by cadmium copper reduction to nitrite. J. Mar. Biol. Assoc. UK 47: 23–31

    Google Scholar 

  • Zinck, A. (1977) Rios de Venezuela. Cuadernos Lagoven. Caracas

    Google Scholar 

Download references

Author information

Authors and Affiliations

Authors

Rights and permissions

Reprints and permissions

About this article

Cite this article

Saunders, J.F., Lewis, W.M. Transport of phosphorus, nitrogen, and carbon by the Apure River, Venezuela. Biogeochemistry 5, 323–342 (1988). https://doi.org/10.1007/BF02180071

Download citation

  • Issue Date:

  • DOI: https://doi.org/10.1007/BF02180071

Key words

Navigation