Biosensors for environment application by danish amin111

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DEPARTMENT OF ELECTRONICS ENGINEERING
SCHOOL OF ENGINEERING AND TECHNOLOGY
PONDICHERRY UNIVERSITY
KALAPET, PUDUCHERRY -- 605014
BIOSENSORS FOR ENVIRONMENTAL
APPLICATIONS
NAME: DANISH AMIN
REG NO: 19304004
SUBJECT: BIOSENSORS
CLASS: 2ND
YEAR (M TECH)
Course: M TECH (ECE)

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INTRODUCTION
In recent years, a growing number of initiatives and legislative actions for
environmental pollution control, with particular emphasis on water quality control,
have been adopted in parallel with increasing scientific and social concern in this
area. The need for disposable systems or tools for environmental monitoring has
encouraged the development of new technologies and more suitable
methodologies, the ability to monitor the increasing number of analyses of
environmental relevance as quickly and as cheaply as possible, and even the
possibility of allowing on-site field monitoring. In this respect, biosensors have
demonstrated a great potential in recent years and thus arise as proposed analytical
tools for effective monitoring in these programs. A biosensor is defined by IUPAC
as a self-contained integrated device that is capable of providing specific
quantitative or semi-quantitative analytical information using a biological
recognition element (biochemical receptor), which is retained in direct spatial
contact with a transduction element.
A biosensor should be clearly distinguished from a bio analytical system, which
requires additional processing steps, such as reagent addition. A device that is both
disposable after one measurement, i.e., is single use, and unable to monitor the
analytic concentration continuously or after rapid and reproducible regeneration
should be designated a single-use biosensor. The main advantages offered by
biosensors over conventional analytical techniques are the possibility of
portability, of miniaturization and working on-site, and the ability to measure
pollutants in complex matrices with minimal sample preparation. Although many
of the systems developed cannot compete with conventional analytical methods in
terms of accuracy and reproducibility, they can be used by regulatory authorities
and by industry to provide enough information for routine testing and screening of
samples. For the time being, the monitoring of water quality has generally relied on
the collection of spot water samples followed by extraction and laboratory-based
instrumental analysis. However, this provides only a snapshot of the situation at
the sampling time and fails to provide more realistic information due to
spatiotemporal variations in water characteristics. Biosensors can be useful, for
example, for the continuous monitoring of a contaminated area. They may also
present advantageous analytical features, such as high specificity and sensitivity
(inherent in the particular biological recognition bioassay). At the same time,
biosensors offer the possibility of determining not only specific chemicals but also
their biological effects, such as toxicity, cytotoxicity, genotoxicity or endocrine
disrupting effects, i.e., relevant information that in some occasions is more
meaningful than the chemical composition itself. They can provide, finally, total
and bio available/bio accessible pollutant concentrations. Despite these advantages,

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the application of biosensors in the environmental field is still limited in
comparison to medical or pharmaceutical applications, where most research and
development has converged. Nevertheless, the majority of the systems developed
are prototypes that still need to be validated before being used extensively or
before their commercialization. Biosensors can be used as environmental quality
monitoring tools in the assessment of biological/ecological quality or for the
chemical monitoring of both inorganic and organic priority pollutants. In this
review article we provide an overview of biosensor systems for environmental
applications, and in the following sections we describe the various biosensors that
have been developed for environmental monitoring, considering the pollutants and
analysis that are usually mentioned in the literature.
IMPORTANCE
As a result of human and technological development, a wide range of man-made
chemicals and by-products formed in industrial or combustion processes have
been, and still are, released in the environment. Some of these substances, such as
pesticides, heavy metals or PCBs, are well recognized contaminants known to
affect the quality of the environment. As a consequence, a variety of biosensors
have already been developed and applied to their environmental determination. For
organ phosphorous and carbamate pesticides, for example, various enzymatic
biosensors based on the activity of the choline oxidase and on the inhibition of
acetyl cholinesterase and butyrylcholinesterase (BChE) have been developed. For
environmental pollution risk assessment, the integration of both chemical and
effect-related analyses (toxicity, endocrine disruption activity, etc.) is essential.
Many efforts have been made during the last years to develop different bioassays
and biosensors for toxicity evaluation of water samples In the case of endocrine
disrupting compounds (EDCs), there is a need to develop integrated analytical
chemistry/toxicity identification evaluation procedures. At present, apart from
biosensors for chemical analysis of some specific EDCs there are other sensors,
based on estrogen receptors (ER), conceived for evaluation of their biological
effects. The natural sensing element most commonly used is the human estrogen
receptor. The binding ability of the chemicals toward the ER is measured in these
biosensors as an indicator of their estrogenic activity. Examples of ER-based
biosensor are the surface Plasmon resonance (SPR) biosensors developed by
Usamietal, Hock et al. and Seifert et al.. Even though the number of chemicals
amenable to analysis by biosensors continuously increases, there is still a lack of
systems suitable for determination of emerging contaminants, such as bisphenol A,
phtalates and polybrominated compounds, many of which act as EDCs.
PRINCIPLE OF BIOSENSOR
Ecology tells us that each organism grows in specific set of conditions (niche) that
can be defined in terms of food, temperature, moisture, pH, etc. One can thus use

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each organism as a biosensor for a set of conditions. After we learn to read these
biosensors, pollution monitoring becomes a simple and quick job. We give below,
a few guiding principles that one can use while learning this technique:
1. Pollution is a result of waste of resources, or in other words, waste is a
misplaced resource.
2. Signs of pollution are visible and unpleasant, of varying degree, and only serve
as warning signals. It is necessary to read this message and not fight with these
signs of pollution (such as odor, pathogens, pests and several other unpleasant
natural phenomena).
3. Biosensors inform us of the band or degree of pollution. This is quite enough to
guide us towards an appropriate action.
4. Appropriate action not only stops the signs of pollution, but display signs of
prosperity. These are clean air, clean water stream, flourishing vegetation, singing
birds, etc. and absence of visible nuisance-causing organisms (pests).
A biosensor is an analytical device composed of a biological sensing element
(enzyme, receptor antibody or DNA) in intimate contact with a physical transducer
(optical, mass or electrochemical) which together relate the concentration of an
analyte to a measurable electrical signal. In theory, and verified to a certain extent
in the literature, any biological sensing element may be paired with any physical
transducer. The majority of reported biosensor research has been directed toward
development of devices for clinical markets; however, driven by a need for better
methods for environmental surveillance, research into this technology is also
expanding to encompass environmental applications.
TYPES OF BIOSENSOR
Biosensors can be grouped according to their biological element or their
transduction element. Biological elements include enzymes, antibodies, micro-
organisms, biological tissue, and organelles. Antibody-based biosensors are also
called immune sensors. When the binding of the sensing element and the analyte is
the detected event, the instrument is described as an affinity sensor. When the
interaction between the biological element and the analyte is accompanied or

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followed by a chemical change in which the concentration of one of the substrates
or products is measured the instrument is described as a metabolism sensor.
The method of transduction depends on the type of physicochemical change
resulting from the sensing event. Often, an important ancillary part of a biosensor
is a membrane that covers the biological sensing element and has the main
functions of selective permeation and diffusion control of analyte, protection
against mechanical stresses, and support for the biological element.
On the basis of the transducing element, biosensors can be categorised as :
Electrochemical :Amperometric and potentiometric transducers are the most
commonly used electrochemical transducers. In amperometric transducers, the
potential between the two electrodes is set and the current produced by the
oxidation or reduction of electro active species is measured and correlated to the
concentration of the analyte of interest. Most electrodes are S0044made of metals
like platinum, gold, sliver, and stainless steel, or carbon-based materials that are
inert at the potentials at which the electrochemical reaction takes place.
Optical: Fiber optic probes on the tip of which enzymes and dyes (often
fluorescent) have been co-immobilized are used. These probes consist of at least
two fibers. One is connected to a light source of a given wave length range that
produces the excitation wave. The other, connected to a photodiode, detects the
change in optical density at the appropriate wavelength.
Calorimetric: Calorimetric transducers measure the heat of a biochemical reaction
at the sensing element. These devices can be classified according to the way heat is
transferred. Isothermal calorimeters maintain the reaction cell at constant
temperature using Joule heating or Peltier cooling and the amount of energy
required is measured. Heat conduction calorimeters measure the temperature
difference between the reaction vessel and an isothermal heat sink surrounding it.
According to the biorecognition principle, biosensors are classified into:
Enzymes: Enzymes are proteins with high catalytic activity and selectivity towards
substrates (see the article Enzyme Kinetics). They have been used for decades to
assay the concentration of diverse analytes. Their commercial availability at high
purity levels makes them very attractive for mass production of enzyme sensors.
Their main limitations are that pH, ionic strength, chemical inhibitors, and
temperature affect their activity.
Antibodies: Antibodies are proteins that show outstanding selectivity. They are
produced by lymphocytes in response to antigenic structures, that is, substances
foreign to the organism. Molecules larger than about 10 kDa can stimulate an
immune response. Smaller molecules like vitamins or steroids can be antigenic
(also called haptens) but they do not cause an immune response unless they are

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conjugated to larger ones like bovine serum albumin. Many antibodies are
commercially available and commonly used in immunoassays.
Microbes: The use micro-organisms as biological elements in biosensors is based
on the measurement of their metabolism, in many cases accompanied by the
consumption of oxygen or carbon dioxide, and is, in most cases, measured
electrochemically .
ENVIRONMENTAL APPLICATIONS
In the following section, we describe biosensors developed for environmental
monitoring, considering first, biosensors that measure an effect such as toxicity and
endocrine effect biosensors and second, biosensors that detect a compound or a
group of compounds based on the specific recognition of a biomolecule. A wide
range of compounds of environmental concern or under suspicion are being
considered for biosensor development. Table 1 lists examples of these reported
biosensors for different environmental applications.

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Toxicity
In environmental pollution monitoring, it is becoming a general opinion that
chemical analysis by itself does not provide sufficient information to assess the
ecological risk of polluted waters and wastewaters. In the European Union, along
with more stringent demands for water treatment (Council Directive 91/271/EEC),
industrial and urban wastewater effluents shall reach certain limits of non toxicity
before the effluent can be discharged into the environment. Thus, much effort has
been made during the last years to develop and use different bioassays and
biosensors for toxicity evaluation of water samples .Whole organisms are used to
measure the potential biological impact (toxicity) of a water or soil sample. That is
the case of the toxicity assays Microtox® (Azure, Bucks, UK), or ToxAlert®
(Merck, Darmstadt, Germany). These systems are based on the use of luminescent
bacteria, Vibrio fischeri, to measure toxicity from environmental samples.
Bacterial bioluminescence has proved to be a convenient measure of cellular
metabolism and, consequently, a reliable sensor for measuring the presence of
toxic chemicals in aquatic samples. Some bioassay methods are integrated now in
biosensors such as the Cellsense®, which is an amperometric sensor that
incorporates Escherichia coli bacterial cells for rapid ecotoxicity analysis. It uses
ferricyanine, a soluble electron mediator, to divert electrons from the respiratory
system of the immobilized bacteria of a suitable carbon electrode. The resulting
current is, thus, a measure of bacterial respiratory activity, and the perturbation by
pollutants can be detected as a change in the magnitude of the current. Cellsense
has been applied to investigate the toxicity of 3, 5-dichlorophenol and other
phenols in wastewater, for the determination of nonionic surfactants and benzene
sulfonate compounds, for the analysis of wastewater treatment works (WWTW)
influent and effluent, and for the toxicity testing of wastewaters and sewage sludge
. Moreover, Cellsense has been proposed as one of the newer rapid toxicity
assessment methods within the direct toxicity assessment (DTA) demonstration
program of the UK Environmental Agency.
Most environmental biosensors have focused on bacterial systems while eukariotic
biosensors are rare; even more rare is the use of mammalian cells. The mammalian
cell, which is more complex than bacteria, can give a more sensitive response
when compared to bacteria while also responding to the estrogenic effects of
chemicals. A recombinant fluorescent Chinese Hamster Ovary cell line, utilizing a
fluorescent reporter system, was used to monitor various toxicants, especially
endocrine-disrupting compounds (EDCs), in diverse aqueous environments. EDCs
have been also analyzed by Guet al.with a multichannel two-stage mini-bioreactor
system using a genetically engineered bioluminescent bacteria. The toxicity of
various samples spiked with known endocrine-disrupting chemicals, and phenol
was investigated.

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Endocrine effect biosensors
Nowadays, there is an increasing concern regarding many environmental
contaminants that produce adverse effects by interfering with endogenous hormone
systems, the so-called EDCs. EDCs constitute a class of substances not defined by
chemical nature, but by biological effect and thus, taking advantage of this feature,
“endocrine effect biosensors” have been developed. Steroid hormones induce
different effects in mammalian cells after binding to specific intercellular
receptors, which are ligand-dependent transcription factors. Many endocrine
disruptors are also believed to bind to the estrogen receptor (ER) as agonists or
antagonists. Thus, the binding ability of the chemicals toward the ER would be a
crucial factor for screening or testing their potential environmental toxicity. Based
on estrogen receptors, several biosensors have been developed which provide
significant and useful information about estrogenic potency of the sample. The
advantage of receptor assays is that they are quite simple to perform and allow the
identification of all endocrine disruptors that act through the corresponding
receptor. These biosensors constitute a similar approach as that described above for
toxicity biosensors, where effects as a general parameter and not a specific
substance are monitored. By employing the commonly utilized human estrogen
receptor, the SPR biosensor BIAcore has been applied in the determination of
estrogens and xenoestrogens and in binding studies of target compounds. In
addition to optical biosensors, electrochemical and piezoelectric biosensors have
been developed also based on estrogen receptors.
Biocides
The extensive use of pesticides for agricultural purposes is the cause of their
widespread presence in natural waters. Concerns about their toxicity and
persistence in the environment has led the European Community to set limits on
the concentration of pesticides in different environmental waters: The directive
98/83/EC on the quality of water for human consumption has set a limit of 0.1 μg/l
for individual pesticides and of 0.5 μg/l for total pesticides. Although conventional
techniques such HPLC/MS and GC/MS gives satisfactory analytical results for
pesticide determination, new assays and sensors for cheaper and faster on-site
analysis are being developed. Enzymatic sensors, based on the inhibition of a
selected enzyme, are the most extended biosensors used for the determination of
these compounds. Based on the inhibition of acetyl cholinesterase (AChE) and
colin oxidase, various biosensors have been developed for the detection of
organophosphorous and carbamate pesticides such as those described by Choi et
al., Vangelis et al., and Andres et al. Although sensitive, biosensors based on AchE
inhibition are not selective (since the AchE is inhibited by neurotoxins, which

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include organophosphorous pesticides (OPs), carbamate pesticides, and many
other compounds) and cannot, therefore, be used for quantitation of either an
individual or a class of pesticides. One approach to solve the lack of specificity of
AchE involves the genetic engineering of cholinesterase enzyme to obtain new
specific enzymes for desired analytes or families. Different expression systems for

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the production of recombinant AChEs for biosensor applications were reviewed by
Schulze et al. The organophosphorous hydrolase (OPH), on the other hand, is able
to hydrolyze a number of OP pesticides such as paraoxon and parathion, and
chemical warfare agents such as sarin and soman. Hydrolysis of these OP
pesticides generates p-nitrophenol, which is an electroactive and chromophoric
product. Thus, OPH could be combined with an optical transducer to measure the
absorbance of p-nitrophenol or with an amperometric transducer to monitor the
oxidation or reduction current of this product. With a different approach, the
capability of various pesticides such as cyanide, diethyldithiocarbamates , and
hydrazines to inhibit the enzyme tyrosinase was also reported. Similarly, diazinon
and dichlorvos were detected at limits around 5 μM and 75 μM, respectively, using
a tyrosinase-based oxygen sensor.
Dithiocarbamate fungicides have been measured by their ability to inhibit the
enzyme aldehyde dehydrogenase (AlDH). Particularly, the detectability of the
pesticide Maneb could be improved to a level of 1.5 μg/l, by using a bienzymatic
system based on the combination of AlDH and diaphorase. Photosynthesis
inhibition is an interesting indicator that rapidly reflects the toxic effect of certain
pollutants. Taking advantage of this feature, some biosensors based on
Photosystem II (PSII) have been reported to be able to detect herbicides in the
environment. About 30 % of herbicides, including phenylurea, triazine, and
phenolic herbicides, inhibit photosynthetic electron flow by blocking the PSII
quinone-binding site and thus modify chlorophyll fluorescence. An amperometric
biosensor de-veloped by Koblizek et al. exhibited, for example, selective
sensitivity to phenylurea and triazine herbicides, whereas phenolic herbicides were
not registered. Heavy metals were also able to inhibit the activity of the PSII
biosensor, but their effect is usually found at much higher concentrations than
those typical for herbicides. Another PSII-based biosensor allowed the detection of
herbicides such as atrazine, simazine, isoproturon, and diuron at sub-μg/l
concentration levels.
In a different approach, biosensors based on immunological assays have been
developed. Wilmer et al., determined 2,4-dichlorophenoxyacetic (2,4-D) acid in
water by an amperometric immunosensor. In this immunosensor, the enzyme
alkaline phosphatase (AP) catalyzes the conversion of PAPP to PAP allowing a
limit of detection of 0.1 μg/l. Based on the evanescent wave (EW) transducing
principle, atrazine was detected at concentrations around 0.1 μg/l and cyclodiene
insecticides in the μg/l range. Mallat et al.applied the “River Analyzer” (RIANA)
immunosensor in the determination of pesticides such as atrazine, simazine,
isoproturon, 2,4-D, alachlor, and paraquat in natural waters. Studies focused on the
evaluation of matrix effects, interferences due to the presence of cross-reactant
substances and on the validation of the sensor. The system was used for monitoring

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of atrazine, simazine, and alachlor in different Spanish and Portuguese regions.
Based also on SPR principle, another immunosensor was used to measure triazine
pesticides achieving a detection limit for simazine of 0.2 μg/l. Analyses carried out
on surface and groundwater samples showed a good correlation with parallel
chromatographic results. An immunosensor for the determination of Irgarol 1051
was applied to the direct analysis of natural waters and water extracts. It allowed
the analysis of samples with an organic solvent content of up to 50 or 25 % of
methanol and acetonitrile, respectively. In spite of the lack of specificity and the
interferences observed in liquid media, some applications have also been reported
on the use of piezoelectric immunosensors for the determination of pesticides such
as atrazine and parathion. Recently, a label-free direct piezoelectric immunosensor
built on a flow-through cell was used for the determination of 2,4-D in water with
a limit of detection around 0.2 μg/l.
Hormones
Endogenous hormones of human or animal origin have been reaching the
environment for thousands of years, even though to an increasing extent they are
due to growing population and more intensive farming. Besides endogenous
hormones, exogenous sex steroids used as growth promoters in several countries
have become a matter of concern not only because of the residues potentially found
in meat, but also because environmental soil and water samples may be
contaminated as result of the animal excreta. These residues may have endocrine-
disrupting activity in aquatic fauna or even terrestrial.
Although very low concentrations (ng/l range) of hormones such as estradiol,
estrone, and ethynilestradiol have been found in water, their widespread use and
their capability to induce responses in fish at concentrations as low as ng/l or even
pg/l level, have alerted scientists to the potential dangerous consequences of their
presence in the aquatic environment. As an example, estrone, along with other
organic pollutants (atrazine and isoproturon), was determined by Rodriguez-Mozaz
et al. , with an optical immunosensor in real water samples. The European Union
(EU) is funding the development of new biosensing strategies for the control of
hormone residues in an effort to improve food quality controls and to protect
public health against the adverse effect of these substances.
As a model of example, in the framework of the EU project “Development of
single and multianalyte affinity sensors for rapid detection of androgen residues in
live an post-mortem animals” (RADAR) (<http://intel.ucc.ie/>), a group of
researchers are developing single and multi-analyte affinity sensors and receptor-
based sensors for the rapid detection of androgens such as testosterone and
metabolites.

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PCBs
Polychlorinated biphenyls (PCBs) are ubiquitous environmental pollutants widely
used as industrial chemicals, particularly as dielectric fluids in electrical
transformers and capacitors. The high toxicity of some PCB congeners represents a
risk for public health as these compounds are still present in the environment, even
though the production of PCBs has been banned in several countries many years
ago.Different biosensor configurations have been designed to determine PCBs in
the environment, and these include the DNA biosensor with chronopotentiometric
detection, and various immunosensors with fluorescence,SPR, and electrochemical
detection principles.
Dioxins
Apart from PCBs, other polychlorinated compounds of environmental concern are
the dioxins, which are released as by-products in a number of chemical processes
involving chlorine. Thus, processes such as the production of some pesticides, the
manufacture of PVC plastics, the chlorine bleaching of pulp and paper and waste
incineration generate dioxins. They are considered carcinogenic and are a potential
threat to human health, and more recently, they have been included in lists of
potential EDCs. Conventional dioxins analysis requires laborious multistep clean-
up procedures that increase the cost of each analysis. A significant number of
immunoassays for dioxins have been developed in an effort to provide simplified
and routine analysis. The SPR biosensor developed by Shimomura et al. for the
determination of PCB (mentioned above) was also employed in the determination
of the dioxin 2,3,7,8-TCDD. Similarly, another biosensor for detection of dioxin-
like chemicals (polyhalogenated dioxins, furans, and biphenyls) based on a
recombinant mouse hepatoma cell line was characterized and optimized by Pasini
et al.
Phenols
Phenolic compounds that appear in the environment originate from the paper and
pulp industry and from the production of drugs, dyes, and antioxidants. Phenolic
compounds, and especially chlorophenols, are important environmental pollutants
because of their high toxicity and possible accumulation in the environment. They
are also considered as precursors of the dioxins. Parellada et al. developed an
amperometric biosensor, with tyrosinase (a polyphenol oxidase with a relatively
wide selectivity for phenolic compounds) immobilized in a higrogel on a graphite
electrode, which correlated satisfactorily with the official method for the
determination of the phenol index in environmental samples.Chlorophenols have
been also detected with a flow-injection chemiluminescence fiber optic biosensor,
exploiting the ability of certain substituted phenols to enhance the
chemiluminescence reaction of luminol, catalyzed by horseradish peroxidases.

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Finally, a Lux-based biosensor was used to assess the toxicity of a paper mill
sludge being some metals (Cd and Cu) and pentachloro-phenol (PCP).
Surfactants
Detergent products use surfactants as the basic “active” component. The anionic
surfactants are the most widely used, while the cationic surfactants represent only 5
% of the total. An amperometric biosensor for detection of anionic surfactants was
constructed with Pseudomonas rathonis T (bearing a plasmid for surfactant
degradation) as a biological element. Oxygen consumption acted as an indicator of
cell metabolism and thus of the surfactant content of the sample. The limit of
detection achieved for sodium dodecyl sulfate (SDS) was within 0.25–0.75 mg/l.
Taranova et al. also studied the sensitivity and selectivity of biosensors based on
bacterial strain Pseudomonas and Achromobacter and their ability to degrade the
anionic surfactants. The degradation of surfactants by the bacteria caused a
decrease in dissolved oxygen and a change in the oxygen electrode current. The
microbial biosensor en-abled detection of surfactants with high selectivity,
sensitivity, and reproducibility. The lower limit reached for SDS was near 0.25
μg/l.
Since the 1960s, a new formula with more biodegradable surfactants such as
alkylbenzene sulphonates (ASs) was introduced. Linear alkylbenzene sulfonates
(LASs) are abundantly used in the formulation of household detergents. Despite
the efficient removal of LASs in wastewater treatment plants, residues of LASs are
still present in surface waters at the low μg/l range. Even though LASs are not
severely toxic, they contribute to the permeation of other pollutants into aquatic
animals. A combination of two whole-cell biosensors was applied to river water
samples for the determination of anionic surfactants. The first biosensor was based
on the detection of the dissolved oxygen consumed in the degradation of LASs by
immobilized LAS-degrading bacteria. On the contrary, the other sensor, which
used T. cutaneum yeast, did not respond to LASs. Values for LAS concentrations
derivedfrom the combined use of both biosensors correlated well with values
determined using conventional methods.
Alkylphenol ethoxylates (APEs) belong to the group of nonionic surfactants,
whose detection have gained more importance due to their endocrine-disrupting
properties. APEs are used on a variety of industrial applications, such as
manufacturing of pulp and paper, metals, textiles, paints, resins, adhesives, latex,
rubber, and plastics. The APEs have been shown to be estrogenic both in vivo and
in vitro. In wastewater treatment processes and in the environment, APEs degrade
to alkylphenols (APs),which tend to be more toxic and show greater estrogenic
activity. Rose et al.described the development of a capillary-based immunoassay
(CIA) for APEs and APs, utilizing glucose dehydrogenase (DH) as label.

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Alkanes, aromatic compounds, and polycyclic aromatic hydrocarbons (PAHs)
Contamination of soils and surface and groundwater supplies with petroleum
products is a serious environmental problem. Of particular concern for drinking
water quality are water-soluble aromatic components (e.g., benzene, toluene,
ethylbenzene, and xylenes) of petroleum products. Although many of these
contaminants are readily biodegradable, they often persist in the environment. A
green fluorescent protein-based Pseudomonas fluorescens strain biosensor was
constructed and characterized for its potential to measure benzene, toluene,
ethylbenzene, and related compounds in aqueous solutions. The biosensor is based
on a plasmid carrying the toluene-benzene transcriptional activator . Another
microbial whole-cell biosensor, using E. coli with the promoter luciferase luxAB
gene, was developed for the determination of water-dissolved linear alkanes by
luminescence. The biosensor was used to detect the bioavailable concentration of
alkanes in heating oil-contaminated groundwater samples.PAHs are carcinogenic
compounds generally formed during incomplete combustion or pyrolysis of
organic matter containing carbon and hydrogen. They are very abundant,
ubiquitous, and recognized carcinogenic compounds. Amperometric biosensors for
naphthalene found in contaminated soils, were constructed using Sphingomonas
yanoikuyae B1. For benzo(a)pyrene (BaP) and related adducts, a fiber optic
fluoroimmunosensor has also been developed in which high sensitivity is achieved
by laser excitation and optical detection . The laser radiation reaches the sensor
probe and excites the BaP bound to the fiber optic probe.
Antibiotics
Medical substances have been released into the environment with very little
attention until recently. The presence of antibiotics in the environment is worrying
since they promote antibiotic resistance. The increasing use of antibiotics for
therapeutic purposes or as growth promoters in dairy cattle and as feed additives in
fish farms or in livestock during the last five decades has caused a genetic selection
of more harmful bacteria, which is a matter of great concern. The widespread
administration of antibiotics raises significant food safety issues since antibiotic
resistance can be transferred to humans on inges-tion of affected meat and milk
products. Therefore, most of the biosensors developed are aimed at determining
them in biological or food samples. For example, a commercial biosensor
BIACORE 3000 was used to study the cross-reactivity between two sulfonamides
(a group of antibiotics): sulfamethazine and furosemide. Sulfonamides sometimes
cause allergic reactions, whereas their effect in the human inmunosystem is of high
interest for their therapeutical application. Sulfamethazine has been also
determined with an optical immunosensor by Akkoyun et al. in animal urine.
Hansen and Sorensen presented three different reporter gene systems from V.
fischeri, E. coli, and Aequorea victoria all combined with a tetracycline inducible

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promoter in the development of three corresponding whole-cell biosensors. They
respond to low levels of tetracyclines by producing galactosidase, light or green
fluorescent protein, respectively. In the field of food monitoring, different
biosensors were able to determine penicillin G or tetracyclines , both in milk. More
references of biosensors for antibiotic determination can be found in a review by
Patel.
Toxins
Toxins are a very heterogeneous group capable of affecting different biochemical
processes including membrane function, ion transport, transmitter release, and
DNA and protein synthesis. In many cases, specific details of the site and mode of
action of a toxin at the molecular level are not known. A number of attempts have
been made to detect toxins in environmental and clinical samples using receptor
sensors. The induction of reporter genes by a promoter, which responds to a wide
variety of toxic compounds, can be used to produce biosensors useful as first
indicators of the presence of pollutants in the environment. When the cells are
exposed to toxic substances, there can be either a reduction (negative signal) or an
activation (positive) in reporter-protein production. Toxin-sensitive cells that
express a reporter gene can be used, therefore, as a biosensor for the nonspecific
detection of toxics, but not for a specific toxin.
A great number of specific sensors for bacterial toxins and mycotoxins have been
developed for food and environmental control. Thus, an integrated optical sensor
has been reported for the analysis of aflatoxin B in corn. A light-addressable
potentiometric immunosensor based on the commercial device (Threshold®) for
the analysis of saxitoxin and ricin has also been described. An impedance- based
immunosensor has been prepared by using an ultrathin platinum film with an
immobilized layer of antibodies against the staphylococcal enterotoxin B. Various
evanescent wave immunosensors have also been reported to be capable of
detecting botulin with very low limits of detection. A rapid and sensitive
immunosensor for the detection of the Clostridium botulinum toxin A has also
been developed. This fiber optic-based biosensor utilizes the evanescent wave of a
tapered optical fiber where antibodies antitoxin A have been covalently
immobilized at the distal end. The toxin could be detected by means of a
rhodamine label, within a minute at concentrations as low as 5 ng/ml. The reaction
was highly specific, and no response was observed against tetanus toxin. With a
similar configuration, it has been described for the detection of the cholera toxin. A
portable fiber optic biosensor for quantification of the staphylococcal enterotoxin
B in diverse media has also been described.
Microorganisms
Bacteria, viruses, and other microorganisms are found widely in polluted,
untreated, and treated waters, which implies a worldwide public health problem. In

17
the case of untreated water systems, fecal coliforms may enter rivers and streams
through agricultural runoff and nonpoint source pollution and via domestic
wastewater. Pathogenic compounds may reach humans by various routes, such as
the use of these waters for recreation or sports, for the irrigation of fruit and
vegetables and as drinking water.
Therefore, surface waters may play an important role in the transmission of
pathogens. Suitable monitoring of the water supply for the presence of pathogens
can assist in preventing disease from these sources. Current methods for detection
of pathogenic viruses, bacteria, protozoa, and helminthes tend to be inaccurate,
time-consuming, and expensive. As a result, indicator bacteria such as Salmonella,
“total fecal coliforms”, and “total fecal streptococci” are commonly used to
determine the risk of fecal contamination and the possible presence of pathogens in
water and wastewaters.
Other emerging pathogenic microorganisms, Campylobacter, Aeromonas, and
Yersinia genera and in recent years, also bacteriophages, have been proposed by
several groups as indicators for the microbial quality of water since they are more
suitable to signal viral contamination of water sources. On the other hand,
monitoring of microorganisms is not only of environmental concern; from a
military point of view, there are a number of pathogenic bacteria that can be
considered possible biological warfare agents.Conventional analytical methods for
microorganisms are based on colony-forming unit (CFU) count and require
selective culture, biochemical, and serological characterization. In most cases, they
require also some enrichment steps. These methods are sensitive and selective, but
time-consuming: days to weeks are needed to get a result. The increasing public
concern over environment safety has led to a search for technologies capable of
rapidly identifying contamination problems at source.
Biosensors capable of detecting an organism quickly will be important in the
environmental monitoring of pathogens in real time. The microbial content of a
sample can be determined by monitoring microbial metabolism. The transducer
can either detect consumption of oxygen or the appearance/disappearance of an
electrochemically active metabolite. However, proliferation of nucleic acid and
immuno-based detection technologies has provided sensitive and specific detection
systems for pathogenic bacteria and viruses. DNA detection may be more specific
than immunologically based detection, and the sensitivity can improve thanks to its
combination with polymerase chain reaction (PCR) methods.Gene probes are
already finding application in detection of disease-causing microorganisms in
water supplies, food, or in plants, animal or human tissues. Immunological
detection, on the other hand, is faster and more robust than DNA detection.
Moreover, it has the ability to detect not only contaminating organisms, but also
their biotoxins . Koubaka et al. reported detection of Salmonella enteriditis and

18
Listeria monocytogenes in real time using an SPR sensor based on antibodies
immobilized on the gold sensor surface. Salmonella and Listeria were detected by
the sensor at concentrations down to 106 cell/ml. Recently, a number of
piezoelectric biosensors formats have been developed for the detection of several
microbial contaminants. Salmonella typhimurium detection in liquid samples by an
immunosensor based on the acoustic wave principle was reported by Pathirana et
al. Limits of detection were around 100 cells/ml in less than 2 min. In another
example of piezoelectric biosensors, 23-mer biotinylated probes sequence, specific
to Aeromonas hydrophila, were immobilized onto the surface of a streptavidin-
coated gold surface of a quartz crystal. This sensor was capable of detecting a PCR
product amplified from a specific gene of A. hydrophila and of distinguishing
between samples that contained the gene and samples that did not. Ercole et al.
described a biosensor for the determination of E. coli in water samples by an
immunochemical potentiometric alternating biosensor. The monitored change in
the redox potential was due to the production of NH3 by a urease-E. coli antibody
conjugate linked with the E. coli cells present in the water. Hasebe et al. described
an amperometric tyrosinase-based biosensor for the detection of E. coli in
wastewater. The detection was based on tyrosinase-catalyzed oxidation of
polyphenolic compounds, which are produced microbiologically from salicylic
acid, and the subsequent signal amplification. The sensor was capable of detecting
103–104 cells/ml after an enrichment step.
The commercialization of current research in biosensor technology will provide
consumers with real-time biosensors capable of maintaining sensitivity better than
100 CFU/ml. Industries such as Caliper Technologies, Cepheid, Nanogen,
ACLARA BioSciences, MICROGEN Systems, and Lawrence Livermore
Laboratories are developing microfabricated systems for detection and
identification of specific microbial agents. Advances in antibody production and
the recent emergence of phage-displayed peptide biosensors offer increased
possibilities for the rapid detection of pathogens but still require time-consuming
preenrichment in order to detect low numbers of pathogens in water.
Metals
The determination of traces of heavy metals such as Cu, Cd, Hg, and Zn in the
environment is very important because of their high toxicity, their increasing
environmental levels (due to their use in industrial processes), and because metals
can bioaccumulate in living organisms, especially in marine organisms. Metals are
usually determined after digestion with strong acids. Common analytical
techniques used are ion chromatography, inductively coupled plasma, and
polarography. Heavy metals can also be determined with ion-selective electrodes.
However, these methods are not able to distinguish between available (potentially
hazardous) and nonavailable (potentially nonhazardous) fractions of metals to

19
biological systems . One advantage of the whole cell-sensors is their ability to react
only to the available fraction of metal ions.
Recent progress has been made in the development of biosensors relying on intact
bacterial cells to monitor toxic metals. Both nonspecific and specific biosensors
that utilize intact cells have been developed for this purpose. Nonspecific microbial
biosensors, which have been used for several years, measure only general toxicity,
such as the alreadymentioned Cellsense. On the other hand, heavy metals are well
known to inhibit the activity of enzymes, and application of this phenomenon to
the determination of these hazardous toxic elements offers several advantages such
as simplicity and sensitivity. Besides, in many cases, the inhibition effect is related
to its biological toxicity. Durrieu and Tran-Minh described a biosensor for the
determination ofheavy metals based on inhibition of the AP present on the external
membrane of Chlorella vulgaris microalgae. The microalgae cells were
immobilized on removable membranes placed in front of the tip of an optical fiber.
Krawczynski vel Krawczyk et al. studied the inhibition effect of mercury and other
heavy metal ions on urea hydrolysis catalyzed by urease immobilized in a
polyvinyl chloride (PVC) layer at the surface of a pH electrode in the form of
potentiometric biosensor. Urease is the most frequently applied enzyme for
inhibition determination of mercury, as it is relatively cheap and easily available.
Because the method was not specific, it was applied for the determination of the
total inhibition effect caused by heavy metal ions in water samples. The application
of another urease-based optical sensor for monitoring low levels of mercury has
also been reported by Yerian and Ruzicka.
Urease immobilized into Nafion film on the surface of an ion-sensitive field
transistor (ISFET) was also used for heavy metal measurement by Volotovsky et
al. In this approach, enzyme immobilization into a negatively charged polymer
seemed to cause an increase in the inhibition effect of metals due to cation
accumulation in the polymeric matrix. A combination of specific additives and
selective rewashing techniques to make the urease-based biosensor sensitive only
to mercury ions was proposed. For the determination of a specific metal,
recombinant bacterial sensors have been constructed and used. Specific biosensors,
based on inducible promoters fused to reporter genes (e.g., those that code for
bioluminescence proteins, such as luciferase), are more sensitive than both
chemical analysis methods and nonspecific toxicity biosensors. The light emitted
can be detected by photometers, illuminometers, and charge-coupled devices.
Recombinant luminescent bacterial sensors were used by Ivask et al. for the
determination of the bioavailable fraction of cadmium, zinc, mercury, and
chromium in soil. In this work, two bacterial recombinant heavy metal sensors
were constructed based on two different receptor-reporter systems: one was
inducible by Zn2+, Cd2+, and Hg2+, and the other by Cr(VI) and Cr(III). The

20
bacterial sensors used were not perfectly specific to one heavy metal, but
responded to some “nontarget” metals as well. In another example, the mer-lux
gene fusion in E. coli was used to estimate bioavailable mercury in soil. The
bioavailable fraction was defined here as being part of the water-leachable fraction.
The mer-promoter was activated when Hg(II), present in the cytoplasm of the
biosensor bacterium, binds to MerR, resulting in transcription of the lux genes and
subsequent light emission. The luminescence-based bacterial sensor strains
Pseudomonas fluorescens OS8 (pTPT11) and Pseudomonas fluorescens OS8 have
also been used for mercury and arsenite detection, respectively, in soil extracts.
Soil samples were extracted with water, ammonium acetate, hydrogen peroxide,
and nitric acid, and the results obtained were compared with those attained with
traditional methods. Other biosensors have been designed, based on bioengineered
proteins. In these cases, the biosensor monitors conformational changes caused by
the binding of the metal ion to the engineered protein. Bontidean et al.used
mercuric ion-binding regulatory proteins as the biological part of the biosensor,
MerR. The conformational change resulting from the binding of the metal ion to
the protein caused a change in the capacitance, which was proportional to the
concentration of the metal ions determined.
Inorganic phosphate
Inorganic phosphate found in surface waters is used as a measure of the degree of
eutrophism. Traditional methods for its determination are chromatography,
volumetric titration, or spectrophotometry. Therefore, the development of simple
and fast biosensors represents an interesting alternative to them. Various enzymatic
phosphate biosensors for phosphate determination have appeared in the literature
in recent years. Parellada et al. [2] described a configuration based on the
sequential action of three enzymes that opens up a way to the construction of
reagentless enzymatic phosphate sensors.
Nitrate
The increasing nitrate levels found in ground and surface waters are of concern
because they can harm the water environment. In line with this, urban wastewater
treatment regulations aim to reduce pollution, including nitrate pollution, from
sewage treatment works and industry. A biosensor containing immobilized
denitrifying bacteria was applied for the determination of NO3 – in tap water.
Through the reduction of NO3– in a reaction chamber, N2O was formed and
determined by a N2O microelectrode, which was the sensing element of the
biosensor. A microscale biosensor for nitrate/nitrite determination was used for in-
site monitoring in an activated sludge plant. The biosensor was based on the
diffusion of nitrate/nitrite through a tip membrane into a dense mass of bacteria
converting the ions into nitrous oxide with subsequent electrochemical detection.

21
Biochemical oxygen demand
Biochemical oxygen demand (BOD or BOD5) is defined as the oxygen required to
neutralize organic wastes over 5 days at 20 °C, and is a parameter widely used to
indicate the amount of biodegradable organic material in water. The conventional
BOD test has certain benefits such as being a universal method of measuring most
wastewater samples, and, furthermore, no expensive equipment is needed.It has,
however, the limitation of being time-consuming, and consequently it is not
suitable for online process monitoring. Thus, it is necessary to develop an
alternative method that could circumvent the weakness of the conventional BOD
test. Fast determination of BOD could be achieved by biosensor- based methods. A
common feature of these sensors is that they consist of a microbial film that can
biooxidize the organic substrate to be quantified, sandwiched between a porous
cellulose membrane and a gas-permeable membrane as the biological recognition
element. The response is usually a change in concentration of dissolved oxygen or
other phenomena such as light emission. Most BOD sensors rely on measuring the
bacterial respiration rate in close proximity to a transducer, commonly Clarktype
(an amperometric sensor for measuring dissolved oxygen developed by Clark in
1956).
Some BOD sensors have been developed and marketed by various manufactures in
both biofilm and bioreactor-type configurations. Most commercially available
BOD sensors are flow-type systems that can be more easily automated, but
generally require high maintenance to prevent fouling and clogging. Instrument
information about many BOD commercial biosensors was provided by Liu and
Mattiason . Despite the good agreement between biosensor results and
conventional BOD analysis, and despite the short response time of biosensors,
current BOD biosensor systems still present a series of limitations that restrict their
industrial applicatios: the lack of standardization and legislation in most countries,
complicated maintenance requirements, and insufficient resistance to various toxic
compounds such as heavy metal ions, CN– and phenol in the wastewater. It is
possible to eliminate the toxic effects of heavy metal ions by using a chelating
agent that complex the ions, e.g., ethylene diamine tetra-acetate (EDTA) and
sodium diethyl dithiocarbamate (DDTC). Prevention of contamination by other
microbes is also important for a reliable biofilm-type BOD sensor.
Many BOD biosensors have been developed for the determination of high BOD
values in industrial wastewater and not adapted to the measurement of low BOD
values. An optical fiber biosensor was developed for the evaluation of low BOD
values in river waters by Chee et al. The immobilized Pseudomonas putida
bacterium membrane was placed on the top of an optode, which was linked to a
photodiode that detected fluorescence signal. The response time was 15 min for
chloride up to 1000 mg/l.

22
CONCLUSION
Most biosensor systems have been tested only on distilled water or buffered
solutions, but more biosensors that can be applied to real samples have appeared in
recent years. In this context, biosensors for potential environmental applications
continue to show advances in areas such as genetic modification of enzymes and
microorganisms, improvement of recognition element immobilization and sensor
interfaces.
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