Piver W T, Lindstrom F T
Environ Health Perspect. 1985 Feb;59:163-77. doi: 10.1289/ehp.59-1568080.
Improper practices in the disposal of polychlorinated biphenyl (PCB) wastes by land burial, chemical means and incineration distribute these chemicals and related compounds such as polychlorinated dibenzofurans (PCDFs) and polychlorinated dibenzodioxins (PCDDs) throughout the environment. The complete range of methods for disposal that have been proposed and are in use are examined and analyzed, with emphasis given to the two most commonly used methods: land burial and incineration. The understanding of aquifer contamination caused by migration of PCBs from subsurface burial sites requires a description of the physical, chemical and biological processes governing transport in unsaturated and saturated soils. For this purpose, a model is developed and solved for different soil conditions and external driving functions. The model couples together the fundamental transport phenomena for heat, mass, and moisture flow within the soil. To rehabilitate a contaminated aquifer, contaminated groundwaters are withdrawn through drainage wells, PCBs are extracted with solvents or activated carbon and treated by chemical, photochemical or thermal methods. The chemical and photochemical methods are reviewed, but primary emphasis is devoted to the use of incineration as the preferred method of disposal. After discussing the formation of PCDFs and PCDDs during combustion from chloroaromatic, chloroaliphatic, as well as organic and inorganic chloride precursors, performance characteristics of different thermal destructors are presented and analyzed. To understand how this information can be used, basic design equations are developed from governing heat and mass balances that can be applied to the construction of incinerators capable of more than 99.99% destruction with minimal to nondetectable levels of PCDFs and PCDDs.
通过陆地掩埋、化学方法和焚烧等方式处置多氯联苯(PCB)废物的不当做法,会使这些化学物质以及多氯二苯并呋喃(PCDFs)和多氯二苯并二恶英(PCDDs)等相关化合物在整个环境中扩散。对已提出并正在使用的所有处置方法进行了审查和分析,重点关注两种最常用的方法:陆地掩埋和焚烧。要了解多氯联苯从地下掩埋场迁移导致含水层污染的情况,需要描述控制非饱和和饱和土壤中迁移的物理、化学和生物过程。为此,针对不同的土壤条件和外部驱动函数开发并求解了一个模型。该模型将土壤内热、质量和水分流动的基本传输现象耦合在一起。为了修复受污染的含水层,通过排水井抽取受污染的地下水,用溶剂或活性炭提取多氯联苯,并采用化学、光化学或热方法进行处理。对化学和光化学方法进行了综述,但主要重点是将焚烧作为首选处置方法。在讨论了氯代芳烃、氯代脂肪烃以及有机和无机氯化物前体在燃烧过程中形成多氯二苯并呋喃和多氯二苯并二恶英的情况后,介绍并分析了不同热破坏器的性能特征。为了理解如何利用这些信息,从控制热和质量平衡出发推导出基本设计方程,这些方程可应用于建造能够实现超过99.99%销毁率且多氯二苯并呋喃和多氯二苯并二恶英含量极低至无法检测的焚烧炉。