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The Transformation of Phosphorus Forms during Co-Composting of Sludge and Wheat Straw

机译:污泥与小麦秸秆共堆肥过程中磷形态的转化

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With sewage sludge (SS) as raw materials, wheat straw bran (WSB, particle size less than 0.5cm) and wheat straw section (WSS, about 3cm) as the conditioner, experiments were carried out to investigate the transformation of phosphorus forms during co-composting of sewage sludge and wheat straw in aerated static pile composting system and natural ventilation fermentation system. The results showed that, in 120 days’ composting period, with the compost maturity, the total phosphorus content of SS+WSB and SS+WSS increased from 2.27g/kg and 2.67g/kg to 6.80g/kg and 6.13g/kg, respectively. The available phosphorus content of SS+WSB and SS+WSS increased from 1.45g/kg and 1.69g/kg to 6.24g/kg and 5.26g/kg, respectively. The organic P content of SS+WSB and SS+WSS increased from 0.72g/kg and 0.83g/kg to 2.53g/kg and 2.16g/kg, respectively. As the composting process in progress, a considerable part of inorganic phosphorus was converted into organic phosphorus, the ratio of organic phosphorus and total phosphorus increased, and adding small sized straw as compost conditioner can be much contributed to the inorganic phosphorus conversion to organic phosphorus. The transformation of inorganic phosphorus forms in the composting process was analyzed by using Hedley grading method. The results showed that the content of H2O-P for SS+WSB was higher than that in SS+WSS throughout the composting process, but the content of Residual-P was reversed for the two treatments. All the forms of phosphorus (H2O-P, NaHCO3-P, NaOH-P, HCl-P and Residual-P) for the two treatments have similar tread of gradual increase during the composting process. Due to the “concentrating effect” and the activation of organic acids on the inorganic phosphorus, the content of various P forms has reached a peak period at the end of the first stage and tend to be stable at the second stage. The difference between total P and organic P should be less than the total content of all kinds of inorganic P.
机译:以污水污泥(SS)为原料,麦麸(WSB,粒径小于0.5cm)和麦秸段(WSS,约3cm)为调节剂,进行了实验研究共沉淀过程中磷的形态转化。曝气静态堆肥系统和自然通风发酵系统对污水污泥和麦秸进行堆肥。结果表明,在堆肥120天后,随着堆肥的成熟,SS + WSB和SS + WSS的总磷含量从2.27g / kg和2.67g / kg增加到6.80g / kg和6.13g / kg , 分别。 SS + WSB和SS + WSS的有效磷含量分别从1.45g / kg和1.69g / kg增加到6.24g / kg和5.26g / kg。 SS + WSB和SS + WSS的有机磷含量分别从0.72g / kg和0.83g / kg增加到2.53g / kg和2.16g / kg。随着堆肥过程的进行,相当一部分无机磷转化为有机磷,有机磷与总磷的比例增加,添加小尺寸的秸秆作为堆肥改良剂可以极大地促进无机磷转化为有机磷。利用Hedley分级法分析了堆肥过程中无机磷形态的转化。结果表明,在整个堆肥过程中,SS + WSB的H2O-P含量均高于SS + WSS的含量,但两种处理的残留P含量却相反。两种处理的所有形式的磷(H2O-P,NaHCO3-P,NaOH-P,HCl-P和残基-P)在堆肥过程中都有逐渐增加的趋势。由于“浓缩效应”和有机酸对无机磷的活化作用,各种P形式的含量在第一阶段结束时已达到峰期,并在第二阶段趋于稳定。总磷与有机磷之差应小于所有无机磷的总含量。

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