Filtration artefacts in bacterial community composition can affect the outcome of dissolved organic matter biolability assays

<p>Inland waters are large contributors to global carbon dioxide (<span class="inline-formula">CO<sub>2</sub></span>) emissions, in part due to the vulnerability of dissolved organic matter (DOM) to microbial decomposition and respiration to <span class=&qu...

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Bibliographic Details
Main Authors: J. F. Dean, J. R. van Hal, A. J. Dolman, R. Aerts, J. T. Weedon
Format: Article
Language:English
Published: Copernicus Publications 2018-11-01
Series:Biogeosciences
Online Access:https://www.biogeosciences.net/15/7141/2018/bg-15-7141-2018.pdf
Description
Summary:<p>Inland waters are large contributors to global carbon dioxide (<span class="inline-formula">CO<sub>2</sub></span>) emissions, in part due to the vulnerability of dissolved organic matter (DOM) to microbial decomposition and respiration to <span class="inline-formula">CO<sub>2</sub></span> during transport through aquatic systems. To assess the degree of this vulnerability, aquatic DOM is often incubated in standardized biolability assays. These assays isolate the dissolved fraction of aquatic OM by size filtration prior to incubation. We test whether this size selection has an impact on the bacterial community composition and the consequent dynamics of DOM degradation using three different filtration strategies: 0.2&thinsp;<span class="inline-formula">µ</span>m (filtered and inoculated), 0.7&thinsp;<span class="inline-formula">µ</span>m (generally the most common DOM filter size) and 106&thinsp;<span class="inline-formula">µ</span>m (unfiltered). We found that bacterial community composition, based on 16S rRNA amplicon sequencing, was significantly affected by the different filter sizes. At the same time, the filtration strategy also affected the DOM degradation dynamics, including the <span class="inline-formula"><i>δ</i><sup>13</sup>C</span> signature. However, the dynamics of these two responses were decoupled, suggesting that filtration primarily influences biolability assays through bacterial abundance and the presence of their associated predators. By the end of the 41-day incubations all treatments tended to converge on a common total DOM biolability level, with the 0.7&thinsp;<span class="inline-formula">µ</span>m filtered incubations reaching this point the quickest. These results suggest that assays used to assess the total biolability of aquatic DOM should last long enough to remove filtration artefacts in the microbial population. Filtration strategy should also be taken into account when comparing results across biolability assays.</p>
ISSN:1726-4170
1726-4189