PA11D-06:
From Sewers to Salix and Tailpipes to Typha: Riparian Plants Reflect Anthropogenic Nitrogen Sources Across Montane to Urban Gradients
Monday, 15 December 2014: 9:30 AM
Steven J Hall1, Rebecca L Hale1, Michelle A Baker2, David R Bowling3 and James R Ehleringer4, (1)University of Utah, Salt Lake City, UT, United States, (2)Utah State Univ, Logan, UT, United States, (3)University of Utah, Biology, Salt Lake City, UT, United States, (4)Univ Utah, Salt Lake City, UT, United States
Abstract:
Urban and suburban streams typically receive anthropogenic nitrogen (N) from multiple sources, and their identification and partitioning is a prerequisite for effective water quality management. However, stream N fluxes and sources are often highly variable, limiting the utility of water samples for source identification. Nitrate in perennial streams can provide an important N source for riparian vegetation in semi-arid environments. Thus, riparian plant tissue may integrate the stable isotope composition (δ
15N) of stream nitrate over longer timescales and assist in source identification. Here, we tested whether δ
15N of riparian plant leaves could provide an effective indicator of spatial variation in N sources across land use gradients spanning wildland to urban ecosystems in Salt Lake City, Utah, and the surrounding Wasatch Range Megapolitan Area. We found that leaf δ
15N varied systematically within and among eight streams and rivers (n = 378 leaf samples) consistent with spatial land use variations. Plants from a suburban stream adjacent to homes with septic systems (δ
15N = 5.1‰) were highly enriched relative to similar species from an adjacent undeveloped stream (δ
15N = -0.7 ‰), suggesting an important contribution of enriched human fecal N to the suburban stream. Plants from a montane stream in a largely undeveloped recreational canyon that permitted off-leash dogs (δ
15N = 1.8 ‰) were enriched relative to an adjacent canyon with similar land use that strictly prohibited dogs but had comparable vehicle traffic (δ
15N = -0.7 ‰), suggesting the contribution of dog waste to stream N. Plants from urban stream reaches were enriched by 1.3 – 2.8 ‰ relative to upstream wildland reaches, and δ
15N increased by 0.2 ‰ per km in the urban streams. Mechanisms leading to this urban enrichment could include leaky municipal sewers, atmospheric N deposition, and/or increased rates of N cycling and gaseous losses. Overall, our results demonstrate the potential utility of riparian plant N isotopes as a simple diagnostic of N source inputs to inform watershed management.