Patent Filing No.: 430/KOL/2013
Arsenic
contamination in groundwater has become a global issue, with more than 200
million are potential at risk, as reported by recent UN report. There are
several reasons of arsenic contamination apart from anthropogenic sources which
includes (i) use of phosphate fertilizers and pesticides which leaches through
the sub-soil and reduces the arsenic binding capacity of the rocks (ii) oxidation
of arseno-pyrites present in rocks due to excessive withdrawal of groundwater and
(iii) untreated release of industrial effluent and wastes. There are widespread
reports of arsenic poisoning of ground water in Bangladesh, Mexico, Vietnam,
Western United States, Taiwan, India, Canada and more than 50 countries which
entailed above World Health Organization limit for drinking water of 10µg/l. Arsenic
poisoning is severe along the Gangetic plains in our country. In certain parts
of West Bengal, arsenic concentration as high as 500 to 2000 ppb has also been
found. Arsenic is found in +3 and +5 state, both of which are toxic for human
health.
Adsorption has been found to be the
most suitable mechanism for removal of arsenic. However, the capacity of the
adsorbent and its regeneration determines the crux of the problem. Almost all
the adsorbents that are available or developed till now require regeneration
because of its low capacity, which ultimately releases the arsenic back to the
environment, thereby becomes an anthropogenic source. Naturally occurring
laterite and ferro-manganese ores exhibits arsenic adsorption. However, the
capacity of these materials needs to be increases for practical application.
The work on removal of arsenic using
naturally occurring laterite has been initiated in the Department of Chemical
Engineering, IIT Kharagpur under the leadership of Prof. Sirshendu De and his
students back in 2006. The idea of using laterite came by examining the geographical
contamination profile in West Bengal. It was observed that seven districts
along the Ganges (Malda, Murshidabad, Nadia,
South and North 24 Parganas, Part of Burdwan, Kolkata) have been badly affected
by arsenic contamination of groundwater. On the other hand, districts in
south-western and western parts of West Bengal
(Midnapore, Bankura, Purulia) do not have this problem. It has been found that
reason lies in the geological nature of the soil of these regions. The red
colored lateritic rock in these parts contains alumina and iron oxide
components which have a natural capacity to adsorb arsenic species. The present
innovation details with acid activated based laterite adsorbent (Development of
high capacity and cost effective arsenic adsorbent using modified laterite,
Filed 614/KOL/2009) which has high arsenic adsorption capacity (both arsenite
and arsenate).
Salient features of the technology
(i) The
total removal capacity of arsenic is 32.5 mg/g, which is highest compared to
all other available arsenic adsorbents.
(ii) Ultra
low cost of the filter media appropriate for the socio-economic conditions of
our country. Filtered water can be produced at 2 paisa per liter ($1.2 for 1000
gallons).
(iii) Power
is required only to operate the pump to lift water into overhead tank. Flow in
the filters is by gravity. In case of household filter, no power required.
(iv) Removal
of arsenic, iron and bacteriological contamination together in a single unit. The
filter is capable to remove iron below the permissible limit in drinking water
(0.3 ppm) and remove more than 98% of pathogenic contaminants.
(v) The
filter bed consists of different layer of materials including bacteriostatic
activated carbon, charcoal, fine granular sand, activated laterite and raw
laterite.
(vi) No
interference from sulphate, chloride, magnesium and iron ions are observed.
(vii) Works
over wide range of pH 5.5 to 8.0.
(viii) The
total arsenic concentration in the filtrate is always less than 10 ppb (WHO
limit).
(ix) The
filter life 5 years in the worst possible condition. The filter will be more if
the influent arsenic concentration is less.
(x) No
regeneration or backwashing is needed during its lifetime, which makes this
technology unique and unparallel.
(xi) The
empty bed contact time is 7.2 hours which is necessary for the adsorption to
occur.
(xii) The
adsorbent binds arsenic by strong chemisorption. The spent adsorbent meets TCLP
protocol and can safely disposed. It can be used for making bricks, road
lining, pavements, cell filling, etc. Therefore, this adsorption provides the
ultimate solution for treatment of arsenic contaminated water.
(xiii) Easy
maintenance and operation.
(xiv) The
cost of domestic filter would be in the range of 2500-3000 rupees (40 to 50
USD).
Units Deployed:
Total
number of Household units deployed so far: 16
Lalgola, Mushidabad, West
Bengal (one unit in August 2012)
Behrampur, Murshidabad, West
Bengal (two units in August 2012)
Baruipur, South 24
Paraganas, West Bengal (one unit in Sep 2012)
Rajarhat, North 24 Parganas,
West Bengal (two units in Oct 2012)
Bamangachi, Barasat, North
24 Parganas, West Bengal (one in March 2011 and remaining 8 in Oct 2012)
Habra, North 24 Parganas,
West Bengal (one unit in Sep 2012)
Total number of community filters deployed: 3
Kashinathpur free primary
school, Rajarhat, North 24 Parganas, West Bengal (installed in Oct 2012) - 500
L/day capacity
Ambika Girls High School,
Rajarhat, North 24 Parganas, West Bengal (installed in December 2012) - 1500
L/day capacity
Choudhuar Primary School,
Manikchawk Block, Malda, West Bengal (installed in December 2014) - 800 L/day
capacity.
The
technology has been developed, demonstrated and deployed in field with active
support from Department of Science & Technology, Govt. of India and UNICEF,
West Bengal. Technology is transferred to one company.
The contributors to this work are –
Sourav Mondal, Barun Kumar Thakur, Kuldeep Yadav, Mrinmoy Mondal, Raka
Mukherjee, Anirban Roy, Biswajit Barman and Sirshendu De, Department of
Chemical Engineering, IIT Kharagpur.