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In this study, stable isotopes of carbon (δ 13 C), sulfur (δ 34 S), oxygen (δ 18 O), hydrogen (δ 2 H),
nitrogen (δ 15 N) and radioactive isotope of hydrogen (tritium) have been applied in combination with
conventional techniques (physiochemical and biological) to investigate Karachi Coastal water
pollution due to Layari and Malir rivers, which mainly carry Karachi Metropolitan domestic and
industrial wastewater, and to determine the effect of seawater on the aquifer system of the area.
Physico-chemical (pH, electrical conductivity and turbidity), biological (fecal coliform),
heavy metal and stable isotope (carbon and sulfur) characteristics of Layari and Malir rivers water,
Karachi coastal waters and sea sediments showed that Karachi Metropolitan domestic sewage and
industrial effluents were the main source of coastal water pollution, and coastal water of Manora
Channel was heavily polluted as compared to water of southeast coastal area of Karachi. However,
the northwest coastal water was marginally polluted. Turbidity and fecal coliform population levels in
seawater of Manora Channel and some locations along southeast coast (Ghizri area and Ibrahim
Haideri) were found above the WHO recommended threshold limits set for seawater bathing.
Heavy metal contents of Manora Channel and southeast coastal waters were higher than the
Swedish guidelines for the quality of seawater. In contrary, heavy metal concentrations in coastal
sediments were found to be significantly higher than that of seawater. Mn and Ni contents in
sediments of entire coast (Manora Channel, southeast and northwest coast) were above USEPA
guidelines except at Buleji site, whereas Cr, Zn and Cu levels only in Manora Channel sediments
were higher than USEPA guidelines. The higher heavy metal contents of Manora Channel water and
sediments can be attributed to an influx of a major portion of untreated industrial and/or domestic
wastewater.
Layari and Malir rivers water was observed to be depleted in δ 13 C (TDIC) and δ 34 S which
showed heavy influx of sewage into these rivers. Manora Channel water was also depleted in δ 13 C TDIC
and δ 34 S during low tide environment showing a large scale domestic wastewater mixing with
seawater. Southeast coastal water was found to be slightly enriched in δ 13 C (TDIC) and δ 34 S and
exhibited mixing of relatively small quantity of sewage with the seawater as compared to Manora
channel. δ 13 C (TDIC) and δ 34 S contents of northwest coastal water were close to the values meant for
normal seawater.
δ 13 C and δ 15 N contents of Karachi coastal seaweed ranged from -31.1 to -4.9 ‰ PDB and 6.1
to 17.8 ‰ Air, respectively. Average δ 15 N values (10.2 ‰ Air) of Ulva spp. collected from non
polluted northwest coast was higher as compared to average δ 15 N contents (8.0 ‰ Air) of Ulva fromii
Manora Channel suggesting that nitrogen isotopic ratios of Ulva spp. could be a good indicator of
sewage pollution.
The results of a two component isotope mass balance equation using δ 13 C and δ 34 S values for
Layari and Malir rivers and coastal water indicated that tide conditions and distance of sampling site
from the pollution source were the main factors to control transport and dissemination of Layari river
pollution into Manora Channel. High tide environment slowed down the Layari river water mixing
with seawater coupled with a gradual decrease in pollution levels from Layari river out fall zone to
Manora Lighthouse.
Physico-chemical characteristics of groundwater showed that shallow aquifer system was not
generally affected by seawater intrusion. Deep groundwater was observed to be moderately (chloride
contents 1000- 2000 ppm) to highly saline (chloride contents > 2000 ppm). However, shallow and
deep well located in vicinity of the Malir and Layari rivers showed fecal coliform contamination
which rendered their water unfit for drinking.
An anion based piper diagram showed predomination of chloride and bicarbonate ions
relative to sulfate (SO 4-2 ) ions in coastal groundwater. It was inferred from Piper diagram that shallow
aquifer system was predominantly replenished by freshwater (mainly Layari and Malir rivers basin),
while salinity of deep aquifer owes to the seawater intrusion or entrapped salinity. The δ 18 O
composition of groundwater and δ 2 H vs. δ 18 O relationship for groundwater of coastal aquifer also
indicated that shallow aquifer system was predominantly recharged through fresh water sources.
Salinity of deep aquifer seemed to originate from seawater intrusion and/or from entrapped salinity.
These finding were strongly endorsed by anion and stable isotope interpretations such as Cl -
concentration vs δ 18 O, Cl - /HCO 3-1 ratio vs δ 18 O values and SO 4-2 contents against SO 4-2 /Cl - ratio of
shallow and deep aquifers.
The present study has demonstrated that stable isotopes (δ 13 C, δ 15 N, δ 34 S, δ 2 H and δ 18 O) can
be effectively used to monitor the marine pollution and to investigate origin of salinity in the coastal
aquifer. This study may also provide a precise and accurate isotopic database for researchers
interested in seawater pollution and its effect on benthic life. |
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