Johnson TE et al. (1987) "Aging in C. elegans: Update 1986."

Foltz NL, Johnson TE

[1987]

Since the last review in this series [Johnson, 1985], many papers have appeared dealing directly with the aging process in both Caenorhabditis elegans and Turbatrix aceti. We will review this work and also briefly review other areas of C. elegans research that may impact on the study of aging. C. elegans has become a major biological model; four "News" articles in Science [Lewin, 1984a,b; Marx, 1984a,b] and inclusion as one of three developmental genetics models in a recent text [Wilkins, 1986] indicate its importance. Recent work has verified earlier results and has advanced progress toward new goals, such as routine molecular cloning. The aging studies reviewed here, together with new findings from other areas of C. elegans research, lay the groundwork for rapid advances in our understanding of aging in nematodes. Several areas of research in C. elegans have been reviewed recently: the genetic approach to understanding the cell lineage [Sternberg and Horvitz, 1984] and a brief summary of cell lineage mutants [Hedgecock, 1985]. The specification of neuronal development and neural connectivity has been a continuing theme in C. elegans research and reviews of these areas have also appeared [Chalfie, 1984; White, 1985]. A major genetic advance is the development of reliable, if not routine, mosaic analysis [Herman, 1984; Herman and Kari, 1985], which is useful for the genetic analysis of tissue-limited gene expression. Hodgkin [1985] reviews studies on a series of mutants involved in the specification of sex. These include her mutations that cause XO worms (normally males) to develop as hermaphrodites and tra mutations that change XX hermaphrodites into phenotypic males. The work on the structure and development of nematode muscle has been summarized by Waterston and Francis [1985]. A comprehensive review of aging research, containing useful reference material on potential biomarkers, has appeared [Johnson and Simpson, 1985], as well as a review including

Fredens J et al. (2014) Methods Mol Biol "Identification of novel protein functions and signaling mechanisms by genetics and quantitative phosphoproteomics in Caenorhabditis elegans."

Larsen MR, Moller-Jensen J, Fredens J, Engholm-Keller K, Faergeman NJ

[Methods Mol Biol, 2014]

Stable isotope labeling by amino acids combined with mass spectrometry is a widely used methodology for measuring relative changes in protein and phosphorylation levels at a global level. We have applied this method to the model organism Caenorhabditis elegans in combination with RNAi-mediated gene knockdown by feeding the nematode on pre-labeled lysine auxotroph Escherichia coli. In this chapter, we describe in details the generation of the E. coli strain, incorporation of heavy isotope-labeled lysine in C. elegans, and the procedure for a comprehensive global phosphoproteomic experiment.

Peredney CL et al. (2000) "Comparison of the toxicological effects of nitrate versus chloride metallic salts on Caenorhabditis elegans in soil."

Williams PL, Peredney CL

[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.