Journal
BIOGEOCHEMISTRY
Volume 119, Issue 1-3, Pages 275-292Publisher
SPRINGER
DOI: 10.1007/s10533-014-9965-2
Keywords
DIC; DOM; POM; Delta C-14; delta C-13; Excitation emission matrix-parallel factor analysis; Stream; Land use; Watershed
Funding
- Mellon Foundation Postdoctoral Fellow Grant from The College of William and Mary
- National Science Foundation [DEB0234533, OCE0327423, EAR0403949, OCE0962277, EAR1003529, DEB 0542645]
- Florida Coastal Everglades Long-Term Ecological Research program under National Science Foundation [DBI0620409]
- Marine Environmental Sciences Consortium Funds [T3-013-UA, T3-020-UA, T4-004-UA]
- Directorate For Geosciences
- Division Of Ocean Sciences [0962277, 0961860] Funding Source: National Science Foundation
- Division Of Environmental Biology
- Direct For Biological Sciences [1237517] Funding Source: National Science Foundation
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The amounts, sources and relative ages of inorganic and organic carbon pools were assessed in eight headwater streams draining watersheds dominated by either forest, pasture, cropland or urban development in the lower Chesapeake Bay region (Virginia, USA). Streams were sampled at baseflow conditions six different times over 1 year. The sources and ages of the carbon pools were characterized by isotopic (delta C-13 and a dagger C-14) analyses and excitation emission matrix fluorescence with parallel factor analysis (EEM-PARAFAC). The findings from this study showed that human land use may alter aquatic carbon cycling in three primary ways. First, human land use affects the sources and ages of DIC by controlling different rates of weathering and erosion. Relative to dissolved inorganic carbon (DIC) in forested streams which originated primarily from respiration of young, C-14-enriched organic matter (OM; delta C-13 = -22.2 +/- A 3 aEuro degrees; a dagger C-14 = 69 +/- A 14 aEuro degrees), DIC in urbanized streams was influenced more by sedimentary carbonate weathering (delta C-13 = -12.4 +/- A 1 aEuro degrees; a dagger C-14 = -270 +/- A 37 aEuro degrees) and one of pasture streams showed a greater influence from young soil carbonates (delta C-13 = -5.7 +/- A 2.5 aEuro degrees; a dagger C-14 = 69 aEuro degrees). Second, human land use alters the proportions of terrestrial versus autochthonous/microbial sources of stream water OM. Fluorescence properties of dissolved OM (DOM) and the C:N of particulate OM (POM) suggested that streams draining human-altered watersheds contained greater relative contributions of DOM and POM from autochthonous/microbial sources than forested streams. Third, human land uses can mobilize geologically aged inorganic carbon and enable its participation in contemporary carbon cycling. Aged DOM (a dagger C-14 = -248 to -202 aEuro degrees, equivalent(14)C ages of 1,811-2,284 years BP) and POM (a dagger C-14 = -90 to -88 aEuro degrees, C-14 ages of 669-887 years BP) were observed exclusively in urbanized streams, presumably a result of autotrophic fixation of aged DIC (-297 to -244 aEuro degrees, C-14 age = 2,251-2,833 years BP) from sedimentary shell dissolution and perhaps also watershed export of fossil fuel carbon. This study demonstrates that human land use may have significant impacts on the amounts, sources, ages and cycling of carbon in headwater streams and their associated watersheds.
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