Abstract
SUMMARY The three major wetland types have characteristic fish communities. River-associated wetlands harbour a rich diversity of fishes which can either survive habitat desiccation during the dry-down, or migrate to and fro with the flood. Endorheic wetlands have a lower diversity of species which are typically ‘r’-selected relative to mainstream riverine or lacustrine forms. Marine wetlands have a variety of peripheral or marine forms, but are not discussed in this account. The dynamics of wetland fish communities are determined by periodically changing abiotic factors, especially water temperature and water level, and biotic factors, especially food availability. Water level fluctuations have several important functions and result in pulses of nutrient input and fish abundance. Wetland fish stocks can usually be sustained as long as the pristine flood regime is retained, but disruption of the flooding pattern interferes with fish breeding and nutrient flow. Fishing yields may be directly correlated with the flood history during the previous two years. Wetland fishes play an important role by converting the resource at the base of the food chain, i.e. living plants, detritus or epiphytes, into food for higher trophic levels. The need to identify and conserve key food supplies is emphasized. Wetland fisheries are relatively poorly developed in southern Africa with notable exceptions, e.g. Pongolo floodplain, Okavango swamp, Lake Liambezi, Elephant Marsh on the Shire River, but even in these systems the resource is probably underutilized. The need to consider the socio-economic implications of upgrading a subsistence fishery are emphasized, and further study on the effect of water level fluctuations on major trophic pathways and on multispecies fisheries is encouraged. Because of the urgent need to manage wetland fisheries, various short-cut methods to obtain first-order estimates of fish production, yields and growth rates should be used until more data are available. The need to manage a floodplain holistically for both the aquatic and terrestrial phases is stressed. In addition, inocula (re-colonizing life history stages) should be conserved to accelerate the recovery of endorheic wetland fish stocks after a drought. As wetlands are of fundamental importance to lake or river metabolism and provide vital breeding and feeding areas for fishes, they should be given the highest conservation priority. Cost-benefit analyses should therefore be performed before any large scale manipulations of wetlands are performed.
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More From: Journal of the Limnological Society of Southern Africa
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