Abstract

Forest to pasture land use change following deforestation in Southern Amazonia can result in changes to stream water quality. However, some pasture streams have riparian forest buffers, while others are dammed for farm ponds. Stream corridor management can have differential effects on hydrology and dissolved organic matter (DOM) characteristics. We examined rainfall-runoff patterns and DOM characteristics in a pasture catchment with a forested riparian buffer, and an adjacent catchment with an impoundment. Total streamflow was 1.5 times higher with the riparian buffer, whereas stormflow represented 20% of total discharge for the dammed stream versus 13% with buffer. Stream corridor management was also the primary factor related to DOM characteristics. In the impounded catchment, DOM was found to be less structurally complex, with lower molecular weight compounds, a lesser degree of humification, and a larger proportion of protein-like DOM. In the catchment with a forested buffer, DOM was dominated by humic-like components, with fluorescence characteristics indicative of DOM derived from humified soil organic matter under native vegetation. Our results suggest that differences in stream corridor management can have important implications for carbon cycling in headwater pasture catchments, and that such changes may have the potential to influence water quality downstream in the Amazon basin.

Highlights

  • The Amazon basin plays a significant role in the global carbon (C) cycle [1]

  • We found that the concentration of dissolved organic carbon (DOC) and dissolved organic matter (DOM) characterization in the dammed stream and the stream with a riparian buffer were significantly influenced by stream corridor land cover

  • Statistical analyses showed that differences in land cover and related differences in hydrologic processes were responsible for variations in DOC concentrations and optical properties of DOM

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Summary

Introduction

The Amazon basin plays a significant role in the global carbon (C) cycle [1]. The basin contains a variety of landscapes spanning from pristine forest to regions impacted by deforestation and fires resulting from agricultural expansion [2]. 1990 and 2015 accounted for 41% of global forest loss during those years (53 out of 129 Mha) [4,5]. The predominant land cover following deforestation has been pasture for livestock, with more recent conversions directly to cropland or from pasture to cropland [7,8]. These changes in land use have had a number of consequences on freshwater ecosystems, especially with respect to hydrology and biogeochemistry of small streams [9,10,11]

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