Arsenic distribution in environment and its bioremediation: A review
enhance mutagenesis by other agents, apparently
(V) was first studied by Frank and Clifford (1986)
by inhibiting DNA repair (Li and Rossman 1989).
utilizing chlorine, monochloramine, and oxygen.
Arsenite can also cause aneuploidy. Unlike
Solid phase oxidants such as birnessite (δ-MnO2)
spindle poisons, arsenite does not inhibit spindle
have also proven to be very useful in the oxidation
fiber formation; instead, it deranges the spindle
of As (III) to As (V) at a optimum pH of about 6.5
apparatus, possibly by accelerating microtubule
(Manning et al. , 2002).
polymerization. Arsenite may act as carcinogen by
Coagulants
such
as
aluminium
alum,
Al2
causing DNA hypomethylation leading to aberrant
(SO4)3.18H2O, ferric chloride, and ferric sulfate are
gene expression (Zhao et al. , 1997). Chronic exposure
effective in removing As from water by utilizing the
to arsenite caused a progressive increase in CpG
electrostatic attachment of negatively charged ions
methylation within the p53 promoter, which would
to the flocs. As (III) occurs in non-ionized form, it is
be expected to block transcription of the p53 gene
not subject to significant removal. Oxidation of As
(Mass et al. , 1997). The p53 gene is an important
(III) to As (V) is thus required as a pretreatment for
tumor-suppressor gene whose protein product plays
efficient removal (Ahmed 2003). Other adsorption
an important role in cell cycle control, apoptosis, and
techniques such as activated alumina, activated
control of DNA repair.
carbon (Ghosh and Yuan 1987) and activated bauxite
Remediation of as contaminated soil and water
(Gupta and Chen 1978) are also proved to be efficient
technologies.
There have been increasing needs of removal of As
from contaminated soils and groundwater to limit
Ion exchange is a physico-chemical process by
the detrimental impacts of As on living beings.
which an ion in the liquid medium is exchanged
There are a plenty of remediation methods have
for saturated ion on the solid phase. Synthetic resin
been developed based on physical, chemical and
saturated with the preferred anion is most widely
biological approaches that may achieve complete or
used for exchangingAs anions in contaminated water
partial removal of As from soil and groundwater or
(Johnston and Heijnen 2001). Generally strong-base
the reduction of its bioavailabity in order to minimize
resins (SBA) and sulfate-selective resins are found to
toxicity.
be most efficient in As removal over a broader pH
range (USEPA 2000. The biggest disadvantage of
Conventional Methods
using the ion exchange process is the non-removal
of As (III) species because of its uncharged behavior
The most commonly used conventional methods
until pH of about 9 (pKa =9.22). This characteristic of
include oxidation, co-precipitation and adsorption,
As (III) anions necessitates a pre-oxidative step for
ion exchange and membrane techniques such as
the conversion of As (III) to As (V) prior to removal
filtration, reverse osmosis etc (Shen 1973; Cheng et
from water. The removal of As (V) is independent
al. , 1994; Kartinen and Martin 1995; Hering et al. ,
of the initial concentration and pH of the liquid
1996; Joshi and Chaudhuri 1996).
medium (Johnston and Heijnen 2001).
Most conventional treatment methods are effective in
Membrane
techniques
like
Reverse
osmosis
removing As in pentavalent form and hence include
(RO), Nano-filtration (NF), Ultra-filtration (UF),
an oxidation step as preteatment to convert arsenite
microfiltration (MF), membrane distillation (MD)
to arsenate. Arsenite can be oxidized by oxygen,
are proved to be capable of removing dissolved As
ozone, free chlorine, hypochlorite, permanganate,
from water with a high efficacy. Membranes are
hydrogen peroxide, and fulton’s reagent (Ahmed
typically synthetic materials with billions of pores
2003). Chemical oxidation of As (III) to As (V)
or microscopic holes that act as a selective barrier
is currently being used in most conventional
allowing the passage of certain constituents with the
treatments. The chemical oxidation of As (III) to As
rejection or exclusion of others in the water (Uddin
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