Abstract

Dissolved organic matter (DOM), particularly dissolved organic nitrogen (DON), is an important source of energy and/or organic nutrients for heterotrophic microorganisms in rivers. Although various factors controlling the quantity and quality of stream and riverine DOM have been extensively studied, DON has been under-researched compared to dissolved organic carbon (DOC). The spatial distribution of DOC and DON concentrations with respect to the C/N ratio and DOM optical properties was investigated in the Ishikari River and its tributaries in Hokkaido, northern Japan. Here, the upper reaches are forested and the middle and lower reaches are encompassed by agricultural land, in particular paddy fields. Furthermore, dark incubation experiments were conducted using filtered riverine water (<0.7 µm) to determine the bioavailability of DOC and DON (particularly due to small microorganisms) considered as a factor controlling the spatial distribution. In the mainstream, DOC and DON concentrations increased with river flow in the upper and middle reaches and remained unchanged in the lower reaches. The C/N ratio of bulk DOM decreased continuously from the upper reaches to lower reaches. The optical properties exhibited changes in the DOM characteristics in terms of higher molecular weight and higher aromaticity from the upper to middle reaches, suggesting that flooded paddy fields largely altered the riverine DOM concentration and composition. In the lower reaches, the C/N ratio of the bulk DOM decreased with the river flow. However, according to principal component analysis, no changes were observed in the optical properties with river flow, suggesting that the C/N ratio of bulk DOM changed owing to in situ biological activity in the river. DOC biodegradation was observed at four sites in the upper and middle reaches but not at the two sites in the lower reaches. However, the DON concentration during the dark incubation experiments at all sites did not differ significantly, which implies that microbial degradation, particularly by small microorganisms, is a factor that decreased the C/N ratio of bulk DOM in the upper and middle reaches. In contrast, large microorganisms possibly degraded C-rich DOM to decrease the C/N ratio of bulk DOM in the lower reaches of the Ishikari River.

Highlights

  • Dissolved organic matter (DOM) in rivers is an essential component of biogeochemical cycles (Findlay and Sinsabaugh, 2003), and three major sources of DOM in rivers include 1) soils, 2) riparian zones, and 3) biological production in situ in rivers (Bertilsson and Jones, 2003; Willett et al, 2004; Yamashita et al, 2010; Bianchi, 2011; Yamashita et al, 2011; Drake et al, 2018)

  • The possible factors contributing to the different degradations of dissolved organic carbon (DOC) and dissolved organic nitrogen (DON) are discussed in the following subsection. Both DOC and DON did not decompose during the 40 days of dark incubation in samples obtained from the lower reaches (Figure 5). These results suggest that the decrease in the C/N ratio of DOM with river flow in the lower reaches might be the result of biodegradation of C-rich DOM by large microorganisms (>0.7 μm) that were not present in the bioassay of the study

  • This study investigated the spatial distribution of DOC and DON concentrations and the C/N ratio with DOM optical properties in the Ishikari River Basin, and dark incubation experiments were conducted to determine the bioavailability of DOC and DON as a factor controlling their spatial distribution

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Summary

Introduction

Dissolved organic matter (DOM) in rivers is an essential component of biogeochemical cycles (Findlay and Sinsabaugh, 2003), and three major sources of DOM in rivers include 1) soils, 2) riparian zones, and 3) biological production in situ in rivers (Bertilsson and Jones, 2003; Willett et al, 2004; Yamashita et al, 2010; Bianchi, 2011; Yamashita et al, 2011; Drake et al, 2018). DOM is the source of energy and carbon in riverine ecosystems, for heterotrophic microorganisms (Wetzel, 1992; Battin et al, 2016), and its bioavailability depends on its composition and structure (Amon and Benner, 1996; Amon et al, 2001). The ratio of dissolved organic carbon (DOC) to DON (i.e., the C/N ratio of DOM) of bio-labile DOM is generally lower than that of bio-refractory DOM in marine environments (Hopkinson and Valino, 2005; Lønborg and Álvarez-Salgado, 2012), implying that nitrogen-containing DOM is relatively consumed by heterotrophic microbes in the ocean. The contribution of protein-like fluorophores to total fluorophores has been related to the bioavailability of bulk DOM (Balcarczyk et al, 2009; Fellman et al, 2009; Petrone et al, 2011), implying that at least fractions of the DON, such as peptides and proteins, are actively involved in the metabolism of lower trophic levels in riverine ecosystems

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