IDENTIFICATION OF MICROBES RESPONSIBLE FOR ACETATE CONSUMPTION IN SOILS UNDER DIFFERENT WETTING REGIMES


Principal Investigator:

Brian D. Lanoil
Assistant Professor and Assistant Environmental Microbiologist
Department of Environmental Sciences
University of California
Riverside, CA 92521

Duration of Project: 2 years

Project Summary

In order to understand the processes governing the storage of carbon in soils, quantify the impacts of anthropogenic inputs on soil carbon dynamics, and assess the roles of soils in greenhouse gas flux, we need to understand the activities and compositions of microbial communities that underlie many of these processes. For example, we do not know which microbial species are involved in the catabolism of soil acetate, primarily due to our inability to culture 99% or more of environmental organisms. Acetate is central to soil organic matter degradation under anaerobic conditions, which arise in soils under conditions of transient (e.g. irrigation) or permanent (e.g. rice paddies) flooding. Acetate is a product of anaerobic fermentation and homoacetogenesis and serves as a substrate for a variety of anaerobic metabolisms. It is one of the most important substrates for denitrification, metal reduction, sulfate reduction, and methanogenesis in soils. In fact, acetate is the carbon and energy source responsible for as much as 80% of methane flux from soils to the atmosphere. In the proposed project, we will use a recently published method, stable isotope probing (SIP), to link the activity of acetate catabolism with the identity of the organisms performing this process. This method combines stable isotope labeling with 16S rRNA methods to identify the acetate catabolizers. We will evaluate SIP with pure and defined mixed cultures, both in the presence and absence of a soil matrix. Once the method is optimized, we will use the approach to identify the components of the microbial community that are critical for acetate consumption in soil microcosms. We will also evaluate how the microbial communities change with changes in the water content (and therefore O2 content) of the soil.