INTERNATIONAL JOURNAL OF SCIENTIFIC & TECHNOLOGY RESEARCH VOLUME 3, ISSUE 7, JULY 2014 ISSN 2277-8616
47
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Laboratory Study Of Arsenic Uptake And
Phytoremediation Potential Of Three Aquatic
Macrophytes Of Meghalaya, India
Marbaniang D., Chaturvedi S.S.
Abstract: Laboratory experiments were performed to evaluate the As uptake capacity by three aquatic macrophytes (Scripus mucronatus, Rotala
rotundifolia and Myriophyllum intermedium). The selected macrophytes were transferred to the laboratory containing nutrient solution and working As
standard solutions of different concentrations (1.0, 2.0, 4.0, 8.0 and 16 mg L
-1
) and harvested at regular time interval of 2, 4, 6, 8 and 10 days. The As
uptake by these macrophytes showed a linear relationship for S. mucronatus, R. rotundifolia and M. intermedium with the exposure time period (2–10 d).
As accumulation in the plant parts was higher in the roots for S. mucronatus but reverse in the case of R. rotundifolia and M. intermedium. The maximum
bioconcentration factor (BCF) values were found at the 8
th
day in all the three aquatic macrophytes and translocation factor (TF) was at the 8
th
day for S.
mucronatus and R. rotundifolia and at the 6
th
day for M. intermedium respectively. The experimental results demonstrated that these three aquatic
macrophytes have a phytoremediation potential for removing As from As -contaminated water.
Keywords: Scripus mucronatus, Rotala rotundifolia, Myriophyllum intermedium, Arsenic uptake, Bioconcentration (BCF), Translocation Factor (TF).
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1. Introduction
Water though an indispensable resource for human life is
yet one of the most badly abused resources. For centuries,
especially in urban areas, water has been polluted and
used as dumping places for all sorts of domestic and
industrial waste as well as sewage. Over 75 to 90 percent
of people in developing countries are exposed to unsafe
drinking water [1], hence proper water treatment is
inevitable in order to ensure healthy life. Nowadays, apart
from other common pollutants, heavy metals are
considered as one of the most important water pollutants
which may have a severe health problem. As
contaminations from natural and anthropogenic sources
has been reported in number of sites worldwide [2]. The
extensive arsenic contamination in the groundwater have
been reported in many countries, especially Taiwan,
Argentina, India, Bangladesh, Mexico, Hungary, and Chile
[3]. Arsenic is the 20
th
abundant element in earth crust [4],
As is a semi-metallic element (atomic number 33, atomic
mass 74.9) belonging to group V. The occurrence of As
naturally in the environment is mainly from minerals and
geogenic sources, but however extensive anthropogenic
activities such as mining, burning of fossil fuels, use of
arsenic containing chemicals in agriculture increases the As
distribution in the environment [5]. As has been widely used
in the fields of medicine, electronics, agriculture (pesticides,
herbicide, insecticides, fertilizer, etc.), livestock (cattle and
sheep dips), and as wood preservatives [6]. A variety of
techniques which includes chemical, physical and biological
technology have been used to remediate heavy metal
contamination from soil or water. Toxic metals from
industrial effluents have been remove by various other
techniques such as precipitation, reduction, artificial
membranes, and ion exchange, but however these
techniques generate a huge amount of waste e.g., sludge,
metal rich waste, etc which is difficult to dispose of and
therefore, dangerous to the environment and they are also
generally expensive, relatively inefficient [7].
Phytoaccumulation, one of the biological indicators which
indicate the degree of absorption of heavy metals in plants
has lately gained its applicability because its cost-
effectiveness, long-term and ecological aspect [8]. Aquatic
macrophytes have received great attention and have shown
to be one of the candidates in the aquatic system for
pollutant uptake and biological indicators of heavy metal [9].
The objective of the present study was to assess the uptake
of As and phytoremediation potential of S. mucronatus R.
rotundifolia and M. intermedium for As under laboratory
conditions. The experiments were performed in a contained
environmental set up inorder to eliminate all external
environmental factors.
2. Materials and Methods
S. mucronatus an emergent and R. rotundifolia and M.
intermedium are submerged macrophytes and they are one
of the major natural constituent of wetland and riverside
vegetation. They are sampled as shown in fig 1 from water
body of Mawlai Umshing, (Lat 25
0
36’36.76N Long
91
0
54’05.11E), Cherrapunjee (Lat 25
0
19’01.38‖N Long
91
0
48’36.51‖E) and Pongkung (25°21’47.69‖ N
91°40’03.34‖ E), Meghalaya, India in the month of October
2012 and collected in polyethylene bags and transferred to
the laboratory. Plants were washed several times with tap
and distilled water in order to remove any adhering soils
and plants of similar size, shape and height were selected
and kept separately in a 40L capacity tank which contained
half strength Hoagland’s solution of pH = 7 [10] and kept for
15 days prior to experimentation for. The Hoagland solution
was modified by omitting ferrous sulfate in order to prevent
the As precipitation by iron. Nevertheless, high level of
phosphorus in the nutrient medium may influence arsenic
uptake by plants. After 15 days the acclimatized plants
were transferred and maintained in 5% Hoagland’s solution
containing working As standard solutions of different
concentrations 1.0, 2.0, 4.0, 8.0 and 16.0 mg L
-1
and then
they were exposed to As concentrations at a time interval of
2, 4, 6, 8 and 10 days. As of analytical grade, were supplied
as As
2
O
3
(Himedia) were used as the source of As.
Experiments were carried out separately for the three
aquatic macrophytes under controlled temperature
(24±1
0
C) and light (3500 Lux) conditions. After each time
interval the plants were collected and washed with
deionised water to remove any metal adhering to its
surface. The washed plant samples were carefully dried the