848 PCBs AND ASSOCIATED AROMATICS
thermodynamics is a concept which describes the energy flow
in a reaction from reactants to products. When there is a high
activation energy barrier, the reactants require more energy
to attain an activated state than when there is a low activa-
tion barrier. Once the reactants have gained enough energy
to form an activated intermediate they can either return to
the reactant form or proceed to a stable product. The bal-
ance between the forward and backward reaction directions
is an equilibrium condition which may be heavily weighted
in favor of either the reactants or products. The high activa-
tion energy in the formation of PCDDs contributes directly
to their low yields. The residue from the trichloro-phenol
distillation in the Monsanto synthesis was reported to be
20 times less effective in producing liver necrosis in rabbits
than the residue of the fraction remaining after heating to
above 230°C. The boiling points of many dioxin precur-
sors are lower than the reaction temperature range in which
PCDDs are formed and therefore there is a loss of precursor
molecules before reaction can occur.
The possibility of pressure differences in the formation
of the residues are only one of several key parameters which
make the comparison difficult. It is, nevertheless, clear that
the residue derived from the high temperature distillation
was substantially more toxic than the pentachloro naphtha-
lene studied. The health effects of PCNs had been described
in the literature some 17 years before but the effect observed
on rabbits left in the operating area after the BASF accident
was surprising—they died from liver necrosis after a one
week exposure!
1957
A review of characteristic chloracne lesions appeared in
1957 by Schwartz et al.
1962
Threshold limit values for PCBs in workroom air were
set in 1962 by the American Conference of Governmental
Industrial Hygienists. Under “Chlorodiphenyl—42%
Chlorine” it was stated that “Acne, systemic poisoning and
even death may result from exposure to chlorinated diphe-
nyls.” The references indicated were [Schwartz, L.: Am.
J. Pub. Health; 26 , 586 (1936) and Drinker, C.K., Warren,
M.F., Bennett, G.A.: J. Ind. Hyg. & Tox.; 19 , 283 (1937)].
A threshold limit value of 1 mg/m^3 was recommended to
offer good protection against severe systemic toxicity but
may not guarantee complete freedom from chloracne. In
other words, it was recognized that there was a risk of severe
systemic toxicity and that chloracne was a separate issue.
FIGURE 4 Formation of polychlorinated diphenyl ethers (PCDPEs) can lead to the formation of polychlorinated dibenzofurans
(PCDFs).
FIGURE 5 Loss of HCl produces cyclization of the diphenyl ether to a dibenzofuran.
FIGURE 6
FIGURE 7 Loss of H 2 from the pre-dioxin produces PCDD.
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