TY - JOUR
T1 - Hydrologic history influences microbial community composition and nitrogen cycling under experimental drying/wetting treatments
AU - Peralta, Ariane L.
AU - Ludmer, Sarah
AU - Kent, Angela D.
N1 - Funding Information:
We would like to thank B. Stikkers and R. Weitekamp at the Champaign County Soil and Water District for logistical support in the field and maintenance of the St. Joseph Wetland. J. Matthews provided expertise in surveying wetland plant communities and identifying upland and wetland sites for this study. We extend our thanks to B. Wills and L. Endriukaitis for help in the field and M. Rout, D. Keymer, D. Li., Y. Lou, D. Lin, M. Porter, C. Smith, C. Mitchell, and M. David for laboratory assistance. J. Matthews, Y. Cao, J. Dalling, M. Wander, S. Paver, and two anonymous reviewers provided helpful comments on this manuscript. This work was supported by the Cooperative State Research, Education and Extension Service and the U.S. Department of Agriculture , under project number ILLU 875-374. This research was also supported, in part, by the Program in Ecology, Evolution, and Conservation Biology at the University of Illinois at Urbana-Champaign and the Illinois Water Resources Center .
PY - 2013/11
Y1 - 2013/11
N2 - Understanding how historical and contemporary environmental conditions interact to affect the relationship between community structure and function is necessary to predict the response of microbial community function to a changing environment. We focused on nitrogen transformations - denitrification and nitrification - which directly impact nitrate concentration in wetland ecosystems. Nitrate removal can occur via denitrification, while nitrate can be generated through nitrification; these two microbial transformations are strongly influenced by hydrology and redox conditions. We carried out a manipulative mesocosm experiment to determine how microbial communities adapted to different hydrologic conditions (upland vs. wetland) respond to experimental soil moisture treatments (dry, wet-dry, saturated). We assessed local soil characteristics (e.g., soil moisture, inorganic nitrogen), and microbial community composition and activity of denitrifiers and ammonia oxidizers (targeted by the nosZ and amoA genes, respectively) before and after moisture treatments. Wetland soils were characterized by higher soil fertility compared to upland soils. In response to the drying/flooding treatments, we observed a small but significant change in community composition of denitrifier assemblages, but no change in the ammonia oxidizer communities. In addition, potential denitrification rates significantly increased under wetter conditions (upland: 62-118% increase; wetland: 78-96% increase), whereas potential nitrification rates generally showed no significant change following experimental drying/flooding treatments, regardless of the hydrologic history. Based on these results, fluctuations in soil moisture are expected to influence denitrification rates to a greater extent than nitrification rates, ultimately influencing nitrate pools in this wetland. This imbalance in microbial functional response may result in a shift in dominant nitrogen cycling transformations within a wetland as a consequence of the different responses of these nitrogen-cycling functional guilds to changes in soil moisture. A shift in nitrogen transformations can be most noticeable under fluctuating hydrologic conditions, and there is potential for the wetland to be resilient to hydrologic change if soil microbes are exposed to dynamic hydrology over the long-term.
AB - Understanding how historical and contemporary environmental conditions interact to affect the relationship between community structure and function is necessary to predict the response of microbial community function to a changing environment. We focused on nitrogen transformations - denitrification and nitrification - which directly impact nitrate concentration in wetland ecosystems. Nitrate removal can occur via denitrification, while nitrate can be generated through nitrification; these two microbial transformations are strongly influenced by hydrology and redox conditions. We carried out a manipulative mesocosm experiment to determine how microbial communities adapted to different hydrologic conditions (upland vs. wetland) respond to experimental soil moisture treatments (dry, wet-dry, saturated). We assessed local soil characteristics (e.g., soil moisture, inorganic nitrogen), and microbial community composition and activity of denitrifiers and ammonia oxidizers (targeted by the nosZ and amoA genes, respectively) before and after moisture treatments. Wetland soils were characterized by higher soil fertility compared to upland soils. In response to the drying/flooding treatments, we observed a small but significant change in community composition of denitrifier assemblages, but no change in the ammonia oxidizer communities. In addition, potential denitrification rates significantly increased under wetter conditions (upland: 62-118% increase; wetland: 78-96% increase), whereas potential nitrification rates generally showed no significant change following experimental drying/flooding treatments, regardless of the hydrologic history. Based on these results, fluctuations in soil moisture are expected to influence denitrification rates to a greater extent than nitrification rates, ultimately influencing nitrate pools in this wetland. This imbalance in microbial functional response may result in a shift in dominant nitrogen cycling transformations within a wetland as a consequence of the different responses of these nitrogen-cycling functional guilds to changes in soil moisture. A shift in nitrogen transformations can be most noticeable under fluctuating hydrologic conditions, and there is potential for the wetland to be resilient to hydrologic change if soil microbes are exposed to dynamic hydrology over the long-term.
KW - Denitrification
KW - Land use legacy effects
KW - Nitrification
KW - Restored wetlands
KW - Soil microorganisms
KW - Structure-function relationship
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U2 - 10.1016/j.soilbio.2013.06.019
DO - 10.1016/j.soilbio.2013.06.019
M3 - Article
AN - SCOPUS:84880766286
SN - 0038-0717
VL - 66
SP - 29
EP - 37
JO - Soil Biology and Biochemistry
JF - Soil Biology and Biochemistry
ER -