This work was carried out with the purpose of developing
effective reagents for decontamination of groundwater
contaminated with chlorocarbons. Zinc metal as a reducing
agent for carbon tetrachloride (CT), chloroform (Chl), and
methylene chloride (MC) in aqueous solution has been studied
in some detail, especially regarding activated forms of
the metal. Chlorocarbon concentrations were monitored
at certain time intervals by gas chromatography/mass
spectrometry (GC/MS) analysis of the headspace and water
phase. Reaction mixture headspace was additionally
studied by a GC/headspace analysis system to detect the
formation of hydrocarbons. Chloroform, methylene
chloride, methyl chloride, methane, and acetylene were
found to be products from CT reduction. For methylene
chloride reduction, traces of cis and trans-1,2-dichloroethene
(DCE) were also found. Activated by cryo or mechanical
treatment, metallic zinc caused an increase in CT
dechlorination rate and conversion into methane. After
the first 2.5 h, more than 20% of CT was converted into
methane by cryochemically activated zinc in comparison to
1.2% by conventional zinc dust. Furthermore, CT reduction
by activated zinc caused the formation of DCEs and
TCE. Pathways are proposed to account for the observed
methane/methylene chloride ratio and DCEs and TCE
formation that include sequential reductive dechlorination
through organometallic and carbonoid species on the
Zn surface. Furthermore, it seems likely that some methane
can be formed in “one metal contact”, since significant
amounts are formed early in the reaction. In attempts to
learn more about morphological changes in the zinc
during its consumption, pore volume/pore radii were
determined, and atomic force microscope images were
obtained. Zinc corrosion takes place rapidly at edges/corners leading to the formation of cavities with wide openings,
large volumes, and increased specific surface areas.
Pyramidal zinc “pillars” are formed during the process.