[
1989]
Classical embryological studies of nematodes, primarily by Van Beneden and Boveri near the turn of the century, have made lasting contributions to our understanding of embryonic development (1). However, during most of this century, nematodes have been eclipsed as a model system for embryology by organisms with more tractable embryos such as sea urchins, insects, amphibians, birds, and mice. Two features of the free-living soil nematode Caenorhabditis elegans have returned nematodes to a prominent place in embryological investigations: its suitability for genetic analysis and its invariant and completely described cell lineage. These two features, combined with technological advances in microscopy and molecular biology, are providing the opportunity to combine experimental embryology with genetic and molecular analyses of embryonic development at the level of individual cells in a single organism. This chapter focuses on efforts to understand the molecular and cellular events of early development in C. elegans with particular emphasis on events relating to the determination of embryonic cell fates. Extensive coverage of the various contributions that the study of Caenorhabditis has made to our knowledge of developmental biology can be found in ref. 2.
[
2000]
There is growing interest in the use of bioindicators to assess metal toxicity in soil. The current ASTM Standard Guide for Conducting Laboratory Soil Toxicity Test with the lumbricid earthworm Eisenia fetida (E 1676-97) uses a common earthworm. The nematode Caenorhabditis elegans is a natural soil inhabitant with many characteristics that make an ideal alternate test organism. It has been used to assess metal toxicity in aquatic media, agar plates and in soil. Work is currently underway on the design of a C. elegans procedure for metals in soil. The objective of this study was to determine differences in LC50S between the chloride salt and the nitrate salt forms of cadmium, copper, lead, nickel, and zinc, in three types of soil: Cecil, Tifton, and ASTM artificial soil. Results indicated that the toxicological effect of the metallic salt varies and is dependent on the particular metal. For Cd and Pb the nitrate form is more toxic while Cu and Ni are more toxic in the chloride form. The composition of the soil also effected toxicity, with the metal being the least toxic in ASTM soil and more toxic in the Tifton soil. This strongly correlated with organic matter and clay content of the soil. It is important to determine the effects of carrier salt form and soil composition on metal toxicity, not only in order to standardize the protocol for C. elegans soil toxicity testing, but also in establishing acceptable exposure concentrations in the soil.