Abstract

River water-quality studies rarely measure dissolved inorganic carbon (DIC) routinely, and there is a gap in our knowledge of the contributions of DIC to aquatic carbon fluxes and cycling processes. Here, we present the THINCARB model (THermodynamic modelling of INorganic CARBon), which uses widely-measured determinands (pH, alkalinity and temperature) to calculate DIC concentrations, speciation (bicarbonate, HCO3−; carbonate, CO32−; and dissolved carbon dioxide, H2CO3⁎) and excess partial pressures of carbon dioxide (EpCO2) in freshwaters. If calcium concentration measurements are available, THINCARB also calculates calcite saturation. THINCARB was applied to the 39-year Harmonised Monitoring Scheme (HMS) dataset, encompassing all the major British rivers discharging to the coastal zone. Model outputs were combined with the HMS dissolved organic carbon (DOC) datasets, and with spatial land use, geology, digital elevation and hydrological datasets. We provide a first national-scale evaluation of: the spatial and temporal variability in DIC concentrations and fluxes in British rivers; the contributions of DIC and DOC to total dissolved carbon (TDC); and the contributions to DIC from HCO3− and CO32− from weathering sources and H2CO3⁎ from microbial respiration. DIC accounted for >50% of TDC concentrations in 87% of the HMS samples. In the seven largest British rivers, DIC accounted for an average of 80% of the TDC flux (ranging from 57% in the upland River Tay, to 91% in the lowland River Thames). DIC fluxes exceeded DOC fluxes, even under high-flow conditions, including in the Rivers Tay and Tweed, draining upland peaty catchments. Given that particulate organic carbon fluxes from UK rivers are consistently lower than DOC fluxes, DIC fluxes are therefore also the major source of total carbon fluxes to the coastal zone. These results demonstrate the importance of accounting for DIC concentrations and fluxes for quantifying carbon transfers from land, via rivers, to the coastal zone.

Highlights

  • River systems provide a vital link in the global carbon (C) cycle, by transferring, storing, and processing organic carbon (OC) and inorganic C (IC) between terrestrial and marine environments

  • The correlation statistics for the relationships between median values of dissolved inorganic carbon (DIC), dissolved OC (DOC), %DIC and EpCO2 for each river sampling site and catchment characteristics are shown in Table 2, and are outlined here, as follows: Catchment area 9948 9895 8231 4587 4390 3430 3315 679 198

  • Despite an overwhelming focus on measuring DOC in rivers, our research shows that DOC represents a minor component of the dissolved carbon fluxes entering the coastal zone from British rivers

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Summary

Introduction

River systems provide a vital link in the global carbon (C) cycle, by transferring, storing, and processing organic carbon (OC) and inorganic C (IC) between terrestrial and marine environments. Dissolved IC (DIC) in river water is composed of three main species: bicarbonate (HCO3−), carbonate (CO32−) and dissolved carbon dioxide (H2CO3⁎). DIC is derived from the combined effects of the weathering of carbonate rocks and soils, together with microbial breakdown of organic matter which releases CO2. The latter provides an additional source of IC to rivers, and influences river-water pH which, in turn, governs the partitioning of DIC between HCO3−, CO32− and H2CO3⁎(Jarvie et al, 1997; Maberly, 1996)

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