Incineration has been proven as one of the most viable
and efficient
waste-to-energy strategies for the handling of rapidly mounting municipal
solid waste (MSW). However, as a generic and key element in MSW, chlorine
(Cl) brings about severe corrosion in boilers and the presence of
Cl-containing species induces the release of toxic dioxins and furans
by acting as chlorine donors. The chlorine release behavior from MSW
during incineration has thus drawn plenty of attention. This paper
has critically reviewed the origin of different chlorine-bearing species
in MSW and their respective thermal decomposition behavior. In general,
chlorine in MSW has two primary sources: plastics, mainly polyvinyl
chloride (PVC), as the source of organic chlorine and household kitchen
and garden waste as the source of inorganic chlorine, mainly chlorides.
Distinct chlorine liberation properties have been observed for these
two different chlorine groups. Chlorine in PVC converts to HCl gas
easily at 300 °C as a result of the thermal decomposition combined
with a depolymerization of the polymer chain. In contrast, the release
of chlorine from inorganic chloride salts is much lower than that
from PVC, mainly attributing to either strong volatilization properties
of alkali chlorides (NaCl and KCl) or the high ionic bonding energies
between some cations, such as Ca2+/Ni2+ and
Cl–. Meanwhile, the decomposition of FeCl2, CoCl2, and MgCl2 is easier with the onset
temperature for HCl release being around 180, 300, and 415 °C,
respectively. Additionally, the addition of SO2, O2, or acidic solids (such as SiO2 and Al2O3) has been found to promote the chlorine release from
chlorides appreciably. However, the exploitation of the underpinning
mechanism is far from completion, especially for CaCl2 and
CoCl2. This requests extra and intensive studies to elucidate
the chlorine liberation mechanism from these inorganic species, even
from the molecular level in terms of their ionic bonding propensity
and breakage at high temperatures.