Showing posts with label mercury. Show all posts
Showing posts with label mercury. Show all posts

Tuesday, June 29, 2021

Lichens as indicators of less air pollution in and around Ranchi city, India.

 

Ranchi is one of the 100 cities chosen as part of India’s smart cities program.

by 

Dr. Nitish Priyadarshi

Assistant Professor, 

Department of Geology,

Ranchi University,

Ranchi

India.

emaiil: nitish.priyadarshi@gmail.com 














Urbanization and migration of people from rural areas to the Ranchi city has badly affected the environment of the city which was earlier known as summer capital of Bihar/ Jharkhand united due to its healthy climate and less pollution. Ranchi is the capital of the Jharkhand, formed in 2000, along with Chhattisgarh, and is one of the 100 cities chosen as part of India’s smart cities program. From the time the state was formed in 2000, the number of vehicles in the city has increased 20 times, contributing to the increase in air pollution. With an increase in population – this erstwhile hill station is now dealing with haphazard construction, insufficient systems for solid waste management leading to open burning and an increase in emissions from transport. Other sources include ones such as the burning of firewood and other organic material for heating and cooking, as well as the open burning of garbage and refuse. The main types of pollutants found in the air in Ranchi would be ones that arise from the number of different combustion sources. These would include materials such as black carbon and volatile organic compounds (VOC's), both of which find origin in the incomplete combustion of both fossil fuels as well as organic material, and as such will be emitted from sources ranging from car engines, factory processes to even the burning of firewood or other raw materials. Some examples of VOC's include chemicals such as benzene, toluene, xylene, methylene chloride and formaldehyde.

 

Other pollutants would be ones such as nitrogen dioxide (NO2), sulfur dioxide (SO2) alongside polynuclear aromatic hydrocarbons, polychlorinated biphenyls, dioxins, furans and even heavy metals such as lead, mercury and cadmium. 

 

Nowadays, more than half of the human population live in urban areas and this number is increasing. This huge and often unregulated phenomenon has changed dramatically the environmental conditions of previous rural and natural areas, causing atmospheric and acoustic pollution, loss of biodiversity and climatic alterations, with harmful consequences for ecosystem functioning and human health.

Photographs posted here are from different areas near to Ranchi city. From Ranchi city lichens are mostly absent. In forest areas lichens are still found on the rocks, and trees indicating good air quality.

The earliest accounts of the high  sensitivities  of lichens to atmospheric pollution appeared around the peak of the Industrial Revolution in western Europe. Grindon (1859) in Manchester and Nylander (1866) in Paris both associated the disappearance of lichens from their respective cities with the grossly polluted town air , smoke and sulphur dioxide then being major components of the pollution.   

Fresh, clean air is wonderful to breathe in. Without the health risks of air pollution, fresh air feels great for our lungs.  Lichens love clean air too- infact their sensitivity to air pollution means they make great air quality indicators.

Basically, lichens depend on atmospheric moisture: rain, fog and dew for growth. There are slow in growth and very sensitive towards the changing environmental conditions. Since, they absorb water and essential nutrients from atmosphere instead of from soil, hence they respond in altered manner to increased concentrations of pollutants in air. Comparison of lichens growth in polluted and healthy environment, a clear cut change in growth as well as addition or reduced growth can be observed.

 

Like small signposts, these curious organisms can tell us a lot about the air we are breathing. Butterflies, nematodes, frogs, and toads are very good indicators of environmental pollutants, but lichens are easier to study and are quicker to respond to environmental change.

Next time you are on a walk, you can look around for the types of lichens that grow in your area. As a rule of thumb, the smaller the size and less variety of lichens in an area, the more polluted is the environment.  Main air pollutants that affect lichen growth are nitrogen, sulphur dioxide, fluorides, ozone, hydrocarbons, and metals such as copper, lead, and zinc.

Lichens look like spots or clumps of colour, like someone has splashed paint onto a branch of a tree. Their colours range from green to brown to white to russet red. Even in these colours, lichens can be understated additions to tree trunks and rocks. Because lichens have no roots or protective surface, they cannot filter what they absorb, so whatever is in the air is taken straight inside. If there are pollutants, it can accumulate in the lichen and can become toxic very quickly.

We breathe in harmless nitrogen gas all the time - in fact it makes up a large part of Earth's atmosphere. But when nitrogren is heated and combined with oxygen (as it is in a car engine), nitrogen oxides are created.

Nitrogen dioxide in the air can be a powerful polluter and becomes harmful for human health in high concentrations.  

In high concentrations, sulphur dioxide can irritate the mucus lining of the eyes, nose, throat and lungs. Exposure to sulphur dioxide may cause coughing and tightness in your chest. People with asthma are more sensitive to sulphur dioxide pollution.  

Throughout history, people have used lichens for food, clothing, dyes, perfume additives, medicines, poisons, tanning agents, bandaging, and absorbent materials. Compounds unique to lichens are used in perfumes, fiber dyes, and in medicines for their antibacterial and antiviral properties.

Lichens have been used in the treatment of diverse diseases like arthritis, alopecia, constipation, kidney diseases, leprosy, pharyngitis rabies, infection, worm and infestation. The medicinal utility of lichens is regarded to presence of secondary compounds like of usnic acid and atranorin.  It is also used in treating wounds, skin disorders, respiratory and digestive issues, and obstetric and gynecological concerns.

References:

Bell, J.N.B. and Treshow, M. (2002). Air pollution and plant life. John Wiley & Sons, Ltd. 309-342.

Grindon, L.H. (1859). The Manchester flora. London: W. White.

Nylander,W. (1866). Les lichens du Jardin du Luxembourg. Bulletin de la Societe Botanique de France 13,364-372

https://www.nhm.ac.uk/discover/nature-and-pollution-what-lichens-tell-us-about-toxic-air.html

https://www.amnh.org/learn-teach/curriculum-collections/young-naturalist-awards/winning-essays/2007/lichens-as-indicators-of-vehicle-pollution.

https://www.iqair.com/india/jharkhand/ranchi


Thursday, October 28, 2010

Coal mining destroying the environment and health of people in Jharkhand state of India.

Longevity has reduced drastically.
by
Dr. Nitish Priyadarshi
Children are more affected.
Contaminated community water source with low pH value
Polluted river bed.
Atmosphere is also polluted.
Black river.
Dust is every where.

The health hazards, degeneration of the health conditions of the people especially tribal women and children and water contamination is one of the most serious impacts of coal mining in Jharkhand.

Jharkhand is an area of abundant coalmines. Most of the coalmines are situated in Hazaribag, Chatra, Palamau, Rajmahal, Dhanbad and Ranchi district. Mighty Damodar River and its tributaries flow through these coalmines.

Jharkhand is the homeland of over a dozen indigenous communities, the major ones being the Santhals, the Mundas, the Oraons and the Hos. Most of their populations are concentrated around the coal mines area.

Today, the picture of Damodar River or Damuda, considered a sacred river by the local tribals, is quite like a sewage canal shrunken and filled with filth and rubbish, emanating obnoxious odours. This river once known as “River of Sorrow” for its seasonal ravages, has now turned into a “River of Agony” from the environmental point of view.

Due to extensive coal mining and vigorous growth of industries in this area water resources have been badly contaminated. The habitants have, however, been compromising by taking contaminated and sometimes polluted water, as there is no alternative source of safe drinking water. Thus, a sizeable populace suffers from water borne diseases.

The Damodar river basin is a repository of approximately 46 per cent of the Indian coal reserves. A high demographic and industrial expansion has taken place in last three decades in the region. Exploitation of coal by underground and open cast mining has lead to a great environmental threat in this area.

Besides mining, coal based industries like coal washeries, coke oven plants, coal fired thermal power plants, steel plants and other related industries in the region also greatly impart towards degradation of the environmental equality vis-a-vis human health.
The most affected part of the natural- resources is water in this region and thereby human health.

Damodar is a small rainfed river (541 km long) originating from the Khamerpet hill (1068 m), near the trijunction of Palamau, Ranchi, and Hazaribag districts of Jharkhand. It flows through the cities Ramgarh, Dhanbad, Asansol, Durgapur, Bardwan and Howrah before ultimately joining the lower Ganga (Hooghly estuary) at Shayampur, 55 km downstream of Howrah. The river is fed by a number of tributaries at different reaches, the principal ones being Jamunia, Bokaro, Konar, Safi, Bhera, Nalkari and Barakar.

The total catchment area of the basin is about 23,170 km of this, three- fourth of the basin lies in Jharkhand and one-fourth in West Bengal. The major part of the rainfall (82%) occurs during the monsoon season with a few sporadic rains in winter. Damodar basin is an important coal bearing area and at least seven coal fields are located in this region.

High increase in the population i.e. from 5.0 million (1951) to 14.6 mil- lion (1991) has been observed during the last four decades which is the out- come of the heavy industrialization in this basin mainly in coal sector.

Due to easy availability of coal and prime cooking coal, several thermal power plants, steel plants have grown up. Discharge of uncontrolled and untreated industrial wastewater, often containing highly toxic metals is the major source of pollution of Damodar River.

Mine water and runoff through overburden material of open cast mines also contribute towards pollution of nearby water resources of the area. Huge amount of overburden materials have been dumped on the bank of the river and its tributaries, which finally get spread in the rivers especially in the rainy season. These activities have resulted in the visible deterioration of the quality of the river water.

The large scale mining operations going on this region have also adversely affected ground water table in many areas with the result that yield of water from the wells of adjoining villages has drastically reduced. Further, effluents discharged from the mine sites have also seriously, polluted the underground water of the area.

Mine water does not have acid mine drainage problem. It may be due to the fact that coal deposits of this basin are associated with minor amounts of pyrites and contain low Sulphur. Iron content in this water is found in the range of 1 to 6 mg/1. Though it is not alarming but it may be toxic to some aquatic species. Mine water is generally bacterially contaminated which is clear from the value lying in the range of 100 to 2500.

Heavy metals like manganese, chromium, lead, arsenic, mercury, floride, cadmium, and copper are also found in the sediments and water of Damodar river and its tributary like Safi River. Permian coal of this area contains all these toxic elements in considerable amount. Presence of lead is high above the alarming level i.e. 300 ppm (parts per million) in the coals of North Karanpura coal field.

The study warned that long term exposure to the lead present in that area might result in general weakness, anorexia, dyspepsia, metallic taste in the mouth, headache, drowsiness, high blood pressure and anaemia etc.

The Damodar sediments are deficient in calcium and magnesium and rich in potassium concentration. Titanium and iron are the dominant heavy metals followed by manganese, zine, copper, chromium, lead, arsenic, and mercury. Other heavy metal like strontium shows more or less uniform concentration throughout the basin. Average concentration of strontium in the sediments of the river is 130 ppm. Silica is also high in the sediments of Damodar River and its tributary. The value is 28ppm.

Arsenic in the water ranges from 0.001 to 0.06 mg/1, mercury ranges from 0.0002 to 0.004 mg/1, floride ranges from 1 to 3 mg/1.

It is obvious that due to extensive coal mining and vigorous growth of industries in this area water resources have been badly contaminated. The habitants have, however, been compromising by taking contaminated and sometimes polluted water, as there is no alternate source of drinking water. Thus, a sizeable populace suffers from water borne diseases.

As per the heath survey of the local people, the most common diseases are dysentery, diarrhoea, skin infection, worm infection, jaundice, and typhoid. Dysentery and skin infections occur in high percentage in the area. If proper steps are not taken up the total population mostly tribals will be on the verge of extinction.

The Agaria tribe and other tribes that inhabit the coalfields of North Karanpura and East Parej, India are faced with severe water contamination. In East Parej, more than 80% of the community lives in poverty. Water for the community comes from hand pumps, dug wells, local streams and rivers. In some areas, mine water and river water is supplied through pipes. But most people are dependent on other sources - which are contaminated - for their water needs. Women and children in these areas have to travel more than 1 kilometer to fetch safe drinking water. Most villagers are left with no choice but to drink contaminated water. Dug wells are generally dried up during the summer and winter. Natural drainage is obstructed and diverted due to the expansion of mining. Villagers in these areas have no concept of how to preserve and purify rainwater.

Our longevity has reduced drastically, said Phulmani Kujur a 38 year old women of East Parej coal field. We avoid taking bath everyday, there are a gap of 5 to 10 days, and do not drink water adequately due to water pollution, said Mahesh a Santhal Tribe of the same village.

Study reveals that average longevity of women in East Parej coal field was found to be 45 and in most of the villages only one or two women had crossed the age of 60. In North Karanpura coal field average longevity of male is 50 years and that of female is 45 years.

The number of deaths in a period of five years, in East Parej, also reveals shocking figures in Dudhmatia village: 6 out of average 80 people, in Agariatola village: 12 out of average 100 people, in Lapangtandi: 13 out of average 115 people, and in Ulhara: 9 (seven were children) out of average 80 people.

Villagers of Agariatola complain that their only source of drinking water has been damaged due to dumping of overburden and expansion of open cast mine. Villagers have no substitute but to drink the water of well provided by the miners which according to the villagers is not good in taste with foul smell and yellow colour. Villagers of Dudhmatia of the same coal field complained about foul smell present in the water of the only hand pump.

Average kilometers travel by the villagers to retrieve safe drinking water is 1 to 2 kilometers. In summer season we have to travel even more to have safe drinking water, alleged women of the affected areas. Sometimes organizations supply us the water through tankers but they are not sufficient, said villagers of the East Parej, North Karanpura and South Karanpura coal field.

In the absence of even primary hospital and doctors in East Parej (there is only one hospital run by Central Coalfields Limited) villagers are more dependent on the quacks as they are the regular visitor in the remote area.

Our children are the most affected due to living in such unhygienic conditions and filth, said villagers of the North Karanpura coal field, one of the biggest coal mines of the area.
These are one of the most common situations in all the coal mines area of Jharkhand. Most of the population in North Karanpura coal field is dependent on Safi River for drinking and other domestic purposes. This river is polluted because of the coalmines waste dumped along the banks of the river at different locations. Water of the area is contaminated with toxic metals like arsenic and mercury. Manganese has crossed the toxic level ( 3.6 milligram per liter against the permissible level of 0.5 mg/l.). According to WHO (World Health Organization) high manganese may affect with the symptoms like lethargy, increased muscle tone and mental disturbances.

Health survey done among the boys and girls in a local school it was found that majority of the children (both tribal and non-tribal) are lethargic may be due to inhalation of coal dust and consumption of contaminated water containing high manganese.

In the coal fields of Jharkhand most of the tribal women are employed in secondary activities such as loading and unloading of the coals. According to Chotanagpur Adivasi Sewa Samiti, a NGO working in Hazaribag district, constant contact with dust pollution and indirectly through contamination of water, air, etc. cause severe health hazard to women workers. As majority of the women workers are contract labourers, and paid on daily wage basis there is no economic security or compensation paid due to loss of workdays on account of health problems. Even during pregnancy women has to work in hazardous conditions amidst noise, air pollution that have adverse affects on their offspring.

Malaria is very common. It is found that there are numerous ditches, stagnant mine water, and open tanks breeding all the species mosquitoes. Majorities of the death were attributed to malaria. Next come the skin diseases such as eczema, rashes on the skin etc. it may be due to lack of care and cleanliness or due to the presence of nickel in drinking water. In some area like East Parej high nickel (0.024 mg/l) have been reported in the water. According to WHO nickel is a common skin allergen.

Many especially children of the coal fields suffer from dysentery and diarrhoea. According to the residents of the coal field, it is because of consuming contaminated water. About 60% of the local people are affected with seasonal allergies. Other diseases found were tuberculosis, headache, joints pain (pain begins at the age of 5 to 10 years, especially in North Karanpura), gastric, cough and cold and asthma.

When asked from the villagers in East Parej and North Karanpura about what do they think about future, they replied situation is going to worsen. They are not very confident about their life span. There is always a threat of displacement due to expansion of coal mining, which finally affects their longevity.

Fluoride, arsenic, nickel, sulfate, and manganese pose the biggest threats to water sources in the region. They have been shown to cause adverse effects when consumed over a long period of time. Health care facilities can improve the situation immensely, but it is more desirable to maintain the philosophy that prevention is better than the cure. Medical checkups can be adopted to improve the situation. Installation of pollution control equipment is needed for monitoring and analyzing pollution data. Seeing that nearly all the water sources under study are contaminated, the only short term solution for safe drinking water is rain water harvesting. Indigenous methods, such as disinfecting and purifying water with the help of medicinal plants, can be adopted for purifying water in ways that are cost efficient.

The international community can also help by providing funds to carry out research and analysis of the problem in more detail. Publishing these results can help other communities around the world figure out the best methods for improving water quality. Awareness programs should be given major importance.

These research project was sponsored to the author by Ministry of Science and Technology, Government of India and Green Grant Fund, U.S.A. and supported by Earth Day Network, U.S.A

Wednesday, January 6, 2010

Importance of Medical Geology in present environment.

It is now a globally emerging discipline.
by
Dr. Nitish Priyadarshi
Humans live in lands. Most of them live in intimate contact with the immediate geological environment, obtaining their food and water directly from it. The unique geochemistry of these tropical environments have a marked influence on their health, giving rise to diseases that affect millions of people. The origin of these diseases is geologic as exemplified by dental and skeletal fluorosis, iodine deficiency disorders, trace element imbalances to name a few.

Medical Geology is an emerging scientific discipline that examines the impacts that geologic materials and processes have on human and ecosystem health. Medical Geology:
· Identifies and characterizes natural and anthropogenic sources of harmful materials in the environment.
· Predicts the movement and alteration of chemical, infectious, and other disease-causing agents over time and space.
· Provides an understanding of how people are exposed to harmful materials and describes what can be done to minimize or prevent such exposure.

The civilized existence of man is made possible by keeping him physically healthy through the application of medical knowledge. Although this is an important aspect of life, surprisingly little serious attention appears to have been given to it by the very persons who should have realized its important role in the study of the effects of various elements and metals on the human body.
Every day we eat, drink and breathe minerals and trace elements, never giving a thought to what moves from the environment and into our bodies. For most of us this interaction with natural materials is harmless, perhaps even beneficial, supplying us with essential nutrients. However, for some, the interaction with minerals and trace elements can have devastating, even fatal effects. These interactions are the realm of medical geology, a fast-growing field that not only involves geoscientists but also medical, public health, veterinary, agricultural, environmental and biological scientists. Medical geology is the study of the effects of geologic materials and processes on human, animal and plant health, with both good and possibly hazardous results.

The relationship between the Earth's surface that we humans inhabit and our health is under debate. The fact that a continuum and indelible link exists is not in doubt. We have obtained food, water, and shelter since Homo arrived, but in the twentieth century we have learned that disease as well as health may by derived from our environment.

The geochemical distribution and biochemical availability of the elements that are required for human existence are not uniformly distributed over the Earth's surface. For example, low concentrations of iodine (I) characterize the soils and rocks at high elevations and in limestone terrains. This is a natural global phenomenon. Medical acumen and geostatistical and epidemiological investigations have identified iodine as an essential nutrient. The thick necks that were depicted in ancient Chinese scrolls, and the cretinism found in mountainous regions, are now recognized as symptoms of the endemic disease goitre. Jharkhand and other Eastern states in India are Iodine deficiency zone. Reduction, but unfortunately not eradication, of this preventable malady is now possible through the use of iodine-enriched table salt and oils.

Fluorine (F), another element that is a constituent of some minerals, is now added to drinking water to minimize the development of dental caries, especially in children. Apart from the beneficial effects of maintaining a healthy oral cavity to aid mastication and minimize pain, it is probable that ingestion of fluorine in small amounts (parts per million) over a lifetime will stave off osteoporosis, or at least serve to preserve the mineral materials in the skeleton in old age. It was the recognition of a connection between high natural fluorine concentrations (100 ppm) in the drinking waters of certain localities in Oklahoma and India and overabundant calcium phosphate mineral deposition in the skeleton that most clearly illustrates the essential and continuing basic interactions between geology, geochemistry, medicine, and biochemistry. The fluorine effect, fully researched, led to applications aimed at reduction, if not prevention, of disease.

Radon is a naturally occurring colourless, odourless gas that is emitted from rocks containing minerals rich in the transuranic elements. The occupational health effects, in particular lung cancer, suffered by some European coal-miners who mine such rocks were ascribed to radiation, but may equally well have been induced by smoking. Granites that underlie portions of the north-east of the United States (New England) are known to contain minerals that emit radon. Recent epidemiological studies that measured environmental exposure (the average was less than 4 picocuries for the region) were not able to demonstrate an association between the incidence of lung cancer and sites where radon concentrations (possible doses) were elevated.
In its broadest sense, medical geology studies exposure to or deficiency of trace elements and minerals; inhalation of ambient and anthropogenic mineral dusts and volcanic emissions; transportation, modification and concentration of organic compounds; and exposure to radionuclides, microbes and pathogens.

Hippocrates and other Hellenic writers recognized that environmental factors affected geographical distributions of human diseases 2,400 years ago. And in 300 B.C., Aristotle noted lead poisoning in miners. Rocks and minerals have also been used for thousands of years to treat various maladies such as the plague, smallpox and fevers.

The geological profession has made considerable progress in studies on the distribution of elements, even in traces, in rock materials to understand their manner of evolution. A geochemist who takes to such studies rarely gives a thought as to which of the elements he has been examining are beneficial or harmful to the human race although the civilized existence of man requires a number of elements and metals. The soil which covers the underlying rock, in the process of weathering, concentrates some of these elements and even transfers some to plants growth on such soil, while groundwater which filters through the soil profile dissolves certain other elements. Civilized man, in order to coax more from the soil, adds fertilizers and uses pesticides for destroying pests which affect crop growth. Also with the good intention of keeping the human body in good conditions, he introduces certain elements in the form of drugs under medical advice. The geological factors which control the distribution and dissemination of these elements, as also their presumed therapeutical effects, is a factor of great importance to which geologists must direct their attention.

The types of rocks that form geologic units in the Earth’s crust supply most of the raw materials from which soils are formed and from which water derives it inorganic constituents. The compositions of what we eat and drink thus depend in part upon the compositions of the source rocks. The contents of individual trace elements vary widely with rock type. Chromium, titanium, nickel, and cobalt are conspicuously concentrated in low-silica igneous rocks that are quantitatively unimportant. Arsenic, iodine, molybdenum, and selenium are conspicuously concentrated in shale and clay. Metallic elements present in source rocks in small amounts-the so called minor elements or trace elements- have been shown to have important effects on human and animal health, resulting from their excess or deficiencies in soils, waters, and plants.

Rocks like Igneous, Sedimentary, and Metamorphics contribute trace elements to the water bodies like fluoride, Arsenic, lead, copper, mercury, zinc, etc. Jharkhand state in India provides an ideal opportunity for the study of the effect of geology on human health. The vast majority of the people of Jharkhand still live in rural areas within areas termed geochemical provinces. Very broadly, one could say that a geochemical province has characteristic chemical composition in soil, water stream sediments and rocks, enabling their delineation from others. The chemical composition is presumed to be have an impact on the health of the inhabitants of the particular geochemical province, particularly because of the fact that their food and water are obtained mostly from the terrain itself. This leads to the concept of "diseases of geochemical origin". Among these are dental fluorosis, iodine deficiency disorders (IDDs) and Arsenic toxicity based diseases.

Author has worked on distribution of trace elements in Permian coals of North Karanpura Coalfield of Jharkhand State of India and its environmental impact. It was found that concentration of arsenic in coal samples range from <0.01 to 0.49ppm with an arithmetic mean of 0.15ppm. (Priyadarshi, 2004). Concentration of arsenic is low compared to most world coals. Average ash% is very high (up to 32.51%). Average concentration of arsenic in the sediments of mine water was 1.4 ppm. Though the concentration of arsenic is low in the surface water ( 0.001-0.002 ppm) it may still affect the local habitants especially during summer season when the consumption of water increases many folds. Main source of arsenic in the water bodies is from the coals of the researched area. Elements like lead, barium, strontium, boron, etc. were also present in sufficient amount in the coals.

The low arsenic concentrations of the coal studied could be related to the geological characteristics of the source area in the basin and to a resulting low degree of arsenic mineralization (realgar or orpiment) of the synsedimentary solutions, which resulted in a paucity of arsenic in the system.

A detailed study has been presented on groundwater metal contents of Sahebgunj district in the state of Jharkhand, India with special reference to arsenic. Both tubewell and well waters have been studied separately with greater emphasis on tubewell waters. Groundwaters of all the nine blocks of Sahebgunj district have been surveyed for iron, manganese, calcium, magnesium, copper and zinc in addition to arsenic. Groundwaters of three blocks of Sahebgunj, namely, Sahebgunj, Rajmahal and Udhawa have been found to be alarmingly contaminated with arsenic present at or above 10 ppb.

Bakhari village, situated about 20 km from the Ranchi district headquarters in Jharkhand state , has a population of nearly 700, comprising mostly tribal and members of socially underprivileged groups. Two-thirds of the villagers have reportedly developed physical deformities as all the sources of drinking water in Bakhari have excess fluoride content.

It is to be expected that in areas characterized by metal-bearing formations, metals will also occur at elevated levels in the water and bottom sediments of the particular area. There is evidence that the high mercury content in rocks encountered in the catchment of La Grande River, Canada, may be responsible for high mercury levels in organisms (Boyle and Jonasson,1973). It was found that the Aphebian Shale in central and northern Quebec- near the headwaters of the La Grande- contained mercury levels averaging 0.5 ppm , which these authors regard as being high.

A study conducted by Colbourne et.al. (1975) confirmed that the stream sediment patterns for arsenic and copper in the Dartmoor area of South-West England may be correlated with significant enrichment of these elements in soils derived from rocks within the metamorphic aureole around the Dartmoor granitic intrusion. Previously it had been concluded that the source of arsenic within the metamorphosed country rocks was the result of hydrothermal activity during phases of granitic intrusion. Similarly, geothermal sources in North Island are a natural source for mercury enrichment.

All living tissues are composed mainly of eleven elements, but to remain viable, minute amounts of a few elements of the transition series also must be present. These act as mediators of the biocatalysts, the enzymes. The trace elements that have been most extensively studied are : Fe, Cu, Mn, Mg, Mo, and Zn. The body as it ages concentrates a large number of other elements; many of these, when present in excess, have been reported as being responsible for the introduction of cancer. Experiments reveal that nickel, cadmium, and some chromium compounds are true metal carcinogens. Arsenic has been strongly indicted as a primary human carcinogen. Asbestos may prove to be a carrier for the carcinogenic metals, nickel and chromium. In the 1980s, earth scientists helped medical scientists to recognize that there was more than one type of material called asbestos, and that the different asbestos materials are not equally carcinogenic. Chrysotile asbestos, for example, is commonly regarded as being less carcinogenic than amphibole asbestos. The last several years have seen renewed public attention on the potential health effects of asbesti form minerals that occur naturally as trace constituents in rocks or mineral deposits. For example, in 1999 the Seattle Post-Intelligencer brought nationwide media and scientific attention to asbestos-related health problems in residents of Libby, Mont. Many residents have diseases that have since been attributed to their exposure to amphibole asbestos minerals. The minerals were naturally inter grown with the vermiculite mined and processed at Libby.

Mercury is regarded as the most toxic metal, followed by cadmium, lead and others although there is no rigid order of toxicity. Contamination of the aqueous environment by cadmium appears to be less widespread than by mercury but has nonetheless hazardous effects on humans. During 1947 an unusual and painful disease of a “rheumatic nature” was recorded in the case of 44 patients from villages (e.g., Fuchu) on the banks of the Jintsu River, Toyama Prefecture, Japan. During subsequent years, it became known as the “itai-itai” disease (meaning “ouch-ouch”) in accordance with the patients shrieks resulting from painful skeletal deformities. However the cause of this disease was completely unknown until 1961, when sufficient evidence led to the postulation that cadmium played a role in its development.

Exposure to toxic levels of trace elements is one of the widespread forms of environmental health problems. Millions of people worldwide suffer health problems because they have been exposed to arsenic, lead, fluorine, mercury, uranium, etc. The devastation caused by excess arsenic in drinking water in Bangladesh, West Bengal India and elsewhere has been headline news. An estimated 25 to 75 million people are at risk of arsenosis in that region.

In Guizhou Province, China, the cool, damp autumn weather forces villagers to bring their harvests of chili peppers and corn indoors to dry. They hang the peppers over unvented stoves that, until the middle of the last century, had been fueled by wood. Due to the destruction of the forests, wood is now scarce so the villagers have turned to the plentiful outcrops of coal for heating, cooking and drying their harvests. But mineralizing solutions in this area have deposited enormous concentrations of arsenic - up to 35,000 parts per million - and other trace elements in these coals.

The chili peppers dried over these arsenic-rich coals are a key component of the villagers' diet and, unfortunately, their principal source of arsenic. Thousands of villagers are now suffering from arsenic poisoning and exhibit typical symptoms, including hyperpigmentation (flushed appearance, freckles), hyperkeratosis (scaly lesions on the skin, generally concentrated on the hands and feet), Bowen's disease (dark, horny, pre-cancerous lesions of the skin), and squamous cell carcinoma.

Most trace elements in drinking water are of concern from a public health point of view because of potential for excess above recommended limits. However, some trace elements are essential to health and so are required to be present at certain concentrations in drinking water or food. Iodine is one such essential element. Deficiency in dietary iodine can lead to a number of iodine-deficiency disorders (IDDs) in humans. No regulations or recommendations are placed on concentrations of iodine in drinking water because such standards are imposed to regulate upper rather than lower limits.

As iodine is an essential element for humans, there is considerable interest in its environmental geochemistry. It is unique amongst the elements in that most iodine in the terrestrial environment does not derive from normal weathering of crustal rocks but derives through volatilisation from the oceans, which represent the major reservoir of iodine on the Earth. As a result of this major source of environmental iodine, soils in coastal regions are strongly enriched in iodine, while those far removed from marine influence generally have low iodine contents.

Iodine concentrations in groundwaters (and surface waters) largely lie in the range 0.01–70 µg/l, depending on geographical location and local geology and soils. Higher concentrations can be found in saline waters such as coastal and arid or semi-arid areas. The principal sources of iodine in groundwater are aquifers and soils and the atmosphere. Iodine is found in low concentrations in most rocks because it is incompatible with most rock-forming (silicate) minerals. It may be present in higher concentrations in sulphide minerals, organic matter and iron oxides. Hence sulphide-, organic- and iron- rich rocks and soils tend to have the highest concentrations. Mineral veins (rich in sulphide minerals) and hydrothermal solutions are also relatively concentrated. Of the sedimentary rocks, muds and shales typically have the highest concentrations. Weathered rocks often have higher iodine concentrations than their pristine equivalents, presumably due to interaction with groundwater.

Uranium is present in the environment in low concentrations in all parts of the world, the most abundant deposits being in sedimentary rocks. The main areas of the world with rich uranium deposits are the Colorado plateau in Wyoming in the United States, Blind River and Beaver Lodge districts in Canada, the Erz Mountains in central Europe, the Ural Mountains in Russia, the Rand Mountains in South Africa, the French Alps, Radium Hill in Australia, Jadugoda in India and the Pirinean Mountain range in Spain. Open pit mining has been the preferred way of uranium production, but some deposits are too deep for this type of mining because it necessitates deep underground mining. The range of uranium content of the most ores is between 0.1-1.0% of U3O8. However, much higher grades are frequently found, presenting higher radiation hazards to miners from beta radiation from the ore and inhalation of uranium dust suspended in the air of the mining environment.

Normal functioning of the kidney, brain, liver, heart, and numerous other systems can be affected by uranium exposure, because in addition to being weakly radioactive, uranium is a toxic metal.

As we contemplate an increase in world population and an ageing population, it becomes apparent that evaluating long-term exposure to natural materials in our environment makes cooperation and coordinated study of geology and medicine essential. The intertwining of these areas of knowledge should enable us to continue to improve health and combat disease, and contribute to better living conditions for all people.

Medical geology, a long-recognized but perhaps underutilized discipline, presents the geoscience community with tremendous opportunities for collaborative work with the biomedical and ecological research communities. Such collaborations have great potential to help understand, mitigate and possibly eradicate environmental health problems that have plagued humans for thousands of years.

Reference:

Boyle, R. W., Jonasson, I.R. 1973. The geochemistry of arsenic and its use as an indicator element in geochemical prospecting. J. Geochem. Explor.2, 251-296.

Colbourne, P., Alloway, B.J., Thornton, I., 1975. Arsenic and heavy metals in soils associated with regional geochemical anaomalies in southwest England. Sci. Total Environ. 4, 359-363.

Forstner,U. and Wittmann, G.T.W. 1979. Metal Pollution in the Aquatic Environment. Springer-Verlag Berlin Heidelberg, New York.

Priyadarshi, N. 2004. Distribution of arsenic in Permian Coals of North Karanpura coalfield, Jharkhand. Jour. Geol. Soc. India, 63, 533-536.

Radhakrishna, B.P. 2005. Medical Geology. Jr. of The Geological Society of India, v.66, no.4. p.395.

http://energy.er.usgs.gov/health_environment/medical_geology/
http://www.mindfully.org/Nucs/DU-Medical-Effects-Mar99.htm
http://www.wateraid.org/documents/plugin_documents/iodine1.pdf.pdf
http://gsa.confex.com/gsa/2009AM/finalprogram/abstract_161522.htm
http://www.agiweb.org/geotimes/nov01/feature_medgeo.html
http://science.jrank.org/pages/47843/medical-geology.html

Wednesday, July 8, 2009

Ganga river pollution in India- A brief report.

Ganga is becoming toxic day by day.
by
Dr. Nitish Priyadarshi



Most ancient civilizations grew along the banks of rivers. Even today, millions of people all over the world live on the banks of rivers and depend on them for their survival. All of us have seen a river - large or small, either flowing through our town, or somewhere else. Rivers are nothing more than surface water flowing down from a higher altitude to a lower altitude due to the pull of gravity. One river might have its source in a glacier, another in a spring or a lake. Rivers carry dissolved minerals, organic compounds, small grains of sand, gravel, and other material as they flow downstream. Rivers begin as small streams, which grow wider as smaller streams and rivers join them along their course across the land. Eventually they flow into seas or oceans. Unfortunately most of the world's major rivers are heavily polluted.

The pollution of environment is the ‘gift’ of the industrial revolution. Prior to this the agrarian cultures created significant environmental deterioration in the form of soil erosion- through deforestation and overgrazing. The environmental degradation is a by product of modern civilization.

There has been a steady deterioration in the quality of water of Indian rivers over several decades. India’s fourteen major, 55 minor and several hundred small rivers receive millions of litres of sewage, industrial and agricultural wastes. Most of these rivers have been rendered to the level of sewage flowing drains. There are serious water quality problems in the cities, towns and villages using these waters. Water borne diseases are rampant, fisheries are on decline, and even cattle are not spared from the onslaught of pollution.
According to World Wide Fund for Nature (WWF) five rivers in Asia serving over 870 million people are among the most threatened in the world, as dams, water extraction and climate change all take their toll.
The Ganges, Indus, Yangtze, Salween-Nu and Mekong-Lancang rivers make up half of the WWF’s “top ten” most threatened river basins.
India has a large number of rivers that are lifelines for the millions living along their banks. These rivers can be categorized into four groups:
1.Rivers that flow down from the Himalayas and are supplied by melting snow and glaciers. This is why these are perennial, that is, they never dry up during the year.
2.The Deccan Plateau rivers, which depend on rainfall for their water.
3.The coastal rivers, especially those on the west coast, which are short and do not retain water throughout the year.
4.The rivers in the inland drainage basin of west Rajasthan, which depend on the rains. These rivers normally drain towards silt lakes or flow into the sand.
River Ganga (Ganges) of India has been held in high esteem since time immemorial and Hindus from all over the world cherish the idea of a holy dip in the river under the faith that by doing so they will get rid of their sins of life. More than 400 million people live along the Ganges River. An estimated 2,000,000 persons ritually bathe daily in the river. Historically also, Ganga is the most important river of the country and beyond doubt is closely connected with the history of civilization as can be noticed from the location of the ancient cities of Hardwar, Prayag, Kashi and Patliputra at its bank. To millions of people it is sustainer of life through multitude of canal system and irrigation of the wasting load. Hundreds of the villages and even the big cities depend for their drinking water on this river. It is believed, a fact which has also been observed, that the water of Ganga never decays even for months and years when water of other rivers and agencies begins to develop bacteria and fungi within a couple of days. This self purification characteristics of Ganga is the key to the holiness and sanctity of its water. The combination of bacteriophages and large populations of people bathing in the river have apparently produced a self-purification effect, in which water-borne bacteria such as dysentery and cholera are killed off, preventing large-scale epidemics. The river also has an unusual ability to retain dissolved oxygen.
With growing civilization and population all over how long Ganga will retain its self purification characteristics only time can judge.
River source:
The Gangotri Glacier, a vast expanse of ice five miles by fifteen, at the foothills of the Himalayas (14000 ft) in North Uttar Pradesh is the source of Bhagirathi, which joins with Alaknanda (origins nearby) to form Ganga at the craggy canyon-carved town of Devprayag. Interestingly, the sources of Indus and the Brahmaputra are also geographically fairly close; the former goes through Himachal Pradesh and fans out through Punjab and Sind (Pakistan) into the Arabian Sea. The latter courses for most of its tremendous length under various names through Tibet/China, never far from the Nepal or Indian borders, and then takes a sharp turn near the northeastern tip of India, gathers momentum through Assam before joining the major stream of the Ganga near Dacca in Bangladesh to become the mighty Padma, river of joy and sorrow for much of Bangladesh. From Devprayag to the Bay of Bengal and the vast Sunderbans delta, the Ganga flows some 1550 miles, passing (and giving life to) some of the most populous cities of India, including Kanpur (2 million), Allahabad, Varanasi, Patna, and Calcutta (14 million).

The largest tributary to the Ganga is the Ghaghara, which meets it before Patna, in Bihar, bearing much of the Himalayan glacier melt from Northern Nepal. The Gandak, which comes from near Katmandu, is another big Himalayan tributary. Other important rivers that merge with the Ganga are the Son, which originates in the hills of Madhya Pradesh, the Gomti which flows past Lucknow.
Previous Work:
A number of investigations have been carried out on the physiochemical and biological characters of the Ganga. Lakshminarayana (1965) published a series of papers reporting the results of studies carried out at Varanasi during the period between March, 1957 and March, 1958. it was observed by him that the values of the most of the parameters decreased during rainy season while no marked variation was observed during winters and summers.
In the same year Chakraborty et.al. (1965) from Kanpur reported the water quality of Ganga at J.K. Rayon’s water intake point and at Golaghat and Bhairoghat pumping stations situated at the upstream of the river. It was concluded that the water quality gradually deteriorated as it passes from Bhairoghat pumping station to the J.K. Rayon water intake point in summers because in this stretch the river received waste waters from number of sewage drains.
A year later Saxena et.al. (1966) made a systematic survey of the chemical quantity of Ganga at Kanpur. According to the study, the biological oxygen demand, i.e. B.O.D. varied from 5.3ppm (minimum) in winter to 16.0ppm (maximum) in summer. The chloride ranged between 9.2 and 12.7 ppm and the river was found to be alkaline in nature except in rainy season. He concluded that the tanneries significantly increased the pollution load of river as they discharge huge amounts of effluents containing organic wastes and heavy metals. It was further reported that forty five tanneries, ten textile mills and several other industrial units discharged 37.15 million gallon per day of waste water generating BOD load of approximately 61630 Kg/day.
Subsequently Agarwal et.al.(1976) studied the bacteriological population of the river water and concluded that addition of untreated waste and sewage was responsible for the presence of pathogenic organisms posing threat to the residents of the Varanasi city.
Hydrobiological features of the river Ganga was studied by Pahwa and Mehrotra (1966). The authors studied a stretch of 1090 kms. of river Ganga extending from Kanpur in west to Rajmahal, in Jharkhand state, in the east. They reported that the turbidity was maximum (1100-2170 ppm) in monsoon and minimum ( less than100 ppm) during January to June. The pH of the river water ranged between 7.45 (minimum) during June to August and 8.30 (maximum) during January to May. The dissolved oxygen, i.e. D.O. count ranged from 5.0 to 10.5 ppm with maximum values during January and February. While the minimum values were recorded in monsoon.
Bhargava (1982) in a survey of total length of the river Ganga found that quality index was far above the prescribed limit at Kanpur. He further found that the Ganga water was having unusually fast regenerating capacity by bringing down B.O.D. owing to the presence of large amount of well adopted micro-organisms. According to the research Ganga is rich in polymers excreted by various species of bacteria. These polymers being excellent coagulants remove turbidity by coagulation, setting the suspended particles at the sewage discharge point.
At the 1981 session of Indian Science Congress at Varanasi, scientists expressed concern at the growing pollution in the river Ganga in presence of the then Prime Minister Mrs. Indira Gandhi who inaugurated the session. At her instance, Dr. M.S. Swaminathan, the then member, Planning Commission asked the Central Board for Preventation and Control of Water Pollution, New Delhi to conduct studies on the state of the river Ganga. In collaboration with the State Pollution Control Boards of Uttar Pradesh, Bihar and Bengal and the centre for study of Man and Environment Kolkata (Calcutta), studies were conducted on the ‘Sources’ of pollution including all human activities, land use pattern and water quality of the river at selected sites during 1981-82 and report entitled “Basin, sub-basin inventory of water pollution in the Ganga basin part-II” was published in 1984. according to this report sewage of 27 class I cities and towns and effluents from 137 major industries were the main source of pollution of the river. In addition cremation of dead human bodies and dumping of carcasses aggrevated the pollution of the river.
It was Chandra (1981) who conducted studies on the pollution status of river Ganga at Allahabad, pointed out that industries manufacturing nitrogenous fertilizers have significant role in polluting the river water.
Study carried out in 1986-87 on physico-chemical properties of river Ganga water at Buxar (Unnao) clearly revealed that extent of pollution varied in different seasons. Usually all the 23 parameters studied showed high values in summer and lower during monsoons except turbidity which was high in rainy season. Values of BOD, COD, DO and H2S were recorded high than the tolerance limits.
Study on water quality of river Ganga at Kalakankar (Pratapgarh in Uttar Pradesh) revealed that even at such a remote and undisturbed place like Kalakankar the river water was not safe for drinking and bathing. It was also noted that the river showed an alkaline trend throughout the course of study.
According to the research done by Mehrotra (1990), the various sources responsible for pollution of the river in Varanasi city are domestic sewage effluents of the industries, burning of dead bodies at the ghats, use of detergents, insecticides and pesticides used in agriculture. Study revealed the presence of toxic metals like mercury ( 65 to 520ppb), Lead( less than 10 to 800 ppm), chromium (less than 10 to 200 ppm) and nickel (less than 10 to 130 ppm) in the sediments of Ganga river at Varanasi city.
Upstream from Varanasi, one of the major pilgrimage sites along the river, the water is comparatively pure, having a low Biochemical oxygen demand and fecal coliform count. Studies conducted in 1983 on water samples taken from the right bank of the Ganga at Patna confirm that escheria coli (E.Coli.), fecal streptococci and vibrio cholerae organisms die two to three times faster in the Ganga than in water taken from the rivers Son and Gandak and from dug wells and tube wells in the same area.
The chemical pollution of the river Ganga in Patna city in Bihar state has been found somewhat alarming beside the storm drain, especially in the regions like Rajapur, Mandiri and Krishnaghat.
According to the report published in a book by Mr. U.K. Sinha (1986), the concentration of iron is higher in sediments collected from 10 metres along the bank at Mandiri region. The concentration of all the toxic metals i.e copper, zinc, nickel and cobalt are higher in all the sediments collected from near the storm drain and diminishes towards mid-region of the river. The concentration of zinc is highest in the sediments collected from near the Mandiri storm drain, Antaghat storm drain and Krishnaghat storm drain.
The concentration of copper is highest in the sediments collected from near the Krishnaghat storm drain suggesting the presence copper due to utensil work being done in Thatheri Bazar and hospital wastes also, said report.
Present situation:
For some time now, this romantic view of the Ganges has collided with India's grim realities. During the past three decades, the country's explosive growth (at nearly 1.2 billion people, India's population is second only to China's), industrialization and rapid urbanization have put unyielding pressure on the sacred stream.

Ganga, the most sacred of rivers for Hindus, has become polluted for some years now. But a recent study by Uttarakhand Environment Conservation and Pollution Control Board says that the level of pollution in the holy river has reached alarming proportions.

Things have come to such a pass that the Ganga water is at present not fit just for drinking and bathing but has become unusable even for agricultural purposes.
As per the UECPCB study, while the level of coliform present in water should be below 50 for drinking purposes, less than 500 for bathing and below 5000 for agricultural use—the present level of coliform in Ganga at Haridwar has reached 5500.

Based on the level of coliform, dissolved oxygen and biochemical oxygen, the study put the water in A, B, C and D categories. While A category is considered fit for drinking, B for bathing, C for agriculture and D is for excessive pollution level.

Since the Ganga waters at Haridwar have more than 5000 coliform and even the level of dissolved oxygen and biochemical oxygen doesn't conform the prescribed standards, it has been put in the D category.

According to the study, the main cause of high level of coliform in Ganga is due to disposal of human faeces, urine and sewage directly into the river from its starting point in Gaumukh till it reaches Haridwar via Rishikesh.

Nearly 89 million litres of sewage is daily disposed into Ganga from the 12 municipal towns that fall along its route till Haridwar. The amount of sewage disposed into the river increases during the Char Dham Yatra season when nearly 15 lakh pilgrims visit the state between May and October each year.

Apart from sewage disposal of half-burnt human bodies at Haridwar and hazardous medical waste from the base hospital at Srinagar due to absence of an incinerator are also adding to pollution levels in the Ganga.

The result has been the gradual killing of one of India's most treasured resources. One stretch of the Yamuna River, the Ganges' main tributary, has been devoid of all aquatic creatures for at least a decade.

In Varanasi, India's most sacred city, the coliform bacterial count is at least 3,000 times higher than the standard established as safe by the United Nations world Health Organization. Coliform are rod-shaped bacteria that are normally found in the colons of humans and animals and become a serious contaminant when found in the food or water supply.

A study by Environmental Biology Laboratory, Department pf Zoology, Patna University, showed the presence of mercury in the Ganga river in Varanasi city. According to the study, annual mean concentration of mercury in the river water was 0.00023 ppm. The concentration ranged from NT (not traceable) to 0.00191 ppm.
Study done by Indian Toxicological Research Centre (ITRC), Lucknow during 1986-1992 showed maximum annual concentration of mercury in the Ganga river water at Rishikesh, Allahabad district and Dakshineswar as 0.081, 0.043 and 0.012 ppb respectively.

Ganga river at Varanasi was found well within the maximum permissible standard of 0.001 ppm prescribed for drinking water by the World Health Organization.
The mercury studied in the Ganga river could be traced in biotic as well as abiotic components of the river at the study site. The Hindu devotees take bath in the river where mercury was detected in 28%, 44%,75%, 96%, 42% and 89% of the river water, sediment, benthic fauna, fish, soil and vegetation samples respectively.

Though mercury contamination of the river water has not reached an alarming extent, its presence in the river system is worrisome. In the study annual mean concentration of the metal in the sediments was 0.067 ppm. Sediments constitute a major pool of mercury in fresh water.

As Ganga enters the Varanasi city, Hinduism’s sacred river contains 60,000 faecal coliform bacteria per 100 millilitres, 120 times more than is considered safe for bathing. Four miles downstream, with inputs from 24 gushing sewers and 60,000 pilgrim-bathers, the concentration is 3,000 times over the safety limit. In places, the Ganges becomes black and septic. Corpses, of semi-cremated adults or enshrouded babies, drift slowly by.

The tannery industry mushrooming in North India has converted the Ganga River into a dumping ground. The tanning industry discharges different types of waste into the environment, primarily in the form of liquid effluents containing organic matters, chromium, sulphide ammonium and other salts. As per an estimate, about 80-90% of the tanneries use chromium as a tanning agent. Of this, the hides take up only 50-70%, while the rest is discharged as effluent. Pollution becomes acute when tanneries are concentrated in clusters in small area like Kanpur. Consequently, the Leather-tanning sector is included in the Red category of industries due to the potential adverse environmental impact caused by tannery wastes.

Highly polluted sediments are adversely affecting the ecological functioning of rivers due to heavy metal mobilization from urban areas into biosphere. Distribution of heavy metals in sediments of the river Ganga and its tributaries have been carried out by several workers. Monitoring of Ganga River from Rishikesh to Varanasi indicated that Kannauj to Kanpur and Varanasi are the most polluted stretches of the river Ganga . Analysis of upstream and down stream water and sediment revealed a 10-fold increase in chromium level.

Reference:

Agarwal, D.K., Gaur, S.D., Tiwari T.C., Narayanswami, N. and Marwah, S.M. 1976.. Physico-chemical characteristics of Ganges water at Varanasi. India J. Environ. Hlth. 18 (3). 210-206.

Bhargava, D.S.1982. Purification power of the Ganges unmatched. L.S.T. Bull. 34. 52.

Chakraborty, R.N., Saxena, K.L. and Khan, A.Q. 1965. Stream pollution and its effect on water supply. A report of survey, Proc. Symp. Problems in Water treatment. Oct. 29-30, Nagpur. 211-219.

Chandra, K. 1981. Pollution from wastes of industries manufacturing nitrogenous fertilizer. A case study from river Ganga near Allahabad. In Proc. Symp. W.R.C.P.A. Roorkee 11-23 Dec. 141-151

Lakshminarayana, J.S.S. 1965. studies of the phytoplankton of the river Ganges, Varanasi, India, Part-I, Physico chemical characteristics of River Ganga. Hydrobiologia. 25. 119-175.

Mehrotra, M.N. 1990. the role of sediments in environmental pollution: A case study of the Ganga at Varanasi. Jour. of the Ind. Association of Sedimentologists, v.9.1-14.

Pahwa, D.V. and Mehrotra, S.N., 1966. Observations on fluctuation in the abundance of plankton in relation to certain hydrobiological vonditions of river Ganges. Proc. Nat. Acad. Sci., India, Sec. 36B (2). 157-89.

Saxena, K.L., Chakraborty, A.K., Khan, A.Q., Chattopadhayay, R.N. and Chandra, H. 1966. Pollution study of river near Kanpur. Indian, J. environ. Hlth. 8. 270.

Sinha,A.K., Singh, V.P. and Srivastava, K.,2000.Physico-chemical studies on river Ganga and its tributaries in Uttar Pradesh- the present status.In Pollution and Biomonitoring of Indian Rivers. (ed.) Dr. R.K. Trivedy. ABD Publishers, Jaipur. 1-29.

Sinha, U.K.,1986. Ganga pollution and health hazard. Inter-India Publication, New Delhi.

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