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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1156
Removal of Arsenic from Ground Water by Electrocoagulation Effluent
Treatment Process using Low Cost Adsorbents
Gauri Kamble1, Aniket Jadhav2, Savani Deshpande3, Jayesh Baviskar4, Dr. Satyajit Deshmukh5
1-4Student, Chemical, Datta Meghe College of Engineering, Airoli, India
5Asst. Professor, Chemical, Datta Meghe College of Engineering, Airoli, India
---------------------------------------------------------------------***----------------------------------------------------------------------
Abstract - Water pollution due to the disposalofheavymetals
continues to be a great concern world- wide. As a result, the
treatment of dirty industrial wastewater remains a topic of
global concern because wastewater collected from
municipalities, communities and industriesmusteventually be
returned to receiving water source [1]. In order to removethis
toxic heavy metals many techniques are used all over the
world. In these pile of techniques ETP (EFFLUENT
TREATMENT PROCESS) that uses ELECTROCOAGULATION
SYSTEM METHOD along with LOW COST ADSORBENTS has
drew serious attention. Lowcostadsorbentsarepreferred over
others due to their low cost, ease of application and eco-
friendliness etc. The various low cost adsorbents are green
shell, peanut husk, zeolites and Fly ash etc. This review paper
acknowledges comparison between adsorbent made up from
green coconut shell that is used in combination with ETP and
ECOAG PROCESS with ferric hydroxide that is also used as an
adsorbent to get rid of toxic heavy metals such as arsenicfrom
ground water.
Key Words: Water pollution, Water treatment, Heavymetal,
Arsenic, E-coagulation, ETP, Low-cost Adsorbents, Green
coconut shell, Iron hydroxide.
1. INTRODUCTION
We know, Arsenic is one of the toxic elements. It affects the
ground water which arises to many health diseases for
humans and animals. There are many ways of detoxing
water where in Electrocoagulation, Membrane Technology,
Effluent Treatment Process (ETP), etc. works for removing
Arsenic from ground water.
1.1 Water Contamination
As commercial global has grown, environmental demanding
situations have additionally increased. A known form of
pollutants the arena is presently suffering with is water
pollutants. Water pollutants may be as a result of a selection
of things consisting of agriculture, sewage and wastewater,
oil pollutants and radioactive substances. Wastewater,
specifically which discarded through industries, can
comprise an extensive variety of heavy metals. The rangesof
heavy metals infection in water which incorporates Pb, As,
Cd, Hg, Cr, Ni etc. in severa water reassets as ground, ground
and tap water etc. A form of heavy metals, some of them are
potentially toxic and are transferred to the surrounding
environment thru via severa pathways. Heavy metal toxicity
has validated to be a main risk and there are various health
risks associated with it. The toxic effects of these metals,
regardless of the truth that they do nownothaveanynatural
role, their toxic effects are despite the fact that risky for the
human body and its proper functioning. [2][3]
1.2 Arsenic
Arsenic is a natural semi steel chemical that is located
anywhere within side the worldwide in numerous water
bodies. Arsenic has 185pm molecular size. The allowed
interest of arsenic in drinking- water is 10 micrograms
consistent with litre [4]. Arsenic,a well-knowncarcinogen,is
regarded as one of the world-wide’s most risky chemicals
[5]. Arsenicosis, a now no longer unusual place name
commonly used for Asrelatedhealthproblemswhichconsist
of pores and pores and skin disorders, pores and pores and
skin cancers, internal cancers (bladder, kidney, and lung),
ailments of the blood vessels of the legs and feet, possibly
diabetes, multiplied blood pressure, and reproductive
disorders[6][7]. Current techniques to remove arsenic
embody precipitation, such as lime or coagulants to water,
the use of membranes to clean out it out, or the use of an ion
ex-trade process [8]. The most inexperienced and used
method for removal of arsenic are MEMBRANE
TECHNOLOGIES, COAGULATION, ADSORBPTION [9]. There
are subtypes for membrane technology and adsorption.
2. METHODS TO REMOVE ARSENIC
Membrane technology is divided into four types, those are
Microfiltration, Ultrafiltration, NanofiltrationandReverse
Osmosis. In Adsorption, we have Activated Alumina, Iron
based sorbents, Zero- valent iron, Indigeneous filters,
miscellaneous sorbents, metal organic framework. Electro-
coagulation is a type of an advanced oxidation reaction. In
this review paper we shall be discuss on electrocoagulation
and low cost adsorbents [10].
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1157
Fig -1: Tree diagram for Arsenic Removal processes [9]
3. PROCESS OF REMOVING ARSENIC
3.1 Electro- coagulation
Electro coagulation (EC) is a manner used for waste water
treatment, wash water treatment, industrially processed
water, and medical treatment. Electrocoagulationisaswiftly
growing place of wastewater treatment due to its ability to
eliminate contaminants which can be usually harder to
eliminate through manner of way of filtration or chemical
treatment systems, which incorporates emulsified oil,
ordinary petroleum hydrocarbons, refractory organics,
suspended solids, and heavy metals [11]. There are many
producers of electro coagulation devices available rangingin
complexity from a clean anode and cathode to lots more
complex devices with control over electrode potentials,
passivation, anode consumption etc. It is essential to be
conscious that electro coagulation era cannot eliminate
infinitely soluble matter. Therefore, ions with molecular
weights smaller than Ca+2 or Mg+2 cannot be dissociated
from the aqueous medium. [12]
Whole Electro-coagulation manner incorporates of four-
stages:-
a) Effluent Tank/ septic tank
b) Pump
c) E-coagulation reactor
d) Settling Tank
(a) Effluent Tank
The septic tank was one of the first treatment devices
invented. They are intended to hold wastewater at low
velocity, under anaerobic conditions for a minimum
detention time of 36 hours. During this period, a high
removal of settled solids was achieved. These solids
decompose within side the backside of the tank with the
formation of fuel line, which entrained within side the solids
reasons them to upward thrust thru the wastewater to the
floor and lie as a scum layer till the fuel line has escaped, and
then the solids settle again. Annual inspectionisto beheld to
put off sludge and for cleansing the effluent tank/septic
tanks [13].
(b) Pump
A pump is a device that moves fluids (liquids or gases), or
sometimes slurries by mechanical action, converting
electrical energy into hydraulic energy. Pumps are classified
into three major groups based on the method they used to
move the fluid: direct lift, displacement, and gravity pumps
[14]
There are basically three types of pumps:-
 positive-displacement
 centrifugal
 Axial- flow pumps.
There are various othertypesinpositive-displacementthose
are:- Rotary lobe pump, Progressive cavity pump, Rotary
gear pump, Piston pump, Diaphragm pump, Screw pump,
Gear pump, hydraulic pump[15]
(c) E- coagulation Reactor
The E- coagulation reactor is made up of non- corrosive
fiberglass with proprietary designed parallel plates of
electrodes. When the DC current from the power supply
flows through the electrode, metal ions are released form
anode into the water (generating the ion Al3+ if the anode is
aluminum and Fe3 if it is steel) simultaneously on the
cathode hydroxyl group and hydrogen are produced. This is
followed by ionization, destabilization, oxido- reduction,
electrolysis, free radical formation, electromagnetic field
formation, and emulsion breaking and separation [16]
(d) Settling Tank
Sedimentation tank, moreover referred to as a settling tank
or clarifier, is a part of a contemporary-day device of water
supply or wastewater treatment. A sedimentation tank
permits suspended particles to settle out of water or
wastewater as it passes slowly via the tank, thereby
imparting some degree of purification. A layer of collected
solids, referred to as sludge, office work at the bottom of the
tank and is periodically removed. In drinking-water
treatment, coagulants are added to the water preceding to
sedimentation so you can facilitate the settling process, this
is then observed via filtration and exclusive treatmentsteps.
To decorate purification overall performance primary
sedimentation want to beobservedvia.Secondarytreatment
(e.g., trickling clean out or activated sludge) to growth
purification efficiencies. Sedimentation is commonly
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1158
preceded via treatment with bar presentations and grit
chambers to remove large objects and coarse solids [16]
. Horizontal flow tanks. ...
• Radial flow tanks. ...
• Inclined settling. ...
• Ballasted sedimentation. ...
• Floc blanket sedimentation.
3.2 Electro- coagulation in combination with Effluent
Treatment Process (ETP)
As Electro-coagulation does not remove infinitely soluble
matter. Therefore, ions with molecular weightssmallerthan
Ca+2 or Mg+2 cannot be dissociated from the aqueous
medium. So to remove all the metal toxicitiesandtogetclean
drinking water Effluent treatment process (ETP) was
introduced.
ETP includes processes like Activated charcoal treatment
(adsorption)
Reverse Osmosis (RO) Ozonization (Chemical oxidation)
Ultra Filtration (UF) etc. ETP has membrane technology as
its core.
Advantages of E-coagulation and Effluent Treatment
Process:-
• Less maintenance and minimal to zero
chemicals.
• Unnecessary water usage during the
processing is eliminated and makes your
industry self-sustainable.
• Helps reduce the contamination of natural
water bodies
• It costs less and create lesser sludgewithless
bound water.
3.3 Membrane Technology
Membrane era has developedtobea dignifiedseparation era
during the last decennia. The foremost pressure of
membrane era is the reality that it really works without the
addition of chemicals, with an exceedingly low strength use
and smooth and well- organized manner. Membranes are
used increasingly frequently for the introduction of manner
water from groundwater, floor water or wastewater. The
membrane separation manner is primarily based totally at
the presence of semi permeable membranes.
The precept is pretty simple: the membrane acts as a
completely particular clear out a good way to permit water
float via, even as it catches suspended solids and different
materials. Membranes occupy area thru a particular
separation wall. Certain materials can by skip via the
membrane, even as different are trapped. Membrane
filtration may be hired as an opportunity to flocculation,
sediment purification procedures, adsorption (sand filters
and lively carbon filters, ion exchangers), extraction and
distillation. [18][19][20]
Membrane filtration is assessed as microandultra-filtration
on the only hand and Nano filtration and Reverse Osmosis
(RO or hyper filtration) on the opposite hand. When the
usage of membrane filtration to get rid of large particles,
micro filtration and ultra-filtration are applied. Because of
the open man or woman of the membranes the
productiveness is excessive even as the stress variations are
low. When salts want to be eliminated from water, Nano
filtration and Reverse Osmosis are applied. Nano filtration
and RO membranes do now no longer paintings in line with
the precept of pores; separation takes region through
diffusion via the membrane. The stress this is required to
carry out Nano filtration and Reverse Osmosis is a greatdeal
better than the stress required for microandultra-filtration,
even as productiveness is a great deal lower. [18][19][20]
3.4 Effluent Treatment Process (ETP)
The precept of operation of ETP is Physio-Chemical
remedy observed through Polishing Treatments which
include Sand Filtration, Activated Charcoal remedy
(Adsorption), Ozonization (Chemical Oxidation), Ultra
Filtration (UF), Reverse Osmosis (RO) and evaporation (If
required). ETP are used for the elimination of excessive
quantities of natural compounds, debris, dirt, grit, pollution,
poisonous,non-poisonoussubstancesandpolymersetc.from
business effluent. Industrial wastewater remedy refers back
to the strategies which can be applied to deal with
wastewaterthisiscreatedthroughindustriesasanunwanted
through-product. After remedy, the dealt with business
wastewater can be reused ordischarged right into a sanitary
sewer or to a floor water within side the environment [21]
[22].
Whole ETP contains of 4 stages:-
• Sand Filter
• Filter Press
• Ultra Filter
• RO system
(a) Sand Filter
Sand filtrationisoneofthemaximumwell-acknowledged
wastewater remedy methods. If well designed, built,
operated, and maintained, a sand clear out produces a
completely excessive fine effluent. Sand filters are beds of
granular material, or sand, tired from under in order that
pretreated wastewater may be treated, accumulated, and
dispensed to the very last remedy and dispersalgadget.They
are generally used to shine effluent from septic tanks or
different remedy strategies earlier than miles dispensed at
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1159
the land. All on-web website online structures are “no-
discharge,” this means that the wastewater should stay
within side the gadget and now no longer go away the
property. The effluent can't input floor water, streams,
ditches, or every other water resources. After the filtrate is
accumulated via way of means of the sand clear out
underdrains miles then disposed of via way of meansofasoil
absorption gadget [23].
(b) Filter Press
Filter press is one of the oldest and most reliable pieces of
dewatering equipment. It’s used for wastewater treatment
across a range of industries and applications. A filter press
separates particles from liquids while also eliminating
contaminants, and suspended solids from industrial
wastewater. This enables plant managers to conveniently
handle and dispose of waste while returning clean water to
their systems.
Filter presses are used to separate liquids and solids.
Specifically, the filter press separates the liquids and solids
using pressure filtration across a filter media.Afterward,the
slurry is pumped into the filter press and then dewaters
under pressure. [24]
What are the Four Main Components of a Filter Press?
• Frame
• Filter Plates
• Manifold (piping and valves)
• Filter Cloth (This is key for optimizing filter
press operations.
Basically, the filter press design is based on the dewatering
volume and type of slurry. [24]
(c) Ultra Filter
In wastewater treatment, ultrafiltration (UF) devices are
used to recycle and reuse water that contains virtually no
physical solids. Ultrafiltration definition, applications and
industries using these process units are covered below.
Ultrafiltration (UF) is a variety of membrane filtration in
which forces like pressure or concentrationgradientsleadto
a separation through a semipermeable membrane.
Suspended solids and solutes of high molecular weight are
retained in the so-called retenate. When treating waterwith
high suspended solids, UF is often integrated into the
process, using primary (screening, flotation and filtration)
and some secondary treatments as pre-treatment stages.
[25]
Ultrafiltration processes are preferred over traditional
treatment methods for the following reasons:
• No chemicals required (aside from cleaning)
• Constant product quality regardless of feed quality
• Compact plant size
• Capable of exceeding regulatory standards of water
quality, achieving 90-100% pathogen removal.
Pore size of Ultra Filtration membrane ranges from
0.005-0.1µm.
(d) Reverse Osmosis (RO)
Reverse Osmosis is a water purification technique that
makes use of strain and a semi-permeable membrane to put
off dissolved solids. The RO water is saved in a maintaining
tank. If the RO water wishes greater purification, a
Deionization System will lessen the conductivity of the RO
water. [26]
Industrial RO Applications:-
• Metallic completing and plating operations
• Published circuit boardand semiconductor manufacturing
• Electroplating processes
• Automobile manufacturing
Pore size of RO ranges from 0.0001-0.001 nm
1. Effluent Tank
2. Pump
3. Electro- coagulation Reactors
4. Settling Tank
5. Sand Filter
6. Filter Press
7. Ultra Filtration (UF)
8. Reverse Osmosis (RO)
Fig -2: Flow sheet of the Technology
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1160
3.4 Low- Cost Adsorbents
An adsorbent is an insoluble material coatedbyliquidonthe
surface, including capillaries and pores. A material is said to
be adsorbent when it has the capacity to contain a definite
amount of liquid in small chambers similar to a sponge.
Adsorbents play a vital role in chemical absorption, which
takes place when a certain substance is trapped on a
material's surface. Properties of a suitable adsorbent are
high selectivity, high absorption capacity, long life, and low
cost. Differentadsorbentpossessesvariouspropertiesdivers
as its active surface, pore diameter, quality of pore
distribution, and surface functional group. Pore sizes of
porous materials are classified generally into three ranges,
according to the IUPAC
• macro pores: "diameter" > 50 nm,
• meso pores (also known as transitional
pores): 2 nm ≤ "diameters" ≤ 50 nm
• Micro pores: "diameters" < 2 nm.
Low-cost adsorbents refer to those materials, which are
found abundantly in the environment or are byproducts or
wastes from industries. Moreover, adsorbents are known as
low costs if they have reduced processing requirements.
Previous adsorption works concentrated on plant wastes
such as, the Peat and coconut fiber , carrots , rice husks ,
Cane papyrus , modified coconut husk , rice bran , and
others, which can be utilized each on the normal compose or
change several alterations physical or chemical. Converting
these materials into adsorbents is an effective way of
reducing the costs of waste disposal and for providing
alternate treatments for replacing the commercially
activated carbons. [27]
(a) Green Coconut Shell:-
Green coconut shell is extensively used as adsorbent in
waste water remedy as miles without difficulty to be had
everywhere
Pre-remedy of the adsorbent:-
Green coconut shells have been furnished through Embrapa
Tropical Agroindustry, CE, Brazil (EMBRAPA/CE). The
adsorbent turned into dealt with NaOH 0.1mol L−1forthree
h after which washed with deionized water, buffer solution
(pH 5.0) and dried at 50 °C. This cloth turned into cooled at
room temperature after which sieved to attain preferred
particle size (0246–0074 mm) [28]
(b) Iron Oxy- Hydroxides:-
Arsenic adsorption theusage ofironcompounds,zero-valent
iron, Iron- primarilybasedtotallybimetal oxides,iron-doped
composite adsorbents are seriously reviewed and their
adsorption efficienciesarecompared.Besidestheadsorption
capacities, the traits of adsorption tactics, which include
thermodynamics, kinetics and massswitchmechanismsalso
are examined. The precise binding among arsenic and iron
turned into deeply investigated via way of means of
numerous spectral technologies. Moreover, a few iron-
primarily based totally adsorbents are magnetic, making an
allowance for a smooth separation of the saturated
substances from water in an outside magnetic field.
Many distinctive substances had been stated to have a very
good affinity in the direction of arsenic, however iron oxy-
hydroxides are the maximum extensively studied due to
their smooth accessibility. The generally used iron oxy-
hydroxides such as, akagan`eite (b-FeOOH), goethite (a-
FeOOH), lepidocrocite (g-FeOOH), ferrihydrites (
Fe10O14(OH)2), inexperienced rusts may be chemically
synthesized via way of means of the precipitation of Fe(III)
or Fe(II) salts via the hydrolysis and oxidation tactics The
solid As(III) oxidation country within side the darkish is
steadily converted to As(V) on ferrihydrites in presence of
mild at pH 5. At the equal time, Fe(III) ions have been
decreased to Fe(II) species at some point of the As(III)
oxidation,56 It turned into located the adsorption rate
(12.4105 M s1 m2 ) on goethite turned into appreciably
quicker than that of ferrihydrites (6.seventy three one
hundred and five M s1 m2 ) at pH 5.fifty seven The
comparable photochemical response turned into
additionally located for As(III)adsorptionongoethitewithin
side the presence of dissolved oxygen Laterite, a herbal iron
oxide mineral containing 91% of goethite, is some other
promisingandcost-powerful fabricforarsenicadsorption.59
The precise adsorption of arsenic isprovenvia wayofmeans
of a sturdy proof of the shift of isoelectric point.[29]
4. CONCLUSIONS:-
In this review paper we focused on removal of Arsenic from
ground water by E-coagulation Effluent treatment process
using Low cost adsorbents. There were many other
processes but E-coagulation and ETP were most efficient. E-
coagulation treatment uses electrode s to remove
contaminants where-as ETP (Effluent Treatment Process)
has its core into membrane technology. As E-coagulation
process cannot remove all the infinitely small contaminants
and heavy metals. There was a need to combine E-
coagulation process with ETP. As this combination of two
processes was not enough to remove all the contaminants
Low cost adsorbents were introduced.
There were two adsorbents studied in this review paper
those are Adsorbent from green coconut shell (natural
adsorbent) and the second wasIronoxyhydroxide(chemical
adsorbent).low cost adsorbents Adsorb most of the
contaminants and heavy metalsontoitssurface.Duetothese
three processes the chances of removal of maximum arsenic
are very high and at the end the treated water goes through
RO where it’s again treated to be drinkable.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1161
References:
[1] A study of the removal characteristics of heavy metals
from wastewater by low-cost adsorbents by Omar E.Abdel
SalamaNeama A.ReiadbMaha M.ElShafeib received 6 July
2010, Revised 14 January 2011, Accepted 21 January 2011,
Available online 11 March 2011.
[2] Heavy Metals Contamination in Water and Their
Hazardous Effect on Human Health-A Review by Mahipal
Singh Sankhla , Mayuri Kumari, Manish Nandan, Rajeev
Kumar, PrashantAgrawal.DateWritten:September22,2016
Posted: 1 Aug 2019.
[3] Removal of heavy metals from aqueous media by
biosorption Ali Redha received 27 Sep 2019, Accepted 31
Mar 2020, Published online: 20 Apr 2020
[4] Arsenic in Water: Determination and Removal by
Ljubinka Rajakovic and Vladana Rajakovic-Ognjanovic
Submitted: November 21st 2017 Reviewed: February 16th
2018Published: July 25th 2018 DOI:
10.5772/intechopen.75531
[5] USEPA, “National Primary Drinking Water Regulations:
Arsenic and Clarifications to Compliance and New Source
Contaminants Monitoring,” Federal Register, vol. 40, CFR
Parts 9, pp. 141–142, 2001.
6] WHO, Guidelines for Drinking-Water Quality,vol.4,World
Health Organization, 2011.
[7] S. C. Santra, A. C. Samal, P. Bhattacharya, S. Banerjee, A.
Biswas, and J. Majumdar, “Arsenic in food chain and
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Procedia Environmental Sciences, vol. 18, pp. 2–13, 2013,
Proceedings of the International Symposium on
Environmental Science and Technology (2013 ISEST).
[8] Arsenic exposure from drinking water, and all-causeand
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Y, Pierce B, Parvez F, et al. The Lancet. 2010; 376
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[9] Technologies for Arsenic Removal from Water: Current
Status and Future Perspectives Nina Ricci Nicomel, 1, 2, 3
Karen Leus, 2 Karel Folens, 1 Pascal Van Der Voort, 2 and
Gijs Du Laing1,* Ravi Naidu, Academic Editor and
Mohammad Mahmudur Rahman,Academic EditorPublished
online 2015 Dec 22. DOI: 10.3390/ijerph13010062
10] Environmental research and public health Published
online 2015 Dec 22. DOI: 10.3390/ijerph13010062
[11] Application of Electrocoagulation In various
Wastewater and Leachate Treatment a Review to cite this
article: L W M Zailani and N S M Zin 2018 IOP Conf. Ser.:
Earth Environ. Sci. 140 012052.
[12] Electrocoagulation process in water treatment: A
review of electrocoagulation modeling Received 20 April
2016, Revised 17 October 2016, Accepted 19 October 2016,
Available online 29 October 2016.
[13] Wastewater treatment Technology Iyyanki V.
Muralikrishna, Valli Manickam, in Environmental
Management, 2017
[14] Fao.org. Retrieved on 2011-05-25.
[15] Engineering Sciences Data Unit (2007). "Radial, mixed
and axial flow pumps. Introduction
[16] Pristine Water, an ISO 9001:2015, 14001:2015,
45001:2018 certified company
[17] Sedimentation tank water treatment By the Editors of
Encyclopaedia Britannica
[18] Osmotech Membranes Pvt. Ltd. © 2019
[19] Qian Wang, Linhe Zhu, Norafiqah Ismail, Qiuyueming
Zhou, Ting He, Yue Zhou, Zhaohui Wang, Zhaoliang Cui* ,
Naser Tavajohi, Annealing of grain-like poly (vinylidene
fluoride-1 trifluoroethylene) membranes with a single-
crystalline electroactive phase and high anti-foulingactivity,
Journal of Membrane Science, Acceptedin16thofNovember
2021.
[20] Lenntech(EuropeanHeadOffice)Distributieweg32645
EG Delfgauw the Netherlands Phone: +31 152 610 900 fax:
+31 152 616 289
[21] ARSENIC IN WASTE WATER FROM PRIMARY COPPER
PRODUCTION PROCESS Biljana Jovanović∗, Milana
PopovićRTB Bor – Copper Smelter and Refinery Bor Đorđa
Vajferta 20, 19210 Bor, Serbia, Received 12.06.2013
Accepted 02.10.2013
[22] Onsite Wastewater Treatment Systems:SandFilters By:
Bruce Lesikar, Professor and Extension Agricultural
Engineer, the Texas A&M System
[23] Adsorption: Fundamental Processes and Applications
Pouran Pourhakkak, Mehrorang Ghaedi, in InterfaceScience
and Technology, 2021
[24] Filter presses for sludge dewatering Posted on18
June 2020
[25] Enzymatic cleaning in ultrafiltration of wastewater
treatment plant effluent Author links open overlay panel
Sandyte PoeleJaapvan der Graaf
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072
© 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1162
[26] Sustainable Processes for Treatment of Waste Water
Reverse Osmosis Concentrate to Achieve Zero Waste
Discharge: A Detailed Study in Water Reclamation Plant
Author links open overlay
panelS.ShanmuganathanaM.A.H.JohiraA.ListowskibS.Vignes
waranaJ.Kandasamya
[27] Cheryan, M. Ultrafiltration and Microfiltration
Handbook, Technomic Publishing Co., Lancaster, PA. 1998.
527
[28] Review Paper. Utilization of Low-Cost Adsorbents for
the AdsorptionProcessofChromiumions.Mohammed Jaafar
Ali Alatabe
1
and Ahmed Alaa Hussein
1
Citation Mohammed
Jaafar Ali Alatabe and Ahmed Alaa Hussein 2021 IOP Conf.
Ser.: Mater. Sci. Eng. 1076 012095
[29] A critical review on arsenic removal from water using
iron-based adsorbents Linlin Hao, ab MengzhuLiu,a Nannan
Wang c and Guiju Li*a . Received 15th October 2018
Accepted 21st November 2018 DOI: 10.1039/c8ra08512a

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Removal of Arsenic from Ground Water by Electrocoagulation Effluent Treatment Process using Low Cost Adsorbents

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1156 Removal of Arsenic from Ground Water by Electrocoagulation Effluent Treatment Process using Low Cost Adsorbents Gauri Kamble1, Aniket Jadhav2, Savani Deshpande3, Jayesh Baviskar4, Dr. Satyajit Deshmukh5 1-4Student, Chemical, Datta Meghe College of Engineering, Airoli, India 5Asst. Professor, Chemical, Datta Meghe College of Engineering, Airoli, India ---------------------------------------------------------------------***---------------------------------------------------------------------- Abstract - Water pollution due to the disposalofheavymetals continues to be a great concern world- wide. As a result, the treatment of dirty industrial wastewater remains a topic of global concern because wastewater collected from municipalities, communities and industriesmusteventually be returned to receiving water source [1]. In order to removethis toxic heavy metals many techniques are used all over the world. In these pile of techniques ETP (EFFLUENT TREATMENT PROCESS) that uses ELECTROCOAGULATION SYSTEM METHOD along with LOW COST ADSORBENTS has drew serious attention. Lowcostadsorbentsarepreferred over others due to their low cost, ease of application and eco- friendliness etc. The various low cost adsorbents are green shell, peanut husk, zeolites and Fly ash etc. This review paper acknowledges comparison between adsorbent made up from green coconut shell that is used in combination with ETP and ECOAG PROCESS with ferric hydroxide that is also used as an adsorbent to get rid of toxic heavy metals such as arsenicfrom ground water. Key Words: Water pollution, Water treatment, Heavymetal, Arsenic, E-coagulation, ETP, Low-cost Adsorbents, Green coconut shell, Iron hydroxide. 1. INTRODUCTION We know, Arsenic is one of the toxic elements. It affects the ground water which arises to many health diseases for humans and animals. There are many ways of detoxing water where in Electrocoagulation, Membrane Technology, Effluent Treatment Process (ETP), etc. works for removing Arsenic from ground water. 1.1 Water Contamination As commercial global has grown, environmental demanding situations have additionally increased. A known form of pollutants the arena is presently suffering with is water pollutants. Water pollutants may be as a result of a selection of things consisting of agriculture, sewage and wastewater, oil pollutants and radioactive substances. Wastewater, specifically which discarded through industries, can comprise an extensive variety of heavy metals. The rangesof heavy metals infection in water which incorporates Pb, As, Cd, Hg, Cr, Ni etc. in severa water reassets as ground, ground and tap water etc. A form of heavy metals, some of them are potentially toxic and are transferred to the surrounding environment thru via severa pathways. Heavy metal toxicity has validated to be a main risk and there are various health risks associated with it. The toxic effects of these metals, regardless of the truth that they do nownothaveanynatural role, their toxic effects are despite the fact that risky for the human body and its proper functioning. [2][3] 1.2 Arsenic Arsenic is a natural semi steel chemical that is located anywhere within side the worldwide in numerous water bodies. Arsenic has 185pm molecular size. The allowed interest of arsenic in drinking- water is 10 micrograms consistent with litre [4]. Arsenic,a well-knowncarcinogen,is regarded as one of the world-wide’s most risky chemicals [5]. Arsenicosis, a now no longer unusual place name commonly used for Asrelatedhealthproblemswhichconsist of pores and pores and skin disorders, pores and pores and skin cancers, internal cancers (bladder, kidney, and lung), ailments of the blood vessels of the legs and feet, possibly diabetes, multiplied blood pressure, and reproductive disorders[6][7]. Current techniques to remove arsenic embody precipitation, such as lime or coagulants to water, the use of membranes to clean out it out, or the use of an ion ex-trade process [8]. The most inexperienced and used method for removal of arsenic are MEMBRANE TECHNOLOGIES, COAGULATION, ADSORBPTION [9]. There are subtypes for membrane technology and adsorption. 2. METHODS TO REMOVE ARSENIC Membrane technology is divided into four types, those are Microfiltration, Ultrafiltration, NanofiltrationandReverse Osmosis. In Adsorption, we have Activated Alumina, Iron based sorbents, Zero- valent iron, Indigeneous filters, miscellaneous sorbents, metal organic framework. Electro- coagulation is a type of an advanced oxidation reaction. In this review paper we shall be discuss on electrocoagulation and low cost adsorbents [10].
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1157 Fig -1: Tree diagram for Arsenic Removal processes [9] 3. PROCESS OF REMOVING ARSENIC 3.1 Electro- coagulation Electro coagulation (EC) is a manner used for waste water treatment, wash water treatment, industrially processed water, and medical treatment. Electrocoagulationisaswiftly growing place of wastewater treatment due to its ability to eliminate contaminants which can be usually harder to eliminate through manner of way of filtration or chemical treatment systems, which incorporates emulsified oil, ordinary petroleum hydrocarbons, refractory organics, suspended solids, and heavy metals [11]. There are many producers of electro coagulation devices available rangingin complexity from a clean anode and cathode to lots more complex devices with control over electrode potentials, passivation, anode consumption etc. It is essential to be conscious that electro coagulation era cannot eliminate infinitely soluble matter. Therefore, ions with molecular weights smaller than Ca+2 or Mg+2 cannot be dissociated from the aqueous medium. [12] Whole Electro-coagulation manner incorporates of four- stages:- a) Effluent Tank/ septic tank b) Pump c) E-coagulation reactor d) Settling Tank (a) Effluent Tank The septic tank was one of the first treatment devices invented. They are intended to hold wastewater at low velocity, under anaerobic conditions for a minimum detention time of 36 hours. During this period, a high removal of settled solids was achieved. These solids decompose within side the backside of the tank with the formation of fuel line, which entrained within side the solids reasons them to upward thrust thru the wastewater to the floor and lie as a scum layer till the fuel line has escaped, and then the solids settle again. Annual inspectionisto beheld to put off sludge and for cleansing the effluent tank/septic tanks [13]. (b) Pump A pump is a device that moves fluids (liquids or gases), or sometimes slurries by mechanical action, converting electrical energy into hydraulic energy. Pumps are classified into three major groups based on the method they used to move the fluid: direct lift, displacement, and gravity pumps [14] There are basically three types of pumps:-  positive-displacement  centrifugal  Axial- flow pumps. There are various othertypesinpositive-displacementthose are:- Rotary lobe pump, Progressive cavity pump, Rotary gear pump, Piston pump, Diaphragm pump, Screw pump, Gear pump, hydraulic pump[15] (c) E- coagulation Reactor The E- coagulation reactor is made up of non- corrosive fiberglass with proprietary designed parallel plates of electrodes. When the DC current from the power supply flows through the electrode, metal ions are released form anode into the water (generating the ion Al3+ if the anode is aluminum and Fe3 if it is steel) simultaneously on the cathode hydroxyl group and hydrogen are produced. This is followed by ionization, destabilization, oxido- reduction, electrolysis, free radical formation, electromagnetic field formation, and emulsion breaking and separation [16] (d) Settling Tank Sedimentation tank, moreover referred to as a settling tank or clarifier, is a part of a contemporary-day device of water supply or wastewater treatment. A sedimentation tank permits suspended particles to settle out of water or wastewater as it passes slowly via the tank, thereby imparting some degree of purification. A layer of collected solids, referred to as sludge, office work at the bottom of the tank and is periodically removed. In drinking-water treatment, coagulants are added to the water preceding to sedimentation so you can facilitate the settling process, this is then observed via filtration and exclusive treatmentsteps. To decorate purification overall performance primary sedimentation want to beobservedvia.Secondarytreatment (e.g., trickling clean out or activated sludge) to growth purification efficiencies. Sedimentation is commonly
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1158 preceded via treatment with bar presentations and grit chambers to remove large objects and coarse solids [16] . Horizontal flow tanks. ... • Radial flow tanks. ... • Inclined settling. ... • Ballasted sedimentation. ... • Floc blanket sedimentation. 3.2 Electro- coagulation in combination with Effluent Treatment Process (ETP) As Electro-coagulation does not remove infinitely soluble matter. Therefore, ions with molecular weightssmallerthan Ca+2 or Mg+2 cannot be dissociated from the aqueous medium. So to remove all the metal toxicitiesandtogetclean drinking water Effluent treatment process (ETP) was introduced. ETP includes processes like Activated charcoal treatment (adsorption) Reverse Osmosis (RO) Ozonization (Chemical oxidation) Ultra Filtration (UF) etc. ETP has membrane technology as its core. Advantages of E-coagulation and Effluent Treatment Process:- • Less maintenance and minimal to zero chemicals. • Unnecessary water usage during the processing is eliminated and makes your industry self-sustainable. • Helps reduce the contamination of natural water bodies • It costs less and create lesser sludgewithless bound water. 3.3 Membrane Technology Membrane era has developedtobea dignifiedseparation era during the last decennia. The foremost pressure of membrane era is the reality that it really works without the addition of chemicals, with an exceedingly low strength use and smooth and well- organized manner. Membranes are used increasingly frequently for the introduction of manner water from groundwater, floor water or wastewater. The membrane separation manner is primarily based totally at the presence of semi permeable membranes. The precept is pretty simple: the membrane acts as a completely particular clear out a good way to permit water float via, even as it catches suspended solids and different materials. Membranes occupy area thru a particular separation wall. Certain materials can by skip via the membrane, even as different are trapped. Membrane filtration may be hired as an opportunity to flocculation, sediment purification procedures, adsorption (sand filters and lively carbon filters, ion exchangers), extraction and distillation. [18][19][20] Membrane filtration is assessed as microandultra-filtration on the only hand and Nano filtration and Reverse Osmosis (RO or hyper filtration) on the opposite hand. When the usage of membrane filtration to get rid of large particles, micro filtration and ultra-filtration are applied. Because of the open man or woman of the membranes the productiveness is excessive even as the stress variations are low. When salts want to be eliminated from water, Nano filtration and Reverse Osmosis are applied. Nano filtration and RO membranes do now no longer paintings in line with the precept of pores; separation takes region through diffusion via the membrane. The stress this is required to carry out Nano filtration and Reverse Osmosis is a greatdeal better than the stress required for microandultra-filtration, even as productiveness is a great deal lower. [18][19][20] 3.4 Effluent Treatment Process (ETP) The precept of operation of ETP is Physio-Chemical remedy observed through Polishing Treatments which include Sand Filtration, Activated Charcoal remedy (Adsorption), Ozonization (Chemical Oxidation), Ultra Filtration (UF), Reverse Osmosis (RO) and evaporation (If required). ETP are used for the elimination of excessive quantities of natural compounds, debris, dirt, grit, pollution, poisonous,non-poisonoussubstancesandpolymersetc.from business effluent. Industrial wastewater remedy refers back to the strategies which can be applied to deal with wastewaterthisiscreatedthroughindustriesasanunwanted through-product. After remedy, the dealt with business wastewater can be reused ordischarged right into a sanitary sewer or to a floor water within side the environment [21] [22]. Whole ETP contains of 4 stages:- • Sand Filter • Filter Press • Ultra Filter • RO system (a) Sand Filter Sand filtrationisoneofthemaximumwell-acknowledged wastewater remedy methods. If well designed, built, operated, and maintained, a sand clear out produces a completely excessive fine effluent. Sand filters are beds of granular material, or sand, tired from under in order that pretreated wastewater may be treated, accumulated, and dispensed to the very last remedy and dispersalgadget.They are generally used to shine effluent from septic tanks or different remedy strategies earlier than miles dispensed at
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1159 the land. All on-web website online structures are “no- discharge,” this means that the wastewater should stay within side the gadget and now no longer go away the property. The effluent can't input floor water, streams, ditches, or every other water resources. After the filtrate is accumulated via way of means of the sand clear out underdrains miles then disposed of via way of meansofasoil absorption gadget [23]. (b) Filter Press Filter press is one of the oldest and most reliable pieces of dewatering equipment. It’s used for wastewater treatment across a range of industries and applications. A filter press separates particles from liquids while also eliminating contaminants, and suspended solids from industrial wastewater. This enables plant managers to conveniently handle and dispose of waste while returning clean water to their systems. Filter presses are used to separate liquids and solids. Specifically, the filter press separates the liquids and solids using pressure filtration across a filter media.Afterward,the slurry is pumped into the filter press and then dewaters under pressure. [24] What are the Four Main Components of a Filter Press? • Frame • Filter Plates • Manifold (piping and valves) • Filter Cloth (This is key for optimizing filter press operations. Basically, the filter press design is based on the dewatering volume and type of slurry. [24] (c) Ultra Filter In wastewater treatment, ultrafiltration (UF) devices are used to recycle and reuse water that contains virtually no physical solids. Ultrafiltration definition, applications and industries using these process units are covered below. Ultrafiltration (UF) is a variety of membrane filtration in which forces like pressure or concentrationgradientsleadto a separation through a semipermeable membrane. Suspended solids and solutes of high molecular weight are retained in the so-called retenate. When treating waterwith high suspended solids, UF is often integrated into the process, using primary (screening, flotation and filtration) and some secondary treatments as pre-treatment stages. [25] Ultrafiltration processes are preferred over traditional treatment methods for the following reasons: • No chemicals required (aside from cleaning) • Constant product quality regardless of feed quality • Compact plant size • Capable of exceeding regulatory standards of water quality, achieving 90-100% pathogen removal. Pore size of Ultra Filtration membrane ranges from 0.005-0.1µm. (d) Reverse Osmosis (RO) Reverse Osmosis is a water purification technique that makes use of strain and a semi-permeable membrane to put off dissolved solids. The RO water is saved in a maintaining tank. If the RO water wishes greater purification, a Deionization System will lessen the conductivity of the RO water. [26] Industrial RO Applications:- • Metallic completing and plating operations • Published circuit boardand semiconductor manufacturing • Electroplating processes • Automobile manufacturing Pore size of RO ranges from 0.0001-0.001 nm 1. Effluent Tank 2. Pump 3. Electro- coagulation Reactors 4. Settling Tank 5. Sand Filter 6. Filter Press 7. Ultra Filtration (UF) 8. Reverse Osmosis (RO) Fig -2: Flow sheet of the Technology
  • 5. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1160 3.4 Low- Cost Adsorbents An adsorbent is an insoluble material coatedbyliquidonthe surface, including capillaries and pores. A material is said to be adsorbent when it has the capacity to contain a definite amount of liquid in small chambers similar to a sponge. Adsorbents play a vital role in chemical absorption, which takes place when a certain substance is trapped on a material's surface. Properties of a suitable adsorbent are high selectivity, high absorption capacity, long life, and low cost. Differentadsorbentpossessesvariouspropertiesdivers as its active surface, pore diameter, quality of pore distribution, and surface functional group. Pore sizes of porous materials are classified generally into three ranges, according to the IUPAC • macro pores: "diameter" > 50 nm, • meso pores (also known as transitional pores): 2 nm ≤ "diameters" ≤ 50 nm • Micro pores: "diameters" < 2 nm. Low-cost adsorbents refer to those materials, which are found abundantly in the environment or are byproducts or wastes from industries. Moreover, adsorbents are known as low costs if they have reduced processing requirements. Previous adsorption works concentrated on plant wastes such as, the Peat and coconut fiber , carrots , rice husks , Cane papyrus , modified coconut husk , rice bran , and others, which can be utilized each on the normal compose or change several alterations physical or chemical. Converting these materials into adsorbents is an effective way of reducing the costs of waste disposal and for providing alternate treatments for replacing the commercially activated carbons. [27] (a) Green Coconut Shell:- Green coconut shell is extensively used as adsorbent in waste water remedy as miles without difficulty to be had everywhere Pre-remedy of the adsorbent:- Green coconut shells have been furnished through Embrapa Tropical Agroindustry, CE, Brazil (EMBRAPA/CE). The adsorbent turned into dealt with NaOH 0.1mol L−1forthree h after which washed with deionized water, buffer solution (pH 5.0) and dried at 50 °C. This cloth turned into cooled at room temperature after which sieved to attain preferred particle size (0246–0074 mm) [28] (b) Iron Oxy- Hydroxides:- Arsenic adsorption theusage ofironcompounds,zero-valent iron, Iron- primarilybasedtotallybimetal oxides,iron-doped composite adsorbents are seriously reviewed and their adsorption efficienciesarecompared.Besidestheadsorption capacities, the traits of adsorption tactics, which include thermodynamics, kinetics and massswitchmechanismsalso are examined. The precise binding among arsenic and iron turned into deeply investigated via way of means of numerous spectral technologies. Moreover, a few iron- primarily based totally adsorbents are magnetic, making an allowance for a smooth separation of the saturated substances from water in an outside magnetic field. Many distinctive substances had been stated to have a very good affinity in the direction of arsenic, however iron oxy- hydroxides are the maximum extensively studied due to their smooth accessibility. The generally used iron oxy- hydroxides such as, akagan`eite (b-FeOOH), goethite (a- FeOOH), lepidocrocite (g-FeOOH), ferrihydrites ( Fe10O14(OH)2), inexperienced rusts may be chemically synthesized via way of means of the precipitation of Fe(III) or Fe(II) salts via the hydrolysis and oxidation tactics The solid As(III) oxidation country within side the darkish is steadily converted to As(V) on ferrihydrites in presence of mild at pH 5. At the equal time, Fe(III) ions have been decreased to Fe(II) species at some point of the As(III) oxidation,56 It turned into located the adsorption rate (12.4105 M s1 m2 ) on goethite turned into appreciably quicker than that of ferrihydrites (6.seventy three one hundred and five M s1 m2 ) at pH 5.fifty seven The comparable photochemical response turned into additionally located for As(III)adsorptionongoethitewithin side the presence of dissolved oxygen Laterite, a herbal iron oxide mineral containing 91% of goethite, is some other promisingandcost-powerful fabricforarsenicadsorption.59 The precise adsorption of arsenic isprovenvia wayofmeans of a sturdy proof of the shift of isoelectric point.[29] 4. CONCLUSIONS:- In this review paper we focused on removal of Arsenic from ground water by E-coagulation Effluent treatment process using Low cost adsorbents. There were many other processes but E-coagulation and ETP were most efficient. E- coagulation treatment uses electrode s to remove contaminants where-as ETP (Effluent Treatment Process) has its core into membrane technology. As E-coagulation process cannot remove all the infinitely small contaminants and heavy metals. There was a need to combine E- coagulation process with ETP. As this combination of two processes was not enough to remove all the contaminants Low cost adsorbents were introduced. There were two adsorbents studied in this review paper those are Adsorbent from green coconut shell (natural adsorbent) and the second wasIronoxyhydroxide(chemical adsorbent).low cost adsorbents Adsorb most of the contaminants and heavy metalsontoitssurface.Duetothese three processes the chances of removal of maximum arsenic are very high and at the end the treated water goes through RO where it’s again treated to be drinkable.
  • 6. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1161 References: [1] A study of the removal characteristics of heavy metals from wastewater by low-cost adsorbents by Omar E.Abdel SalamaNeama A.ReiadbMaha M.ElShafeib received 6 July 2010, Revised 14 January 2011, Accepted 21 January 2011, Available online 11 March 2011. [2] Heavy Metals Contamination in Water and Their Hazardous Effect on Human Health-A Review by Mahipal Singh Sankhla , Mayuri Kumari, Manish Nandan, Rajeev Kumar, PrashantAgrawal.DateWritten:September22,2016 Posted: 1 Aug 2019. [3] Removal of heavy metals from aqueous media by biosorption Ali Redha received 27 Sep 2019, Accepted 31 Mar 2020, Published online: 20 Apr 2020 [4] Arsenic in Water: Determination and Removal by Ljubinka Rajakovic and Vladana Rajakovic-Ognjanovic Submitted: November 21st 2017 Reviewed: February 16th 2018Published: July 25th 2018 DOI: 10.5772/intechopen.75531 [5] USEPA, “National Primary Drinking Water Regulations: Arsenic and Clarifications to Compliance and New Source Contaminants Monitoring,” Federal Register, vol. 40, CFR Parts 9, pp. 141–142, 2001. 6] WHO, Guidelines for Drinking-Water Quality,vol.4,World Health Organization, 2011. [7] S. C. Santra, A. C. Samal, P. Bhattacharya, S. Banerjee, A. Biswas, and J. Majumdar, “Arsenic in food chain and community health risk: a study in gangetic west Bengal,” Procedia Environmental Sciences, vol. 18, pp. 2–13, 2013, Proceedings of the International Symposium on Environmental Science and Technology (2013 ISEST). [8] Arsenic exposure from drinking water, and all-causeand chronic-disease mortalities in Bangladesh (HEALS): a prospective cohort study. Argos M, Kalra T, RathouzPJ,Chen Y, Pierce B, Parvez F, et al. The Lancet. 2010; 376 (9737):252-8. Arsenic in tube well water in Bangladesh: health and economic impacts and implications for arsenic mitigation. Flanagan SV, JohnstonRB,Zheng Y.Bulletinofthe World Health Organization. 2012; 90:839 -46. [9] Technologies for Arsenic Removal from Water: Current Status and Future Perspectives Nina Ricci Nicomel, 1, 2, 3 Karen Leus, 2 Karel Folens, 1 Pascal Van Der Voort, 2 and Gijs Du Laing1,* Ravi Naidu, Academic Editor and Mohammad Mahmudur Rahman,Academic EditorPublished online 2015 Dec 22. DOI: 10.3390/ijerph13010062 10] Environmental research and public health Published online 2015 Dec 22. DOI: 10.3390/ijerph13010062 [11] Application of Electrocoagulation In various Wastewater and Leachate Treatment a Review to cite this article: L W M Zailani and N S M Zin 2018 IOP Conf. Ser.: Earth Environ. Sci. 140 012052. [12] Electrocoagulation process in water treatment: A review of electrocoagulation modeling Received 20 April 2016, Revised 17 October 2016, Accepted 19 October 2016, Available online 29 October 2016. [13] Wastewater treatment Technology Iyyanki V. Muralikrishna, Valli Manickam, in Environmental Management, 2017 [14] Fao.org. Retrieved on 2011-05-25. [15] Engineering Sciences Data Unit (2007). "Radial, mixed and axial flow pumps. Introduction [16] Pristine Water, an ISO 9001:2015, 14001:2015, 45001:2018 certified company [17] Sedimentation tank water treatment By the Editors of Encyclopaedia Britannica [18] Osmotech Membranes Pvt. Ltd. © 2019 [19] Qian Wang, Linhe Zhu, Norafiqah Ismail, Qiuyueming Zhou, Ting He, Yue Zhou, Zhaohui Wang, Zhaoliang Cui* , Naser Tavajohi, Annealing of grain-like poly (vinylidene fluoride-1 trifluoroethylene) membranes with a single- crystalline electroactive phase and high anti-foulingactivity, Journal of Membrane Science, Acceptedin16thofNovember 2021. [20] Lenntech(EuropeanHeadOffice)Distributieweg32645 EG Delfgauw the Netherlands Phone: +31 152 610 900 fax: +31 152 616 289 [21] ARSENIC IN WASTE WATER FROM PRIMARY COPPER PRODUCTION PROCESS Biljana Jovanović∗, Milana PopovićRTB Bor – Copper Smelter and Refinery Bor Đorđa Vajferta 20, 19210 Bor, Serbia, Received 12.06.2013 Accepted 02.10.2013 [22] Onsite Wastewater Treatment Systems:SandFilters By: Bruce Lesikar, Professor and Extension Agricultural Engineer, the Texas A&M System [23] Adsorption: Fundamental Processes and Applications Pouran Pourhakkak, Mehrorang Ghaedi, in InterfaceScience and Technology, 2021 [24] Filter presses for sludge dewatering Posted on18 June 2020 [25] Enzymatic cleaning in ultrafiltration of wastewater treatment plant effluent Author links open overlay panel Sandyte PoeleJaapvan der Graaf
  • 7. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 03 | Mar 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 1162 [26] Sustainable Processes for Treatment of Waste Water Reverse Osmosis Concentrate to Achieve Zero Waste Discharge: A Detailed Study in Water Reclamation Plant Author links open overlay panelS.ShanmuganathanaM.A.H.JohiraA.ListowskibS.Vignes waranaJ.Kandasamya [27] Cheryan, M. Ultrafiltration and Microfiltration Handbook, Technomic Publishing Co., Lancaster, PA. 1998. 527 [28] Review Paper. Utilization of Low-Cost Adsorbents for the AdsorptionProcessofChromiumions.Mohammed Jaafar Ali Alatabe 1 and Ahmed Alaa Hussein 1 Citation Mohammed Jaafar Ali Alatabe and Ahmed Alaa Hussein 2021 IOP Conf. Ser.: Mater. Sci. Eng. 1076 012095 [29] A critical review on arsenic removal from water using iron-based adsorbents Linlin Hao, ab MengzhuLiu,a Nannan Wang c and Guiju Li*a . Received 15th October 2018 Accepted 21st November 2018 DOI: 10.1039/c8ra08512a