摘要
Mercury emissions from acetylene hydrochlorination processes in polyvinyl chloride (PVC) production pose severe environmental risks yet remain poorly quantified due to methodological limitations in high-reactivity C2H2/HCl atmospheres. We reported an advanced operando mercury speciation platform named PVC-OHM, engineered through systematic optimization of the Ontario Hydro method (OHM), achieving simultaneous real-time detection of elemental mercury (Hg0) and divalent mercury (Hg2+) with unprecedented sensitivity (0.12 μg/m3) under industrially relevant conditions. Our mechanistic investigation reveals three dominant mercury escape pathways: (1) thermal desorption, wherein localized hotspots accelerate HgCl2 decomposition and elevate the saturated vapor pressure at carbon-mercury interface (from 0.9 to 20.3 atm), contributed to 80% of total Hg loss; (2) C2H2 driven reductive decomposition of HgCl2 catalyst at carbon–mercury interfaces, responsible for 65–78% of Hg0 emissions and (3) excess chlorine adsorption-induced desorption ([HgCl2/AC] Cl5, Eads > 0) accounting for >10% of Hg2+ emissions. Quantitative tracking demonstrates alarming mercury loss of per gram catalyst (5 wt % Hg) reached as 3.08 mg Hg0 and 9.01 mg Hg2+, directly linked to localized thermal gradients (ΔT = 250–300 °C) at reaction hotspots. This work establishes the first experimentally validated framework for mercury fate prediction in carbide-based PVC synthesis, providing actionable strategies for emission control through hotspot mitigation and coordination environment optimization.
危险品化学品经营许可证(带存储)