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March 2009 - Volume 3, Issue
2
DOMESTIC ENERGY AND THE HEALTH
PROBLEMS OF MAN AND ANIMALS
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1. Enwereji, E. E. (corresponding author)
College of Medicine
Abia State University, Uturu,
Abia State, Nigeria.
2. Ezeama, Matina C.
College of Medicine
Imo State University
Owerri, NIGERIA
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| ABSTRACT
Pollutants produced by several
types of domestic energy could have adverse effects
on the health of living things especially that of man
and animals. The health problems found in human beings
were that of chronic cough, eye irritation, headache,
and others. These were common in individuals exposed
to pollutants from coal and firewood. Similar health
problems also occur in animals in environments where
domestic energy is used. Common health problems found
among animals were loss of ciliated epithelium in the
upper respiratory tract, lysis of erythrocyte within
alveolar capillaries and breakdown of capillary endothelium
and others. However, one problem of this study is the
dearth of literature on the health problems of living
things exposed to domestic energy in Nigeria. There
was little or no literature available for review at
the time of study.
The paper recommends a systematic
collection of data on the health problems of living
things exposed to chemical residues from different sources
of domestic energy in Nigeria. This is necessary because
research has shown that exposure to sources of domestic
energy such as coal, kerosene, firewood, gas, sawdust
and others, has adverse effects not only on the health
of human beings but also on that of animals.
Key Words: Exposure
to domestic energy, erythrocyte, epithelium, Nigeria.
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INTRODUCTION
Domestic energy in this paper refers
to substances such as coal, kerosene, firewood, gas, electricity,
sawdust and others that are used for generating energy in
homes. The paper documents the various pollutants these sources
of energy emit and the resultant health problems on living
things especially on man and animals. Studies by Coffin and
Gardner, (1972) and Graedal, (1978) have shown that domestic
sources of energy also produce chemical residues, which destroy
plant growth. Plants produce oxygen for respiration (Coffin
and Gardner 1972). The destruction of plants causes depletion
of the levels of oxygen in the atmosphere. This depletion
of the levels of oxygen in the atmosphere the studies uphold,
adversely affect the respiratory systems of both man and animals
(Goran, 1995, Radim, 1966 and Yoko (1974). The studies further
showed that gases emitted from domestic energy directly or
indirectly affect the health of women more than that of other
users. The studies argued that the gender roles women take
on; expose them to the hazards of different sources of domestic
energy more than men. As such, women more than men are at
risk of the effects of the pollutants emitted by domestic
sources of energy. Studies by Goldberg (1996) and Spin et.
al. (1993) confirm the findings of Gorna (1995) and Yoko (1974)
that the gender roles women take on expose them to the hazards
of different sources of domestic energy more than men. For
instance, the findings of Spin et.al. (1993) Dejmek, et al.
(1995) and Goldberg et al. (1996) maintain that some gases
transverse the mammary gland especially that of nursing mothers
and contaminate the breast milk thereby endanger the life
of breastfeeding babies. Among the pollutants or chemical
residues identified by these authors include sulfur oxide,
carbon monoxide, oxides of nitrogen and volatile organic compounds.
These pollutants were found to accumulate in the body systems
to form toxic levels (Rasmussen1992). The studies by Rasmussen
(1992) and Nakazawa (1990) argue that individuals exposed
to smoke from coal and firewood are particularly more at risk
than others of developing nasal discharge, tachycardia (excessive
rapid heart beat), asthma (asphyxia due to contraction of
the airways) and phlegm (mucus secreted by the mucosa of the
air passages).
Further evidence from Ko (1996) and
Yoko (1974), showed that nitrogen oxide constitutes pollutants
that adversely affect health by producing photochemical and
other chemical agents that affect the respiratory system of
man and animals. In man, nitrogen oxide causes fibrosis of
the lungs, phlegm, chronic cough, breathlessness, ataxia,
confusion, pneumonia, eye irritation, tachycardia, and arrhythmias.
In animals, nitrogen oxide causes increase in the frequency
of respiration, decrease in tidal volume as well as inflammation
of cells in the tonsil. The findings of Klassen (1980) Nakazawa
(1990), Romm and Ervin (1996) argue that indoor cooking with
kerosene and gas stoves, produce pollutants that affect the
health of living things as much as other indoor activities
like cigarette smoking, using ultraviolet lamps, electrostatic
precipitators, photocopying machines and odour control equipment.
The findings of Nakazawa (1990) specifically confirm that
while the pollutants produced by indoor cooking with kerosene
and gas stoves are more of nitric oxide, and ozone, these
indoor activities such as cigarette smoking, using ultraviolet
lamps, electrostatic precipitators, photocopying machines
and odour control equipment produce more of ozone, carbon
monoxide, sulfur dioxide and nitrogen oxide than other gases.
Evidence from Fetner (1962), Selevan (1995), White (1976),
Stephen (1973) and Freeman (1973) confirm that the primary
targets of ozone are the respiratory tract especially the
pulmonary parenchyma and the reproductive system.
Exposure to ozone has various effects
on living things. For instance, several findings reveal that
in man, exposure to ozone causes metaplasia and fibrosis of
bronchiolar epithelium (White 1976) as well as breakage of
chromosomes ( Fetner 1962). In rats, it causes pulmonary oedema,
while in dogs it results in haemorrhage and death ( Stephen
1973). Generally, ozone causes a reduction in the number of
alveolar cells especially those that synthesize deoxyribonucleic
acid (DNA) and ribonucleic acid (RNA) ( Selevan (1995). In
guinea pigs, ozone causes increase in respiration as well
as a decrease in tidal volume while in rabbits, exposure to
ozone causes inflammation of the cells of the tonsil Freeman
et.al. (1973). Also the studies by Yoko (1974) and Coffin
(1972) reported that other gases like nitrogen dioxide and
sulfur dioxide also have effects on other laboratory animals.
For instance, in cats, nitrogen dioxide caused erythrocyte
lysis in alveolar capillaries and a breakdown of capillary
endothelium (Yoko 1974).
In cats, exposure to sulphur dioxide
results in swelling of type I alveolar cells as well as loss
of ciliated epithelium while in rabbits, exposure to sulfur
dioxide causes inflammation of the cells in the tonsil (Coffin
1972). Generally, the researchers observed that animals exposed
to a mixture of nitrogen oxide and sulfur dioxide had loss
of phagocytic and macrophagic properties of the pulmonary
alveolar cells as well as a complete loss of motor activities
and that such animals suffered decrease in resistance to bacterial
infections ( Coffin 1972 and Yoko (1974).
On the effects of exposure to carbon
monoxide poisoning, the findings of Radim (1966) stressed
that it produces carboxyhaemoglobin (irreversible combination
with hemoglobin) as well as pneumonia, asthma, cardiovascular
diseases, chronic cough, confusion, eye irritation, and non-productive
cough. The aim of this paper is to highlight the health problems
of man and animals, that are exposed to pollutants from various
sources of domestic energy.
MATERIALS AND METHODS
Documents were reviewed in this study.
In this review, the effects of exposure to various sources
of domestic energy on the health of living things especially
on man and animals were examined. In doing this, extensive
review of relevant literature was done. This helped to unravel
the specific health problems encountered by human beings and
animals exposed to pollutants, emitted from various sources
of domestic energy. In addition, the frequencies of the health
problems as noted in the review were computed so as to give
an overview of the magnitude of the problems in society.
| Table
1. Health problems of individuals exposed to different
sources of domestic energy. |
| Health
problems of individuals |
Sources of domestic energy |
| |
Gas |
Coal |
Kerosene |
Firewood |
Other indoor
activities (Cigarette smoking, ultraviolet lamps, electrostatic
precipitators, photocopying machines and odour control
equipment) |
| Phlegm |
20% |
11% |
5% |
20% |
5% |
| Nasal
discharge |
12% |
50% |
14% |
12% |
11% |
| Asthma |
2% |
5% |
3% |
2% |
4% |
| Emphysema
|
12% |
15% |
13% |
12% |
1% |
| Flu
epidemics |
2% |
3% |
2% |
2% |
7% |
| Tachycardia |
7% |
40% |
9% |
7% |
19% |
| Metaplasia
of bronchiolar epithelium |
30% |
32% |
20% |
30% |
7% |
| Atelectasis |
3% |
21% |
2% |
13% |
18% |
| Pneumonia
|
1% |
5% |
1% |
7% |
5% |
| Chronic
cough |
40% |
33% |
38% |
40% |
24% |
| Hair
loss |
14% |
21% |
18% |
14% |
18% |
| Headache
|
2% |
2% |
1% |
2% |
6% |
| Eye
irritation |
22% |
23% |
21% |
22% |
15% |
| Chromosomal
abnormality |
9% |
15% |
10% |
9% |
19% |
| Bronchitis |
16% |
30% |
12% |
16% |
9% |
| Low
sperm count |
10% |
12% |
19% |
9% |
3% |
| Abortion/miscarriage |
21% |
20% |
17% |
13% |
14% |
| Low
birth weight babies |
17% |
28% |
10% |
17% |
19% |
| Premature
babies |
16% |
24% |
12% |
16% |
25% |
These frequencies represent the compilation
of various health problems of individuals reported in the
literature reviewed.
| Table
2. Health problems of animals exposed to different
sources of Domestic energy |
| Health problems in animals |
Types of domestic energy |
| |
Gas |
Coal |
Kerosene |
Firewood |
Other
indoor activities (Cigarette smoking, ultraviolet lamps,
electrostatic precipitators, photocopying machines and
odour control equipment) |
| Loss
of ciliated epithelium |
4% |
15% |
10% |
18% |
18% |
| Pulmonary
oedema |
2% |
20% |
7% |
10% |
6% |
| Hemorrhage |
1% |
11% |
3% |
14% |
27% |
| Destruction
of type I alveolar cells |
3% |
17% |
1% |
22% |
33% |
| Destruction
of type II alveolar cells |
2% |
23% |
4% |
25% |
30% |
| Swelling
of type I alveolar cells |
8% |
36% |
11% |
38% |
29% |
| Lysis
of erythrocyte within alveolar capillaries |
6% |
33% |
8% |
33% |
35% |
| Increased
frequency of respiration and decrease in tidal volume |
- |
3% |
1% |
8% |
24% |
| Metaplasia
and fibrosis of bronchiolar epithelium |
1% |
27% |
5% |
34% |
22% |
| Inflammation
of cells in the tonsil |
15 |
32% |
1% |
35% |
38% |
| Production
of free radicals |
5% |
30% |
7% |
36% |
30% |
| Chronic
lung disease |
1% |
25% |
3% |
19% |
20% |
| Increase
in concentration of enzymes |
6% |
32% |
10% |
29% |
19% |
| Loss
of motor activity |
1% |
I7% |
4% |
35% |
15% |
These frequencies represent the compilation
of health problems of experimental animals reported in the
literature reviewed
ANALYSIS OF RESULT
The finding showed that exposure
to pollutants from coal, firewood, gas, and kerosene stoves
produced several health problems including influenza epidemics,
pneumonia, asthma, lung cancer, cardiovascular diseases, chronic
cough, wheezing, breathlessness, hair loss, ataxia, confusion,
pneumonia, eye irritation, non-productive cough, tachycardia,
arrhythmias and impaired lung function in man and animals.
The study established that indoor activities like cigarette
smoking and cooking with gas stoves produce nitrogen oxide,
while ultraviolet lamps, electrostatic precipitators, photocopying
machines and odour equipment increase the level of ozone in
the atmosphere. These gases as produced, especially ozone,
affect the respiratory tract particularly the pulmonary parenchyma,
causing metaplasia, fibrosis of the bronchiolar epithelium,
atelectasis, bronchopneumonia and emphysema. The study noted
that ozone at 740g/m3 (0.37ppm), sulfur dioxide at 960g/m3
(0.37ppm) had synergistic actions and individuals exposed
to them developed severe chronic obstructive lung diseases.
In addition, the study confirmed that ozone induces chromosome
breakage in man. The study established that increase in the
levels of ozone, sulfur dioxide, nitrogen oxide and carbon
monoxide in the environment killed green plants thereby giving
rise to the depletion of oxygen in the atmosphere. In rats
and dogs, the study found that exposure to ozone caused oedema
in rats, haemorrhage and death in dogs. Generally, there was
degeneration and destruction of type I alveolar cells as well
as that of type II epithelial cells in both rats and dogs.
Further findings showed that in cats, exposure to ozone resulted
in loss of ciliated epithelium in the upper respiratory tract,
swelling of type I alveolar cells, lysis of erythrocyte within
alveolar capillaries, as well as complete loss of motor activities.
Detailed analysis of the findings showed that exposure to
ozone in both man and animals resulted in the reduction of
alveolar cells particularly those that synthesize deoxyribonucleic
acid (DNA) and ribonucleic acid (RNA). In guinea pigs, the
finding identified increased rate of respiration and decrease
in tidal volume. In rabbits, the study identified metaplasia
and fibrosis of the lungs as well as inflammation of the cells
in the tonsil. Further analysis on the effects of exposing
experimental animals to ozone showed increase in the activities
of the enzymes that protect against intracellular oxidation
of unsaturated fatty acids.
This effect was noted in the experimental
animals both in vivo and in vitro. Also the finding showed
that ozone reacted with the animals' body to produce free
radicals that initiated peroxidation of other unsaturated
fatty acids. In all, the animals with vitamin E deficiency
were found more susceptible to the adverse effects of ozone
than others. Further, the study found that some experimental
animals lacked the ability to synthesize both deoxyribonucleic
acid (DNA) and ribonucleic acid (RNA) and as such, they were
highly susceptible to bacteria and virus infections.
The study noted that lung cancer
and cardiovascular diseases are common among individuals living
in areas where no demarcation exists between plants and residential
areas. The finding noted that gases like ozone, nitrogen oxide,
sulfur dioxide and carbon monoxide had lethal effects on green
plants. This effect caused a reduction in the amount of oxygen
the plants produced in the atmosphere. The study found that
constant smoke/fumes from coal and firewood affect the respiratory
organs as well as the reproductive system. It noted that 35%
of men who by the nature of their jobs were constantly exposed
to smoke /fumes from coal and firewood had reproductive health
problems. About 45% of women whose husbands worked as Cooks
and Stewards had problems with conception. Specifically, these
men who worked as Cooks were diagnosed with low semen quality.
The finding further confirmed that about 45 (55%) of the pregnant
women living in areas where coal, during winter, was used
to heat the living rooms had premature births, low birth weight
babies, and miscarriages and that 69 (36%) of others whose
pregnancies were carried to term had babies with congenital
abnormalities.
The finding also noticed that individuals
as well as animals exposed to ozone had difficulty in synthesizing
DNA and RNA. Health problems like phlegm, chronic cough, wheezing,
breathlessness, hair loss, ataxia, confusion, pneumonia, eye
irritation, non-productive cough, tachycardia, arrhythmias
and impaired lung function were common among individuals exposed
to nitrogen oxide, sulfur dioxide and carbon monoxide. The
study noted that experimental animals when exposed to nitrogen
oxide and sulfur dioxide developed several health problems.
For instance, in cats, nitrogen oxide caused erythrocyte lysis
with alveolar capillaries and a breakdown of capillary endothelium
while exposure to sulfur dioxide resulted in swelling of type
I alveolar cells as well as loss of ciliated epithelium. In
rabbits, exposure to sulfur dioxide caused inflammation of
the cells in the tonsil. Generally, animals exposed to nitrogen
oxide and sulfur dioxide exhibited impaired phagocytic properties
in the pulmonary alveolar macrophages and also had complete
loss in motor activities. As a result, the animals suffered
decrease in resistance to bacteria infections. The Tables
below contain the compilation of the health problems of individuals
and animals exposed to domestic energy as noted in the study.
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DISCUSSION
The study highlighted the types of
health problems human beings and animals experience when exposed
to pollutants from different types of domestic energy. The
finding showed that gas stoves, kerosene stoves, firewood,
coal, electric stoves, cigarette smoking, ultraviolet lamps,
electrostatic precipitators, photocopying machines and odour
control equipment all emit ozone, nitrogen oxide, sulfur dioxide,
and carbon monoxide which adversely affect health. The study
found that exposure to coal and firewood produced more health
problems than other types of domestic energy. This finding
confirms that of Goran, et al. (1995), Romm and Ervin (1996),
Selevan ,et al. (1995), and Spin, et al. (1993), which observed
that exposure to smoke/fumes from coal and firewood produce
more health problems than others and that the effects are
more on the respiratory organs. Goran, et al. (1995), as well
as Dejmek, et .al. (1995) Selevan et al. (1995) found adverse
health effects on the reproductive systems. In man, exposure
caused low sperm count while in women, exposure caused miscarriages
and infertility. This health problem may be as a result of
the large amounts of pollutants generated by burning coal
and firewood, which were the main sources of energy used.
Subsequently, coal and firewood produce more ozone and nitrogen
oxide than other sources of domestic energy ( Coffin and Gardner
1972, and Goldberg et. al. 1996). These authors found that
exposure to ozone and nitrogen oxide gives more health problems
than other pollutants. Rasmussen (1992) identified that health
problems like phlegm, chronic cough, wheezing, breathlessness,
hair loss, ataxia, confusion, pneumonia, eye irritation, non-productive
cough, tachycardia, arrhythmias and lung cancer were common
among individuals exposed to ozone and nitrogen oxide.
Four important issues were noted
in this study. First, respiratory tract mortality levels were
significantly high in both man and animals. The study showed
that the larger the amount of pollutants generated, the higher
the respiratory tract mortality levels. This is consistent
with the views of (Kagawa, and Toyama 1975, Ko 1996, Ng et.al.1993
Spin et.al. 1993 Freeman et.al.1973, and Yoko 1974). Secondly,
the finding showed that exposure of man and animals to ozone
reduces their resistance to bacterial infection. This observation
agrees with that of Coffin, and Gardner (1972) Goran et al.
(1995), White et al (1976) and Stephen et al.(1973) in which
low immunity was noted as a result of the general impairment
of the phagocytic properties of microphages on microorganisms.
As a result, microorganisms continuously invade the immune
system. The study found that in such animals, that they develop
complete loss of motor activities. This view is consistent
with that of (Coffin, and Gardner, 1972). Thirdly, exposure
to high levels of pollutants directly reduces growth in children
( Kagawa. and Toyama 1975, longevity in adult) Graedal 1978,
and Holland et al. 1979). Also, exposure to high levels of
pollutants retard the sexual capacities in man ( Goran et.
al. 1995, and Selevan et. al. 1995), and also that in animals
( Stephen et al. 1973, and Freeman et al. 1973). Exposure
also increases miscarriages in women (Fetner et.al.1962 and
Dejmek et al 1995). Additionally, this exposure caused mothers
to give birth to children with congenital abnormalities (
Dejmek et al 1995). The study argues that this condition in
which some babies were born with congenital abnormalities,
may be as a result of the effects of ozone on chromosomes.
Ozone induces the breakage of chromosomes by adversely affecting
the synthesis of deoxyribonucleic acid (DNA) and ribonucleic
acid (RNA) in living things (Fetner et al 1962). The living
things exposed to high levels of pollutants were susceptible
to bacteria and virus infections. The findings are consistent
with that of Stephen et al. (1973), Freeman et al. (1973),
Yoko (1974), and Coffin and Gardner (1972) in which laboratory
animals exposed to ozone and nitrogen oxide presented faulty
motor activities. Finally, individuals exposed to pollutants
from coal and firewood presented with similar health problems
as those exposed to cigarette smoking, ultraviolet lamps,
electrostatic precipitators, photocopying machines and odour
control equipment. This agrees with the findings of Coffin
and Gardner, (1972), Klassen (1980), Ng et al.(1993), and
Radim et al.(1966).
Additionally, respiratory tract problems
were common among individuals living in areas where there
is no demarcation between plants and residential quarters.
Specifically, lung cancer and cardiovascular diseases were
common among individuals living in these areas. This condition
may be as a result of the quantity of oxygen available to
the lungs during respiration. The finding noted that gases
like ozone, nitrogen oxide, sulfur dioxide and carbon monoxide
exterminate green plants thereby reducing the amount of oxygen
that the plants can produce in the atmosphere. Depletion of
oxygen levels in the atmosphere may reduce the amount of oxygen
reaching the lungs during respiration. This can cause impaired
lung function. This finding confirms that of (Ko, 1996, Nakazawa
1990 and Rasmussen, 1992).
The findings have important implications
on the health status of all living things in Nigerian society.
This is because many individuals especially in rural areas
do not have clear demarcation between the living apartments
and plants. In addition to this, most individuals who have
no kitchen, cook under these trees. In many of the living
quarters, ventilation is deficient and at times, people cook
and sleep in the same room.
The study recommends educating individuals
on the risks of excessive exposure to domestic energy. At
the same time, since there is inadvertent exposure of individuals
to domestic energy as a result of the living conditions and
gender roles, the paper recommends periodic clinical and epidemiological
studies to ascertain the extent of the problem in Nigerian
society. This is necessary because the bulk of the study was
from developed countries, with little or nothing from developing
countries including Nigeria.
The paper also recommends cooking
in the open and less crowded areas so as to enhance the atmospheric
absorption of pollutants produced by the use of domestic energy.
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