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T.SUBRAMANI et al Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 2), June 2014, pp.270-273
www.ijera.com 270 | P a g e
Impact of Sewage and Industrial Effluent on Soil Plant Health
Act on Environment
T. Subramani1
M. Mangaiyarkarasi2
C. Kathirvel3
1
Professor & Dean, Department of Civil Engineering, VMKV Engineering College, Vinayaka Missions
University, Salem, India.
2,3,
PG Student of Environmental Engineering, Department of Civil Engineering, VMKV Engineering College,
Vinayaka Missions University, Salem,
ABSTRACT
Effect of continuous irrigation with sewage effluent on soil properties and status of nutrients and pollutant
elements in soils and plants in the adjoining areas of Agra and Mathura cities of Uttar Pradesh was ascertained.
The physical properties of soils improved due to sewage water irrigation. An appreciable increase in organic
carbon, available N, P, K contents was recorded in the sewage water irrigated soils. Electrical conductivity of
sewage water irrigated soils was much below the threshold limit of salinity.
Application of sewage water resulted in the accumulation of heavy metals in surface soil. The mean
contents of total Cd, Cr, Pb in the soils irrigated with sewage water were 2.85, 75.40 and 40.26 mg kg- 1,
respectively. The mean values of available Cd, Cr and Pb in soils were 0.21, 0.33 and 1.27 mg kg-1,
respectively. The concentration of Cr in lettuce, cabbage and be seem plants grown on sewage water was higher
as compared to its tolerance level indicating their accumulation in plants. In general, Cd was relatively higher in
lettuce (0.88 mg kg-1). On the other hand, be seemed contained relatively higher amount of Cr and Pb.
KEYWORDS: Impact, Sewage, Industrial Effluent, Soil Plant Health, Environment.
I. INTRODUCTION
It provides farmers with a nutrient enriched
water supply and society with a reliable and
inexpensive system for wastewater treatment and
disposal. Some of these effluents are a rich source of
plant nutrients, therefore soil provides the logical
sink for their disposal. But many untreated and
contaminated sewage and industrial effluents may
have high concentration of several heavy metals such
Cd, Ni, Pb and Cr. Field study was conducted in
Salem area, to evaluate the effects of using sewage
water to irrigate the fields near ground water wells in
this region. Many quality parameters like pH, EC,
total alkalinity, total hardness, Ca+2, Mg+2, Cl-1,
So4-2, Na+1 and Potassium.
The analysis of samples showed alkaline nature
of the water in research area. Also the results refer to
high salt water levels compared with classifications
of WHO. The two most common treatments prior to
sludge applications to agriculture seem to be
anaerobic digestion and lime stabilization. In some of
the old Member States (EU15), land application of
raw and/or limited treated sludge is diminishing and
composting and other treated products are
increasingly used. There is also an increase of
advanced treated sludge to be used in non-
agricultural applications. Sludge is also used as a soil
improver on degraded soils at mine sites,
construction sites, and other disturbed areas such as
in Portugal (Duarte) where sludge has been used for
stabilizing soils after forest fires. However, use of
sludge in forests is relatively uncommon or even
prohibited in some Member States.
Most Member States are, in general, moving
away from land filling to recycling sludge to land
and/or – to a lesser extent – incineration with some
recovery of energy.
II. EFFECTS ON BIOLOGICAL,
PHYSICAL, SOCIAL AND
ECONOMICAL ENVIRON Nuisance
(Odor, Noise, Vermin and Fire)
2.1 Impacts
There will not be odor, noise and vermin
problems at the plant that can affect the residents.
Even the worker(s) will not be affected by the odor.
However, there is the possibility of mosquito
breeding in the open aeration tank of the plant and
also in the water pond, where the effluent will be
discharged, which can cause nuisance to the people
during the summer months. The plant will not attract
RESEARCH ARTICLE OPEN ACCESS
T.SUBRAMANI et al Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 2), June 2014, pp.270-273
www.ijera.com 271 | P a g e
flies, rodents and other animals. Occurrence of fire is
not possible unless the biogas release valves do not
function properly and create explosive situations.
2.2 Water Impacts
In general, the existence of the WWTP will have
a positive impact on the surface and ground water
quality of the area because it will eliminate the
existing septic tanks in the western part of the village,
which cause pollution and create health problems.
However, the discharge of treated effluents from the
plant to the runoff channel will have some slight
impacts, particularly during the wet season,
extending from November to April. In addition, the
water stream located in the vicinity of the plant may
be contaminated if effluents do not meet the
standards. During the dry season the discharged
water can be used for irrigation of forest trees, or
used by farmers. If the removed grease from the
grease trap is dumped haphazardly at the plant site it
will impact the surface waters, particularly during the
wet season when the rains carry them down into the
valley.
2.3 Air Impacts
Air pollution will result during the excavation
and construction phase. Dusty conditions will occur.
Also vehicular emissions will take place. But this will
occur for a period of 2 to 3 months. During the
operational phase of the plant no such conditions will
result. Gaseous and particulate emissions will have
their impacts on the natural vegetation. If flaring of
biogas does not take place, methane gas will be
released into the atmosphere, which is a powerful
greenhouse gas and it will have negative impact on
the global climate.
2.4 Climate Impacts
The existence of the WWTP will not have any
negative effect on the microclimate of the area. This
will be improved against the climate extremities
(wind and storms), by planting trees in the
neighborhood of the plant. Greenhouse gases, such as
methane gas, will be produced in the bio-digesters of
the plant and if released, this will have negative
impact on the climate.
2. 5 Soil Impacts
Sandy soil and rocks will be excavated during
the construction phase of the treatment plant. If it
coincides with the rainy season, this will cause soil
erosion at the site. However, since the site is already
dug, minimal excavation work is required. The use of
treated wastewater for irrigation will improve the
fertility of agricultural lands of the area. But when
unsatisfactorily treated effluents are released, these
might contaminate the soils. If the grease and sludge
(once in 20 years) are not properly handled and
managed they can contaminate the nearby soils and
create unsighty conditions.
2.6 Landscape Impact
The bio-digesters of the WWTP/2 will be
constructed underground at a distance of at least
1000m far from the nearest house. The WWTP will
be the only structure in the area. But since the
digesters are going to be partially buried inside the
abandoned quarry, they will be hidden by the
surrounding natural fence of trees, which will
surround it. Therefore, the visual impact on the
project would be positive.
2.7 Fauna Impacts
The fauna in the project area is very limited. It
consists of some birds, rodents, snakes and turtles.
During the construction phase of the plant these
animals will be disturbed and their habitat affected.
The physical existence of the plant might scare the
birds. Effluents of the WWTP will have some minor
impact on the soil microorganisms, particularly in the
immediate vicinity of the water pond, where it will be
discharged. In dry season the plant effluents can
become a water source for the wild animals and
birds.
2.8 Impacts of sewage effluents
Sewage effluents have historically been
discharged through outfall in shallow coastal and
waters (Young-Jin Suh and Rousseaux P., 2001,
Mclntyre 1995, Klaus Koop and Pat Hutchings 1996)
and is one of the major stresses impacting coastal
ecosystems. There are usually significant effects on
water quality and on marine life arising from sewage
disposal. Water quality deterioration is one of the
most important water resource issues of the 21st
century. Therefore the quality status of coastal
surface water is very important and would always be
under public scrutiny because of health risk
associated with sewage contamination.
The potential deleterious effects of pollutants
from sewage effluents on the receiving water quality
of the coastal environment are manifold and depend
on volume of the discharge, the chemical
composition and concentrations in the effluent. It also
depends on type of the discharge for example
whether it is amount of suspended solids or organic
matter or hazardous pollutants like heavy metals and
organo chlorines, and the characteristics of the
receiving waters (NAP, 1984, Canter W., 1996:
Nemerow and Dasgupta, 1991). High levels of
soluble organics may cause oxygen depletion (Peter
and Robin, 2002) with a negative effect on aquatic
biota. Contamination of the coastal water may result
in changes in nutrient levels, abundance, biomass and
diversity of organisms, bioaccumulation of organic
T.SUBRAMANI et al Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 2), June 2014, pp.270-273
www.ijera.com 272 | P a g e
and inorganic compounds and alteration of trophic
interaction among species.
III. SEWAGE WATER
Raw sewage water available from cities is a
mixture of domestic, commercial and industrial
activities. Currently more than 450 cities in India
generate more than 17 million cubic meters of raw
sewage water per day Since the raw sewage water is
rich in organic matter and essential nutrients, sewage
farming is quite common in all urban areas. In the
country as a whole, about 200 sewage farms,
covering as area of about 50,000 ha, are utilizing
sewage waters to supplement the nutrients and water
supply. Some city sewage waters where industrial
effluent is discharged in to sewer system may contain
toxic metals in high amounts. Thus the composition
of domestic sewage may be changed with the type of
industries discharging their effluents.
3.1 Composition of Sewage Water
The composition of sewage water is quite
variable depending upon the contributing source,
mode of collection and treatment provided. Although
a large proportions of these sewage waters is organic
in nature and contains essential plant nutrients but
sometimes toxic metals are also present in
appreciable amounts. The sewage water generated in
India contains more than 90% water. The solid
portion contains 40-50% organics, 30-40% inert
materials, 10-15% bio-resistant organics and 5-8%
miscellaneous substances.
It was within normal range and irrigation
with these waters in not going to cause any
significant change in the soil pH due to high
buffering capacity of the soils.
Table 3.1
IV. RECOMMENDED MAXIMUM
CONCENTRATION (MG L-1) OF
HEAVY METALS FOR USE OF
EFFLUENTS IN AGRICULTURE
The Central Pollution Control Board (CPCB)
formulated a Ganga project in 1984 to clean the water
of Ganga river. This project aimed at the installation
of sewage treatment plants at various sites along
Ganga river in the important cities and towns. Cities
selected for the installation of sewage treatment
plants include 26 cities in Uttar Pradesh, 15 in Bihar
and 59 in West Bengal have been identified as the
worst polluting cities because they contribute 84% of
the total pollutants of the Ganga. Physical
properties of sewage and well -irrigated soils table
4.1 given below.
V. POSSIBLE SOLUTIONS OF
PROBLEMS ASSOCIATED WITH THE
SEWAGE AND INDUSTRIAL
EFFLUENTS
 To exploit the sewage waters as a potential
source of irrigation and maintain
environment, the sewage waters must be
diluted either with canal or underground
waters to avoid the excessive accumulation
of soluble salts in the soils. It will help in
maintaining the productivity of agricultural
crops without any harmful effect on soil
properties. Entry of heavy metals into food
chain can be reduced by adopting soil and
crop management practices, which
immobilize these metals in soils and reduce
their uptake by plants.
 Heavy phosphate application and also the
application of kaolin/zeolite to soils can
reduce the availability of heavy metals.
 Raising hyper accumulator plants
(mustard/trees) in toxic metals contaminated
soils is recommended to avoid the entry of
toxic metals in the food chain.
VI. CONCLUSION
The major environmental concern is an
urbanizing India relate to high levels of water
T.SUBRAMANI et al Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 4, Issue 6( Version 2), June 2014, pp.270-273
www.ijera.com 273 | P a g e
pollution due to poor waste disposal, inadequate
sewerage and drainage, and improper disposal of
industrial effluents. The sewage and industrial
effluents contain essential nutrients or possess
properties which can easily be utilized for irrigating
the field crops. But the sewage water of many cities
where industrial effluent is mixed in the sewage
system contained toxic metals. Continuous use of
sewage and industrial effluents irrigation recorded
improvement in water retention, hydraulic
conductivity, organic C and build-up of available N,
P, K and micronutrient status and soil microbial
count.
REFERENCES
[1]. Adhikari, S.; Gupta, S.K. & Banerjee, S.K.
(1993). Heavy metals content of city sewage
and sludge. Journal of Indian Society of Soil
Science, 41: 160-172.
[2]. Adhikari, S.; Gupta, S.K. & Banerjee, S.K.
(1997). Long-term effect of raw sewage
application on the chemical composition of
ground water. Journal of Indian Society of
Soil Science, 45: 392-394.
[3]. Antil, R.S. & Narwal, R.P. (2005). Problems
and prospectus of utilization of sewer water
in Haryana. In: Management of Organic
Wastes for Crop Production, K.K. Kapoor,
P.K. Sharma, S.S. Dudeja & B.S. Kundu,
(Ed.), 159- 168, Department of Microbiology,
CCS Haryana Agricultural University, Hisar,
India.
[4]. Antil, R.S. & Narwal, R.P. (2008). Influence
of sewer water and industrial effluents on soil
and plant health. In: Groundwater resources:
Conservation and management, V.D.Puranik,
V.K. Garg, A. Kaushik, C.P. Kaushik, S.K.
Sahu, A.G. Hegde, T.V. Ramachandarn, I.V.
Saradhi & P. Prathibha, (Ed.), 37-46,
Department of Environmental Science and
Engineering, GJU Science and Technology
Hisar, India.
[5]. Gupta, S.K. & Mitra, A. (2002). In: Advances
in Land Resource Management for 21st
Century, 446-469, Soil Conservation Society
of India, New Delhi. Indian Standards (IS)
(1982). Tolerance limits for inland surface
water subject to pollution, Indian Standards
IS, 2296.
[6]. IISS Annual Report (2006-07). Recycling and
rational use of different waste in agriculture
and remediation of contaminated soils.
Annual Report of Indian Institute of Soil
science (ISSS), pp 72-83, Bhopal, India.
[7]. Joshi, P.K. & Yadav, R.K. (2005). Effect of
sewage on microbiological and chemical
properties and crop growth in reclaimed
alkali soil. Proceedings of the International
Conference on Soil, water and Environment
Quality, Issues and Stratigies, Jan. 28 – Feb.
1, 2005, New Delhi.
[8]. Singh, J. & Kansal, B.D. (1985b). Effect of
long term application of municipal waste
water on some chemical properties of soil.
Journal of Research Punjab Agricultural
University, 22: 235-242.
[9]. United States Salinity Laboratory Staff
(USSL) (1954). Diagnosis and improvement
of saline and alkali soils, Agriculture
Handbook No. 60, U.S. department of
Agriculture of agriculture, Washington, D.C.
[10]. Verma, K.B. & Kumar, P. (2004). Effect of
agro based industrial effluents on the growth
and development of wheat (Triticum aestivum
L. var. RR21), maize (Zea mays L.) and
mustard (Brassica compestris L.). Indian
Journal of Ecology, 31: 93-96.

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An04602270273

  • 1. T.SUBRAMANI et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 4, Issue 6( Version 2), June 2014, pp.270-273 www.ijera.com 270 | P a g e Impact of Sewage and Industrial Effluent on Soil Plant Health Act on Environment T. Subramani1 M. Mangaiyarkarasi2 C. Kathirvel3 1 Professor & Dean, Department of Civil Engineering, VMKV Engineering College, Vinayaka Missions University, Salem, India. 2,3, PG Student of Environmental Engineering, Department of Civil Engineering, VMKV Engineering College, Vinayaka Missions University, Salem, ABSTRACT Effect of continuous irrigation with sewage effluent on soil properties and status of nutrients and pollutant elements in soils and plants in the adjoining areas of Agra and Mathura cities of Uttar Pradesh was ascertained. The physical properties of soils improved due to sewage water irrigation. An appreciable increase in organic carbon, available N, P, K contents was recorded in the sewage water irrigated soils. Electrical conductivity of sewage water irrigated soils was much below the threshold limit of salinity. Application of sewage water resulted in the accumulation of heavy metals in surface soil. The mean contents of total Cd, Cr, Pb in the soils irrigated with sewage water were 2.85, 75.40 and 40.26 mg kg- 1, respectively. The mean values of available Cd, Cr and Pb in soils were 0.21, 0.33 and 1.27 mg kg-1, respectively. The concentration of Cr in lettuce, cabbage and be seem plants grown on sewage water was higher as compared to its tolerance level indicating their accumulation in plants. In general, Cd was relatively higher in lettuce (0.88 mg kg-1). On the other hand, be seemed contained relatively higher amount of Cr and Pb. KEYWORDS: Impact, Sewage, Industrial Effluent, Soil Plant Health, Environment. I. INTRODUCTION It provides farmers with a nutrient enriched water supply and society with a reliable and inexpensive system for wastewater treatment and disposal. Some of these effluents are a rich source of plant nutrients, therefore soil provides the logical sink for their disposal. But many untreated and contaminated sewage and industrial effluents may have high concentration of several heavy metals such Cd, Ni, Pb and Cr. Field study was conducted in Salem area, to evaluate the effects of using sewage water to irrigate the fields near ground water wells in this region. Many quality parameters like pH, EC, total alkalinity, total hardness, Ca+2, Mg+2, Cl-1, So4-2, Na+1 and Potassium. The analysis of samples showed alkaline nature of the water in research area. Also the results refer to high salt water levels compared with classifications of WHO. The two most common treatments prior to sludge applications to agriculture seem to be anaerobic digestion and lime stabilization. In some of the old Member States (EU15), land application of raw and/or limited treated sludge is diminishing and composting and other treated products are increasingly used. There is also an increase of advanced treated sludge to be used in non- agricultural applications. Sludge is also used as a soil improver on degraded soils at mine sites, construction sites, and other disturbed areas such as in Portugal (Duarte) where sludge has been used for stabilizing soils after forest fires. However, use of sludge in forests is relatively uncommon or even prohibited in some Member States. Most Member States are, in general, moving away from land filling to recycling sludge to land and/or – to a lesser extent – incineration with some recovery of energy. II. EFFECTS ON BIOLOGICAL, PHYSICAL, SOCIAL AND ECONOMICAL ENVIRON Nuisance (Odor, Noise, Vermin and Fire) 2.1 Impacts There will not be odor, noise and vermin problems at the plant that can affect the residents. Even the worker(s) will not be affected by the odor. However, there is the possibility of mosquito breeding in the open aeration tank of the plant and also in the water pond, where the effluent will be discharged, which can cause nuisance to the people during the summer months. The plant will not attract RESEARCH ARTICLE OPEN ACCESS
  • 2. T.SUBRAMANI et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 4, Issue 6( Version 2), June 2014, pp.270-273 www.ijera.com 271 | P a g e flies, rodents and other animals. Occurrence of fire is not possible unless the biogas release valves do not function properly and create explosive situations. 2.2 Water Impacts In general, the existence of the WWTP will have a positive impact on the surface and ground water quality of the area because it will eliminate the existing septic tanks in the western part of the village, which cause pollution and create health problems. However, the discharge of treated effluents from the plant to the runoff channel will have some slight impacts, particularly during the wet season, extending from November to April. In addition, the water stream located in the vicinity of the plant may be contaminated if effluents do not meet the standards. During the dry season the discharged water can be used for irrigation of forest trees, or used by farmers. If the removed grease from the grease trap is dumped haphazardly at the plant site it will impact the surface waters, particularly during the wet season when the rains carry them down into the valley. 2.3 Air Impacts Air pollution will result during the excavation and construction phase. Dusty conditions will occur. Also vehicular emissions will take place. But this will occur for a period of 2 to 3 months. During the operational phase of the plant no such conditions will result. Gaseous and particulate emissions will have their impacts on the natural vegetation. If flaring of biogas does not take place, methane gas will be released into the atmosphere, which is a powerful greenhouse gas and it will have negative impact on the global climate. 2.4 Climate Impacts The existence of the WWTP will not have any negative effect on the microclimate of the area. This will be improved against the climate extremities (wind and storms), by planting trees in the neighborhood of the plant. Greenhouse gases, such as methane gas, will be produced in the bio-digesters of the plant and if released, this will have negative impact on the climate. 2. 5 Soil Impacts Sandy soil and rocks will be excavated during the construction phase of the treatment plant. If it coincides with the rainy season, this will cause soil erosion at the site. However, since the site is already dug, minimal excavation work is required. The use of treated wastewater for irrigation will improve the fertility of agricultural lands of the area. But when unsatisfactorily treated effluents are released, these might contaminate the soils. If the grease and sludge (once in 20 years) are not properly handled and managed they can contaminate the nearby soils and create unsighty conditions. 2.6 Landscape Impact The bio-digesters of the WWTP/2 will be constructed underground at a distance of at least 1000m far from the nearest house. The WWTP will be the only structure in the area. But since the digesters are going to be partially buried inside the abandoned quarry, they will be hidden by the surrounding natural fence of trees, which will surround it. Therefore, the visual impact on the project would be positive. 2.7 Fauna Impacts The fauna in the project area is very limited. It consists of some birds, rodents, snakes and turtles. During the construction phase of the plant these animals will be disturbed and their habitat affected. The physical existence of the plant might scare the birds. Effluents of the WWTP will have some minor impact on the soil microorganisms, particularly in the immediate vicinity of the water pond, where it will be discharged. In dry season the plant effluents can become a water source for the wild animals and birds. 2.8 Impacts of sewage effluents Sewage effluents have historically been discharged through outfall in shallow coastal and waters (Young-Jin Suh and Rousseaux P., 2001, Mclntyre 1995, Klaus Koop and Pat Hutchings 1996) and is one of the major stresses impacting coastal ecosystems. There are usually significant effects on water quality and on marine life arising from sewage disposal. Water quality deterioration is one of the most important water resource issues of the 21st century. Therefore the quality status of coastal surface water is very important and would always be under public scrutiny because of health risk associated with sewage contamination. The potential deleterious effects of pollutants from sewage effluents on the receiving water quality of the coastal environment are manifold and depend on volume of the discharge, the chemical composition and concentrations in the effluent. It also depends on type of the discharge for example whether it is amount of suspended solids or organic matter or hazardous pollutants like heavy metals and organo chlorines, and the characteristics of the receiving waters (NAP, 1984, Canter W., 1996: Nemerow and Dasgupta, 1991). High levels of soluble organics may cause oxygen depletion (Peter and Robin, 2002) with a negative effect on aquatic biota. Contamination of the coastal water may result in changes in nutrient levels, abundance, biomass and diversity of organisms, bioaccumulation of organic
  • 3. T.SUBRAMANI et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 4, Issue 6( Version 2), June 2014, pp.270-273 www.ijera.com 272 | P a g e and inorganic compounds and alteration of trophic interaction among species. III. SEWAGE WATER Raw sewage water available from cities is a mixture of domestic, commercial and industrial activities. Currently more than 450 cities in India generate more than 17 million cubic meters of raw sewage water per day Since the raw sewage water is rich in organic matter and essential nutrients, sewage farming is quite common in all urban areas. In the country as a whole, about 200 sewage farms, covering as area of about 50,000 ha, are utilizing sewage waters to supplement the nutrients and water supply. Some city sewage waters where industrial effluent is discharged in to sewer system may contain toxic metals in high amounts. Thus the composition of domestic sewage may be changed with the type of industries discharging their effluents. 3.1 Composition of Sewage Water The composition of sewage water is quite variable depending upon the contributing source, mode of collection and treatment provided. Although a large proportions of these sewage waters is organic in nature and contains essential plant nutrients but sometimes toxic metals are also present in appreciable amounts. The sewage water generated in India contains more than 90% water. The solid portion contains 40-50% organics, 30-40% inert materials, 10-15% bio-resistant organics and 5-8% miscellaneous substances. It was within normal range and irrigation with these waters in not going to cause any significant change in the soil pH due to high buffering capacity of the soils. Table 3.1 IV. RECOMMENDED MAXIMUM CONCENTRATION (MG L-1) OF HEAVY METALS FOR USE OF EFFLUENTS IN AGRICULTURE The Central Pollution Control Board (CPCB) formulated a Ganga project in 1984 to clean the water of Ganga river. This project aimed at the installation of sewage treatment plants at various sites along Ganga river in the important cities and towns. Cities selected for the installation of sewage treatment plants include 26 cities in Uttar Pradesh, 15 in Bihar and 59 in West Bengal have been identified as the worst polluting cities because they contribute 84% of the total pollutants of the Ganga. Physical properties of sewage and well -irrigated soils table 4.1 given below. V. POSSIBLE SOLUTIONS OF PROBLEMS ASSOCIATED WITH THE SEWAGE AND INDUSTRIAL EFFLUENTS  To exploit the sewage waters as a potential source of irrigation and maintain environment, the sewage waters must be diluted either with canal or underground waters to avoid the excessive accumulation of soluble salts in the soils. It will help in maintaining the productivity of agricultural crops without any harmful effect on soil properties. Entry of heavy metals into food chain can be reduced by adopting soil and crop management practices, which immobilize these metals in soils and reduce their uptake by plants.  Heavy phosphate application and also the application of kaolin/zeolite to soils can reduce the availability of heavy metals.  Raising hyper accumulator plants (mustard/trees) in toxic metals contaminated soils is recommended to avoid the entry of toxic metals in the food chain. VI. CONCLUSION The major environmental concern is an urbanizing India relate to high levels of water
  • 4. T.SUBRAMANI et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 4, Issue 6( Version 2), June 2014, pp.270-273 www.ijera.com 273 | P a g e pollution due to poor waste disposal, inadequate sewerage and drainage, and improper disposal of industrial effluents. The sewage and industrial effluents contain essential nutrients or possess properties which can easily be utilized for irrigating the field crops. But the sewage water of many cities where industrial effluent is mixed in the sewage system contained toxic metals. Continuous use of sewage and industrial effluents irrigation recorded improvement in water retention, hydraulic conductivity, organic C and build-up of available N, P, K and micronutrient status and soil microbial count. REFERENCES [1]. Adhikari, S.; Gupta, S.K. & Banerjee, S.K. (1993). Heavy metals content of city sewage and sludge. Journal of Indian Society of Soil Science, 41: 160-172. [2]. Adhikari, S.; Gupta, S.K. & Banerjee, S.K. (1997). Long-term effect of raw sewage application on the chemical composition of ground water. Journal of Indian Society of Soil Science, 45: 392-394. [3]. Antil, R.S. & Narwal, R.P. (2005). Problems and prospectus of utilization of sewer water in Haryana. In: Management of Organic Wastes for Crop Production, K.K. Kapoor, P.K. Sharma, S.S. Dudeja & B.S. Kundu, (Ed.), 159- 168, Department of Microbiology, CCS Haryana Agricultural University, Hisar, India. [4]. Antil, R.S. & Narwal, R.P. (2008). Influence of sewer water and industrial effluents on soil and plant health. In: Groundwater resources: Conservation and management, V.D.Puranik, V.K. Garg, A. Kaushik, C.P. Kaushik, S.K. Sahu, A.G. Hegde, T.V. Ramachandarn, I.V. Saradhi & P. Prathibha, (Ed.), 37-46, Department of Environmental Science and Engineering, GJU Science and Technology Hisar, India. [5]. Gupta, S.K. & Mitra, A. (2002). In: Advances in Land Resource Management for 21st Century, 446-469, Soil Conservation Society of India, New Delhi. Indian Standards (IS) (1982). Tolerance limits for inland surface water subject to pollution, Indian Standards IS, 2296. [6]. IISS Annual Report (2006-07). Recycling and rational use of different waste in agriculture and remediation of contaminated soils. Annual Report of Indian Institute of Soil science (ISSS), pp 72-83, Bhopal, India. [7]. Joshi, P.K. & Yadav, R.K. (2005). Effect of sewage on microbiological and chemical properties and crop growth in reclaimed alkali soil. Proceedings of the International Conference on Soil, water and Environment Quality, Issues and Stratigies, Jan. 28 – Feb. 1, 2005, New Delhi. [8]. Singh, J. & Kansal, B.D. (1985b). Effect of long term application of municipal waste water on some chemical properties of soil. Journal of Research Punjab Agricultural University, 22: 235-242. [9]. United States Salinity Laboratory Staff (USSL) (1954). Diagnosis and improvement of saline and alkali soils, Agriculture Handbook No. 60, U.S. department of Agriculture of agriculture, Washington, D.C. [10]. Verma, K.B. & Kumar, P. (2004). Effect of agro based industrial effluents on the growth and development of wheat (Triticum aestivum L. var. RR21), maize (Zea mays L.) and mustard (Brassica compestris L.). Indian Journal of Ecology, 31: 93-96.