[
2005]
RNA interference (RNAi) is a recently discovered phenomenon in which doublestranded RNA (dsRNA) silences endogenous gene expression in a sequencespecific manner (Fire et al., 1998). Since its discovery, the use of RNAi has become widely employed in many organisms to specifically knock down gene function. RNAi shares a remarkable degree of similarity with silencing phenomena in other organisms (Cogoni et al., 1999a; Sharp, 1999). For instance, RNAi, posttranscriptional gene silencing in plants and cosuppression in fungi can all be activated by the presence of aberrant RNAs (Maine, 2000; Tijsterman et al., 2002a). Additionally, plant, worm, and fly cells or extracts undergoing RNA-mediated interference all contain small dsRNAs, around 25 nucleotides in length, identical to the sequences present in the silenced gene (Baulcombe, 1996; Hammond et al., 2000; Zamore et al., 2000; Catalanotto et al., 2000). The high degree of similarity between these RNA-mediated silencing phenomena supports the notion that they were derived from an ancient and conserved pathway used to regulate gene expression, presumably to eliminate defective RNAs and to defend against viral infections and transposons. (Zamore, 2002). Components of RNAi have also been implicated in developmental processes, suggesting that RNAi may play a broader role in regulating gene expression (Smardon et al., 2000; Knight et al., 2001; et al., Ketting et al., 2001). Although we have learned much about the general mechanisms underlying RNAi, a detailed understanding of how RNAi works remains to be elucidated. In this chapter we will discuss first the biology of RNAi, then the genes required for its function, and we will end with a discussion on recent findings that have implicated chromatin silencing in the mechanism of RNAi.
[
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.