Effects of agricultural land use on the composition of fluvial dissolved organic matter

Nearly 40% of the Earth’s ice-free surface area is cropland or pasture. Measurements of dissolved organic matter along a gradient of agricultural land use suggest that agricultural watersheds contain less complex, more microbially derived dissolved organic matter than natural wetlands. Nearly 40% of the Earth’s ice-free surface area is cropland or pasture1. Agricultural land use can increase the delivery of nutrients such as nitrogen and phosphorus to fluvial ecosystems2, but the impact of farming on riverine dissolved organic carbon is still largely unknown, despite increasing recognition that rivers act as important modifiers in the global carbon cycle3,4. Here, we examine the character of riverine dissolved organic matter in 34 watersheds along a gradient of agricultural land use. We show that changes in the character of dissolved organic matter are related to agricultural land use, nitrogen loading and wetland loss. Specifically, we find that the structural complexity of dissolved organic matter decreases as the ratio of continuous croplands to wetlands increases. At the same time, the amount of microbially derived dissolved organic matter increases with greater agricultural land use. Furthermore, we find that periods of soil dryness are associated with a decrease in the structural complexity of dissolved organic matter. We suggest that these effects of land use and climate on the character of riverine dissolved organic matter have important implications for global carbon cycling, owing to their potential to control rates of microbial carbon processing (for example, uptake, retention and outgassing) in agricultural systems.

[1]  D. McKnight,et al.  Fluorescence spectroscopy reveals ubiquitous presence of oxidized and reduced quinones in dissolved organic matter. , 2005, Environmental science & technology.

[2]  E. O’Loughlin,et al.  Molecular weight, polydispersity, and spectroscopic properties of aquatic humic substances. , 1994, Environmental science & technology.

[3]  Wayne C. Palmer,et al.  Keeping Track of Crop Moisture Conditions, Nationwide: The New Crop Moisture Index , 1968 .

[4]  A. Baker,et al.  Protein‐like fluorescence intensity as a possible tool for determining river water quality , 2004 .

[5]  D. McKnight,et al.  Chemical characterization of DOM in channels of a seasonal wetland , 2007, Aquatic Sciences.

[6]  N. Oh,et al.  Anthropogenically enhanced fluxes of water and carbon from the Mississippi River , 2008, Nature.

[7]  R. Boone,et al.  Fluorescence characteristics and biodegradability of dissolved organic matter in forest and wetland soils from coastal temperate watersheds in southeast Alaska , 2008 .

[8]  M. B. David,et al.  Export of dissolved organic carbon from agricultural streams in Illinois, USA , 2005, Aquatic Sciences.

[9]  C. Jambert,et al.  Characterization of dissolved organic carbon in cleared forest soils converted to maize cultivation , 1997 .

[10]  J. Meyer The microbial loop in flowing waters , 1994, Microbial Ecology.

[11]  B. Avril,et al.  Distribution and optical properties of CDOM in the Arabian Sea during the 1995 Southwest Monsoon , 1998 .

[12]  Aaron I. Packman,et al.  Biophysical controls on organic carbon fluxes in fluvial networks , 2008 .

[13]  Lawrence A. Baker,et al.  Transformations in dissolved organic carbon through constructed wetlands , 2000 .

[14]  T. Filley,et al.  The role of hydrology in annual organic carbon loads and terrestrial organic matter export from a midwestern agricultural watershed , 2007 .

[15]  B. Sulzberger,et al.  Characterizing the properties of dissolved organic matter isolated by XAD and C-18 solid phase extraction and ultrafiltration , 2005, Aquatic Sciences.

[16]  M. Moran,et al.  The role of nitrogen in chromophoric and fluorescent dissolved organic matter formation , 2007 .

[17]  R. Benner,et al.  Bacterial utilization of different size classes of dissolved organic matter , 1996 .

[18]  S. Carpenter,et al.  Global Consequences of Land Use , 2005, Science.

[19]  L. Geoffroy,et al.  Dissolved organic matter fluorescence spectroscopy as a tool to estimate biological activity in a coastal zone submitted to anthropogenic inputs , 2000 .

[20]  G. Hofman,et al.  Characterization of soil organic matter fractions from grassland and cultivated soils via C content and delta13C signature. , 2002, Rapid communications in mass spectrometry : RCM.

[21]  P. Raymond,et al.  Bacterial consumption of DOC during transport through a temperate estuary , 2000 .

[22]  E. Soyeux,et al.  Changes in the character of DOC in streams during storms in two Midwestern watersheds with contrasting land uses , 2008 .

[23]  M. Xenopoulos,et al.  Ecosystem and Seasonal Control of Stream Dissolved Organic Carbon Along a Gradient of Land Use , 2008, Ecosystems.

[24]  Á. Zsolnay,et al.  Differentiating with fluorescence spectroscopy the sources of dissolved organic matter in soils subjected to drying , 1999, Chemosphere.

[25]  M. Pace,et al.  Interactions of Photobleaching and Inorganic Nutrients in Determining Bacterial Growth on Colored Dissolved Organic Carbon , 1998, Microbial Ecology.

[26]  C. Cronan,et al.  Influence of land use and hydrology on exports of carbon and nitrogen in a Maine River Basin , 1999 .

[27]  P. Doran,et al.  Spectrofluorometric characterization of dissolved organic matter for indication of precursor organic material and aromaticity , 2001 .

[28]  E. Matzner,et al.  Biodegradation of soil-derived dissolved organic matter as related to its properties , 2003 .

[29]  S. Carpenter,et al.  NONPOINT POLLUTION OF SURFACE WATERS WITH PHOSPHORUS AND NITROGEN , 1998 .

[30]  J. Downing,et al.  Plumbing the Global Carbon Cycle: Integrating Inland Waters into the Terrestrial Carbon Budget , 2007, Ecosystems.