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首页> 外文期刊>Journal of soils & sediments >Impact of the nature of organic matter and/or its organo-mineral interaction on microbial activity in dam sediment
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Impact of the nature of organic matter and/or its organo-mineral interaction on microbial activity in dam sediment

机译:有机质和/或其有机矿物相互作用对坝沉积物微生物活性的影响

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Purpose Two models serve to explain organic matter (OM) bioavailability in soil through the nature of the OM and/or its degree of attachment to the organo-mineral matrix. This work directly measures the extracted aerobic biomineralization of OM pools in order to determine the model more heavily affecting bioavailability in dam sediment. Materials and methods The OM from four dam sediments was extracted according to a physicochemical sequential protocol. For each step, an extracted phase and a residual phase were recovered. These extraction steps were then coupled with biochemical oxygen demand (BOD) measurements over a 20-day period. The BOD is measured as follows: (i) on the total sediment; (ii) on the residual phase, thus allowing for a BOD determination of the OM linked to the matrix (OML); and (iii) on the extracted free OM (OMF). Results and discussion The total sediment BOD cannot be correlated with either the total extracted carbon or global C/N ratio. The BOD of each OM(L)has been assessed, revealing that the labile phase achieves the highest rate of aerobic biodegradability (2.3 mgO(2)/mgC), while contributing a small portion to total sediment biodegradability (6 to 22%). The other phases contributing to sediment biodegradability are particulate phase (labile) weakly linked phase strongly linked phases, with a corresponding contribution to BOD of 15-46% 22-41% 0-30%. An analysis conducted on the OM(F)shows that the BOD rates of the strongly linked phases are equivalent to those of the labile phases. Conclusion Organic matter bioavailability and, hence, its biodegradability are mainly affected by the strength of interaction with the organo-mineral matrix. The C/N ratio subsequently alters the biodegradability of bioaccessible OM from dam sediment.
机译:目的,两种模型用于通过OM和/或其附着程度的有机矿物基质解释土壤中的有机物(OM)生物利用度。这项工作直接测量OM池的提取的有氧生物矿化,以确定模型在坝沉积物中更严重影响生物利用度。材料和方法根据物理化学顺序方案提取来自四个坝沉积物的OM。对于每个步骤,回收提取的相和残余相。然后将这些提取步骤与20天的生物化学需氧量(BOD)进行偶联。该BOD如下测量:(i)总沉积物; (ii)在残留阶段,从而允许BOD确定与基质(OM1)连接的OM; (iii)在提取的自由OM(OMF)上。结果和讨论不能与总提取的碳或全局C / N比的总沉积物BOD相关。已经评估了每个OM(L)的BOD,揭示了不稳定的阶段实现了有氧生物降解性的最高速率(2.3 MgO(2)/ MgC),同时有助于总沉积物生物降解性(6〜22%)。有助于沉积物生物降解性的其他相是颗粒相(不稳定)>弱连接的相>强连接的相,对应的相应贡献为15-46%> 22-41%> 0-30%。在OM(F)上进行的分析表明,强连接阶段的BOD速率与不稳定相的稳定性相同。结论有机物生物利用度,因此,其生物降解性主要受与有机矿物基质相互作用的强度的影响。 C / N比随后改变了来自坝沉积物的生物可接近OM的生物降解性。

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