典型生活垃圾焚烧电厂尾部烟气中汞的迁移和转化特性

Migration and transformation characteristics of mercury in the tail-end flue gas of typical municipal solid waste incineration power plants

  • 摘要: 选择典型炉排炉(GF)和循环流化床(CFB)垃圾焚烧炉开展现场实测研究,采集不同空气污染物控制设施(APCDs)前后的烟气和焚烧产生副产物(底渣和飞灰)进行分析,用以揭示汞(Hg)在尾部烟气中的迁移与转化特性。结果表明:烟气中的Hg存在多种形态,主要以氧化态汞(Hg2+)形态存在,其次是颗粒态汞(Hgp),而零价汞(Hg0)的占比则较少。烟气中总汞(HgT)浓度随时间的变化波动较大,且不同电厂之间多种形态的Hg浓度差异较大。不同APCDs对多种形态Hg的转化及脱除率不同,半干法脱酸塔(SD-FGD)促进了Hg2+向Hgp的转化,布袋除尘器(FF)对多种形态的Hg均具有良好的脱除率(54.35%~95.60%)。垃圾中的HgT经焚烧后在底渣中的富集较少,主要迁移到飞灰中,占比为78.27%~93.39%。相较于GF焚烧炉,CFB焚烧炉焚烧过程中HgT的释放占比更高。排放大气中的Hg以Hg2+为主,其HgT排放因子为0.008~0.526 mg/kg。

     

    Abstract: A field measurement study was conducted on typical grate furnaces (GF) and circulating fluidized bed (CFB) waste incinerators. Flue gas and by-products (bottom ash and fly ash) were collected upstream and downstream of different air pollution control devices (APCDs) to investigate the migration and transformation characteristics of mercury (Hg) in the tail-end flue gas. The results showed that mercury in the flue gas existed in multiple forms, predominantly as oxidized mercury (Hg2+), followed by particulate-bound mercury (Hgp), with zero-valent mercury (Hg0) accounting for a relatively small proportion. The total mercury (HgT) concentration in the flue gas exhibited significant temporal fluctuations, with notable variations in mercury species concentrations across different incineration plants. Different APCDs exhibited varying efficiencies in transforming and removing mercury species. The semi-dry flue-gas desulfurization (SD-FGD) tower promoted the conversion of Hg2+ to Hgp, whereas the fabric filter (FF) demonstrated high removal efficiency (54.35%~95.60%) for various forms of mercury. After incineration, only a small fraction of HgT from the waste accumulated in the bottom ash, whereas the majority (78.27%-93.39%) was distributed in the fly ash. Compared with the GF incinerator, the CFB incinerator released a higher proportion of HgT during combustion. The mercury emitted into the atmosphere was dominated by Hg2+, with an HgT emission factor ranging from 0.008 to 0.526 mg/kg.

     

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