Switchgrass ecotypes alter microbial contribution to deep-soil C

Authors

Damaris Roosendaal, USDA, Agricultural Research Service
Catherine E. Stewart, USDA-ARSFollow
Karolien Denef, Colorado State University - Fort Collins
Ronald F. Follett, Retired
Elizabeth Pruessner, USDA, Agricultural Research Service
Louise H. Comas, USDA, Agricultural Research Service
Gary E. Varvel, University of Nebraska-LincolnFollow
Aaron Saathoff, LI-COR Biosciences
Nathan Palmer, University of Nebraska–LincolnFollow
Gautam Sarath, USDA, Agricultural Research Service, University of Nebraska-LincolnFollow
Virginia L. Jin, USDA, Agricultural Research Service, University of Nebraska-LincolnFollow
Marty Schmer, USDA, Agricultural Research Service, University of Nebraska-LincolnFollow
Madhavan Soundararajan, University of Nebraska - LincolnFollow

Document Type

Article

Date of this Version

2016

Citation

SOIL, 2, 185–197, 2016

Comments

© Author(s) 2016.

Open access

doi:10.5194/soil-2-185-2016

Abstract

Switchgrass (Panicum virgatum L.) is a C₄, perennial grass that is being developed as a bioenergy crop for the United States. While aboveground biomass production is well documented for switchgrass ecotypes (lowland, upland), little is known about the impact of plant belowground productivity on microbial communities down deep in the soil profiles. Microbial dynamics in deeper soils are likely to exert considerable control on ecosystem services, including C and nutrient cycles, due to their involvement in such processes as soil formation and ecosystem biogeochemistry. Differences in root biomass and rooting characteristics of switchgrass ecotypes could lead to distinct differences in belowground microbial biomass and microbial community composition. We quantified root abundance and root architecture and the associated microbial abundance, composition, and rhizodeposit C uptake for two switchgrass ecotypes using stable-isotope probing of microbial phospholipid fatty acids (PLFAs) after ¹³CO₂ pulse–chase labeling. Kanlow, a lowland ecotype with thicker roots, had greater plant biomass above- and belowground (gm^-2), greater root mass density (mg cm^-3), and lower specific root length (mg^-1) compared to Summer, an upland ecotype with finer root architecture. The relative abundance of bacterial biomarkers dominated microbial PLFA profiles for soils under both Kanlow and Summer (55.4 and 53.5%, respectively; P = 0.0367), with differences attributable to a greater relative abundance of Gram-negative bacteria in soils under Kanlow (18.1%) compared to soils under Summer (16.3%; P = 0.0455). The two ecotypes also had distinctly different microbial communities process rhizodeposit C: greater relative atom% ¹³C excess in Gram-negative bacteria (44.1±2.3 %) under the thicker roots of Kanlow and greater relative atom% ¹³C excess in saprotrophic fungi under the thinner roots of Summer (48.5±2.2 %). For bioenergy production systems, variation between switchgrass ecotypes could alter microbial communities and impact C sequestration and storage as well as potentially other belowground processes.