Control of the snail hosts of schistosomiasis by environmental manipulation: a field and laboratory appraisal in the Ibadan area, Nigeria

Abstract

An account is given of an ecological investigation of freshwater habitats near Ibadan, Nigeria, which was designed to identify and evaluate key factors that might be m anipulated to achieve control of the snail hosts of schistosomiasis and fascioliasis. Statistical analyses of data from 24 stations from both lentic and lotic habitats showed that there were statistically significant tendencies for the following snail species to coexist: at the macro-distribution levelLanistes libycusandBulinus(P.)globosus, in lotic habitats,Lymnaea natalensis,Bulinus forskali,Biomphalaria pfeifferiandBulinus rohlfsiin lentic habitats; at the micro-distributional level,B. rohlfsi,B. pfeifferi,B. forskaliandAnisus coretus. Several species of aquatic macrophytes, including species that occur at water margins (Acroeasand Commelinaspp.) and those that occur in more persistent aquatic habitats (NymphaeaandCeratophyllumspp.) also coexist to a statistically significant extent both with each other and with snail species in the same microhabitats. However,Salviniaproved exceptional as it was negatively associated with four of the snail species. Persistent snail refugia, including areas at stream origins, backwaters and the deeper bays or inlets in lentic habitats, were characterized by the presence of particular macrophyte species. The reasons for the associations between snails and macrophytes are discussed and it is argued that they may be mutualistic. The snails proved tolerant to a wide range of chemical conditions with the exception of low oxygen concentration. However, the absence of aquatic macrophytes and lentic refugia in head waters and the presence of fast flowing water and high temperatures in shallow water are harmful. Although the indigenous snails,L. libycusandAplexa waterloti, proved to be efficient predators on the eggs and juveniles of snail hosts, other laboratory and field evidence appear to preclude the possibility that they may be useful as biological control agents. In contrast, there is evidence thatMelanoides tuberculatamight exclude the snail hosts from eroding substrates in lentic habitats. The following integrated control measures in lotic habitats are discussed: (a) judicious drainage and canalization of marshy areas at stream origins, combined with replacement of key marginal macrophytes; (b) dredging and straightening of stream courses; (c) replacement of key macrophytes along the banks; (d) introduction ofM. tuberculataif not present. In lentic habitats the following control measures are discussed: (a) prevention of immigration of both macrophytes and snails from feeder streams; (b) control of subaquatic emergent plant species by using grazing domestic animals or competitor species; (c) maximizing wind-generated surface currents to exclude floating plants; (d) eradication of submerged rooting plants by herbivorous fish or invertebrates; (e) the management of such water bodies as either plankton herbivorous fish or plankton - herbivorous fish - carnivorous fish systems; (f) introduction of efficient, detritivorous non-host molluscs or fish to feed on bottom deposits.