Validamycin is a biological fungicide used in the agriculture sector. It can control sheath blight caused by Rhizoctonia solani in rice, potatoes, vegetables, as well as damping off diseases in vegetable seedlings, cotton, sugar beets and other plants on a large scale (NIOSH, 1993). It is absorbed by cells of Rhizoctonia solani and hydrolyzed to a potent inhibitor of trehalase-validoxylamine A. Validamycin has been considered as a low-toxicity material that can be degraded easily by some bacterium, such as Flavobacterium saccharophilum, Pseudomonas sp. HZ519 and Stenotrophomonas maltrophilia CCTCC M 204024 under lab conditions (Asano et al., 1984; Zheng et al., 2005; zhang et al., 2005). To the best of our knowledge, few studies have focused on the effects of validamycin formulation on the agro-ecosystem. Crystal proteins of Bacillus thuringiensis (Bt) also serve as a biological pesticide, also regarded as non-toxic several decades ago. However, following the emergence of Bt-transgenic plants, some reports showed that Bt toxins could accumulate in the soil, resulting in potential risks to soil biological processes including microorganism biomass and soil enzyme activity (Castaldini et al., 2005; Donegan et al., 1995; Wang et al., 2005; Wu et al., 2004a, b). In essence, a biological pesticide is a chemical substance with a definite molecular weight, and can also cause environmental disturbance, just like chemical pesticides (Shen, 1997). Bearing in mind these concerns, it is necessary to assess the effects of validamycin formulation on agro-ecosystem and the corresponding risks. The widespread and nonjudicious agricultural use of pesticides results in their entry into the soil and water ecosystems. Soil is the most diverse terrestrial habitat, and soil microbial communities play important roles in decomposition, nutrient cycling, and energy flow (Waldrop and Firestone, 2006; Wardle and Giller, 1997). Much work has been directed towards understanding the complexity of pesticide–microbial interactions in soil, indicating that in general soil microbial populations are affected by pesticide (Griffiths et al., 2006; Lu et al., 2006). Conventional microbial methods that rely on microbial cultivation can only identify a small fraction (0.01–10%) of the total microbial biomass (Ferguson et al., 1984), because they are unable to culture the majority of microorganisms from soil samples. This was a main obstacle for the better understanding of microbial ecology and diversity. Recently, soil microbiologists have developed several molecular methods to overcome this limitation by allowing particular genes to be monitored directly in the environment. Such methods include the polymerase chain reaction (PCR), and microarray-based genomic technology. Real-time PCR is a method based on the use of fluorescent probes or dyes to quantify the copy number of target DNA in a sample. This technology, which is not limited by the cultivability of soil microorganisms, has been successfully applied in the medical and environmental fields for the quantification of bacteria (Kolb et al., 2003), viruses (Schaade et al., 2000) and fungi (Lees et al., 2002). In this investigation, we developed a real-time PCR assay that can quantify soil bacteria and fungi by using specific primers based on 16S H. Qian (&) D. Cao W. Chen X. Xu Y. Lu College of Biological and Environmental Engineering, Zhejiang University of Technology, Hangzhou, Zhejiang 310032, China e-mail: hfqian@126.com
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