Abstract

Benthic biofilms are often assumed to control terrestrially-derived dissolved organic carbon (tDOC) uptake in streams. We tested this by comparing 13C-enriched ryegrass leachate uptake in an agricultural and a forest stream, hypothesizing that a greater abundance of autotrophic biofilms in the agricultural stream would cause its whole-stream tDOC uptake to be comparatively low. We measured whole-stream and biofilm tDOC tracer uptake, metabolism, bacterial and algal diversity, and nutrient status of benthic epilithic biofilms, and assessed whole-stream hydromorphology. Whole-stream uptake of tDOC was six times lower in the agricultural (3.0 mg m−2 day−1) than in the forest (19.0 mg m−2 day−1) stream, and tDOC uptake velocity indicated lower tDOC demand in the agricultural (1.2 mm min−1) than in the forest (1.9 mm min−1) stream. The agricultural stream differed from the forest stream by slightly lower transient storage capacity and higher benthic biofilm bacterial abundance and production, lower biofilm biomass and lower biofilm molar C:N, C:P, and N:P ratios. Changes in epilithic biofilms contributed little to the differences in whole-stream tDOC tracer uptake between streams, as biofilm tDOC uptake only amounted to 4% and 13% of whole-stream uptake in the forest and agricultural stream, respectively. This comparison of a forest and an agricultural stream suggests that agricultural stressors have the potential to diminish both whole-stream tDOC uptake and uptake efficiency. Furthermore, the weak link between biofilm and whole-stream tDOC uptake implies that benthic biofilms characteristics are poor predictors for human impacts on tDOC uptake in agricultural streams and that hot spots of tDOC uptake are likely situated in the hyporheic zone or in the stream water column.

Highlights

  • The largest part of organic carbon in fluvial ecosystems is usually dissolved organic carbon (DOC) from terrestrial sources (Tank et al 2010)

  • There are three significant implications for our understanding of how human activities impact stream terrestriallyderived DOC (tDOC) dynamics that emerge from this two-stream comparison

  • Benthic epilithic biofilms in both streams played a smaller role in tDOC uptake than predicted from previous studies

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Summary

Introduction

The largest part of organic carbon in fluvial ecosystems is usually dissolved organic carbon (DOC) from terrestrial sources (Tank et al 2010) This terrestriallyderived DOC (tDOC) drives the metabolism of stream ecosystems, and shapes stream microbial food webs (Prairie 2008; Stanley et al 2012). Changes in stream epilithic biofilm characteristics should affect in-stream DOC uptake (Qu et al 2017), with cascading effects on higher trophic levels. This is relevant to land-use change in the riparian zone of streams, which alters the hydrodynamics, light, and nutrient status (Gucker et al 2009; Boechat et al 2011) that define stream biofilm structure (Battin et al 2016)

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