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    污泥与煤泥混合燃烧过程砷、硒和铅迁移转化特性

    Migration and transformation characteristics of arsenic, selenium and lead during co-combustion of sewage sludge with coal slime

    • 摘要: 以同一地区污水处理厂污泥和选煤厂煤泥为研究对象,考察了燃烧温度、燃烧时间、掺混比例等燃烧条件对污泥和煤泥混燃过程砷、硒和铅迁移转化特性的影响,以及燃烧产物中砷、硒和铅的环境影响行为。污泥和煤泥中砷、硒和铅释放率随温度升高而增大,最终释放率由高到低依次为硒>砷>铅,且砷、硒和铅释放率随污泥掺混比例增加而增大。污泥和煤泥中砷、硒和铅释放率随燃烧时间延长先快速增大然后趋于平缓,且达到最大释放率用时由高到低依次为铅>砷>硒。在恒温燃烧条件下,1 200 ℃时污泥和煤泥中砷、硒和铅的释放速率均快于900 ℃,且在燃烧初期煤泥中砷、硒和铅的释放速率略快于污泥。污泥和煤泥中砷、硒和铅的赋存形态分布特性是其释放行为的主要影响因素。污泥和煤泥中砷、硒和铅均主要以无机结合态存在,且污泥中无机结合态砷、硒和铅占比高于煤泥。煤泥和污泥中有机结合态砷、硒和铅主要在低于500 ℃的燃烧温度下随挥发分一同释放,在800~1 200 ℃燃烧温度范围内,煤泥和污泥中碳酸盐+硫酸盐+氧化物结合态和硫化物结合态砷含量显著降低,碳酸盐+硫酸盐+氧化物结合态和硫化物结合态铅主要释放温度区间则分别略微延迟到900 ℃和1 200 ℃。在酸性浸取环境下,污泥和煤泥燃烧产物中硒均处于中风险区域,其浸出率明显高于砷和铅;除SPLP方法对污泥燃烧产物的砷浸出率处于低风险区域外,其余燃烧产物中砷浸出率处于中风险区域;燃烧产物中铅浸出率最低,只有TCLP方法对煤泥燃烧产物的铅浸出率处于中风险,其余均为低风险区域。

       

      Abstract: Sewage sludge and coal slime were collected from sewage treatment plant and coal washing plant in the same area, respectively. The effects of combustion temperature, combustion time and mixing ratio on the migration and transformation characteristics of arsenic (As), selenium (Se) and lead (Pb) during co-combustion of sewage sludge with coal slime were investigated by a temperature-programmed tubular furnace and a sequential chemical extraction method. In addition, two acid leaching methods were used to investigate the environmental effects of As, Se and Pb in the combustion products of sewage sludge and coal slime. The release ratios of As, Se and Pb in sewage sludge and coal slime increased with the increase of combustion temperature and the final release ratio order is Se > As > Pb. Moreover, the release ratios of As, Se and Pb increase with the increase of sewage sludge mixing ratio. The release ratios of As, Se and Pb in sewage sludge and coal slime increase rapidly with the combustion time and then tend to be stable. The time required to reach the maximum release ratio is Pb > As > Se from high to low. Under the constant temperature combustion conditions, the release rates of As, Se and Pb in sewage sludge and coal slime at 1 200 ℃ are faster than those at 900 ℃, and the release rates of As, Se and Pb in coal slime at the initial stage of combustion are slightly faster than that of sewage sludge. The speciation distribution characteristics of As, Se and Pb in sewage sludge and coal slime are the main factors affecting the release behavior. As, Se and Pb in sewage sludge and coal slime mainly exist in inorganic bound states, and the proportions of inorganic bound As, Se and Pb in sewage sludge are higher than those in coal slime. Organic bound state As, Se and Pb in sewage sludge and coal slime are mainly released together with volatile matter when the combustion temperature is below 500 ℃. In the combustion temperature range of 800 ℃ to 1200 ℃, the content of carbonate + sulfate + oxide and sulfide bonded As in sewage sludge and coal slime is significantly reduced. The main release temperature ranges of carbonate + sulfate + oxide and sulfide bonded Pb is slightly delayed to 900 ℃ and 1 200 ℃, respectively. In the acid leaching environment, the leaching ratios of Se in the sewage sludge and coal slime combustion products are the highest, which are in the medium risk area. However, the leaching ratios of Pb are the lowest, which are basically in the low risk area.

       

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