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Turnover Rates of Intermediate Sulfur Species ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , [Formula: see text]) in Anoxic Freshwater and Sediments

The microbial reduction of sulfate to sulfide coupled to organic matter oxidation followed by the transformation of sulfide back to sulfate drives a dynamic sulfur cycle in a variety of environments. The oxidative part of the sulfur cycle in particular is difficult to constrain because the eight ele...

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Autores principales: Findlay, Alyssa J., Kamyshny, Alexey
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Frontiers Media S.A. 2017
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5743037/
https://www.ncbi.nlm.nih.gov/pubmed/29312234
http://dx.doi.org/10.3389/fmicb.2017.02551
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author Findlay, Alyssa J.
Kamyshny, Alexey
author_facet Findlay, Alyssa J.
Kamyshny, Alexey
author_sort Findlay, Alyssa J.
collection PubMed
description The microbial reduction of sulfate to sulfide coupled to organic matter oxidation followed by the transformation of sulfide back to sulfate drives a dynamic sulfur cycle in a variety of environments. The oxidative part of the sulfur cycle in particular is difficult to constrain because the eight electron oxidation of sulfide to sulfate occurs stepwise via a suite of biological and chemical pathways and produces a wide variety of intermediates ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , and [Formula: see text]), which may in turn be oxidized, reduced or disproportionated. Although the potential processes affecting these intermediates are well-known from microbial culture and geochemical studies, their significance and rates in the environment are not well constrained. In the study presented here, time-course concentration measurements of intermediate sulfur species were made in amended freshwater water column and sediment incubation experiments in order to constrain consumption rates and processes. In sediment incubations, consumption rates were [Formula: see text] [Formula: see text] [Formula: see text] S(4) [Formula: see text] S(2) [Formula: see text] , which is consistent with previous measurements of [Formula: see text] , S(4) [Formula: see text] , and S(2) [Formula: see text] consumption rates in marine sediments. In water column incubations, however, the relative reactivity was [Formula: see text] [Formula: see text] [Formula: see text] S(2) [Formula: see text] S(4) [Formula: see text]. Consumption of thiosulfate, tetrathionate and sulfite was primarily biological, whereas it was not possible to distinguish between abiotic and biological polysulfide consumption in either aqueous or sediment incubations. [Formula: see text] consumption in water column experiments was biologically mediated, however, rapid sedimentary consumption was likely due to reactions with iron minerals. These experiments provide important constraints on the biogeochemical reactivity of intermediate sulfur species and give further insight into the diversity of biological and geochemical processes that comprise (cryptic) environmental sulfur cycling.
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spelling pubmed-57430372018-01-08 Turnover Rates of Intermediate Sulfur Species ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , [Formula: see text]) in Anoxic Freshwater and Sediments Findlay, Alyssa J. Kamyshny, Alexey Front Microbiol Microbiology The microbial reduction of sulfate to sulfide coupled to organic matter oxidation followed by the transformation of sulfide back to sulfate drives a dynamic sulfur cycle in a variety of environments. The oxidative part of the sulfur cycle in particular is difficult to constrain because the eight electron oxidation of sulfide to sulfate occurs stepwise via a suite of biological and chemical pathways and produces a wide variety of intermediates ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , and [Formula: see text]), which may in turn be oxidized, reduced or disproportionated. Although the potential processes affecting these intermediates are well-known from microbial culture and geochemical studies, their significance and rates in the environment are not well constrained. In the study presented here, time-course concentration measurements of intermediate sulfur species were made in amended freshwater water column and sediment incubation experiments in order to constrain consumption rates and processes. In sediment incubations, consumption rates were [Formula: see text] [Formula: see text] [Formula: see text] S(4) [Formula: see text] S(2) [Formula: see text] , which is consistent with previous measurements of [Formula: see text] , S(4) [Formula: see text] , and S(2) [Formula: see text] consumption rates in marine sediments. In water column incubations, however, the relative reactivity was [Formula: see text] [Formula: see text] [Formula: see text] S(2) [Formula: see text] S(4) [Formula: see text]. Consumption of thiosulfate, tetrathionate and sulfite was primarily biological, whereas it was not possible to distinguish between abiotic and biological polysulfide consumption in either aqueous or sediment incubations. [Formula: see text] consumption in water column experiments was biologically mediated, however, rapid sedimentary consumption was likely due to reactions with iron minerals. These experiments provide important constraints on the biogeochemical reactivity of intermediate sulfur species and give further insight into the diversity of biological and geochemical processes that comprise (cryptic) environmental sulfur cycling. Frontiers Media S.A. 2017-12-21 /pmc/articles/PMC5743037/ /pubmed/29312234 http://dx.doi.org/10.3389/fmicb.2017.02551 Text en Copyright © 2017 Findlay and Kamyshny. http://creativecommons.org/licenses/by/4.0/ This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) or licensor are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
spellingShingle Microbiology
Findlay, Alyssa J.
Kamyshny, Alexey
Turnover Rates of Intermediate Sulfur Species ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , [Formula: see text]) in Anoxic Freshwater and Sediments
title Turnover Rates of Intermediate Sulfur Species ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , [Formula: see text]) in Anoxic Freshwater and Sediments
title_full Turnover Rates of Intermediate Sulfur Species ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , [Formula: see text]) in Anoxic Freshwater and Sediments
title_fullStr Turnover Rates of Intermediate Sulfur Species ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , [Formula: see text]) in Anoxic Freshwater and Sediments
title_full_unstemmed Turnover Rates of Intermediate Sulfur Species ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , [Formula: see text]) in Anoxic Freshwater and Sediments
title_short Turnover Rates of Intermediate Sulfur Species ([Formula: see text] , S(0), S(2) [Formula: see text] , S(4) [Formula: see text] , [Formula: see text]) in Anoxic Freshwater and Sediments
title_sort turnover rates of intermediate sulfur species ([formula: see text] , s(0), s(2) [formula: see text] , s(4) [formula: see text] , [formula: see text]) in anoxic freshwater and sediments
topic Microbiology
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5743037/
https://www.ncbi.nlm.nih.gov/pubmed/29312234
http://dx.doi.org/10.3389/fmicb.2017.02551
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