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Oxidation and Evaporation Behaviors of Cr, Cu and As During Incineration of Wood Treated by Chromated Copper Arsenate Preservative

机译:铬酸砷铜防腐剂处理木材过程中铬,铜和砷的氧化和蒸发行为

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Woody materials treated by chromated copper arsenate (CCA) preservative containing copper, chromium and arsenic had been widely used, and thus it is anticipated that a lot of wood waste treated by CCA will be generated as the industrial waste in the future. The environmental pollution by the released heavy metals becomes a serious problem when the wood treated by CCA was incinerated inadequately. There needs the investigation for the behaviors of heavy metals during incineration of wood treated by CCA. The wood sample treated by CCA was incinerated at temperature range between 873 and 1673 K with the oxygen partial pressure between 0.21 and 0.40 atm completely. The proportion of evaporated arsenic increased with increasing temperature and most of arsenic evaporated at about 1600 K. It was suggested that arsenic evaporated as As_2O_3 or As_4O_6 during the incineration. On the other hand, most of copper and chromium remained in the bottom ash. The evaporation behaviors of arsenic largely depended on the incineration temperature, while the effects of the oxygen partial pressure of inlet gas and gas flow rate on those were small. Powder XRD analysis of bottom ash revealed that copper and chromium existed as CuCr_2O_4 and CuCrO_2. CuCr_2O_4 was mainly contained in the bottom ash incinerated at temperature below 1273 K, whereas the ratio of CuCrO_2 increased with increasing incineration temperature above 1273 K. Therefore, most of copper and chromium were bivalent and trivalent, respectively, in the bottom ash, and some copper was converted to a monovalent over 1273 K. Almost all arsenic was contained as pentavalent Cu_3(AsO_4)_2, and arsenic was not identified in bottom ash incinerated at temperature above 1273 K.
机译:用含铜,铬和砷的铬酸砷化铜(CCA)防腐剂处理的木质材料已被广泛使用,因此,预计将来将通过CCA处理的大量木屑作为工业废弃物产生。当通过CCA处理的木材未充分焚化时,释放的重金属对环境的污染成为一个严重的问题。需要对CCA处理的木材焚烧过程中重金属的行为进行研究。经CCA处理的木材样品在873至1673 K的温度范围内完全焚化,氧分压在0.21至0.40 atm的范围内完全焚化。砷的蒸发比例随温度升高而增加,大部分砷在1600 K左右蒸发。建议在焚烧过程中砷以As_2O_3或As_4O_6的形式蒸发。另一方面,大多数铜和铬保留在底灰中。砷的蒸发行为在很大程度上取决于焚烧温度,而入口气体的氧分压和气体流量对其的影响很小。底灰的粉末XRD分析表明,铜和铬以CuCr_2O_4和CuCrO_2的形式存在。 CuCr_2O_4主要包含在低于1273 K的温度下焚烧的底灰中,而CuCrO_2的比例随焚烧温度高于1273 K的增加而增加。因此,底灰中的大部分铜和铬分别为二价和三价,有些铜在1273 K上转化为单价。几乎所有的砷都以五价Cu_3(AsO_4)_2的形式存在,在高于1273 K的温度下焚烧的底灰中未鉴定出砷。

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