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SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732
Venkateswarlu and Venkatrayulu, 2019
DOI:10.21276/SSR-IIJLS.2019.5.5.3
Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2387
Assessment of Heavy Metals in Water of Selected Places of Nellore
coast of Andhra Pradesh through Atomic Absorption Spectroscopy
Vardi Venkateswarlu1*
, Chenji Venkatrayulu2
1
Research Scholar, Department of Marine Biology, Vikrama Simhapuri University, Nellore-524320, Andhra Pradesh,
India
2
Assistant Professor, Department of Marine Biology, Vikrama Simhapuri University, Nellore-524320, Andhra Pradesh,
India
*Address for Correspondence: Mr. Vardi Venkateswarlu, Research Scholar, Department of Marine Biology, Vikrama
Simhapuri University, Nellore– 524320, Andhra Pradesh, India
E-mail: venkat9160@gmail.com
Received: 13 Apr 2019/ Revised: 21 Jul 2019/ Accepted: 16 Aug 2019
ABSTRACT
Background: The rapid industrialization of the coastal areas has resulted in marine pollution in different regions of the Southeast
coast of India. The quality of coastal and marine water affected by the toxic pollutants released from the industrial activities and
urbanization has been assessed in terms of pollution. The present study area also referred that the industrial activity is more
responsible for marine pollution, causing toxic effects by heavy metals.
Methods: For the present study water samples collected from Nelaturu, Krishnapatnam coastal villages of Nellore and samples
brought to the laboratory for heavy metals analysis by Atomic Absorption Spectroscopy (AAS) standard methods followed by
American Public Health Association (APHA).
Results: During the present study the heavy metals Arsenic, Lead, Cadmium, Mercury, Iron, Manganese, Copper, Zinc
concentrations were observed, shown in Table 1 and discussed the levels when compared with water quality standards given by
the Indian Standards (IS: 10500) and WHO guidelines.
Conclusion: The present study sites are one of the famous places for marine fishing area having near thermal power plants and
port activities. In our study, there were eight heavy metals were determined, which were observed in 2 sampling sites i.e.
Nelaturu, Krishnapatnam in Nellore district. The study had been concluded with the future impact of heavy metals in the marine
environment and to the aquatic life as well as to human life at Nellore coast.
Key-words: Atomic Absorption Spectroscopy (AAS), Coastal water pollution, Heavy metals, Mineralogical contamination, Nellore
coast
INTRODUCTION
Coastal water pollution is one of the major
environmental problems in the worldwide. The coastal
water pollution is due to the mineralogical
contamination and dumping of the untreated industrial
and municipal wastes directly into the sea coasts through
canals. Heavy metals are generally water-soluble, no
degradable, vigorous oxidizing agents and are strongly
How to cite this article
Venkateswarlu V, Venkatrayulu C. Assessment of Heavy Metals in
Water of Selected Places of Nellore coast of Andhra Pradesh
through Atomic Absorption Spectroscopy. SSR Inst. Int. J. Life Sci.,
2019; 5(5): 2387-2392.
Access this article online
https://iijls.com/
bonded with many biochemicals inhibiting their
functions. The rapid industrialization in coastal regions
resulted in environmental pollution and higher quantities
of heavy metals are being added into the natural
estuarine and coastal environments. The heavy metal
contamination in the coastal water has connections
directly to the biota and indirectly to human life. They
will also cause irregularity in blood; badly affect the
major functioning organs like kidneys and liver. Heavy
metals including both essential and nonessential
elements have a particular significance in ecotoxicology
since they are highly persistent and all have the potential
to be toxic to the living organisms [1]
.
Heavy metals are considered the foremost
anthropogenic contaminants in coastal and marine
environments worldwide [2]
.
Research Article
SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732
Venkateswarlu and Venkatrayulu, 2019
DOI:10.21276/SSR-IIJLS.2019.5.5.3
Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2388
They pose a serious threat to human health, natural
ecosystems and living organisms because of their
toxicity, persistence and bioaccumulation characteristics
[3]
. Numerous substantial heavy metals are known to be
toxic or carcinogenic to humans [4]
and also play a
significant role as sensitive indicators for monitoring
contaminants in aquatic systems [5]
. Several studies have
demonstrated that marine sediments are highly polluted
by heavy metals [6]
. Therefore; the evaluation of metal
distribution in surface sediment is useful to assess
pollution in the marine environment along the east coast
of India. Industrial activities, economic development, and
urbanization of all over the globe have risen very quickly
in recent years and substantial quantities of
contaminants are introduced into rivers, estuarine areas
and coastal regions [7]
. The water which provides habitats
for many aquatic organisms was polluted with various
forms of hazardous and toxic substances, including heavy
metals [8]
. As a result, they are considered to be
important carriers as well as the heavy metals in the
aquatic cycle is important to know the distribution and
concentration of heavy metals in the study area. In
several studies, many authors investigated the
distribution of heavy metals and the pollution status
using environmental assessment indices.
The present work would be of assistance to the relevant
researchers in ensuring a heavy metals status of the
neighboring coastal water bodies in Nellore, Andhra
Pradesh and would function as a foundation for further
work for the present study area.
This work carried out to elucidate the coastal
management by providing primary data sets for decision-
making policyholders. Also beside, the baseline
information will form a flat form for the stakeholders to
monitor the coastal pollution by inexpensive biomarkers
and also manage and conserve the study area from
further pollution hazards. Further, the pollution levels for
the study area can be constantly monitored to safeguard
the fishing community and biodiversity.
MATERIALS AND METHODS
The present study conducted during the month of April
2019 by the Department of Marine Biology, Vikrama
Simhapuri University, Nellore, Andhra Pradesh, India.
Study Area- The Nellore district has a 169 km of the
coastal line with habitation of fishermen community
along the east coast of India. The Nellore coastal region
is suitable for the brackishwater aquaculture farming,
recently gradually increased some industrial activities.
The present sampling sites of Nelaturu and
Krishnapatnam coastal areas have thermal power
industries and also shipping activities from this coastal
region (Fig. 1).
Fig. 1: Map showing the study areas of Nelaturu and Krishnapatnam coastal regions of Nellore coast of Andhra
Pradesh in India
SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732
Venkateswarlu and Venkatrayulu, 2019
DOI:10.21276/SSR-IIJLS.2019.5.5.3
Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2389
Sample collection- The coastal saltwater samples were
collected by following the quality sample assortment
protocol and tips given in Indian Standards strategies IS
3025 part-1 and APHA twenty-second edition. The
special precautions were taken throughout the sampling
of water within the elite places of study areas. Before the
gathering of the samples, the sample containers square
measure soaked night long in a pair of aqua fortis and
washed with double H2O and dried during a clean space.
At every sampling location, water samples were
collected in 2 pre-cleaned containers for duplicate
mensuration. The bottles were rinsed thrice with the
coastal saltwater sample of the actual location. Total 0.5
mL of above pure grade aqua fortis was added into the
collected samples to avoid the contamination and also to
stop the loss of metals from the sample. All the collected
samples were preserved at 4o
C by employing a thermo-
coal box with ice packs at the sample assortment site.
Sample preparation for analysis- The digestion
procedure for water samples was carried out by
transferring a measured volume (50 mL) of well-mixed
acid preserved water sample to a conical flask then 5 mL
of concentrated nitric acid (Conc. HNO3) was added into
the flask. The water sample and Nitric acid mixture were
boiled and evaporated on a hot plate to the lowest
volume of up to 10 to 20 ml. Continued the heating and
adding conc. Nitric acid (HNO3) to the sample digestion
was complete to show by a light color clear solution in
the sample digestion conical flask. After that conical flask
was washed down with distilled water and filtered. Then
the filtrate was transferred into 10 mL volumetric flask
with two 5 ml of water, adding these rinsing to the
volumetric flask and cooled and diluted to the mark and
mixed thoroughly followed by Brooks et al. [9]
. A portion
of the sample solution was taken for the required metal
determinations flowed by APHA [10]
.
Heavy metals analysis by Atomic Absorption
Spectroscopy- AAS is most widely using an analytical
technique for the determination of trace and heavy
metals up to parts per billion levels. AAS is a very useful
technique to determine trace levels of multi-elements in
single aspiration. AA-6800 AAS coupled with GFA-EX7
graphite furnace atomizer and ASC-6100 auto sampler
from Shimadzu (Koyoto, Japan) was used for heavy metal
analysis. A high-density graphite tube was used for
atomization. Normal single hollow cathode lamps were
used for irradiation followed by APHA [10]
.
RESULTS
The ranges of the heavy metals viz., Arsenic (As), Lead
(Pb), Cadmium (Cd), Mercury (Hg), Iron (Fe), Manganese
(Mn), Copper (Cu) and Zinc (Zn) presented in the coastal
water of Nelaturu, Krishnapatnam regions of Nellore
coast in summer April 2019 during the study period
observed the industrial activities in thermal power
station and shipping activities are more. The
concentration of Pb maximum range 4.67±0.12 was
observed at Nelaturu coast, and 3.03±1.13 found at
Krishnapatnam. Cd maximum range 3.03±1.13 was
observed at Krishnapatnam than Nelaturu 2.66±0.09.
The levels of As observed nearly in Krishnapatnam
1.20±0.001 and in Nelaturu 1.16±0.02 was observed.
However the concentration of Cu was 0.09±0.001
observed more than the permissible range at
Krishnapatnam coast and As, Pb, Cd, Cu were more than
permissible levels and Fe and Zn were observed within
the ranges of IS 10500 and WHO water safety guidelines.
Hg, Mn, Cu, Zn were not observed at Nelaturu coast
whereas, Hg and Mn were not observed at
Krishnapatnam coast. The concentrations of heavy
metals obtained from AAS analysis is presented in Table
1.
Table 1: Heavy metals in the coastal water of (Nelaturu, Krishnapatnam) Nellore (mg/lt) Mean±SD (n=6) in Andhra
Pradesh, comparison with WHO and IS: 10500 standards
S.No.
Name of the
Metal
Nelaturu COAST
(Mean±SD)
Krishnapatnam Coast
(Mean±SD)
IS 10500
Standards
W.H.O
Standards
1 Arsenic (As) 1.16±0.02 1.20±0.001 0.01 0.01
2 Lead (Pb) 4.67±0.12 3.64±0.02 0.01 0.01
3 Cadmium (Cd) 2.66±0.09 3.03±1.13 0.003 0.003
SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732
Venkateswarlu and Venkatrayulu, 2019
DOI:10.21276/SSR-IIJLS.2019.5.5.3
Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2390
4 Mercury (Hg) N.D N.D 0.001 0.001
5 Iron (Fe) 0.04±0.004 0.01±0.0.001 0.3 0.2
6 Manganese (Mn) N.D N.D 0.1 0.5
7 Copper (Cu) N.D 0.09±0.001 0.05 2.0
8 Zinc (Zn) N.D 0.01±0.002 5.0 3.0
N.D= Not Detected
DISCUSSION
The ranges of the heavy metals were present in the
coastal water of Nelaturu, Krishnapatnam coastal regions
of Nellore coast in the present study obtained from AAS
analysis as discussed below. Although there was no clear
definition of what a heavy metal density is in most cases
taken to be the defining factor. Heavy metals are thus
generally defined as those having a specific density of
more than 5 g/cm3
. Heavy metals are among the most
common environmental pollutants, and their occurrence
in water and biota indicate the presence of natural or
anthropogenic sources. Although adverse health effects
of heavy metals have been known for a long time,
discharge of heavy metals continues and is even
increasing in some areas are particularly in less
developed countries. The main threats to human health
from heavy metals are associated with exposure to lead,
cadmium and mercury. Their accumulation and
distribution in soil, sediments and aquatic environment
are increasing at an alarming rate thereby affecting
marine life [11-13]
.
A number of elements are normally present in relatively
low to high concentrations, usually more than a few
mg/L, in conventional irrigation water and are called
trace elements. Heavy metals are a special group of trace
elements which have been shown to create definite
health hazards when taken up by plants. The observed
experimental value was very much higher than the
permissible limit of iron, which was 0.3 mg/L. The
presence of a high concentration of Fe may increase the
hazard of pathogenic organisms; since most of these
organisms need Fe for their growth [14]
.
Arsenic (As) concentrations were observed 1.16 mg/L in
Nelaturu beach, 1.20 mg/L in Krishnapatnam coast. The
maximum concentrations were observed in both study
areas. The permissible limit for Arsenic as per IS: 10500 is
0.01 mg/L and maximum guideline value as per the WHO
is 0.01 mg/L. However, the observed concentration
levels of Arsenic in the study area were observed as
excess than acceptable limits given by the IS: 10500 and
WHO guidelines. Long-time exposure to arsenic in
drinking water can cause cancer in the skin, lungs,
bladder, and kidney. It can also cause other skin changes
such as thickening and pigmentation [15]
.
Lead (Pb) concentrations were observed 4.67 mg/L in
Nelaturu, 3.64 mg/L in Krishnapatnam coast. The
maximum concentrations were observed in both study
areas. The permissible limit for Lead is as per IS: 10500 is
0.01 mg/L. Lead is a highly toxic metal substance,
exposure to which can produce a wide range of adverse
health effects in both adults and children. Every year,
industries producing about 2.5 million tons of lead
throughout the world that used for making batteries. In
adults, lead can increase blood pressure and cause
infertility problems, nerve disorders, muscle and joint
pain, irritability and memory or concentration problems
come [16,18]
.
Cadmium (Cd) concentrations were observed 2.66 mg/L
in Nelaturu, 3.03 mg/L in Krishnapatnam coast the
maximum concentrations were observed in both study
areas. The permissible limit for Cadmium is as per IS:
10500 is 0.003 mg/L. cadmium is widely distributed in
the earth’s crust and is principally used in many
industries and in agriculture, according to USPH
standards. Higher values of Cd in wastewater effluent
samples suggest the high level of pollution due to dyes
paints and pigments manufacturing industries [14]
.
Cadmium targets the liver, placenta, kidneys, lungs,
brain, and bones. Consumption of food or drinking water
with very high cadmium levels severely irritates the
stomach, leading to vomiting and diarrhea and
sometimes causes death [17]
.
Mercury (Hg) concentrations were observed <1.0 mg/L
below Detection Level (BDL) in Nelaturu and
Krishnapatnam coast. The maximum acceptable limit for
Mercury as per IS: 10500 is 0.001 mg/L permissible value
SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732
Venkateswarlu and Venkatrayulu, 2019
DOI:10.21276/SSR-IIJLS.2019.5.5.3
Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2391
and values are within the permissible limits given by IS:
10500 and WHO guidelines. There are three forms of
mercury and among these the most toxic one is the
organic form, viz., methyl mercury. Methyl mercury is a
microbiologically transformed form of inorganic mercury
when it reaches aquatic environments, water bodies or
in soils. Inorganic and organic mercury is toxic to the
human body in different ways, affecting different organs
in different ways it may primarily expose to mercury via
food, where fish is the major source of methyl mercury
exposure by biomagnification. Mercury has no necessary
function in any living organism and is considered as a
non-essential metal, and is among the most toxic
elements to man and many higher animals [19]
.
Iron concentrations were observed 0.0487 mg/L in
Nelaturu, 0.0107 mg/L in Krishnapatnam coast. The
maximum acceptable limit for iron as per IS: 10500 is 0.3
mg/L and no guideline value was given by the WHO for
Iron content. However, the observed concentration
levels of Iron found within the permissible given by the
IS: 10500 CPCB [20]
.
Manganese (Mn) concentrations were observed <1.0
mg/L BDL in Nelaturu and Krishnapatnam coast. The
maximum acceptable limit for Manganese as per IS:
10500 is 0.1 mg/L and permissible value 0.3 mg/L and
provisional guideline value as per the WHO is 0.4 mg/L.
The observed manganese values were within the
permissible limits given by IS: 10500 and WHO guidelines
CPCB[20]
.
Copper (Cu) concentrations were observed <1.0 mg/L
BDL in Nelaturu, 0.096 mg/L in Krishnapatnam coast. It is
within the permissible limits at Nelaturu given by IS:
10500 and WHO guidelines. Copper is one of the
essential metals to life despite being as inherently toxic
as non-essential heavy metal exemplified by lead and
mercury. Plants and animals rapidly accumulate it. It is
toxic at minute low concentration in water and is known
to cause brain damage in mammals. The natural inputs
of copper to the marine aquatic environment are from
erosion of mineralized rocks or maybe from the
industries. Anthropogenic inputs of copper are from
industries and paints. It also forms complexes with
organic molecules. Mollusks have a tremendous capacity
to accumulate copper from contaminated water CPCB
[20]
.
Zn concentrations were observed <1.0 mg/L BDL in
Nelaturu, 0.01 mg/L in Krishnapatnam coast. It is within
the permissible limits at Nelaturu given by IS: 10500 and
WHO guidelines. Zinc is an essential nutrient for the
human body and has importance for health also it acts as
a catalytic or structural component in many enzymes
that are involved in energy metabolism also. Symptoms
of zinc toxicity are slow reflexes, tremors, paralyzation of
extremities, anemia, metabolic disorder, teratogenicity
effects and increased mortality in humans CPCB [20]
.
In the present seawater study, the heavy metals of
mercury, manganese and copper concentrations in the
seawater have been observed in BDL<1.0 mg/L.
Increased toxic heavy metal concentrations in the water
lead to the Bioaccumulation factor in the aquatic food
chain and it showed the transfer of metals especially
arsenic, lead, cadmium, mercury are warning signal for
fish consumption by humans towards food safety [20,21]
.
CONCLUSIONS
The environmental parameters of water can be
affected by the toxicity of the metal either by influencing
the physiology of organisms or by altering the chemical
form of the metal in water. The increased ambient heavy
metal concentration will result in accumulation in the
tissues of commercially important edible finfish, shell
fish. It is an inherent danger of higher bioaccumulation
of toxins in the edible species that may result in severe
health hazards to the consumers especially human. It
was evident that the present study on heavy metals in
the water of the Nellore coast suggested adopting
effective heavy metal removal technologies to control
the toxic metal contamination in coastal water.
Further bioaccumulation study to be needed for better
understanding the metal toxicity in the coastal and
marine environment.
ACKNOWLEDGMENTS
Authors are thankful to the Vimta Laboratories Pvt. Ltd.
Nellore, for Atomic Absorption Spectroscopy analysis.
CONTRIBUTION OF AUTHORS
Research concept- Dr. Ch. Venkatrayulu
Research design- Dr. Ch. Venkatrayulu
Supervision- Dr. Ch. Venkatrayulu
Materials- Mr. V. Venkateswarlu
Data collection- Mr. V. Venkateswarlu
Data analysis and Interpretation- Mr. V. Venkateswarlu
Literature search- Mr. V. Venkateswarlu
Writing article- Mr. V. Venkateswarlu
Critical review- Mr. V. Venkateswarlu
SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732
Venkateswarlu and Venkatrayulu, 2019
DOI:10.21276/SSR-IIJLS.2019.5.5.3
Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2392
Article editing- Dr. Ch. Venkatrayulu
Final approval- Dr. Ch. Venkatrayulu
REFERENCES
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[2] Naser HA. Assessment and management of heavy
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[3] DeForest D, Brix K, Adams W. Assessing metal
bioaccumulation in aquatic environments: The
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[4] Fu F, Wang Q. Removal of heavy metal ions from
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[5] Ozkan EY, Buyu KB. Geochemical and statistical
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[6] Pande N, Nayak GN. Understanding distribution and
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[7] Ravichandran R, Manickam S. Heavy metal
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[13]Okafor EC, Opuene K. Preliminary assessment of
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[14]Tiwana NS, Jerath N, Singh G, Ravleen M. (Eds.)
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[16]Gopinathan KM, Amma SR. Bioaccumulation of toxic
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[17]Sindhu PS. Environ. Chem., 2002 pp.75–243, 1st
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Assessment_Heavy_Metals_Water_Selected_Places_Nellore coast_AAS.pdf

  • 1. SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732 Venkateswarlu and Venkatrayulu, 2019 DOI:10.21276/SSR-IIJLS.2019.5.5.3 Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2387 Assessment of Heavy Metals in Water of Selected Places of Nellore coast of Andhra Pradesh through Atomic Absorption Spectroscopy Vardi Venkateswarlu1* , Chenji Venkatrayulu2 1 Research Scholar, Department of Marine Biology, Vikrama Simhapuri University, Nellore-524320, Andhra Pradesh, India 2 Assistant Professor, Department of Marine Biology, Vikrama Simhapuri University, Nellore-524320, Andhra Pradesh, India *Address for Correspondence: Mr. Vardi Venkateswarlu, Research Scholar, Department of Marine Biology, Vikrama Simhapuri University, Nellore– 524320, Andhra Pradesh, India E-mail: venkat9160@gmail.com Received: 13 Apr 2019/ Revised: 21 Jul 2019/ Accepted: 16 Aug 2019 ABSTRACT Background: The rapid industrialization of the coastal areas has resulted in marine pollution in different regions of the Southeast coast of India. The quality of coastal and marine water affected by the toxic pollutants released from the industrial activities and urbanization has been assessed in terms of pollution. The present study area also referred that the industrial activity is more responsible for marine pollution, causing toxic effects by heavy metals. Methods: For the present study water samples collected from Nelaturu, Krishnapatnam coastal villages of Nellore and samples brought to the laboratory for heavy metals analysis by Atomic Absorption Spectroscopy (AAS) standard methods followed by American Public Health Association (APHA). Results: During the present study the heavy metals Arsenic, Lead, Cadmium, Mercury, Iron, Manganese, Copper, Zinc concentrations were observed, shown in Table 1 and discussed the levels when compared with water quality standards given by the Indian Standards (IS: 10500) and WHO guidelines. Conclusion: The present study sites are one of the famous places for marine fishing area having near thermal power plants and port activities. In our study, there were eight heavy metals were determined, which were observed in 2 sampling sites i.e. Nelaturu, Krishnapatnam in Nellore district. The study had been concluded with the future impact of heavy metals in the marine environment and to the aquatic life as well as to human life at Nellore coast. Key-words: Atomic Absorption Spectroscopy (AAS), Coastal water pollution, Heavy metals, Mineralogical contamination, Nellore coast INTRODUCTION Coastal water pollution is one of the major environmental problems in the worldwide. The coastal water pollution is due to the mineralogical contamination and dumping of the untreated industrial and municipal wastes directly into the sea coasts through canals. Heavy metals are generally water-soluble, no degradable, vigorous oxidizing agents and are strongly How to cite this article Venkateswarlu V, Venkatrayulu C. Assessment of Heavy Metals in Water of Selected Places of Nellore coast of Andhra Pradesh through Atomic Absorption Spectroscopy. SSR Inst. Int. J. Life Sci., 2019; 5(5): 2387-2392. Access this article online https://iijls.com/ bonded with many biochemicals inhibiting their functions. The rapid industrialization in coastal regions resulted in environmental pollution and higher quantities of heavy metals are being added into the natural estuarine and coastal environments. The heavy metal contamination in the coastal water has connections directly to the biota and indirectly to human life. They will also cause irregularity in blood; badly affect the major functioning organs like kidneys and liver. Heavy metals including both essential and nonessential elements have a particular significance in ecotoxicology since they are highly persistent and all have the potential to be toxic to the living organisms [1] . Heavy metals are considered the foremost anthropogenic contaminants in coastal and marine environments worldwide [2] . Research Article
  • 2. SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732 Venkateswarlu and Venkatrayulu, 2019 DOI:10.21276/SSR-IIJLS.2019.5.5.3 Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2388 They pose a serious threat to human health, natural ecosystems and living organisms because of their toxicity, persistence and bioaccumulation characteristics [3] . Numerous substantial heavy metals are known to be toxic or carcinogenic to humans [4] and also play a significant role as sensitive indicators for monitoring contaminants in aquatic systems [5] . Several studies have demonstrated that marine sediments are highly polluted by heavy metals [6] . Therefore; the evaluation of metal distribution in surface sediment is useful to assess pollution in the marine environment along the east coast of India. Industrial activities, economic development, and urbanization of all over the globe have risen very quickly in recent years and substantial quantities of contaminants are introduced into rivers, estuarine areas and coastal regions [7] . The water which provides habitats for many aquatic organisms was polluted with various forms of hazardous and toxic substances, including heavy metals [8] . As a result, they are considered to be important carriers as well as the heavy metals in the aquatic cycle is important to know the distribution and concentration of heavy metals in the study area. In several studies, many authors investigated the distribution of heavy metals and the pollution status using environmental assessment indices. The present work would be of assistance to the relevant researchers in ensuring a heavy metals status of the neighboring coastal water bodies in Nellore, Andhra Pradesh and would function as a foundation for further work for the present study area. This work carried out to elucidate the coastal management by providing primary data sets for decision- making policyholders. Also beside, the baseline information will form a flat form for the stakeholders to monitor the coastal pollution by inexpensive biomarkers and also manage and conserve the study area from further pollution hazards. Further, the pollution levels for the study area can be constantly monitored to safeguard the fishing community and biodiversity. MATERIALS AND METHODS The present study conducted during the month of April 2019 by the Department of Marine Biology, Vikrama Simhapuri University, Nellore, Andhra Pradesh, India. Study Area- The Nellore district has a 169 km of the coastal line with habitation of fishermen community along the east coast of India. The Nellore coastal region is suitable for the brackishwater aquaculture farming, recently gradually increased some industrial activities. The present sampling sites of Nelaturu and Krishnapatnam coastal areas have thermal power industries and also shipping activities from this coastal region (Fig. 1). Fig. 1: Map showing the study areas of Nelaturu and Krishnapatnam coastal regions of Nellore coast of Andhra Pradesh in India
  • 3. SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732 Venkateswarlu and Venkatrayulu, 2019 DOI:10.21276/SSR-IIJLS.2019.5.5.3 Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2389 Sample collection- The coastal saltwater samples were collected by following the quality sample assortment protocol and tips given in Indian Standards strategies IS 3025 part-1 and APHA twenty-second edition. The special precautions were taken throughout the sampling of water within the elite places of study areas. Before the gathering of the samples, the sample containers square measure soaked night long in a pair of aqua fortis and washed with double H2O and dried during a clean space. At every sampling location, water samples were collected in 2 pre-cleaned containers for duplicate mensuration. The bottles were rinsed thrice with the coastal saltwater sample of the actual location. Total 0.5 mL of above pure grade aqua fortis was added into the collected samples to avoid the contamination and also to stop the loss of metals from the sample. All the collected samples were preserved at 4o C by employing a thermo- coal box with ice packs at the sample assortment site. Sample preparation for analysis- The digestion procedure for water samples was carried out by transferring a measured volume (50 mL) of well-mixed acid preserved water sample to a conical flask then 5 mL of concentrated nitric acid (Conc. HNO3) was added into the flask. The water sample and Nitric acid mixture were boiled and evaporated on a hot plate to the lowest volume of up to 10 to 20 ml. Continued the heating and adding conc. Nitric acid (HNO3) to the sample digestion was complete to show by a light color clear solution in the sample digestion conical flask. After that conical flask was washed down with distilled water and filtered. Then the filtrate was transferred into 10 mL volumetric flask with two 5 ml of water, adding these rinsing to the volumetric flask and cooled and diluted to the mark and mixed thoroughly followed by Brooks et al. [9] . A portion of the sample solution was taken for the required metal determinations flowed by APHA [10] . Heavy metals analysis by Atomic Absorption Spectroscopy- AAS is most widely using an analytical technique for the determination of trace and heavy metals up to parts per billion levels. AAS is a very useful technique to determine trace levels of multi-elements in single aspiration. AA-6800 AAS coupled with GFA-EX7 graphite furnace atomizer and ASC-6100 auto sampler from Shimadzu (Koyoto, Japan) was used for heavy metal analysis. A high-density graphite tube was used for atomization. Normal single hollow cathode lamps were used for irradiation followed by APHA [10] . RESULTS The ranges of the heavy metals viz., Arsenic (As), Lead (Pb), Cadmium (Cd), Mercury (Hg), Iron (Fe), Manganese (Mn), Copper (Cu) and Zinc (Zn) presented in the coastal water of Nelaturu, Krishnapatnam regions of Nellore coast in summer April 2019 during the study period observed the industrial activities in thermal power station and shipping activities are more. The concentration of Pb maximum range 4.67±0.12 was observed at Nelaturu coast, and 3.03±1.13 found at Krishnapatnam. Cd maximum range 3.03±1.13 was observed at Krishnapatnam than Nelaturu 2.66±0.09. The levels of As observed nearly in Krishnapatnam 1.20±0.001 and in Nelaturu 1.16±0.02 was observed. However the concentration of Cu was 0.09±0.001 observed more than the permissible range at Krishnapatnam coast and As, Pb, Cd, Cu were more than permissible levels and Fe and Zn were observed within the ranges of IS 10500 and WHO water safety guidelines. Hg, Mn, Cu, Zn were not observed at Nelaturu coast whereas, Hg and Mn were not observed at Krishnapatnam coast. The concentrations of heavy metals obtained from AAS analysis is presented in Table 1. Table 1: Heavy metals in the coastal water of (Nelaturu, Krishnapatnam) Nellore (mg/lt) Mean±SD (n=6) in Andhra Pradesh, comparison with WHO and IS: 10500 standards S.No. Name of the Metal Nelaturu COAST (Mean±SD) Krishnapatnam Coast (Mean±SD) IS 10500 Standards W.H.O Standards 1 Arsenic (As) 1.16±0.02 1.20±0.001 0.01 0.01 2 Lead (Pb) 4.67±0.12 3.64±0.02 0.01 0.01 3 Cadmium (Cd) 2.66±0.09 3.03±1.13 0.003 0.003
  • 4. SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732 Venkateswarlu and Venkatrayulu, 2019 DOI:10.21276/SSR-IIJLS.2019.5.5.3 Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2390 4 Mercury (Hg) N.D N.D 0.001 0.001 5 Iron (Fe) 0.04±0.004 0.01±0.0.001 0.3 0.2 6 Manganese (Mn) N.D N.D 0.1 0.5 7 Copper (Cu) N.D 0.09±0.001 0.05 2.0 8 Zinc (Zn) N.D 0.01±0.002 5.0 3.0 N.D= Not Detected DISCUSSION The ranges of the heavy metals were present in the coastal water of Nelaturu, Krishnapatnam coastal regions of Nellore coast in the present study obtained from AAS analysis as discussed below. Although there was no clear definition of what a heavy metal density is in most cases taken to be the defining factor. Heavy metals are thus generally defined as those having a specific density of more than 5 g/cm3 . Heavy metals are among the most common environmental pollutants, and their occurrence in water and biota indicate the presence of natural or anthropogenic sources. Although adverse health effects of heavy metals have been known for a long time, discharge of heavy metals continues and is even increasing in some areas are particularly in less developed countries. The main threats to human health from heavy metals are associated with exposure to lead, cadmium and mercury. Their accumulation and distribution in soil, sediments and aquatic environment are increasing at an alarming rate thereby affecting marine life [11-13] . A number of elements are normally present in relatively low to high concentrations, usually more than a few mg/L, in conventional irrigation water and are called trace elements. Heavy metals are a special group of trace elements which have been shown to create definite health hazards when taken up by plants. The observed experimental value was very much higher than the permissible limit of iron, which was 0.3 mg/L. The presence of a high concentration of Fe may increase the hazard of pathogenic organisms; since most of these organisms need Fe for their growth [14] . Arsenic (As) concentrations were observed 1.16 mg/L in Nelaturu beach, 1.20 mg/L in Krishnapatnam coast. The maximum concentrations were observed in both study areas. The permissible limit for Arsenic as per IS: 10500 is 0.01 mg/L and maximum guideline value as per the WHO is 0.01 mg/L. However, the observed concentration levels of Arsenic in the study area were observed as excess than acceptable limits given by the IS: 10500 and WHO guidelines. Long-time exposure to arsenic in drinking water can cause cancer in the skin, lungs, bladder, and kidney. It can also cause other skin changes such as thickening and pigmentation [15] . Lead (Pb) concentrations were observed 4.67 mg/L in Nelaturu, 3.64 mg/L in Krishnapatnam coast. The maximum concentrations were observed in both study areas. The permissible limit for Lead is as per IS: 10500 is 0.01 mg/L. Lead is a highly toxic metal substance, exposure to which can produce a wide range of adverse health effects in both adults and children. Every year, industries producing about 2.5 million tons of lead throughout the world that used for making batteries. In adults, lead can increase blood pressure and cause infertility problems, nerve disorders, muscle and joint pain, irritability and memory or concentration problems come [16,18] . Cadmium (Cd) concentrations were observed 2.66 mg/L in Nelaturu, 3.03 mg/L in Krishnapatnam coast the maximum concentrations were observed in both study areas. The permissible limit for Cadmium is as per IS: 10500 is 0.003 mg/L. cadmium is widely distributed in the earth’s crust and is principally used in many industries and in agriculture, according to USPH standards. Higher values of Cd in wastewater effluent samples suggest the high level of pollution due to dyes paints and pigments manufacturing industries [14] . Cadmium targets the liver, placenta, kidneys, lungs, brain, and bones. Consumption of food or drinking water with very high cadmium levels severely irritates the stomach, leading to vomiting and diarrhea and sometimes causes death [17] . Mercury (Hg) concentrations were observed <1.0 mg/L below Detection Level (BDL) in Nelaturu and Krishnapatnam coast. The maximum acceptable limit for Mercury as per IS: 10500 is 0.001 mg/L permissible value
  • 5. SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732 Venkateswarlu and Venkatrayulu, 2019 DOI:10.21276/SSR-IIJLS.2019.5.5.3 Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2391 and values are within the permissible limits given by IS: 10500 and WHO guidelines. There are three forms of mercury and among these the most toxic one is the organic form, viz., methyl mercury. Methyl mercury is a microbiologically transformed form of inorganic mercury when it reaches aquatic environments, water bodies or in soils. Inorganic and organic mercury is toxic to the human body in different ways, affecting different organs in different ways it may primarily expose to mercury via food, where fish is the major source of methyl mercury exposure by biomagnification. Mercury has no necessary function in any living organism and is considered as a non-essential metal, and is among the most toxic elements to man and many higher animals [19] . Iron concentrations were observed 0.0487 mg/L in Nelaturu, 0.0107 mg/L in Krishnapatnam coast. The maximum acceptable limit for iron as per IS: 10500 is 0.3 mg/L and no guideline value was given by the WHO for Iron content. However, the observed concentration levels of Iron found within the permissible given by the IS: 10500 CPCB [20] . Manganese (Mn) concentrations were observed <1.0 mg/L BDL in Nelaturu and Krishnapatnam coast. The maximum acceptable limit for Manganese as per IS: 10500 is 0.1 mg/L and permissible value 0.3 mg/L and provisional guideline value as per the WHO is 0.4 mg/L. The observed manganese values were within the permissible limits given by IS: 10500 and WHO guidelines CPCB[20] . Copper (Cu) concentrations were observed <1.0 mg/L BDL in Nelaturu, 0.096 mg/L in Krishnapatnam coast. It is within the permissible limits at Nelaturu given by IS: 10500 and WHO guidelines. Copper is one of the essential metals to life despite being as inherently toxic as non-essential heavy metal exemplified by lead and mercury. Plants and animals rapidly accumulate it. It is toxic at minute low concentration in water and is known to cause brain damage in mammals. The natural inputs of copper to the marine aquatic environment are from erosion of mineralized rocks or maybe from the industries. Anthropogenic inputs of copper are from industries and paints. It also forms complexes with organic molecules. Mollusks have a tremendous capacity to accumulate copper from contaminated water CPCB [20] . Zn concentrations were observed <1.0 mg/L BDL in Nelaturu, 0.01 mg/L in Krishnapatnam coast. It is within the permissible limits at Nelaturu given by IS: 10500 and WHO guidelines. Zinc is an essential nutrient for the human body and has importance for health also it acts as a catalytic or structural component in many enzymes that are involved in energy metabolism also. Symptoms of zinc toxicity are slow reflexes, tremors, paralyzation of extremities, anemia, metabolic disorder, teratogenicity effects and increased mortality in humans CPCB [20] . In the present seawater study, the heavy metals of mercury, manganese and copper concentrations in the seawater have been observed in BDL<1.0 mg/L. Increased toxic heavy metal concentrations in the water lead to the Bioaccumulation factor in the aquatic food chain and it showed the transfer of metals especially arsenic, lead, cadmium, mercury are warning signal for fish consumption by humans towards food safety [20,21] . CONCLUSIONS The environmental parameters of water can be affected by the toxicity of the metal either by influencing the physiology of organisms or by altering the chemical form of the metal in water. The increased ambient heavy metal concentration will result in accumulation in the tissues of commercially important edible finfish, shell fish. It is an inherent danger of higher bioaccumulation of toxins in the edible species that may result in severe health hazards to the consumers especially human. It was evident that the present study on heavy metals in the water of the Nellore coast suggested adopting effective heavy metal removal technologies to control the toxic metal contamination in coastal water. Further bioaccumulation study to be needed for better understanding the metal toxicity in the coastal and marine environment. ACKNOWLEDGMENTS Authors are thankful to the Vimta Laboratories Pvt. Ltd. Nellore, for Atomic Absorption Spectroscopy analysis. CONTRIBUTION OF AUTHORS Research concept- Dr. Ch. Venkatrayulu Research design- Dr. Ch. Venkatrayulu Supervision- Dr. Ch. Venkatrayulu Materials- Mr. V. Venkateswarlu Data collection- Mr. V. Venkateswarlu Data analysis and Interpretation- Mr. V. Venkateswarlu Literature search- Mr. V. Venkateswarlu Writing article- Mr. V. Venkateswarlu Critical review- Mr. V. Venkateswarlu
  • 6. SSR Inst. Int. J. Life Sci. ISSN (O): 2581-8740 | ISSN (P): 2581-8732 Venkateswarlu and Venkatrayulu, 2019 DOI:10.21276/SSR-IIJLS.2019.5.5.3 Copyright © 2015 - 2019| SSR-IIJLS by Society for Scientific Research under a CC BY-NC 4.0 International License Volume 05 | Issue 05 | Page 2392 Article editing- Dr. Ch. Venkatrayulu Final approval- Dr. Ch. Venkatrayulu REFERENCES [1] Storelli MM, Storelli A, D’Addabbo R, Marano C, Bruno R, et al. Trace elements in loggerhead turtles (Caretta caretta) from the eastern Mediterranean Sea: overview and evaluation. Environ. Pollut., 2005; 135: 163-70. [2] Naser HA. Assessment and management of heavy metal pollution in the marine environment of the Arabian Gulf: review. Marine Pollut. Bull., 2013; 72: 06–13. [3] DeForest D, Brix K, Adams W. Assessing metal bioaccumulation in aquatic environments: The inverse relationship between bioaccumulation factors, trophic transfer factors and exposure concentration. Aquat. Toxicol., 2007; 84: 236–46. [4] Fu F, Wang Q. Removal of heavy metal ions from waste waters. A review. J. Environ. Manag., 2011; 92: 407–18. [5] Ozkan EY, Buyu KB. Geochemical and statistical approach for assessing heavy metal accumulation in the southern Black Sea sediments. Ekoloji., 2012; 21(83): 11–24. [6] Pande N, Nayak GN. Understanding distribution and abundance of metals with space and time in estuarine mud flat sedimentary environment. Environ. Earth Sci., 2013; 70: 2561–75. [7] Ravichandran R, Manickam S. Heavy metal distribution in the coastal sediment of Chennai Coast. IIOAB J., 2012; 3(2): 12–18. [8] Baran A, Tarnawski M. Assessment of heavy metals mobility and toxicity in contaminated sediments by sequential extraction and a battery of bio assays. Eco. Toxicol., 2015; 24(6): 1279–93. [9] Matoso E, Kubota LT, Cadore S. Talanta. Use of silica gel chemically modified with zirconium phosphate for pre-concentration and determination of lead and copper by flame atomic absorption spectrometry. Talanta, 2003; 60(6): 1105-11. [10]APHA. Standard methods for examination of water and waste water. 22nd Edition. American Public Health Association, Washington DC., 2012. [11]Koukal B, Dominik J, Vignati D, Arpagaus P, et al. Assessment of water quality and toxicity of polluted rivers Fez and Sebou in the region of Fez (Morocco). Benaabidate, Environ. Pollut., 2004; 31(1): 163-72. [12]Mohiuddin KM, Zakir HM, Otomo K, Sharmin S, et al. Geochemical distribution of trace metal pollutants in water and sediments of downstream of an urban river. Int. J. Environ. Sci. Tech., 2010; 7(1): 17-28. [13]Okafor EC, Opuene K. Preliminary assessment of trace metals and polycyclic aromatic hydrocarbons in the sediments. Int. J. Environ. Sci. Tech., 2007 4(2): 233-40. [14]Tiwana NS, Jerath N, Singh G, Ravleen M. (Eds.) Heavy metal pollution in Punjab rivers, in Newsletter Environmental Information System (ENVIS), 3(1): pp.03–07, Punjab State Council for Science and Technology, India. [15]Ferner DJ. Toxicity and Heavy Metals. eMed. J., 2001; 2(5): 01. [16]Gopinathan KM, Amma SR. Bioaccumulation of toxic heavy metals in the edible soft tissues of green mussel (Perna viridis L.) of Mahe region. Project report submitted to the Department of Science, Technology and Environment (DSTE), Government of Pondicherry, 2008, 01-32. [17]Sindhu PS. Environ. Chem., 2002 pp.75–243, 1st ed., New Age International (P) Ltd., New Delhi. [18]Salem HM, Eweida A, Azza F. Heavy metals in drinking water and their environmental impact on human health, Center for Environmental Hazards Mitigation, 2000; pp. 542-56. [19]Jarup L. Hazards of heavy metal contamination. British Med. Bull., 2003; 68: 167-82. [20]CPCB. Impact of Coal Mine Waste water Discharge on surroundings with reference to heavy metals. Central Pollution Control Board Bhopal, 2011. [21]Utete B, Nhiwatiwa T, Barson M, Mabika N. Heavy metal bioaccumulation in edible fish species from an industrially polluted river and human health risk assessment. Int. J. Water Sci., 2013; 2(4): 01-08. Open Access Policy: Authors/Contributors are responsible for originality, contents, correct references, and ethical issues. SSR-IIJLS publishes all articles under Creative Commons Attribution- Non-Commercial 4.0 International License (CC BY-NC). https://creativecommons.org/licenses/by-nc/4.0/legalcode