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14th IRCSA Conference, Kula Lumpur, Malaysia, 3-6th August 2009

                Importance of Rainwater Harvesting in Human Health
                            C.S. Weeraratna* and Tanuja Ariyananda**
             Lanka Rainwater Harvesting Forum, Subadrarama Lane, Nugegoda, Sri Lanka,
                        (E-mail: * csweera@sltnet.lk and ** tanuja@sltnet.lk)


ABSTRACT

Water used for drinking and other purposes may contain elements such as arsenic, cadmium or
anions such as fluoride, and nitrates at toxic levels. Drinking of such contaminated/polluted water
can cause considerable health problems. Arsenic in water causes many health problems collectively
referred to as Arsenicosis. Cadmium in toxic levels cause Chronic Renal Failure. Excess fluoride in
water cause dental and skeletal Fluorosis., and high levels of nitrates result in a condition called
Methemoglobinemia. The facilities to purify water effectively are not adequate in most countries. .
Hence, a large number of people in many countries have to drink unpurified water resulting in
numerous diseases, some of which are incurable. Water obtained directly from rain ie. Rainwater
harvesting is the best alternative to prevent occurrence of such diseases.

KEYWORDS
arsenic; cadmium, fluorides; nitrates, rainwater harvesting

INTRODUCTION

Rain is the main source of water in many parts of the world. However, the water used for drinking
is obtained mostly from wells, reservoirs, rivers and lakes. Water obtained from these sources in
many parts of the world are contaminated with various cations or anions. Among the cations
commonly found in toxic levels in water are arsenic, and cadmium. Nitrates, and fluorides are
among the common anions found at toxic levels in water. These toxic substances enter water bodies
as a result of ground water pollution as illustrated in Figure 1.

Figure 1
ARSENIC

Arsenic is one of the element reported to be present in toxic levels in drinking water in some
countries. Arsenic enters drinking water supplies mainly from natural deposits in the earth. In a
survey reported by Khan (2000) that that 50% of tube well water in 44 districts of Bangldesh,
contains arsenic above the WHO maximum permissible limit of 0.05 mg per litre of water. The
depth of contaminated tube wells ranged from 50 - 110 feet. In 59 districts of Bangladesh out of its
64 districts, arsenic has been found in groundwater at levels above 0.05 mg/l of water which is the
WHO maximum permissible limit. ( Das et.al. 2000) High arsenic levels in water also has been
reported in six districts of West Bengal covering an area of 34 000 km2 with a population of 30
million. In addition to Bangladesha and West Bengal, high concentrations of arsenic in drinking-
water are found in various parts of the world including China,and Taiwan, Cambodia, Lao People
Democratic Republic, Pakistan, Myanmar, Vietnam, and Nepal. (Anonymous 2009).

Arsenic dissolved in water is acutely toxic and can lead to a number of health problems. Long-term
exposure to arsenic in drinking-water causes increased risks of cancer in the skin, lungs, bladder
and kidney. It also leads to other skin-related problems such hyperkeratosis and changes in
pigmentation. Consumption of arsenic also leads to disturbance of the cardiovascular and nervous
system functions and eventually leads to death.. Increased risks of lung and bladder cancer and of
arsenic-associated skin lesions have been reported for consuming drinking-water with arsenic
concentrations equal to or greater than 50 parts per billion (or microgram per liter). (Anonymous,
2009) . These health effects – sometimes collectively referred to as arsenicosis – have been
demonstrated in many studies. Among the 44 districts surveyed by Khan arsenicosis cases were
identified in 26 districts. . It has been estimated that more than 35 million people in Bangladesh are
at risk of arsenic toxicity Khan (2000).

CADMIUM

Cadmium has been reported to be present in high concentrations in water in five reservoirs of the
North Central Province, located in the Dry Zone of Sri Lanka. ( Bandara et. al. 2008). The
dissolved cadmium in the water samples ranged from 0.03-0.06 mg/l, 19 fold increase over
maximum contaminant level set by WHO.

Chronic Renal Failure has been reported among 5,000 inhabitants in many parts of the Dry Zone of
Sri Lanka (Atapaatu, 2006). Athuraliya et.al (2003) too reported that around 5% of the farming
community in North central Province of Sri Lanka are affected by CRF. Bandara et.al. (2008)
carried out intensive studies and attributed high levels of cadmium in water to Chronic Renal
Failure reported by Atapattu (2006) and Athuraliya et al. (2003).

NITRATE

Nitrate is one of the most common groundwater contaminants in rural areas. The high nitrate
content in groundwater is mainly from irrigation run-off from agricultural fields where chemical
fertilizers have been used indiscriminately. Nitrate in groundwater originates primarily from
fertilizers, septic systems, and manure storage or spreading operations. Fertilizer nitrogen that is not
taken up by plants, volatilized, or carried away by surface runoff leaches to the groundwater in the
form of nitrate. This not only makes the nitrogen unavailable to crops, but also can elevate the
concentration of nitrates in groundwater above the levels acceptable for drinking water quality.
Melvani (2004) and Liyanage et.al (2000) reported that the ground water in Kalpitiya in Sri Lanka
contains nitrate levels above 10mg per liter which is the WHO standards for drinking water.

Short-term exposure to drinking water with a nitrate level at or just above the health standard of 10
mg/l nitrate-N is a potential health problem primarily for infants. Babies consume large quantities
of water relative to their body weight, especially if water is used to mix powdered or concentrated
formulas or juices. Also, their immature digestive systems are more likely than adult digestive tracts
to allow the reduction of nitrate to nitrite. In particular, the presence of nitrite in the digestive tract
of newborns can lead to a disease called Methemoglobinemia, which is the most significant health
problem associated with nitrate in drinking water. Blood contains an iron-based compound called
hemoglobin, which carries oxygen. When nitrite is present, hemoglobin can be converted to
methemoglobin, which cannot carry oxygen. In the blood of adults, enzymes continually convert
methemoglobin back to hemoglobin, but newborn infants have lower levels of these enzymes, and
their methemoglobin level is usually 1 to 2 percent. Anything above that level is considered
methemoglobinemia. (McCasland et.al. ) Few clear cut symptoms are associated with
methemoglobin levels between 1 and 10 percent. At higher levels, symptoms of cyanosis usually
appear. Babies with this condition have bluish mucous membranes and may also have digestive and
respiratory problems. At methemoglobin levels above 20 to 30 percent, the primary effects result
from the blood's severely reduced oxygen-carrying capacity and are referred to as anoxia. At
methemoglobin levels around 50 to 70 percent, brain damage or death can occur.(McCasland et.al.

FLUORIDE

In a number of small villages in Sicily, Turkey and India there is naturally occurring fluoride in the
water ranging from 0.7 to 5.4 ppm. (Yiamouyiannis, J (1993) Fluoride concentration of ranging
from6-8 mg/liter in drinking water has been reported in some parts of the Dry Zone of Sri lanka.
(Padmasiri and Wickramasingha (2004), Ileperum, et.al (2004) reported that water in dug wells in
some parts of Anuradhapura District has a fluoride content of 1.0-4.0 ppm. High fluoride levels in
potable water has been reported from China and India. many countries (Fawell et. al. 2006).
High fluoride levels in potable water causes children to have brown decaying teeth; young adults
often have none. Young men are bent over and crippled with pain in their joints and hips. There is
premature hardening of the arteries, and loss of appetite. (Yiamouyiannis, J (1993). Fluoride at
high levels can cause severe skeletal fluorosis including pains in bones and joints , reduced appetite
backache, osteoarthritis As fluoride builds up in different parts of the body over decades it can
disrupt the actions of many key enzymes. (Fawell et. al. 2006).

Facilities to purify water effectively are not adequate in most countries. . Hence, a large number of
people in many countries have to drink unpurified water. In such situations water obtained directly
from rain ie. Rainwater harvesting is the best alternative. Das et. Al. (2000) and . Ahmed (2000)
have proposed that rainwater harvesting is used to prevent arsenic poisoning in Bangladesh.

RAINWATER HARVESTING

Rainwater harvesting is collecting the run-off from a structure or other impervious surface to be
stored for later use. Traditionally, this involves harvesting the rain from a roof. The rain will collect
in gutters that channel the water into downspouts and then into a storage vessel. Rainwater
collection systems can by as simple as collecting rain in a rain barrel or as elaborate as harvesting
rainwater into large tanks.

Rainwater is relatively the most pure form of water. Some factors such as pollution by extraneous
matter (eg. bird faecal matter etc.) on roof surface may affect the quality of rainwater collected.
The quality of the rainwater can vary depending on the atmospheric pollution, harvesting method
and storage. While the quality of collected rainwater may vary, on the whole, harvested quality is
found to be equal to that of the regular treated water supplied through the public mains. Heyworth
(2001) showed that in Adelaide, under-fives in rainwater supplied, rural households were at no
greater risk to diarrhea than those who drank the treated piped water. Evans et al. ( 2007) in a study
conducted in Eastern Australia indicated that roof harvested rainwater was satisfactory , and
Ariyananda (1999, 2007) have shown that rainwater harvesting could be effectively practiced, and
has many benefits. .Ahmed (1999) and Das et. al (2000) have shown that rainwater harvesting is an
effective practice to overcome arsenic poisoning.

Rainwater harvesting is becoming increasingly popular as the availability of good quality water
decreases. Rainwater harvesting is acknowledged as a sustainable source of water that has less
impact on the environment. In 2004, 17% of households in Australia had rainwater as a source of
water. In rural Western Australia 62% of the households owned rainwater tanks and 53% had
rainwater as their main drinking source. (Australian Bureau of Statistics 2004) .

CONCLUSION

Rainwater is a good alternative for drinking water in those areas where ground water contains a
high concentrations of toxic materials such as arsenic/cadmium/nitrates/fluorides. Hence, rainwater
harvesting need to be popularised in areas where water available for drinking contains high levels of
such toxic ions.

REFERENCES

   Ahmed, M.F (1999) Rainwater harvesting Potentials in Bangladesh. 25th The Water,
   Engineering and Development Centre (WEDC) Conference, Addis Ababa, Ethiopia

   Ahmed, M.F (2000) Potentials for Rainwater Harvesting in Bangladesh . 3rd International
   Arsenic Conference , Dhaka, Bangladesh

   Anonymous (2009) Arsenic established carcinogen http://www. sos-aresic.net

   Ariyananda, T( 1999 ) Rainwater Harvesting for Domestic use in Sri Lanka. 25th The
   Water,Engineering and Development Center (WEDC) Conference, Addis Ababa, Ethiopia.

   Ariyananda (2007 ).Improving water security in Tsunami Affected areas in Sri Lanka through
   domestic rainwater harvesting . Proceedings of the Thirteenth International Conference on Rain
   Water Catchments Systems, Sydney, Australia.

   Australian Bureau of Statistics (2004) Canberra.

   Bandara, J.M.R.S; Seneviratna, D.M.A.N; Dassanayaka, D.M.R.S.B; Herath, V; Bandara,
   J.M.R.P., Abeysekara, T a,d Rajapaksha, K.H. (2008). Chronic Renal Failur among farm
   families in cascade irrigation systems in Sri Lanka associated with dietary cadmium levels in
   rice and freshwater fish(Tilapia). Environ Geochem Health. 30:465-478

   Das, R, Bidyut, J.Y; Shohel,A.E; Protik, T.H; Islam,S; Uddin, M; and Islam, A(2000)
   Rainwater Harvesting: New Technique for Throughout the Year. 3rd International Arsenic
   Conference , Dhaka, Bangladesh

   Evans, C; Coombes, P; Dunstan, H; Harrison, T; Martin, A; and Morrow, A. (2007) Roof
   Harvested Rainwater - Indicator Organisms, Water Quality and Risk Assessment Proceedings of
   the Thirteenth International Conference on Rain Water Catchments Systems, Sydney, Australia.

   Fawell,J; Bailey,K; Chilton,J; Dahi, E; Fewtrell,L and Magara Y. (2006) Fluoride in Drinking-
   water , World Health Organization. Published by IWA Publishing, Alliance House, 12 Caxton
   Street, London SW1H 0QS, UK
Heyworth, J.S. (2001) A diary of gastroenteritis and tank water consumption in young children
in S. Australia. Proc. 10th International Conference on Rain Water Catchments Systems,
Mannheim, Ger many

Ileperum, O.A and Dharmagunawardena, H and Herath, K.R.P.K (2004) Chronic Renal Failure
in the Anuradhapura District. Awareness Raising on Millennium Development Goals in Water
Supply and Sanitation through WASH programme & Dissemination of Water Supply and
Sanitation Research Findings. Colombo, Sri Lanka

Liyanage, C.E; Thabrew,M.L and Kuruppuarachchi D,S.P (2000) Nitrate pollution in ground
water of Kalpitiya. J. National. Sci. Council of Sri Lanka, 28 (2) 101-112

Margaret, M; Trautmann, N.M; Porter, K.S; and Wagenet, R.J Nitrate: Health Effects in
Drinking Water High levels of fluoride in many countries. Natural Resources Cornell Extension.

Melvani , K (2004) Bioremediation of drinking water in Nawakkaduwa , Kalpitiya. Awareness
Raising on Millennium Development Goals in Water Supply and Sanitation through WASH
programme & Dissemination of Water Supply and Sanitation Research Findings. Colombo, Sri
Lanka

Padmasiri, J.P and Wickramasingha, N.I. (2004) Community based Defluooridation of fluoride
rich water in Dry Zone in Sri Lanka. Awareness Raising on Millennium Development Goals in
Water Supply and Sanitation through WASH programme & Dissemination of Water Supply and
Sanitation Research Findings. Colombo, Sri Lanka

Das, R; Jamal, S.S; Elahi, A, Safiqui Islam, Uddin, M and Salim Md (2000) Arsenic
Contamination in Ground Water and Its Effect on Human Health with Particular Reference to
Bangladesh 3rd International Arsenic Conference , Dhaka, Bangladesh

Shearer, L.A., J.R. Goldsmith, C. Young, et al. 1972. Methemoglobin levels in infants, in an
area with high nitrate water supply. Amer. J. of Public Health, 62:1174-80.

Shuval, H.I., and N. Gruener. 1972. Epidemiological and toxicological aspects of nitrates and
nitrites in the environment. Amer. J. of Public Health, 62:1045-51.

Wadud Khan (2000) Arsenic Contamination in Ground Water and Its Effect on Human Health
with Particular Reference to Bangladesh 3rd International Arsenic Conference , Dhaka,
Bangladesh

Yiamouyiannis, J. (1993) Fluoride, The Aging Factor Health Action Press,

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Malaysia; Importance of Rainwater Harvesting in Human Health

  • 1. 14th IRCSA Conference, Kula Lumpur, Malaysia, 3-6th August 2009 Importance of Rainwater Harvesting in Human Health C.S. Weeraratna* and Tanuja Ariyananda** Lanka Rainwater Harvesting Forum, Subadrarama Lane, Nugegoda, Sri Lanka, (E-mail: * csweera@sltnet.lk and ** tanuja@sltnet.lk) ABSTRACT Water used for drinking and other purposes may contain elements such as arsenic, cadmium or anions such as fluoride, and nitrates at toxic levels. Drinking of such contaminated/polluted water can cause considerable health problems. Arsenic in water causes many health problems collectively referred to as Arsenicosis. Cadmium in toxic levels cause Chronic Renal Failure. Excess fluoride in water cause dental and skeletal Fluorosis., and high levels of nitrates result in a condition called Methemoglobinemia. The facilities to purify water effectively are not adequate in most countries. . Hence, a large number of people in many countries have to drink unpurified water resulting in numerous diseases, some of which are incurable. Water obtained directly from rain ie. Rainwater harvesting is the best alternative to prevent occurrence of such diseases. KEYWORDS arsenic; cadmium, fluorides; nitrates, rainwater harvesting INTRODUCTION Rain is the main source of water in many parts of the world. However, the water used for drinking is obtained mostly from wells, reservoirs, rivers and lakes. Water obtained from these sources in many parts of the world are contaminated with various cations or anions. Among the cations commonly found in toxic levels in water are arsenic, and cadmium. Nitrates, and fluorides are among the common anions found at toxic levels in water. These toxic substances enter water bodies as a result of ground water pollution as illustrated in Figure 1. Figure 1
  • 2. ARSENIC Arsenic is one of the element reported to be present in toxic levels in drinking water in some countries. Arsenic enters drinking water supplies mainly from natural deposits in the earth. In a survey reported by Khan (2000) that that 50% of tube well water in 44 districts of Bangldesh, contains arsenic above the WHO maximum permissible limit of 0.05 mg per litre of water. The depth of contaminated tube wells ranged from 50 - 110 feet. In 59 districts of Bangladesh out of its 64 districts, arsenic has been found in groundwater at levels above 0.05 mg/l of water which is the WHO maximum permissible limit. ( Das et.al. 2000) High arsenic levels in water also has been reported in six districts of West Bengal covering an area of 34 000 km2 with a population of 30 million. In addition to Bangladesha and West Bengal, high concentrations of arsenic in drinking- water are found in various parts of the world including China,and Taiwan, Cambodia, Lao People Democratic Republic, Pakistan, Myanmar, Vietnam, and Nepal. (Anonymous 2009). Arsenic dissolved in water is acutely toxic and can lead to a number of health problems. Long-term exposure to arsenic in drinking-water causes increased risks of cancer in the skin, lungs, bladder and kidney. It also leads to other skin-related problems such hyperkeratosis and changes in pigmentation. Consumption of arsenic also leads to disturbance of the cardiovascular and nervous system functions and eventually leads to death.. Increased risks of lung and bladder cancer and of arsenic-associated skin lesions have been reported for consuming drinking-water with arsenic concentrations equal to or greater than 50 parts per billion (or microgram per liter). (Anonymous, 2009) . These health effects – sometimes collectively referred to as arsenicosis – have been demonstrated in many studies. Among the 44 districts surveyed by Khan arsenicosis cases were identified in 26 districts. . It has been estimated that more than 35 million people in Bangladesh are at risk of arsenic toxicity Khan (2000). CADMIUM Cadmium has been reported to be present in high concentrations in water in five reservoirs of the North Central Province, located in the Dry Zone of Sri Lanka. ( Bandara et. al. 2008). The dissolved cadmium in the water samples ranged from 0.03-0.06 mg/l, 19 fold increase over maximum contaminant level set by WHO. Chronic Renal Failure has been reported among 5,000 inhabitants in many parts of the Dry Zone of Sri Lanka (Atapaatu, 2006). Athuraliya et.al (2003) too reported that around 5% of the farming community in North central Province of Sri Lanka are affected by CRF. Bandara et.al. (2008) carried out intensive studies and attributed high levels of cadmium in water to Chronic Renal Failure reported by Atapattu (2006) and Athuraliya et al. (2003). NITRATE Nitrate is one of the most common groundwater contaminants in rural areas. The high nitrate content in groundwater is mainly from irrigation run-off from agricultural fields where chemical fertilizers have been used indiscriminately. Nitrate in groundwater originates primarily from fertilizers, septic systems, and manure storage or spreading operations. Fertilizer nitrogen that is not taken up by plants, volatilized, or carried away by surface runoff leaches to the groundwater in the form of nitrate. This not only makes the nitrogen unavailable to crops, but also can elevate the concentration of nitrates in groundwater above the levels acceptable for drinking water quality. Melvani (2004) and Liyanage et.al (2000) reported that the ground water in Kalpitiya in Sri Lanka contains nitrate levels above 10mg per liter which is the WHO standards for drinking water. Short-term exposure to drinking water with a nitrate level at or just above the health standard of 10 mg/l nitrate-N is a potential health problem primarily for infants. Babies consume large quantities
  • 3. of water relative to their body weight, especially if water is used to mix powdered or concentrated formulas or juices. Also, their immature digestive systems are more likely than adult digestive tracts to allow the reduction of nitrate to nitrite. In particular, the presence of nitrite in the digestive tract of newborns can lead to a disease called Methemoglobinemia, which is the most significant health problem associated with nitrate in drinking water. Blood contains an iron-based compound called hemoglobin, which carries oxygen. When nitrite is present, hemoglobin can be converted to methemoglobin, which cannot carry oxygen. In the blood of adults, enzymes continually convert methemoglobin back to hemoglobin, but newborn infants have lower levels of these enzymes, and their methemoglobin level is usually 1 to 2 percent. Anything above that level is considered methemoglobinemia. (McCasland et.al. ) Few clear cut symptoms are associated with methemoglobin levels between 1 and 10 percent. At higher levels, symptoms of cyanosis usually appear. Babies with this condition have bluish mucous membranes and may also have digestive and respiratory problems. At methemoglobin levels above 20 to 30 percent, the primary effects result from the blood's severely reduced oxygen-carrying capacity and are referred to as anoxia. At methemoglobin levels around 50 to 70 percent, brain damage or death can occur.(McCasland et.al. FLUORIDE In a number of small villages in Sicily, Turkey and India there is naturally occurring fluoride in the water ranging from 0.7 to 5.4 ppm. (Yiamouyiannis, J (1993) Fluoride concentration of ranging from6-8 mg/liter in drinking water has been reported in some parts of the Dry Zone of Sri lanka. (Padmasiri and Wickramasingha (2004), Ileperum, et.al (2004) reported that water in dug wells in some parts of Anuradhapura District has a fluoride content of 1.0-4.0 ppm. High fluoride levels in potable water has been reported from China and India. many countries (Fawell et. al. 2006). High fluoride levels in potable water causes children to have brown decaying teeth; young adults often have none. Young men are bent over and crippled with pain in their joints and hips. There is premature hardening of the arteries, and loss of appetite. (Yiamouyiannis, J (1993). Fluoride at high levels can cause severe skeletal fluorosis including pains in bones and joints , reduced appetite backache, osteoarthritis As fluoride builds up in different parts of the body over decades it can disrupt the actions of many key enzymes. (Fawell et. al. 2006). Facilities to purify water effectively are not adequate in most countries. . Hence, a large number of people in many countries have to drink unpurified water. In such situations water obtained directly from rain ie. Rainwater harvesting is the best alternative. Das et. Al. (2000) and . Ahmed (2000) have proposed that rainwater harvesting is used to prevent arsenic poisoning in Bangladesh. RAINWATER HARVESTING Rainwater harvesting is collecting the run-off from a structure or other impervious surface to be stored for later use. Traditionally, this involves harvesting the rain from a roof. The rain will collect in gutters that channel the water into downspouts and then into a storage vessel. Rainwater collection systems can by as simple as collecting rain in a rain barrel or as elaborate as harvesting rainwater into large tanks. Rainwater is relatively the most pure form of water. Some factors such as pollution by extraneous matter (eg. bird faecal matter etc.) on roof surface may affect the quality of rainwater collected. The quality of the rainwater can vary depending on the atmospheric pollution, harvesting method and storage. While the quality of collected rainwater may vary, on the whole, harvested quality is found to be equal to that of the regular treated water supplied through the public mains. Heyworth (2001) showed that in Adelaide, under-fives in rainwater supplied, rural households were at no greater risk to diarrhea than those who drank the treated piped water. Evans et al. ( 2007) in a study conducted in Eastern Australia indicated that roof harvested rainwater was satisfactory , and Ariyananda (1999, 2007) have shown that rainwater harvesting could be effectively practiced, and
  • 4. has many benefits. .Ahmed (1999) and Das et. al (2000) have shown that rainwater harvesting is an effective practice to overcome arsenic poisoning. Rainwater harvesting is becoming increasingly popular as the availability of good quality water decreases. Rainwater harvesting is acknowledged as a sustainable source of water that has less impact on the environment. In 2004, 17% of households in Australia had rainwater as a source of water. In rural Western Australia 62% of the households owned rainwater tanks and 53% had rainwater as their main drinking source. (Australian Bureau of Statistics 2004) . CONCLUSION Rainwater is a good alternative for drinking water in those areas where ground water contains a high concentrations of toxic materials such as arsenic/cadmium/nitrates/fluorides. Hence, rainwater harvesting need to be popularised in areas where water available for drinking contains high levels of such toxic ions. REFERENCES Ahmed, M.F (1999) Rainwater harvesting Potentials in Bangladesh. 25th The Water, Engineering and Development Centre (WEDC) Conference, Addis Ababa, Ethiopia Ahmed, M.F (2000) Potentials for Rainwater Harvesting in Bangladesh . 3rd International Arsenic Conference , Dhaka, Bangladesh Anonymous (2009) Arsenic established carcinogen http://www. sos-aresic.net Ariyananda, T( 1999 ) Rainwater Harvesting for Domestic use in Sri Lanka. 25th The Water,Engineering and Development Center (WEDC) Conference, Addis Ababa, Ethiopia. Ariyananda (2007 ).Improving water security in Tsunami Affected areas in Sri Lanka through domestic rainwater harvesting . Proceedings of the Thirteenth International Conference on Rain Water Catchments Systems, Sydney, Australia. Australian Bureau of Statistics (2004) Canberra. Bandara, J.M.R.S; Seneviratna, D.M.A.N; Dassanayaka, D.M.R.S.B; Herath, V; Bandara, J.M.R.P., Abeysekara, T a,d Rajapaksha, K.H. (2008). Chronic Renal Failur among farm families in cascade irrigation systems in Sri Lanka associated with dietary cadmium levels in rice and freshwater fish(Tilapia). Environ Geochem Health. 30:465-478 Das, R, Bidyut, J.Y; Shohel,A.E; Protik, T.H; Islam,S; Uddin, M; and Islam, A(2000) Rainwater Harvesting: New Technique for Throughout the Year. 3rd International Arsenic Conference , Dhaka, Bangladesh Evans, C; Coombes, P; Dunstan, H; Harrison, T; Martin, A; and Morrow, A. (2007) Roof Harvested Rainwater - Indicator Organisms, Water Quality and Risk Assessment Proceedings of the Thirteenth International Conference on Rain Water Catchments Systems, Sydney, Australia. Fawell,J; Bailey,K; Chilton,J; Dahi, E; Fewtrell,L and Magara Y. (2006) Fluoride in Drinking- water , World Health Organization. Published by IWA Publishing, Alliance House, 12 Caxton Street, London SW1H 0QS, UK
  • 5. Heyworth, J.S. (2001) A diary of gastroenteritis and tank water consumption in young children in S. Australia. Proc. 10th International Conference on Rain Water Catchments Systems, Mannheim, Ger many Ileperum, O.A and Dharmagunawardena, H and Herath, K.R.P.K (2004) Chronic Renal Failure in the Anuradhapura District. Awareness Raising on Millennium Development Goals in Water Supply and Sanitation through WASH programme & Dissemination of Water Supply and Sanitation Research Findings. Colombo, Sri Lanka Liyanage, C.E; Thabrew,M.L and Kuruppuarachchi D,S.P (2000) Nitrate pollution in ground water of Kalpitiya. J. National. Sci. Council of Sri Lanka, 28 (2) 101-112 Margaret, M; Trautmann, N.M; Porter, K.S; and Wagenet, R.J Nitrate: Health Effects in Drinking Water High levels of fluoride in many countries. Natural Resources Cornell Extension. Melvani , K (2004) Bioremediation of drinking water in Nawakkaduwa , Kalpitiya. Awareness Raising on Millennium Development Goals in Water Supply and Sanitation through WASH programme & Dissemination of Water Supply and Sanitation Research Findings. Colombo, Sri Lanka Padmasiri, J.P and Wickramasingha, N.I. (2004) Community based Defluooridation of fluoride rich water in Dry Zone in Sri Lanka. Awareness Raising on Millennium Development Goals in Water Supply and Sanitation through WASH programme & Dissemination of Water Supply and Sanitation Research Findings. Colombo, Sri Lanka Das, R; Jamal, S.S; Elahi, A, Safiqui Islam, Uddin, M and Salim Md (2000) Arsenic Contamination in Ground Water and Its Effect on Human Health with Particular Reference to Bangladesh 3rd International Arsenic Conference , Dhaka, Bangladesh Shearer, L.A., J.R. Goldsmith, C. Young, et al. 1972. Methemoglobin levels in infants, in an area with high nitrate water supply. Amer. J. of Public Health, 62:1174-80. Shuval, H.I., and N. Gruener. 1972. Epidemiological and toxicological aspects of nitrates and nitrites in the environment. Amer. J. of Public Health, 62:1045-51. Wadud Khan (2000) Arsenic Contamination in Ground Water and Its Effect on Human Health with Particular Reference to Bangladesh 3rd International Arsenic Conference , Dhaka, Bangladesh Yiamouyiannis, J. (1993) Fluoride, The Aging Factor Health Action Press,