The Amendment to the Waste Disposal and Public Cleansing Law in Japan
has introduced new regulation of waste requiring strict management. In
this regulation, the fly ash generated in the Municipal Solid Waste (
MSW) incinerator process was designated as specially controlled solid
waste because of relatively high concentrations of lead, and cadmium.
Furthermore, antimony is a regulated constituent within the Basel Conv
ention on the control of transboundary movements of hazardous wastes a
nd their disposal and was designated a monitor item of environmental s
tandards on water pollution. Thus, in order to understand where the pr
oblems lie, the behaviors of these heavy metals in the MSW incinerator
was investigated. Also investigated were the kinds of products causin
g the fly ash to be contaminated. As a result, the amount of lead, cad
mium and antimony in household waste was about 120, 3.5 and 7.6 g/T, r
espectively. The major origins of Pb, Cd and Sb from household waste a
re small sealed lead batteries, nickel-cadmium batteries and flame-pro
ofed products such as curtains and plastic covers. By incineration tre
atment, these metals shifted to the fly ash (EP ash); the transfer rat
io of Pb, Cd and Sb was about 33, 92 and 45%, respectively. The observ
ed results indicated that the partitioning of metals in the MSW incine
rator showed the influence of the vapor pressure of the elements and t
heir compounds. Clearly, to produce precise estimates of this behavior
, it will be necessary to determine not only the concentration of the
elements in the waste but also the compounds used and the changes thes
e would undergo in the furnace. Finally, several measures which will b
e helpful in solving these problems are introduced to discuss the futu
re direction of environmentally-friendly social systems. (C) 1997 Else
vier Science Ltd.