13 research outputs found
Adaptabilidade e estabilidade fenotĂpica de cultivares de cafĂ© arĂĄbica em Minas Gerais
Methane-Derived Carbon in the Benthic Food Web in Stream Impoundments
<div><p>Methane gas (CH<sub>4</sub>) has been identified as an important alternative source of carbon and energy in some freshwater food webs. CH<sub>4</sub> is oxidized by methane oxidizing bacteria (MOB), and subsequently utilized by chironomid larvae, which may exhibit low ÎŽ<sup>13</sup>C values. This has been shown for chironomid larvae collected from lakes, streams and backwater pools. However, the relationship between CH<sub>4</sub> concentrations and ÎŽ<sup>13</sup>C values of chironomid larvae for in-stream impoundments is unknown. CH<sub>4</sub> concentrations were measured in eleven in-stream impoundments located in the Queich River catchment area, South-western Germany. Furthermore, the ÎŽ<sup>13</sup>C values of two subfamilies of chironomid larvae (i.e. Chironomini and Tanypodinae) were determined and correlated with CH<sub>4</sub> concentrations. Chironomini larvae had lower mean ÎŽ<sup>13</sup>C values (â29.2 to â25.5 â°), than Tanypodinae larvae (â26.9 to â25.3 â°). No significant relationships were established between CH<sub>4</sub> concentrations and ÎŽ<sup>13</sup>C values of chironomids (p>0.05). Mean ÎŽ<sup>13</sup>C values of chironomid larvae (mean: â26.8â°, range: â29.2â° to â25.3â°) were similar to those of sedimentary organic matter (SOM) (mean: â28.4â°, range: â29.3â° to â27.1â°) and tree leaf litter (mean: â29.8 â°, range: â30.5â° to â29.1â°). We suggest that CH<sub>4</sub> concentration has limited influence on the benthic food web in stream impoundments.</p></div
Locations of the study impoundments in the Queich River catchment area.
<p>Locations of the study impoundments in the Queich River catchment area.</p
Relationships between pore-water CH<sub>4</sub> concentrations and ÎŽ<sup>13</sup>C values.
<p>TNP 4<sup>th</sup>, CMI 3<sup>rd</sup>, CMI 4<sup>th</sup> and SOM stands for Tanypodinae fourth generation, Chironomini third and fourth generation, and sedimentary organic matter, respectively.</p
Average CH<sub>4</sub> concentrations (”mol L<sup>â1</sup>) and bulk sediment characteristics (TOC, C:N ratio, porosity and ÎŽ<sup>13</sup>C) of samples from the studied impoundments (in parentheses are standard errors, ±SE (when applicable).
<p>Average CH<sub>4</sub> concentrations (”mol L<sup>â1</sup>) and bulk sediment characteristics (TOC, C:N ratio, porosity and ÎŽ<sup>13</sup>C) of samples from the studied impoundments (in parentheses are standard errors, ±SE (when applicable).</p
Correlations (<i>rho</i>-values) between ÎŽ<sup>13</sup>C values, C:N ratio of bulk sediment, water residence time (min) and CH<sub>4</sub> concentrations (<sup>*</sup><i>p</i><0.05).
<p>ÎŽ<sup>13</sup>C<sub>SOM</sub>, ÎŽ<sup>13</sup>C of bulk sediment; CMI 4<sup>th</sup>, fourth instar Chironomini; CMI 3<sup>rd</sup>, third instar Chironomini; TNP 4<sup>th</sup>, fourth instar Tanypodinae.</p><p>Correlations (<i>rho</i>-values) between ÎŽ<sup>13</sup>C values, C:N ratio of bulk sediment, water residence time (min) and CH<sub>4</sub> concentrations (<sup>*</sup><i>p</i><0.05).</p