Entomopathogenic Nematode - Applications

Applications

Although the biological control industry has acknowledged EPNs since the 1980s, relatively little is understood about their biology in natural and managed ecosystems (Georgis 2002). Nematode-host interactions are poorly understood, and more than half of the natural hosts for recognized Steinernema and Heterorhabditis species remain unknown (Akhurst and Smith 2002). Information is lacking because isolates of naturally infected hosts are rare, so native nematodes are often baited using Galleria mellonella, a lepidopteran that is highly susceptible to parasitic infection. Laboratory studies showing wide host ranges for EPNs were often overestimates, because in a laboratory, contact with a host is assured and environmental conditions are ideal; there are no “ecological barriers” to infection (Kaya and Gaugler 1993, Gaugler et al. 1997). Therefore, the broad host range initially predicted by assay results has not always translated into insecticidal success.

The lack of knowledge about nematode ecology has resulted in unanticipated failures to control pests in the field. For example, parasitic nematodes were found to be completely ineffective against blackflies and mosquitoes due to their inability to swim (Lewis et al.1998). Efforts to control foliage-feeding pests with EPNs were equally unsuccessful, because nematodes are highly sensitive to UV light and desiccation (Lewis et al.1998). Comparing the life histories of nematodes and target pests can often explain such failures (Gaugler et al. 1997). Each nematode species has a unique array of characteristics, including different environmental tolerances, dispersal tendencies, and foraging behaviors (Lewis et al. 1998). Increased knowledge about the factors that influence EPN populations and the impacts they have in their communities will likely increase their efficacy as biological control agents.