We are grateful to the Director, Directorate of Weed Science Research (ICAR), Jabalpur, MP, India, for providing the research facilities to complete the PG dissertation work of S.S. “
“Microorganisms are responsible for the decomposition of plant litter due selleck kinase inhibitor to their enhanced enzyme capabilities. Among extracellular enzymes, those involved in lignin decomposition are especially relevant in leaf degradation. However, the knowledge of the bacterial contribution to the decomposition of phenol-derived compounds in submerged leaf litter is

limited. We have used the large unit of the multicomponent bacterial phenol hydroxylase (LmpH) as a genetic proxy to describe changes in the phenol-degrading bacterial community during the decomposition of Platanus acerifolia leaves in a forested stream. Significant differences were found in the phenol-degrading community when three decomposition stages, initial (day 7), midterm (day 58), and late (day 112), were compared. Estimated Shannon’s diversity values decreased significantly from 1.93 (initial) to 0.98 (late). According to the deduced amino acid sequences and

the corresponding theoretical kinetic parameters of phenol hydroxylases, the initial community showed a low degree of specialization, presumably resulting from random colonization of leaves. At the late decomposition stage, the bacterial community became more specialized, and LmpH genes similar to high-affinity phenol hydroxylases of Comamonas sp. and Burkholderia cepacia increased. The observed Sulfite dehydrogenase Metformin clinical trial changes in the bacterial community suggested an active role of bacteria during litter decomposition in aquatic environments. In forested rivers and streams, the input of leaf litter from riparian vegetation represents a fundamental organic matter source for microbial decomposers (Pascoal et al., 2003; Gulis et al., 2008). Fungi and bacteria decompose and mineralize plant material, which then enters the river food web (Hieber & Gessner, 2002). The most

important microbial enzymes for leaf litter decomposition are those that break down plant fibers, such as cellulases, hemicellulases, pectinases, and phenol oxidases (Sinsabaugh et al., 2002). During leaf litter decomposition, different enzymatic activities may arise in function of the available material in the leaf and of the biodegradability and/or recalcitrance of this material. Because lignin is one of the most recalcitrant compounds, its specific degradation might be a relevant limiting step for complete mineralization of plant material. Major enzymes involved in lignin degradation include phenol oxidases, which oxidize phenols at the expense of oxygen. Phenol oxidase activity has been related to an increase in the relative content of lignin and free phenolic compounds (Sinsabaugh, 2010; Artigas et al., 2011).