Bhopal Gas Disaster: Review on Health Effects of Methyl Isocyanate
This study reviews health effects of gas exposures from published human studies and discusses some of the clinical and experimental issues being debated. Because of the relative paucity of information. Some of these studies have helped to highlight specific health problems from the disaster and initiate more organized research to address these problems.
April 30, 2010; Accepted: May 13, 2010;
Published: August 13, 2010
Reviewed the studies of human health effects that resulted from exposure to
methyl isocyanate gas that leaked from the Union Carbide plant in Bhopal, India,
in Dec. 1984. The studies were conducted during both the early and late recovery
periods. The Bhopal gas tragedy is undoubtedly one of the worst industrial disasters
in the history of mankind resulting in mortality of 2500-6000 and debilitating
over 200 000 people. Inhabitants in the township were exposed to different degrees
and there are more than 500 000 registered victims that survived the tragedy
(Mishra et al., 2009).
The accident was apparently initiated by the introduction of water into the Methyl Iso Cyanate (MIC) storage tank resulting in an uncontrollable reaction with liberation of heat and escape of MIC in the form of a gas.
The multi-disciplinary study of histopathology and toxicology of Bhopal gas
tragedy resolved several issues. First, the progression of severe pulmonary
oedema to chronic fibrosis was confirmed experimentally, following a single
exposure to MIC. Analysis of the residue in Tank 610 revealed over 21 chemicals.
Apart from MIC and HCN, some of them were tracked down to the blood and viscera
of dead and living exposees. The rationale of NaTS therapy was substantiated
by elevated urinary NaSCN levels in Double Blind Clinical Trials as well as
patients. Apart from cyanide, the cherry red discolouration was
also shown to result from binding of MIC to end-terminal valine residues of
Hb, as shown by changes in 2-3DPG levels and blood gas profiles. The finding
of Ncarbamoylation of several other end-terminal amino acids of tissue proteins
confirmed the distribution of MIC within the body, although the underlying mechanism
is not yet fully understood. Possibly, the much faster S-carbamoylated compounds
of the blood like glutathione and other sulphydrylcontaining enzymes like rhodanese
could be responsible for re-circulation of MIC and protracted cyanide toxicity.
It is hoped that eventually the enigma of the Bio-chemical Lesion of MIC toxicity
will be unraveled (Sriramachari, 2004).
The two ICMR projects on histopathology and toxicology have more than fulfilled the initial hopes and expectations. The sequence of pathological changes in the acute, sub-acute and chronic stages have been clearly delineated. Experimental studies with MIC and its aqueous derivatives have confirmed the pathogenesis and pulmonary changes after single exposure are comparable to human autopsy findings.
Toxicological properties of MIC: MIC is highly irritant to the skin,
eyes and mucus membranes of the respiratory tract. This irritant property is
based on its reactivity with water which enables it to penetrate tissues and
interact with protein. Absorption through the skin is known to occur (Irving,
Mortality and morbidity: Of the more than 200,000 persons exposed to
the gas, the initial death toll within a week following the accident was over
2500. In Nov. 1989, the Dept. of Relief and Rehabilitation, Govt of Madhya Pradesh
the toll at 3598 and by 1994, the toll was estimated to be over 6000 (Governament
of Madhya Pradesh, 1989).
Symptom prevalence surveys conducted by the ICMR indicate that morbidity was
higher in the exposed areas (26%) as compared with the control area (18%).Respiratory,
neurological, psychiatric and ophthalmic symptoms also showed a strong gradient
by exposure category (Indian Council of Medical Research,
Clinical studies: Clinical studies have shown chronic illnesses such
as pulmonary fibrosis, bronchial asthma, Chronic Obstructive Pulmonary Disease
(COPD), emphysema, recurrent chest infections, keratopathy and corneal opacities
in exposed cohorts. Survivors continue to experience higher incidence of reported
health problems including febrile illnesses, respiratory, neurologic, psychiatric
and ophthalmic symptoms. In utero exposure to methyl isocyanate in the
first trimester of pregnancy caused a persistent immune system hyper responsiveness,
which was in an evident way genetically linked with the organic exposure (Mishra
et al., 2009).
Ophthalmic problems: The intensely irritating effect of MIC on the cornea
resulted in severe ocular burning, watering, pain and photophobia (Anderson
et al., 1988). Examination of the eye showed involvement of the corneal
and conjunctival epithelium with redness of the eye, corneal ulceration and
lid swelling (Andersson et al., 1984; Dwivedi
et al., 1985).
Andersson et al. (1986) performed a follow-up
study on the eyes of survivors 9 months after the accident and reported that
no case of blindness could be found that could be attributed to gas exposure
among the nearly 20,000 persons attending the Bhopal Eye Hospital. However,
they did find persistent eye watering and other chronic irritant symptoms like
burning, itching and redness. Raizada and Dwiwedi studied eye pathology 24 among
1140 exposed persons and found that the main chronic lesions were chronic conjunctivitis,
deficiency of tear secretion and persistent corneal opacities (Andersson,
No information is given on the prevalence of these conditions in the control area. Though there is no evidence that severe damage to the eye's external and internal structures has occurred.
Respiratory and pulmonary problems: Acute symptoms of the respiratory
tract were mainly due to the irritant action of MIC on tissues. Because MIC
is moderately soluble in water, lesions were seen in both the upper and lower
respiratory tract. Predominant symptoms were cough accompanied by frothy expectoration,
a feeling of suffocation, chest pain and breathlessness (Mishra
et al., 1988). Other symptoms included dryness and irritation of
the throat and rhinorrhea.
Autopsies on 300 victims revealed severe necrotizing lesions in the lining
of the upper respiratory tract as well as in the bronchioles, alveoli and lung
capillaries. Enlarged and edematous lungs, consolidation, hemorrhage, bronchopneumonia
and acute bronchiolitis were seen (Indian Council of Medical
Reproductive toxicity: Concerns that the gas leak had effects on reproductive
health were raised early in 1985 when reports indicated that menstrual cycle
disruption, leucorrhea and dysmenorrheal had occurred in gas-exposed women (Bang
and Sadgopal, 1990). Risk to the fetus was also considered not only because
of exposure to the gas but other factors like stress, anoxia and ingestion of
various prescribed drugs like antibiotics, bronchodilators, and analgesics.
An epidemiological survey by Varma showed pregnancy loss and infant mortality
to be high in gas-exposed women (Varma, 1987). In a
sample of 865 women who lived within 1 km of the plant and who were pregnant
at the time of the gas leak, 43% of the pregnancies did not result in a live
birth. Of the 486 live births, 14% of babies died in the first 30 days as compared
to a death rate of 2.6 to 3% for previous deliveries in the 2 years preceding
the accident in the same group of women.
Animal experiments conducted by Schwetz exposing pregnant mice to MIC by inhalation
showed that this exposure does indeed have a fetotoxic effect (Schwetz
et al., 1987). This finding was replicated by Varma
et al. (1987), who observed a concentration-dependant increase in
embryo loss, decrease in fetal and placental weights and a 20% reduction in
mandible length and bones of the extremities.
Genotoxicity and carcinogenicity: Methyle isocyanate (MIC) was assayed in a number of in vitro and in vivo genetic toxicity tests in mammalian cells to determine its ability to interact with DNA and to induce genetic damage. In vitro tests included the mammalian microsome test gene mutation. In vitro and in vivo tests provide convincing evidence that is capable of inducing chromosomal damage and that this genetic toxicity is not strongly expressed in vivo, perhaps because of the selective reactivity of MIC with proteins and up to now effects of MIC on bacterial DNA not documented and its Possible that MIC may have caused mutations in bacteria, which may have led to their capacity to cause previously undocumented morbidities related to infection caused by these mutated bacteria.
Isocyanates are able to modulate biomolecules, resulting in a series of biotransformations
(Shelby et al., 1987; Pearson
et al., 1990; Slatter et al., 1991),
which in turn may affect health adversely (Tamura et
al., 1992), yet they have a wide array of industrial applications. MIC,
a reactive byproduct, is a detrimental to numerous organ systems (Worthy,
1985; Gupta and Prabha, 1996). It forms DNA cross
links/adducts by reacting with exocyclic amino group of dNTPs, in turn contributing
to cytotoxicity (Yoon et al., 2001). MIC intermediates
(N-methylcarbamate) are also toxic to cultured mammalian cells (Hagmar
et al., 1993; Kuo et al., 2008).
Isocyanates, including MIC have wide industrial applications, although they
are mutagenic, alter the genome (Mason et al., 1987;
Anderson et al., 1988; Kar
et al., 1989) and can produce varied chromosomal abnormalities in
individuals exposed to them (Goswami et al., 1990;
Ghosh et al., 1990). Details of the complex molecular
mechanisms underlying genetic hazards of occupational or accidental exposures
to these chemicals on bacteria are still unknown.
A single, 2 h exposure to concentration of 0, 3, 10 and 30 ppm MIC produced
no evidence of chromosomal effects in the bone marrow, although significant
cell cycle delay was observed. In four experiments involving exposure on 4 consecutive
days to 0, 1, 3 or 6 ppm, delay in bone marrow cell cycle were again observed
. Increases in SCE and chromosomal aberration were observed in bone marrow cell
cycle were again observed (Shelby et al., 1987).
A population-based cancer registry has been established in Bhopal in 1986 to study possible carcinogenic effects of the gas leak. Relative risks of 1.4, 1.3 and 0.7 (all non-significant) were found for lung, oropharynx, and oral cavity cancers, respectively, for 1992 in comparison to the years 1987-90 and gas unaffected regions combined. Using a case-control design, cancer cases of the above sites were selected from the registry and controls from a tobacco survey conducted in the Bhopal population. A marginally increased risk was found only for oro pharyngeal cancer (RR = 1.5, 95% CI = 1.1-2.2), after adjustment for age and tobacco use. No dose-response relationships were evident in the geographic distribution of cases.
Biochemical studies: Biochemical studies conducted by the ITRC, Lucknow
, India, revealed that some multi-systemic complaints were persistent and occurred
even in those patients who did not have significant respiratory damage (Gupta
et al., 1988). In a sample from a gas exposed population studies
3 MO after the accident biochemical indicators of stress response were observed,
blood ceruloplasmin levels were increased 200% over control values in more than
45% of those tested (Srivastava et al., 1988).
In these studies, urinary creatinine was significantly higher than in controls.
Blood glutathione was significantly depressed in approximately 40% of the population
Buchner (Tice et al., 1987), in this review
of the health effects research done on MIC, states that if MIC is shown to bind
to normal hemoglobin (Carbamoylation), this would provide evidence that the
chemical crosses the alveolar barrier and would, therefore, support MICs
potential for systemic exposure.
While N-carbamoylation cannot be undone, it would appear that sulphydryl radicals
contained in Acetyl Choline Esterase (ACE), aldolase and especially rhodanese
are periodically reactivated and chronic cyanide metabolism corrected.
Normalcy is attained only when the MIC stored in the body is fully depleted.
But, in the exigencies of an alarming human disaster, it has not been possible
to try other potent sulphane donors described by Cohen and Oppenheimer16. It
seems that the Biochemical Lesion of Bhopal disaster may lie between the interplay
of N- and S-carbamoylation (Sriramachari, 2004).
Immunotoxicity: Following exposure to the gas in Bhopal, there was concern
amongst the health authorities that the population might experience an increased
rate of infections. Immune function was studied in exposed subjects from the
ITRC sample two and a half months after exposure to ascertain whether any change
had occurred in the immune status (Saxena et al.,
1988). Humoral immunity was assessed by quantitation of immunoglobulins
(IgG, IgM, IgA) in over 300 exposed and 10 non-exposed persons. Cell-Mediated
Immunity (CMI) was assessed by phagocytic activity of lymphocytes and quantitation
of T-cell rosettes in 19 exposed and 8 non-exposed persons. Results from this
study showed that no difference in mean immunoglobulin levels was found when
compared to controls. The T-cell population (28%) was found to be less than
half that found normally in the Indian population (65%). Significant depression
of phagocytic activity of lymphocytes was found as compared to controls.
Limitations of the human studies include the relatively small sample sizes, choice of control groups and unclear exposure ascertainment. The above limitations make it difficult to arrive at definitive conclusions regarding immunotoxicity from MIC exposure for the gas victims.
Psychological and neuro-behavioral toxicity: Srinivasamurthy and Isaac
noted that psychological problems of Bhopal survivors fell into four major categories
(Murthy and Isaac, 1987). These observations were based
on visits by the authors to medical clinics as well as the homes of affected
Fifty-two MIC victims were subjected to detailed medical examination and clinical
psychometry one year after the accident (Misra and Kalita,
1997). The neurological included examination of mental status, cranial nerves,
motor and sensory systems. Clinical psychometry included the Benton Visual Retention
Test (BVRT), Wechsler memory scale, and Standard Progressive Matrices (SPM).
Severely affected victims had significant impairment on SPM, associate learning,
motor speed, and precision test. In the moderately affected victims, associate
learning, motor speed, and precision was significantly impaired. Some degree
of dose-response was noted in some tests when compared with controls and within
the exposed groups. The authors concluded that the persistence of cognitive
impairment one year after the accident suggested significant MIC neurotoxicity.
Neuromuscular toxicity: Neuromuscular symptoms in Bhopal survivors have persisted since the gas leak. These symptoms are mainly tingling, numbness, a sensation of pins and needles in the extremities and muscle aches.
To assess whether MIC was toxic to muscle, Anderson et al evaluated the effects
of MIC on rat muscle cells in culture (Anderson et al.,
1988). At lower doses, the formation of muscle fibers was prevented. At
higher doses, death of fibroblasts and myoblasts was seen. The findings suggested
either an effect on muscle differentiation or selective toxicity to myoblasts.
There has been no evidence to support the second hypothesis that MIC is converted
to a form of cyanide in the body. Animals exposed to MIC by inhalation have
not shown any evidence of cyanide in the blood (Bucher et
Ferguson and Alarie have demonstrated that there may be a physiopathological
basis for the persistence of multi-systemic symptoms in Bhopal survivors (Ferguson
et al., 1988). Their studies on experimental animals have shown that
radio-labeled MIC is capable of being absorbed and distributed throughout the
body. These findings have been confirmed by Bhattacharya et al who have shown
that MIC binds covalently to tissue proteins in its active form and not as its
breakdown product, methylamine (Bhattacharya et al.,
1988). There is no known antidote for MIC toxicity.
Recent experimental studies have provided mechanistic understanding of methyl
isocyanate exposure at a molecular level. Immuno toxic implications, toxico-genomic
effect, inflammatory response, elicitation of mitochondrial oxidative stress,
chromosomal and microsatellite instability have been studied comprehensively
in cultured mammalian cells. Besides providing a framework for understanding
potential mechanisms of toxicity of a host of other exposures, these studies
may also uncover unique abnormalities thereby stimulating efforts to design
newer and effective diagnostic and therapeutic strategies (Mishra
et al., 2009).
In-depth molecular studies of ocular, respiratory, reproductive, immunological, genetic and psychological health carried out so far have helped to understand the extent and severity of long term effects associated with the disaster.
Long-term monitoring of the affected community and use of appropriate methods of investigation that include well-designed cohort studies for such conditions, characterization of personal exposure and accident analysis have helped to determine several clinical and epidemiological inadequacies, including poor study design, bias and inaccurate exposure classification of studies conducted previously on victims of the tragedy.
Studies aimed at understanding increasing morbidity of MIC exposure carried out on human cultured cellular model systems have provided a framework of understanding the potential mechanism of toxicity of a host of other exposures and that might uncover unique abnormalities in the survivors thereby stimulating efforts to design newer and more effective diagnostic and therapeutic strategies for helping the survivors.
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