2021
DOI: 10.5194/bg-18-5231-2021
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Spatial and temporal variability of <i>p</i>CO<sub>2</sub> and CO<sub>2</sub> emissions from the Dong River in south China

Abstract: Abstract. CO2 efflux at the water–air interface is an essential component of the riverine carbon cycle. However, the lack of spatially resolved CO2 emission measurements prohibits reliable estimation of the global riverine CO2 emissions. By deploying floating chambers, seasonal changes in river water CO2 partial pressure (pCO2) and CO2 emissions from the Dong River in south China were investigated. Spatial and temporal patterns of pCO2 were mainly affected by terrestrial carbon inputs (i.e., organic and inorga… Show more

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Cited by 8 publications
(10 citation statements)
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“…Based on the riverine CO 2 partial pressure ( p CO 2 ) and gas transfer velocity ( k ) data we collected in the ERB during five rounds of field campaigns from December 2018 to October 2019, including two (December and October) during the dry season (October–March) and three (April, July, and August) during the wet season (April–September), the total annual riverine CO 2 emissions was computed. Our earlier study in the ERB (B. Liu et al., 2021) showed that the spatial and temporal variability of CO 2 emissions mainly exhibited in three ways: (a) variability in CO 2 emissions among three sub‐basins in the ERB (i.e., the Upper, Middle, and Lower ERB) was driven by changes in their land use covers; (b) spatial variability in CO 2 emissions between large downstream rivers (fourth‐ to seventh‐order streams) and small headwater rivers (first‐ to third‐order streams) was regulated by their differences in hydrological conditions and controls of riverine p CO 2 and (c) temporal variability in CO 2 emissions between the wet and dry seasons was affected by seasonal changes in climate and hydrological conditions. Therefore, in each sub‐basin, we calculated the areal CO 2 emission fluxes from each Strahler stream order according to: FnormalCnormalO2=k×k0×()pnormalCnormalO2normalwnormalanormaltnormalenormalrpnormalCnormalO2normalanormalinormalr ${F}_{\mathrm{C}\mathrm{O}2}=k\times {k}_{0}\times \left({p\mathrm{C}\mathrm{O}}_{2}^{\mathrm{w}\mathrm{a}\mathrm{t}\mathrm{e}\mathrm{r}}-{p\mathrm{C}\mathrm{O}}_{2}^{\mathrm{a}\mathrm{i}\mathrm{r}}\right)$ where, k is the gas transfer velocity (m d −1 ), k 0 is the solubility constants for CO 2 corrected for temperature and pressure (mol L −1 atm −1 ) from Weiss (1974), pnormalCnormalO2normalwnormalanormaltnormalenormalr ${p\mathrm{C}\mathrm{O}}_{2}^{\mathrm{w}\mathrm{a}\mathrm{t}\mathrm{e}\mathrm{r}}$ is the mean riverine p CO 2 for a given stream order within a given sub‐basin, and pnormalCnormalO2normalanormalinormalr ${p\mathrm{C}\mathrm{O}}_{2}^{\mathrm{a}\mathrm{i}\mathrm{r}}$ is average atmospheric p CO 2.…”
Section: Methodsmentioning
confidence: 98%
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“…Based on the riverine CO 2 partial pressure ( p CO 2 ) and gas transfer velocity ( k ) data we collected in the ERB during five rounds of field campaigns from December 2018 to October 2019, including two (December and October) during the dry season (October–March) and three (April, July, and August) during the wet season (April–September), the total annual riverine CO 2 emissions was computed. Our earlier study in the ERB (B. Liu et al., 2021) showed that the spatial and temporal variability of CO 2 emissions mainly exhibited in three ways: (a) variability in CO 2 emissions among three sub‐basins in the ERB (i.e., the Upper, Middle, and Lower ERB) was driven by changes in their land use covers; (b) spatial variability in CO 2 emissions between large downstream rivers (fourth‐ to seventh‐order streams) and small headwater rivers (first‐ to third‐order streams) was regulated by their differences in hydrological conditions and controls of riverine p CO 2 and (c) temporal variability in CO 2 emissions between the wet and dry seasons was affected by seasonal changes in climate and hydrological conditions. Therefore, in each sub‐basin, we calculated the areal CO 2 emission fluxes from each Strahler stream order according to: FnormalCnormalO2=k×k0×()pnormalCnormalO2normalwnormalanormaltnormalenormalrpnormalCnormalO2normalanormalinormalr ${F}_{\mathrm{C}\mathrm{O}2}=k\times {k}_{0}\times \left({p\mathrm{C}\mathrm{O}}_{2}^{\mathrm{w}\mathrm{a}\mathrm{t}\mathrm{e}\mathrm{r}}-{p\mathrm{C}\mathrm{O}}_{2}^{\mathrm{a}\mathrm{i}\mathrm{r}}\right)$ where, k is the gas transfer velocity (m d −1 ), k 0 is the solubility constants for CO 2 corrected for temperature and pressure (mol L −1 atm −1 ) from Weiss (1974), pnormalCnormalO2normalwnormalanormaltnormalenormalr ${p\mathrm{C}\mathrm{O}}_{2}^{\mathrm{w}\mathrm{a}\mathrm{t}\mathrm{e}\mathrm{r}}$ is the mean riverine p CO 2 for a given stream order within a given sub‐basin, and pnormalCnormalO2normalanormalinormalr ${p\mathrm{C}\mathrm{O}}_{2}^{\mathrm{a}\mathrm{i}\mathrm{r}}$ is average atmospheric p CO 2.…”
Section: Methodsmentioning
confidence: 98%
“…Due to the monsoon climate, precipitation is high and with substantial seasonal variability. The multi‐annual average precipitation is about 1,800 mm, of which 80% falls in the wet season from April to September (B. Liu et al., 2021). The multi‐annual average water discharge at the Boluo Hydrological Gauge, the lowermost gauge of the East River mainstem channel, is 2.37 × 10 10 m 3 yr −1, and about 80%–90% of the discharge is transported during the wet season (Y. D. Chen et al., 2011; S. Zhang et al., 2008).…”
Section: Methodsmentioning
confidence: 99%
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