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Biochar Impacts on Soil Silicon Dissolution Kinetics and their Interaction Mechanisms

机译:生物炭对土壤硅溶解动力学的影响及其相互作用机理

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摘要

Effects of biochars on soil silicon dissolution kinetics remain unaddressed. Si-rich rice husk (RH) and rice straw (RS), and Si-deficient wood sawdust (WB) and orange peel (OP) were applied to prepare biochars at 300–700 °C. The silicon dissolution of Si-rich biochars was relatively high in comparison with Si-deficient biochars, and increased with the pyrolysis temperature. The mechanism of silicon release is suggested to be controlled by a protective carbon-silicon interaction, as accompanied by carbon release. After mixing with soil, the addition of Si-rich biochar leads up to 72.7–121% improvement in silicon dissolution in a high-silicon soil (HSS) compared to 147–243% improvement in a low-silicon soil (LSS). The total cumulative amount of silicon dissolved decreased compared to the theoretical value due to the adsorption of silicic acid by the biochar. The addition of WB700 or OP700 as Si-deficient biochars leads to a cumulative Si dissolution decrease of 15.7 and 12.1%, respectively. The adsorption of silicic acid in the biochar and the protection of soil dissolved Fe make biochar a reservoir of soil silicon. Thus, Si-rich biochar could serve as a source of Si with slow release, while Si-deficient biochar could serve as an extra Si sink in agricultural paddy soil.
机译:生物炭对土壤硅溶解动力学的影响尚未解决。在300–700°C的温度下,使用富含硅的稻壳(RH)和稻草(RS)以及缺乏硅的木屑(WB)和橙皮(OP)来制备生物炭。与缺乏硅的生物炭相比,富含硅的生物炭的硅溶解度相对较高,并且随着热解温度的增加而增加。硅的释放机制建议通过碳与硅的保护性相互作用以及碳的释放来控制。与土壤混合后,添加高硅生物炭可以使高硅土壤(HSS)中的硅溶解提高72.7–121%,而低硅土壤(LSS)中提高147–243%。由于生物炭吸附硅酸,与理论值相比,溶解的硅的总累积量减少了。 WB700或OP700作为缺硅生物炭的添加导致累积的Si溶出量分别减少15.7%和12.1%。生物炭中硅酸的吸附以及对土壤中溶解的铁的保护使生物炭成为土壤硅的储集层。因此,富硅生物炭可以作为缓慢释放的硅源,而缺硅生物炭可以作为农业稻田土壤中多余的硅汇。

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