Abstract

Headwater streams are in close contact with the landscape and known to mediate disturbances to downstream waterways through important ecological interactions. We studied how elevated chloride from road deicer, a pollutant of rising concern in urban ecosystems, influenced the leaf-microbial matrix in streams, and subsequent processing of C and N. In a multi-factorial laboratory experiment, we determined if elevated chloride interacts with nitrogen loading and invertebrate consumer feeding to alter rates of leaf litter breakdown and N immobilization. Naturally colonized leaf litter, the dominant C source in small streams, was collected from five Piedmont streams (Maryland, USA) and subjected to a gradient of NaCl (0, 1,000, 5,000 mg Cl l−1) and dissolved nitrogen (ambient, elevated), and an invertebrate treatment (presence, absence) in a total of 60 microcosms. Loss rate and C:N content were determined from remaining leaf litter after 16 d of incubation. Chloride loading significantly (P < 0.05) reduced loss rate regardless of N loading, and C:N content significantly (P < 0.05) increased with Cl concentration, interacting marginally (P < 0.10) with N loading. Invertebrate feeding had a marginally-significant (P < 0.10), negative effect on loss rate, but not C:N content. Overall, elevated chloride significantly influenced organic matter loss rate and N immobilization, despite N loading and the presence of invertebrates. We conclude that there is the potential for chloride loading as road deicer runoff to negatively influence microbial processing of C and N by stream-dwelling microbial communities.

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