Skip to main content
Log in

Studies on decomposition ofCeratophyllum demersum litter under laboratory and field conditions: losses of dry mass and nutrients, qualitative changes in organic compounds and consequences for ambient water and sediments

  • Published:
Hydrobiologia Aims and scope Submit manuscript

Abstract

A study was made of decomposition ofCeratophyllum demersum litter over a 17-day period under controlled conditions of temperature and oxygen (5, 10 and 18 °C; aerobic and anaerobic) and over a 169-day period in the field (Lake Vechten, The Netherlands). Litter, water and sediment were sampled on the 0, 2, 4, 7 and 17th day under controlled conditions and on the 0, 17, 49, 127 and 169th day in the field. The litter was analyzed quantitatively for dry mass, ash, carbon, nitrogen, phosphorus and qualitatively of organic composition by pyrolysis mass spectrometry. The water was analyzed for the elemental concentrations of organic carbon (total and dissolved), nitrogen (total, ammonia and particulate) and phosphorus (total and orthophosphate) and for the concentrations of photosynthetic pigments and bacteria. The sediment was analyzed for the elemental concentrations of nitrogen, carbon and phosphorus, and for bacterial numbers.

The pattern of litter mass loss fitted an exponential model fairly well. Mass decreased faster under controlled aerobic than under anaerobic conditions and the decrease was stimulated by increasing temperature, relatively more in the range of 5 to 10 °C (by 20%) than in the range of 10 of 18 °C (by 2%). The residual mass ranged from 73 to 43% of initial under controlled aerobic conditions and from 84 to 65% under anaerobic conditions after 17 days. It decreased far less in the field, to 38% of initial mass in the field after 169 days.

The litter initially lost a carbohydrate fraction by leaching in all treatments. The protein content decreased initially as well but increased subsequently at increasing temperature stimulated under anaerobic conditions. The changes in organic composition were correlated with those in nitrogen but not with those in carbon and phosphorus contents. The organic composition of litter incubated in the field differed from that of litter incubated in the laboratory. The field residues contained less proteinaceous material than the laboratory residues.

The changes in carbon, nitrogen and phosphorus concentrations in the litter showed different patterns. The carbon concentration generally increased, the nitrogen concentration initially dropped and increased subsequently, and the phosphorus concentration initially dropped and remained relatively constant subsequently. Chemical immobilization of the decomposition process may have occurred in the laboratory, but was unlikely in the field.

Carbon, nitrogen and phosphorus left the litter initially largely in particulate form and were recovered in the water. The ratio dissolved: total nutrient concentration was lower under controlled aerobic than under anaerobic conditions. Increasing temperature stimulated bacterial use of dissolved organic carbon and nitrogen. A rapid nutrient flow occurred from macrophyte litter, via water to sediment.

The phytoplankton biomass in the water was greatly stimulated by substances freed from the decomposing litter. Diatoms increased generally relatively more than green algae, predominating alternatively with green algae under aerobic conditions and continuously under anaerobic conditions. Bacterial numbers in the water initially increased, partly due to transgression of bacteria from the sediment-water interface to the water and partly due to an actual increase in community biomass. The bacteria returned largely to the sediment-water interface, stimulated by increasing temperature, as most of the substrate readily usable by them had left the litter in the litter-bag and was associated with the upper sediment layers.

It is feasible that the annual die-off of theC. demersum population of Lake Vechten barely affects nutrient cycling in the lake, because the contribution to the nutrient pools of the lake when fully mixed is only small. However, small particles originating from decomposingC. demersum litter may influence the lake considerably by decreasing water transparency and serving as a food source for filter-feeders and detritivorous macrofauna.

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

  • Alexander, M., 1977. Soil Microbiology. Wiley, New York.

    Google Scholar 

  • Bastardo, H., 1979. Laboratory studies on decomposition in littoral plants. Pol. Arch. Hydrobiol. 26: 267–299.

    Google Scholar 

  • Best, E. P. H., 1982. The aquatic macrophytes of Lake Vechten. Species composition, spatial distribution and production. Hydrobiologia 95: 65–79.

    Google Scholar 

  • Best, E. P. H. & J. H. A., Dassen, 1987. Biomass, strand area, primary production characteristics and oxygen regime of the Ceratophyllum demersum L. population in Lake Vechten, The Netherlands. Arch. Hydrobiol./Suppl. 76: 347–367.

    Google Scholar 

  • Best, E. P. H. & H. W. C. Visser, 1987. Seasonal growth of the submerged macrophyte Ceratophyllum demersum L. in mesotrophic Lake Vechten in relation to insolation, temperature and reserve carbohydrates. Hydrobiologia 148: 231–243.

    Article  Google Scholar 

  • Boon, J. J., W. Windig, R. G. Wetzel & G. L. Godshalk 1983. The analytical pyrolysis of particulate residues of decomposing Myriophyllum heterophyllum. Aquat. Bot. 15: 307–320.

    Article  Google Scholar 

  • Briggs, S. V., M. T. Maher, & D. J. Tongway 1985. Dry matter and nutrient loss from decomposing Vallisneria spiralis L.. Aquat. Bot. 22: 387–392.

    Article  Google Scholar 

  • Dvorák, J. & E. P. H. Best, 1982. Macro-invertebrate communities associated with the macrophytes of Lake Vechten: structural and functional relationships. Hydrobiologia 95: 115–127.

    Google Scholar 

  • Freier, R. K., 1964. Wasser Analyse. Walter de Gruyter & Co, Berlin. 128 p.

    Google Scholar 

  • Godshalk, G. L. & R. G. Wetzel, 1978. Decomposition of aquatic angiosperms. II. Particulate components. Aquat. Bot. 5: 301–327.

    Article  Google Scholar 

  • Golterman, H. L., 1970. Methods for chemical analysis for fresh waters. IBP Handbook no. 8. Blackwell Sci.Publications, Oxford, Edinburgh.

    Google Scholar 

  • Gons, H. J., 1983. The carbon cycle in three Dutch lakes. In: S. Parma, H. M. van Emden & J. Castelein (eds). Ecology of lakes and ponds. Wageningen, Pudoc. Biologische raad Reeks: 85–117 (In Dutch).

    Google Scholar 

  • Gulati, R. D. & S. Parma, 1982. Studies on Lake Vechten and Lake Tjeukemeer, The Netherlands. Developments in Hydrobiology 11. Dr. W. Junk Publ., The Hague-Boston-London. 383 p.

    Google Scholar 

  • Gulati, R. D., K. Siewertsen & G. Postema, 1982. The zooplankton: its community structure, food and feeding, and role in the ecosystem of Lake Vechten. Hydrobiologia 95: 127–165.

    Google Scholar 

  • Hoogerbrugge, R., S. J. Willig & P. G. Kistemaker, 1983. Discriminant analysis by double stage principal component analysis. Anal. Chem. 55: 1711–1713.

    Google Scholar 

  • Iwamura, T., H. Nagai & S. Ichimura, 1970. Improved method for determining contents of chlorophyll, protein, ribonucleic acid and deoxyribonucleic acid in planktonic populations. Int. Rev. ges. Hydrobiol. 55: 131–147.

    Google Scholar 

  • Janssens, B. H., 1984. A simple method for calculating decomposition and accumulation of ‘young’ soil organic matter. Plant & Soil 76: 297–304.

    Google Scholar 

  • Jenny, H., S. P. Gessel & F. T. Bingham, 1949. Comparative study of decomposition rates of organic matter in temperature and tropical regions. Siol Sci. 68: 419–432.

    Google Scholar 

  • Jones, J. G. & B. M. Simon, 1975. An investigation of errors in direct counts of aquatic bacteria by epifluorescence microscopy, with reference to a new method for dying membrane filters. J. Appl. Bact. 39: 317–329.

    Google Scholar 

  • Minderman, G., 1968. Addition, decomposition and accumulation of organic matter in forests. J. Ecol. 56: 355–362.

    Google Scholar 

  • Minshall, G. W., R. W. Petersen, K. W. Cummins, T. L. Bott,et al., 1983. Interbiome comparison of stream ecosystem dynamics. Ecol. Monogr. 53: 1–25.

    Google Scholar 

  • Nichols, D. S. &D. R. Keeney,1973. Nitrogen and phosphorus release from decaying water milfoil. Hydrobiologia 42: 509–525.

    Google Scholar 

  • Novak, J. T., A. S. Goodman & D. L. King, 1975. Aquatic weed decay and color production. J. Am. Water Works Assoc. 67: 134–139.

    Google Scholar 

  • Pomogyi, P., E. P. H. Best, J. J. Boon & J. H. A. Dassen, 1984. On the relation between age, plant composition and nutrient release from living and killed Ceratophyllum plants. Aquat. Bot. 19: 243–250.

    Article  Google Scholar 

  • Rogers, K. H. & C. M. Breen, 1982. Decomposition of Potamogeton crispus L.: The effects of drying on the patterns of mass and nutrient loss. Aquat. Bot. 12: 1–12.

    Article  Google Scholar 

  • Scheiner, D., 1978. Determination of ammonia in Kjeldahl nitrogen by indophenol method. Wat. Res. 10: 31–36.

    Article  Google Scholar 

  • Short, R. A. & J. V. Ward, 1980. Leaf litter processing in a regulated Rocky Mountain stream. Can. J. Fish. Aquat. Sci 37: 123–127.

    Google Scholar 

  • Verdouw, H., C. J. A. van Echteld & E. M. J. Dekkers, 1978. Ammonia determination based on indophenol formation with sodium salicilate. Wat. Res. 12: 399–402.

    Article  Google Scholar 

  • Webster, J. R. & E. F. Benfield, 1986. Vascular plant breakdown in freshwater ecosystems. Ann. Rev. Ecol. Syst. 17: 567–594.

    Article  Google Scholar 

  • Webster, J. R. & J. B. Waide, 1982. Effects of forest clearcutting on leaf breakdown in a southern Appalachian stream. Freshwat. Biol. 12: 331–344.

    Google Scholar 

  • Wohler, J. R., D. B. Robertson & H. R. Loube, 1975. Studies on the decomposition of Potamogeton diversifolius. Bull. Torrey Bot. Club 102: 76–78.

    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. Mar. Biol. Ass. U. K. 47: 23–31.

    Google Scholar 

Download references

Author information

Authors and Affiliations

Authors

Rights and permissions

Reprints and permissions

About this article

Cite this article

Best, E.P.H., Dassen, J.H.A., Boon, J.J. et al. Studies on decomposition ofCeratophyllum demersum litter under laboratory and field conditions: losses of dry mass and nutrients, qualitative changes in organic compounds and consequences for ambient water and sediments. Hydrobiologia 194, 91–114 (1990). https://doi.org/10.1007/BF00028411

Download citation

  • Received:

  • Revised:

  • Accepted:

  • Issue Date:

  • DOI: https://doi.org/10.1007/BF00028411

Key words

Navigation