MILESTONES OF NANOSCIENCE IN ENVIRONMENTAL BIOTECHNOLOGY- A

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IJBPAS, December, 2015, 4(12): 6541-6564

ISSN: 2277–4998

MILESTONES OF NANOSCIENCE IN ENVIRONMENTAL BIOTECHNOLOGY- A REVIEW SAIMA SHAKIL MALIK*, ZEHRA KAZMI, NAILA SAFDAR Fatima Jinnah Women University, The Mall Rawalpindi, 46000 (Pakistan). *For correspondence: [email protected]; Phone # +92- 333-8403698 Financial assistance: There was no particular grant or financial assistance available for this study. Conflict of interest: All the authors declare no conflict of interests. ABSTRACT Nanotechnology is an emerging field that has the ability to consistently change and modify the properties of nanostructures by controlling their surface properties and structure at a nanoscale level. These valuable characteristics make nanoparticles highly attractive candidates for use in the field of environmental biotechnology ranging from fundamental scientific studies to commercially useable treatment technologies. Nanotechnology had played immense role in sensing and detecting various pollutants, pollution prevention and in vast number of remediation treatment technologies. It plays a vital role in the development of new methodologies to produce novelnano-products, to replace already existing equipment and to reformulate new chemicals and materials with enhanced performance and efficacy. All these improvements results in less energy consumption, detection and sensing of pollutants, environmental remediation, water, soil and air purification, cleaner production and prevention of food contamination and spoilage which in turns provides great human health and life style benefits. Environmental applications of nano science not only addresses the development of solutions to cope with existing environmental problems but also elaborate different preventive measures for various problems that may occur in the future. This review discusses the recent advances and application of nanotechnology in the field of environmental biotechnology. It sheds light on the process and pros and cons of almost

6541 IJBPAS, December, 2015, 4(12)

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Review Article

all the nanomaterials such as metal oxides, metal nanoparticles, zeolites, carbon compounds, filtration membranes, nanoadsorbents, and photocatalysts for efficient environment treatment and remediation. Not only the beneficial properties but their comparisons with conventional processes are also reported. This review briefly illustrates the commercialization aspect together with the future prospects of nanotechnology related to environment, health and production process. Keywords: Nanoscience, nanomaterials, pollutants, nanoadsorbents, photocatalysts nanoparticles, environmental remediation. INTRODUCTION AND BACKGROUND With rapid industrialization and enhanced

nausea,

anthropogenic activities, different grades of

reduced work capacity, cancer, premature

pollutants had been generated. Common

death,

pollutants

cardiovascular problems,

are

carbon

monoxide

(CO),

pulmonary

congestion,

influenza,

visual

asthma,

impairment, less

manual

chlorofluorocarbons (CFCs), heavy metals

dexterity along with stomach problems, liver

(arsenic, chromium, lead, cadmium, mercury

toxicity and neurological disorders. For

and zinc), hydrocarbons, nitrogen oxides,

environmental cleanup process, different

organic

techniques have been used and the most

compounds

(volatile

organic

compounds and dioxins), sulphur dioxide and

recent

particulates. Major factors that are meant to

Nanotechnology is the understanding and

be the cause of pollution in water include

management

waste disposal, oil spills, and release of

between

fertilizers, herbicides and pesticides, by-

nanometers, where unique phenomena enable

products

novel

of

industrial

processes

and

one

of

is

nanotechnology.

matter

at

dimensions

approximately

1

and

applications

Nanoscience

concerned

Gaseous and solid waste pollutants include

characterization, evaluation and application

molds, germs, viruses, mites, allergens, dust

of devices together with materials on

particles, pungent odor, toxicants, smoke and

nanoscale. Nanomaterials are highly reactive,

VOCs. Water is also contaminated by a

have large specific surface area, high degree

number of pollutants including organic and

of

inorganic wastes. Health effects of pollutants

dependent

include

properties make them suitable for large

problems,

coughing,

functionalization

design,

is

combustion and extraction of fossil fuels [1].

respiratory

with

[2].

100

and

characteristics.

synthesis,

various

size

All

these

6542 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

Review Article

number of applications in different areas.

water comprises of proteins, carbohydrates,

Nanoscience has played its great role in

oils and fats, surfactants, bacteria, viruses

different environmental remediation and

and other microorganisms. The treatment

detection techniques and this review paper

process of wastewater is based on the

illustrates

composition

good

examples

of

these

techniques.

of

the

wastewater.

The

conventional treatment of the wastewater

NANOTECHNOLOGY

IN

consists of certain steps which are given in

WASTEWATER TREATMENT

the figure 1. Introduction of the tertiary

Any water which is contaminated by

treatment process greatly ensures the purity

microorganisms,

bacteria,

industrial

of the wastewater after treatment [3].

effluents,

metals

organic

Unfortunately it is too expensive that

heavy

and

pollutants is termed as wastewater. Waste

• Remove coarse aand suspended solid materials • upto 0.01mm size

Preliminary treatment

Primary treatment

• Remove both organic and inorganic suspended solid materials •0.1mm - 35µm

•Biological treatment • Degrade organic matter and other nutrients

Secondary treatment

Tertiary treatment

industries fails to find any interest in it.

•Remove remaining organic and inorganic materials together with microbes and viruses • Includes filtration and chemical disinfection

Figure 1: Scheme of conventional wastewater treatment process

Industrial wastewater contains a wide variety

processes of water purification and there is a

of effluents depending upon its source like

scarcity of water on the Earth. In the

wastewater from agriculture, steel, iron, food

developing countries approximately 90% of

and mining industry. Uncontrolled human

the diseases are caused by the usage of

population and increased industrialization

contaminated water [4]. Therefore it is

without planning disturbed

necessary to treat and purify the water before

the

natural

6543 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al its

consumption.

Review Article

But

the

conventional

There

are

two

features

nanosorbents

treatment to such an extent that it can be

effective. a) They have high specific surface

called as safe for human consumption. So, it

areas which helps in increased affinity

has been a great challenge to find out such a

towards

cost effective

and efficient wastewater

contaminants. b) Their pores are of nano size

treatment processes. Nanotechnology offers a

so, efficient sorption of contaminants takes

great potential for this purpose.

place. It has been illustrated that 3D

Nanotechnology for efficient wastewater

flowerlike

treatment:

nanostructures can efficientlyabsorb organic

Recently, different techniques and tools have

dyes and remove heavy metal ions from the

been developed by nanotechnology, in order

wastewater [6]. Nanoparticles are magnetic

to purify water and provides new alternatives

in nature. So, it is easy to separate and

for wastewater treatment in more efficient

regenerate them by magnetic separation and

and cost effective way [3]. Some of the

catalytic combustion respectively. Some of

important features of nanomaterials that

the important nanomaterials which serves as

made them so important are:

sorbents are given in the Table# 1.

a. They are very small and highly reactive in their action.

make

them

of

methods were not efficient in the wastewater

the

which

salient

more

greater number of target

iron

oxide(self-assembled)

Photocatalysis: Photocatalysis is one of the important

b. They provides precise and accurate results.

treatment technology used for wastewater. It

c. Nanomaterials

uses nanostructured catalyst medium (light

are

cost

effective

and

environment friendly. Different

Nano-science

active) for the degradation of a range of based

treatment

pollutants in the water. It is a surface

technologies are available for wastewater

phenomenon

treatment

mechanism comprising of 5 different steps

[5]

including

Nanosorbents,

Photocatalysis and Nanofiltration.

illustrated

and

in

involves

a

figure

complex

2.

Nanosorbents:

6544 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

Reactants diffusion on catalysts surface

Review Article

Reactants adsorption on catalysts surface

Products desorption from the surface of catalyst

Reaction at the catalysts surface

Products diffusion from the surface of catalyst

Figure 2: Basic steps involved in photocatalysis

An ideal photocatalyst should be highly

this separation technique pressure-driven

photoactive, biologically and chemically

membrane is used to purify the water by

inert, non-toxic, photo-stable and cost

high permeation rate and repulsion property

effective [7]. Titanium dioxide, ferric oxide,

based on charge. It uses minimum energy

zinc oxide, cadmium sulfide and zinc sulfide

and is much popular in the developed

are commonly used examples of nano-

countries. It gains importance in different

structured semiconductor photo-catalysts. It

industries

like

pharmaceuticals,

has been greatly used to degrade harmful

petrochemical

industry

textiles,

organic

industry and many more. It can not only

contaminants,

heavy

metals

(recovery of gold, platinum, rhodium &

filter

removal of mercury & cadmium) and

contaminants but also the microbes because

microbes

of various membrane [8].

(Escherichia

coli

&

out

the

organic

and

dairy

inorganic

Staphylococcus aureus) from the waste

Carbon nanomaterials are often studied and

water [5].

used because of their high mechanical

Nanofiltration:

robustness, ease of preparation and excellent

Filtration is the most common and older

ability to reject contaminants. Their pore

technology and had passed through a

size ranges from 1-10µm. So, only water can

number of changes with reference to pore

pass through it. Metal oxides are also used

size and filtering material with the passage

as another low cost alternative for the

of

fabrication

time.

Conventional

filtration,

of

nano-filter

membranes.

microfiltration and then even ultrafiltration

Common metal oxides used are TiO2, ZnO,

fails to remove some of the contaminants

SiO2 and ZrO2 [5].

from the wastewater. So, scientists move

Zeolites also find enormous applications in

towards a better option, nanofiltration. In

nanofiltration because of their chemical and 6545

IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

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thermal stability. They are microporous

their pore sizes ranges from sub-nanometer

crystalline aluminosilicate materials and

to nanometer scale [8, 9].

Table 1: Some important nanomaterials as sorbents Principle Properties Uses (Removal/ reduction) Derived from ↓cost, ↑efficiency, Derivatives of agricultural& ↓biological&agricultural dioxins. biological materials. sludge, Used for the removal no need of additional nutrient Organic of pollutants which ®enerative contaminants. are present in minute quantities in water. Heavy metals

Nanosorbents Biosorbents DNA matrix -Trioleinembedded biosorbents -Chitosan-based sorbents -Bio-sorbent from black liquor

References [10]

[11]

[12]

Carbon nanotubes (CNTs)

Nano zero valent iron

Metal Oxide Nanosorbents -Iron and silicon oxides

Adsorption of pollutants depends upon the morphology & surface status of CNTs. Newly discovered for the removal of a wide range of organic & inorganic pollutants from water.

highly specific,chemically and thermally stable, reactivity can be varied by functionalizing their surface

Metal oxides are used as adsorbent materials.

Materials used are of low cost. Easily functionalized to tune adsorption capacity and selectivity.

Highly reactive and short lifetime, surface-modified, emulsified, bimetallic, better distribution on carbon support

Pb(II), Cu(II), Cd(II), Zn(II) & Ni(II) 1, 2-dichlorobenzene with Cd & Pb. Dyes.

[13] [14, 15]

Heavy metals (Cu, Ag reduced & Zn, Cd adsorbed). Precipitation &adsorption for As, Cr, Cu, Pb, Ba, Co & U ions.

[16]

[17]

Organic pollutants Heavy metals [18, 19, 20] Organic dyes

-Tungsten oxide Carbon Nanosorbents

Carbon nanomaterials are used for the adsorption of different organic &inorganic pollutants present in water.

↑adsorption capacity, ↑thermal stability,↑resistance against attrition losses ↓cost.

Benzene & toluene. Hg(II), Co(II), Ni(II), Cu(II) Cd(II), Pb(II), Cr(III) & Cr(VI)

[21]

NANOTECHNOLOGY IN GASEOUS

Electrostatic Filters, Ozone gas, Ultraviolet

TREATMENT

radiations

Nanotechnology also plays an important role

complete removal or excellent results can

in

only

cleaning

environment.

toxic

gases

Different

from

the

treatment

and

be

many others. But

observed

by

using

the

the

nanotechnology (photocatalyst).

technologies are available for the removal of

Applications

germs, molds, viruses, allergens, mites, dust

comparison with conventional treatment

particles, specific odor, toxicants, smoke and

methodologies

volatile organic compounds including High

Polychlorinated

Efficiency

polychlorinated dibenzofuran are extremely

Particulate

Air

Filters,

of

nanotechnology

biphenyls,

dioxins

in

and

6546 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

Review Article

toxic and stable pollutants. Adsorbents like

Factory (BASF), a chemical company along

γ-aluminum oxide, clay, zeolites and even

with

activated carbon were unable to remove

photocatalyst using solar energy to convert

these toxic compounds [22]. So, Long and

CO2 into ethanol and explains its potential

coworkers explores the use of carbon

use as fuel.

nanotubes for their complete removal or

Removal of VOCs especiallytoluene, hexane

degradation [23].

and acetaldehyde can be efficiently done by

Continuous efforts had been made to find

manganese oxide (highly porous) with gold

out the treatment technologies for the

nanoparticles

removal of oxides of nitrogen, sulphur and

conventional catalyst methods [26].

carbon from air. Various adsorbents were

In 2014 Prof Tony Ryan (scientist) and Prof

used for nitrogen oxides and carbon dioxide

Simon Armitage (poet) from University of

removal like zeolites, ferric oxy-hydroxide

Sheffield, UK had made a poster coated with

(FeOOH), activated carbon [24] and zeolite,

nanoparticles (titanium dioxide) which can

activated carbon and silica respectively. But

clean the air from different sized dust

they are unable completely remove these

particles and nitrogen dioxide as well

oxides and also cause some hazardous

[27].Different

problems[25]. Use of chemically modified

nanotechnology based approaches to clean

CNTs,

the environment along with their potential

and

a

nanocatalyst

containing

platinum and cobalt particles provides

different

universities

as

prepared

compared

industries

to

a

the

using

benefits are given in the Table 2.

astonishing results. Baden Aniline and Soda Table 2: Companies, products and their benefits for the treatment of wastewater and air by nanotechnology Product/year launch Company Benefits [References] Capillary ultrafiltration membrane University of Stellenbosch Cost effective,excellent removal of Fe, Al & technology (2003) &Water Research Mn oxides from industrial, sea & Commission (South Africa) wastewater[28] Nano-composite catalyst (2004) NanoStellar Low cost technology due to less use of (United States) platinum [29] Nanofiltration membrane (2006) Saehan Industries Used in China & Iran. Requires less energy (Korea) than reverse osmosis [30] Manganese Oxide nanopowder American Elements Removal of VOCs from industrial emissions (2006) (United States) in the air [29] Nanorust or *CBEN’s arsenicRice University low-cost technology to remove arsenic from removing technology (2009) (United States) water [30, 31] Virus-free water (2009) Rice University Silicone &TiO2 were used to disinfect water (United States) in min. than hours [32, 33] Membranes based on nanotube Poriferia Efficient removal of carbon dioxide [29] (2009) (Greece) Quad-Nano Extreme (a metal Air OasisAir Purifiers Air clarifier, reduces ozone in the catalyst) (2006) (United States) environment to a safer level [34]

6547 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

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Gens Nano (a photocatalyst) (2009) Elbegast (2012)

Green Earth Nano Science Inc. (Canada) Goldemar (United States)

Removes formaldehyde, NOx, benzene, VOCs & automobiles exhaust [35]

Low cost as compared to platinum & removes VOCs, CO, SOOT, HCs & NOx [36] *CBEN- Center for Biological and Environmental Nanotechnology

APPLICATION OF

halogenated

NANOTECHNOLOGY FOR

pentachlorophenol,

TREATMENT OF CONTAMINATED

trichloroethane,

SOILS

trinitrotoluene. These chemicals are also

Various

organic

chemicals

compounds

like

trichloroethylene, dinitrotoulene,

and

are

placed in the EPA list of priority pollutants.

resistant to biodegradation are mainly

As these carcinogenic contaminants are also

contributing to the contamination of surface

immune to biodegradation and persist in the

and subsurface soils. These are posing a

environment (Vogel et al., 1987).

serious threat to safety of living organisms

Remediation techniques

and their natural habitats as many of these

Different remediation techniques have been

are of toxic and mutagenic nature. These

used for the soils contaminated with PAHs.

persistent

These

chemicals

which

organic

include

polycyclic

include

various

chemical

and

aromatic hydrocarbons (PAHs) comprising

biological approaches like Fenton reaction

heavier fractions of petroleum with two or

for pyrene removal (Chang et al., 2003).

more benzene rings and relative stability.

Moreover,

Due

U.S.

subsurface soils with different surfactants is

Environmental protection Agency (EPA) has

also tested. As four column experiments

enlisted 16 of these PAHs as priority

have been conducted to evaluate the

pollutants. Some of these chemicals are used

potential

to manufacture different kind of stuff like

tertrachloroethylene extraction from sand

dyes, explosives, medicinal drugs etc.

particles.

However exposure of soil to these pollutants

phenanthrene from soil by using different

may be caused by industrial activity

surfactants is also reported (Pennell et al.,

including oil leaks, improper disposal and

1994). However, Wilson and Jones (1993)

incomplete combustion (Chang et al., 2005).

found that use of in situ techniques for

In addition, several sites are also found

removal of most of the PAHs from

which

contaminated soil do not give sufficient

to

their

are

hazardous

heavily

nature,

contaminated

with

treatment

of

In

of

aqueous

addition,

surface

surfactants

separation

and

for

of

6548 IJBPAS, December, 2015, 4(12)

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results. Therefore, more effective techniques

like chlorinated ethylenes, halomethanes,

are required to effectively remove PAHs.

nitroaromatic

Permeable

pentachlorophenol, chlorinated pesticides

reactive

barrier

(PRB)

compounds,

technology

such as DDT, polychlorinated biphenyls,

The traditional methods for treatment of

atrazine etc. (Reddy, 2010). It involves use

halogenated contaminants like soil washing,

of zero-valent iron Fe○ as reactive medium

thermal desorption and bioremediation are

for de-halogenation of contaminants as they

considered less effective due to their high

react with iron and are reduced into non-

cost, secondary waste production and slow

toxic form (Sharma and Reddy, 2004).

rate. Permeable reactive barrier (PRB)

Possible reductive reactions between zero-

technique is effectively used to treat ground

valent iron and a halogenated compound are

water contaminated with various compounds

given as following;

Reactions of zero-valent iron (Fe0) with a halogenated organic compound (RX) in water Reaction

Mechanism

Anaerobic corrosion of iron

Fe + 2H 2O = Fe2+ + H2 + 2 OH-

Aerobic corrosion of iron

2Fe + O 2 + 2H2O = 2Fe2+ + 4OH

Possible reductive reactions of iron with RX Reaction of RX with ferrous ion in the aqueous phase

RX + 2Fe2+ + H+ = 2 Fe3+ + RH + X

Reaction of RX at the surface of the metal (electron transferreaction)

RX + Fe + H + = RH + Fe2+ + X

Adsorption of RX to the metal surface and the

Fe = Fe2+ + 2e-

subsequent surface reaction of the organic radical R*

RX + e- = R* + X R* + H+ + e- = RH

ii) Air contact reduces the ability of iron

Limitations of PRB Although PRB technique has advantage of

to reduce halogenated compounds.

being relatively economical due to low cost

iii) Variation in reactivity of zero-valent



of Fe , easy handling and operational

iron for different compounds thus

activity.

reaction rate is not predictable.

However,

its

efficiency

is

compromised by following factors; i) Formation of oxide surface film which reduces the reactivity of Fe○.

These

limiting

factor

reduce

the

effectiveness of PRB for long term in situ remediation (Reddy, 2010).

6549 IJBPAS, December, 2015, 4(12)

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Use of Nano-scale iron particles (NIP) for

In contrast, nanoscale iron particles are

soil treatment

widely used due to their environment

Nanotechnology

the

friendly nature, low cost, easy injecting

remediation techniques with the tool of

procedure and fast reaction which results in

nanoscale zerovalent iron particles (NIP)

production of less toxic waste products.

which can be used for treatment of various

Reactivity of NIP

non-degradable organic compounds from

Reaction time, concentration of both NIP

soil and groundwater. These particles are

and contaminant act as limiting factors for

more effective than PRB due to following

reactivity of NIP. Whereas, rate of reaction

properties;

is affected by pH, temperature and absence

i)

has

equipped

Higher reducing ability and rate of

or presence of oxygen etc. The reaction

reaction as compared to PRB

involves following steps;

technique. ii)

In

a) Halogenated

situ

detoxification

of

compounds by direct injection of NIP into contaminated soil as compared

to

PRB

in

which

contaminated water passes through the PRB. iii)

move

from solution towards iron particles. b) Absorption of these compounds at surface of iron. c) Reduction reactions resulting in dehalogenation of compounds. d) Desorption of compounds from iron

Increased surface to volume ratio which

contaminants

makes

the

NIP

more

reactive.

particles. e) Movement of reduced products back into the solution (Shih et al., 2008).

Moreover, several studies have reported the

Modification of NIP to increase the

effectiveness of nanoscale iron particles as

reactivity and stability

compared to iron fillings which is used in

Increased

permeable reactive barrier method (Cao et

achieved by modification of NIP. Reactivity

al., 2005).

is increased by synthesis of composite

Though several nanoscale metal oxides are

nanoparticles/ bimetallic particles which

considered

soil

involves combining NIP with a noble metal

treatment. However, some of these like ZnO

e.g. Ag/Fe, Cu/Fe, Ni/Fe. The noble metal

and AgO2 are avoided due to their toxicity.

protects the iron core against oxidation

suitable

for

use

for

reactivity

and

stability

are

6550 IJBPAS, December, 2015, 4(12)

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reactions and acts as a catalyst (Li et al.,

with high permeability when used with

2006). Since these particles are prone to

pressurized delivery system. Whereas, soils

clustering due to magnetic properties and

with low permeability need electro kinetic

van der walls attractions. Furthermore, these

delivery system for effective transport of

have greater density as compared to water

lactate modified NIP (Reddy, 2010).

which results in quick settlement. Thus the

NANOTECHNOLOGY

rate of NIP delivery to contaminated zone is

ENVIRONMENTAL MONITORING

compromised

Anthropogenic

due

to

clustering

and

IN

activities

particularly

sedimentation. This problem can be solved

industrialization and extensive utilization of

by increasing the stability of iron particles

chemicals in

by using different modifiers like polyacrylic

pollution in soil, water and air. Monitoring

acid, potato starch, guar gum etc. which

pollution and contaminants in air, water and

modify the surface of NIP and increase both

soil are very important to assess risks in

their reactivity and movement towards

environment. Detection of environmental

contaminated sites (Saleh et al., 2007).

pollutants is required for the safety of living

Soil treatment with NIP and modified

organisms [50]. Environmental monitoring

NIP

includes

Soils can be directly injected with NIP

monitoring emissions in air and drinking

slurry due to their small particle size.

water, aquatic environment, air quality and

However, reaction rate is slower in soil as

depositions. Conventional chromatography

compared to aqueous media (Varanasi et al.,

and

2007). Reaction rate can be increased by

environmental monitoring like (GC/MS) and

both increasing the concentration of NIP and

(HPLC/MS) are time consuming, expensive

reaction time. Use of NIP has been proved

and requires a lot of expertise. For water

to remove 60% of pyrene from soils in

samples it is difficult to carry out these

Taiwan (Chang et al., 2007). However

activities outside laboratory [50, 51]. Instead

modification may compromise the transport

of relying on conventional procedures,

and reactivity of NIP which can be avoided

electrochemical

by using suitable modifier like lactate

techniques

modification

delivery

developing biosensors with rapid and on-site

system. It is considered effective in soils

monitoring [52]. Recently different types of

and

appropriate

`agriculture have caused

various

aspects

spectroscopic

is

and gaining

including

techniques

for

immunoassay importance

for

6551 IJBPAS, December, 2015, 4(12)

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biosensors have been utilized for the

nano

purpose

monitoring.

quantization of nano materials are the key

Biosensors can be defined as the analytical

factors due to which nano-materials exhibit

devices

material

very different properties. Laws of absolute

incorporated in them and it is linked with a

quantum chemistry or classical physics are

physiochemical transducer which can be

not followed by nano-materials [55]. As

optical,

nanoparticles are smaller than characteristic

of

environmental

with

a

biological

electrochemical,

micromechanical,

magnetic,

systems

and

size

or

length they exhibit new chemistry, new

piezoelectric detector [53]. Biosensors can

physics and thus new properties which is

be classified on the basis of biological signal

largely

(enzyme, antibody, DNA, cell based and

Nanotechnology has

biomimetic) or transducer (electrochemical,

scientific industry and nano-materials have

piezoelectric,

optical).

been utilized in many different commercial

Many of the biosensors are commercially

industries. Nano-materials find immense

available Biosensors field has flourished to

applications

an extent that it has allowed to develop

technology. It has a promising role in

biochip for real time monitoring with low

pollution sensing field due to the unique

costs [54].

properties of nano-materials

In the search of perfection, quest of

surface area, great catalytic efficiency, high

developing next generation biosensors has

surface reactivity and strong adsorption

led us to the point where incorporation of

capacity

nano-materials in biosensors takes place and

candidates for sensing devices [58].Because

reveals a great state of the art technology

of high sensitivity and great recognition,

with bright prospects.

nanosensors are labeled as “smart devices”

ROLE

OF

thermometric

crystalline

calorimetric

and

NANO-SENSORS

IN

influenced

in

by

the

makes

the

size

[56].

revolutionized

field

of

the

sensing

[57].Large

nano-materials

ideal

[59]. Nanosensors can possess the capability

ENVIRONMENT

of

Size of nano-materials is smaller than 100

microorganisms in minute amounts [57].

nm.

properties

There are many advantages of nano-material

different form other materials as they are

enabled biosensors including sensitivity,

smaller than solids but larger than individual

selectivity, small size, low cost and fast

atoms and molecules. High dispersity of

response

Nano-materials

exhibit

detecting

time

pollutants,

[52,

45].

toxins

Varieties

and

of 6552

IJBPAS, December, 2015, 4(12)

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nanomaterial have been employed for

with their specifications used within the last

environmental monitoring with different

ten years have been described in Table 3.

modifications.

Some of the nanosensors

Signal transduction method Electrochemical Change in sensor resistance Optical properties (color/ refractive index) changes when exposed to organic vapors

Chemosensor for colorimetric recognition, Color change

Table 3. Nanosensors and their specifications Recognition element Type of Nano-particle employed Solids-state Gas sensor Metal oxide is coated with coupled with GIS modeling electrodes on substrate, incorporation of GIS modeling Volatile organic Vapochromic complex is used compounds as a sensing material and ESA (electrostatic self-assembly) method to build nano-cavities on optical fiber by depositing ionic monolayers doped with vapochromic complex Mercury ions Chemically synthesized azochromophores fabricated with compact nanopore compact discs available as strips

Electrochemical, AC voltage and frequency

Humidity sensor

LiCl doped TiO 2electrospunnanofibers

Multiple depending on particular type e.g., fluorescence, colorimetric

Small organic molecules, proteins, metal ions

Photoluminescence

Hydrogen gas sensing at room temperature

Change in Refractive index/ color detection by optical spectroscopy

DNA, proteins, enzymatic activity

Aptamer (oligonucleotide) functionalized Nanobiosensors, a number of nanomaterials can be employed most successful are silver and gold nanoparticles Single ZnO nanowire sensor invented utilizing focused ion beam instrument LSPR-based nano-biosensors, metal nanoparticles prepared by nanolithography incorporated to sensor moiety

Electrical current and sensor resistance

Selective and sensitive detection of NO2gas

Fluorescence/ magnetic fluorescence/ surface plasmon resonance/ Surface enhanced Raman spectroscopy

Pathogens detection in water

Electrochemical

Microorganisms, toxins, small organic molecules

Single walled carbon nanotubes

Electrochemical detection, Oxidation, reduction current of enzymatic products, change in pH

Organophosphorus pesticides and nerve agents

Gold nanoparticles and chemically reduced graphene oxide nanosheets

Nanosensor based on tungstenoxide mesocages, hollow spheres and nanowires Quantum dots, metals, carbon nanotubes, magnetic nanoparticles, dye doped nanoparticles

Comments

Ref.

Gas adsorption and sensitivity increased at nanoscale

[60}

High reproducibility, efficient, nano-cavity sensitive to alcoholic vapors

[61]

Visual detection of ultra-trace HgII ions, Cost effective, energy saving system and ecofriendly, analysis can be done on site and in-situ without need of complex sample treatments Highly sensitive, stable, can measure humidity at room temperature, good reproducibility Highy selective interaction of oligonucleotide (DNA/RNA) with sample, high amplification signal, pH, viscosity ionic strength affects oligonucleotide Possible to tune gas response and selectivity

[62]

Refractive index sensitivity of metal nanoparticles can be influenced by size and shape, combining SPR in metal films and LSPR by nanostructures enables detection of biochemical interactions inside nanoholes Inexpensive, scalable synthesis method, significant response at low concentration Whole cell detection of water borne pathogens, differentiation of viable from non-viable cells and detection of viable but non-culturable cells is still a challenge High response, magnificent sensing behavior, rapid, labelfree Stability, trace pesticide detection, optimization for broad substrates required

[66]

[63]

[64]

[65]

[67]

[68, 69]

[70]

[65]

6553 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

Review Article

It can be stated explicitly that a variety of

IMPACT OF NANOTECHNOLOGY ON

nanosensors have been employed in a

ENVIRONMENT

number

environmental

With the advancement in nanotechnology its

monitoring. Design of nanosensors differs

impacts on environment and public health

according to the type of nanoparticle used,

need to be considered. Vast research is

signal transduction method and type of

needed in this regard to identify the

recognition element which it has to detect.

environmental

Nanosensors allow more rapid and sensitive

opportunities to eradicate that problem and to

detection of analyte as compared to the

evaluate the impact of nanotechnology in

conventional methods of detection. Thus,

environment. For cleanup of environment

structure of nanosensors largely depends on

nanomaterials are used that include nanoscale

the function it will be carrying out. Efforts

zeolites, metal oxides, carbon nanotubes and

are underway to design advanced and

fibers,

modernizednanosensors that can accumulate

[mainly as bimetallic nanoparticles (BNPs)],

present advantages of nanosensors with the

and titanium dioxide. One of the most

provision of environmental monitoring on

commonly used nanomaterial is zero-valent

site with naked eye.

iron (nZVI).

of

studies

Compound TiO2 based nanoparticles

Iron based nanoparticles

bimetallic nanoparticles

Nanoclays

for

Dendrimes

various

Table 4: Environmental Nanoparticles: Advantages and Disadvantages Advantages Disadvantages  Non-toxic Large volume of sludge generation  photo-stable  Difficult recovery  water insoluble  Costly Soil & water insitu remediation  Safe  Cost effective  removal persistent organic compound such as hexachloroccyclohexane Highly reactive in redox reactions

 low cost unique structures  Highly stable  Reusable  high sorption capacity  easy to recover  large surface area  Adsorption of heavy metals, anions and organic pollutants  high thermal and electrical conductivity  Rigid and stable  renewable 

Nanotube

enzymes,

problems,

 Hard recovery  Sludge generation  Sludge disposal is expensive  Negative health impacts DNA damage, lipid peroxidation, and oxidative damage of proteins  Hard recovery  Sludge generation  Difficult disposal  Production of toxic products large amount of sludge generation  poor porosity

different

noble

References [71]

[72-74]

[75]

[75, 76]

high operational cost generation of sludge difficult to recover poses health problems

[77]

Conformational dynamics and 3-D

[78]

   

metals

6554 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

Review Article 

magnetite nanoparticles

Carbon nanotubes

large binding capacity  cost-effective  pollutant reduction adsorb organic pollutants and heavy metals less sludge generation

structure are not well understood

 highly specific, thermally & chemically stable

 

GREEN

SYNTHESIS

FOR

[75]

Requires external magnetic field for separation  Highly expensive.

[2]

Lung diseases  Cancer Alzheimer’s disease

vomiting and diarrhea. In some cases

ENVIRONMENT

respiratory problems and allergies were also

With the advancement in nanotechnology,

reported so scientists tried to degrade it with

green chemistry and green technology are

the help of nano-particles.Most frequently

working on finding ways to eliminate toxic

iron

ingredients from the manufacturing processes

synthesized using different plants extracts.

in

Tea extract was most commonly used plant

order

to

reduce

their

release

in

and

magnetic

resource

established that require low temperature,

nanoparticles. Hoag with his coworkers

consume less energy and use renewable

synthesized iron based nanparticle from

resources

Green

Camellia sinensis (green tea) extract. Tea

nanotechnology is trying to incorporate these

polyphenols act as reducing agents. They

ideas and aims to not only contribute to

have iron chelates, used for bromothymol

lessen the environmental problems, but also

blue degradation [80].

to

synthesize

such

possible.

nanomaterials

the

synthesis

of

were

environment. Such processes need to be

wherever

for

nanoparticles

iron

and

products that have minimum negative impact

Another study used three different types of

on the environment and human health. If all

tea extracts, namely, green tea (GT), oolong

the aforementioned prerequisites are full

tea (OT), and black tea (BT) to synthesize

filled precisely, green nanotechnology should

iron nanoparticles. These nanoparticles were

results in environmentally friendly and

tested for their capacity to act as a catalyst

energy efficient manufacturing processes

for

[79].

monochlorobenzene (MCB). It is a solvent

Bromothymol blue is a dye and it can cause

and a chemical intermediate.

skin and eye irritation. It is also associated

inhalation exposure to animals produced

with ingestion problems and May cause

narcosis, restlessness, muscle spasms and

gastrointestinal

tremors. Long-term exposure to humans

irritation

with

nausea,

Fenton-like

oxidation

of

Its acute

6555 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

Review Article

affects the central nervous system. Signs of

modified yeast cells was three times more

neurotoxicity in humans include cyanosis,

than that of unmodified yeast cells [84].

numbness,

Banana peel ash extract was also utilized to

muscle

spasms

and

hyperesthesia.Highest (69%) removal of

produce

MCB was observed with green tea based iron

aqueous extract of Colocasia esculenta leaves

nanoparticles.

was

Green

tea

based

iron

iron

used

oxide

to

nanoparticles,

reduce

graphene

and

oxide.

nanoparticles were also able to oxidatively

Nanohybrids of iron oxide/reduced graphene

degrade 81% of MCB along with a 31%

oxide were synthesized and they were able to

reduction in chemical oxygen demand [81].

remove 10 ppm of tetrabromobisphenol A in

Huang et al also used Oolong tea extract for

30 minutes, lead and cadmium in 10 minutes

synthesizing iron nanoparticles to efficiently

at optimum experimental conditions [85].

degrade Malachite green dye (75.5% in 60

Plantain

minutes) which is otherwise difficult to

Venkateswarlu

degrade [82].

magnetite nanoparticles as a low-cost bio-

Eucalyptus globules leaf extract was used as

reducing

a bio-reducing agent to synthesize nZVI.

nanaoparticle is mesoporous, possess ample

Plant extract contain polyphenolic compound

surface area (11.31 m2/g) and have high

named oenothein B which is responsible for

saturation magnetization. Due to these

synthesis

and

stabilization

nanaoparticle. These

peel

extract

was

used

by

et al. for synthesis of

agent.

The

structure

of

of

iron

properties these nanoparticles can be used in

nanoparticles

were

the field of environmental remediation for

found to be stable even after two months and

the removal of toxic metals and dyes [86].

a very small quantity was sufficient to

CONCLUSION

remove a huge amount of (98.1%) hexavalent

PROSPECTS

chromium just within 30 minutes [83].

With

Iron nanoparticles were synthesized using

urbanization and industrialization, huge list

pomegranate leaf extract and were coated on

of

the two strains of heat-killed yeast cells

environment so, past efforts and treatment

Yarrowia lipolytica. This bionanocomposite

methods are not sufficient to sequester them.

was used to degrade hexavalent chromium.

So, there is a need of technologies that can

The

make pollution free environment. With

sorption

capacity

of

magnetically

rapid

pollutants

AND

increase

is

FUTURE

in

population,

contaminating

the

emerging technology like phytoremediation, 6556 IJBPAS, December, 2015, 4(12)

Saima Shakil Malik et al

Review Article

nanotechnology offers great deals to treat [1] Krantzberg G, Tanik A, do Carmo J S A, contaminants.

Nanoengineered

materials

Indarto A and Ekda A, Advances in water

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Nanomaterials and nanoparticles: Sources

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