Food Safety Concerns of Pesticides, Veterinary Drug Residues and Mycotoxins in Meat and Meat Products
The aim of this review was to focus on food safety in relation to pesticide and veterinary drug residues and mycotoxins in meat and meat products. The impact of these consumers awareness is a large concern for the meat industry. In order to be more prepared, the consumer strive to have more complete information on the sources of inputs in their products, because consumers are becoming more worried about this. Residues in meat and their products are generally classified as naturally present, caused by man and arise secondarily. In the past, most contamination of meat resulted from natural toxicants. However, usage of synthetic chemicals for regular house-hold and agricultural practices while benefiting society has also provided new sources of potential contamination. The levels of pesticide residues are now over alarming situation in certain countries. Drug residues in meat are relatively uncommon whereas, aflatoxin or ochratoxin are rarely found. Residues from secondary residues also occur less frequently. This study reviews the causes of residues in meat, types of residues found, their detection methods, incidences and their regulation with emphasis on public health risk and their assessment.
Residues in the widest sense may be defined as undesirable substances present in meat. These substances are chemical or biological in nature and have always been present in a small amount or can be introduced into the environment by various technological practices, can arise as a result of incorrect storage of food stuff, can get in to the food chain due to modern agricultural practices and thus introduced into the foods or they may be results of medicines given to the animals or of processing methods.
Surveillance/monitoring on the occurrence of residues in meat and their products
were relatively a neglected area until last decade. But with the advancement
of technological intervention regarding livestock rearing, disease control and
intensive crop production system, the chances of residues in foods of animal
origin increased tremendously. This results a potential risk of various life
threatening diseases such as cancer, leukemia, reproductive disorder besides
disruption of bodys immune, endocrine and nervous system (Van
Wendel de Joode et al., 2001; Horrigan et
al., 2002). The growing awareness of public perception about this reduces
the confidence among the consumers and resultant adverse impact on global economy.
Ideally, meat food should be completely free from such types of contaminants.
This is a utopian goal considering current agricultural and technological practices.
Many develop countries in the world have already been tracking this problem
by fixing statutory limitations of pesticides, veterinary drug residues and
microbial toxins in meat and meat products and their enforcement through monitoring
to ensure safe food supply to consumers. Monitoring of such types residues in
foods of animal origin can reveal current status of contamination, thus enabling
preventive and control measures to be initiated before contamination becomes
so serious or wide spread that threatens human health or causes serious economic
Source of Exposure
Pesticides have unique status of all food residues because these compounds
are regularly used in agricultural fields to meet worldwide food demands. It
is estimated that, without pesticides, world production of food would be reduced
by 30%. Despite the obvious benefits, however, occasional misuse of such chemicals
has resulted in intoxication of animals and/or accumulation of residues in meat,
poultry and meat products. Among all pesticides, organochlorine (OC) compounds
such as DDT, lindane or hexachlorobenzene, heptachlor, heptachlor epoxide, aldrin/dieldrin
are mostly persistent in the environment and cause major health hazard effects.
Some of these compounds such as mercury, arsenic etc. also contain toxic elements
which, when break down in the soil, produce the actual residues. The industrial
chemicals (chlorinated hydrocarbons) such as PCB, the dioxin, or perchlorethylene
(PER) play the main parts, but organometal compounds such as tetraethyl lead
in fuel, benzopyrene and other substances are also important (Table
In contrast to pesticides, residues of veterinary medicinal products are most
common in foods of animal origin as are directly exposed to the animals (Table
2). But this could be avoided, if used properly with sufficient withdrawal
period of times. Drug residues in meat occur, when these are used via parental
or oral route or as feed additives in food animals. The range of veterinary
medicinal products used in regular animal husbandry practices is extremely wide,
ranging from teat dips to hormones. Approximately, 42% of all veterinary pharmaceuticals
used world-wide are used as feed additives, 19% are used as anti-infectives,
13% as parasiticides, 11% are used as biologicals and 15% represent other pharmaceuticals.
|| Maximum Residue Limits (MRLs) of pesticides (ppm) in meat
|-: Data not available, Source: MOHFW (2004)
||Codex Maximum Residues Limit (MRLs) and Acceptable Daily Intake
(ADI) levels of some important antimicrobial drugs in food of animal origin
|Data not available
All of them are administered to animals either by injections (intramuscularly,
intravenous, subcutaneous) or orally in the feed and water, topically on the
skin and by intra-mammary and intra-uterine infusions (Mitchell
et al., 1998). Injectables were responsible for 46% of the violative
residues in meat followed by oral administration at 20% (feed, water and bolus)
and intra-mammary infusions at 7%. Several other factors have contributed to
the residues problem such as poor treatment records or failure to identify the
animals and result from the use of a drug in same manner that is inconsistent
with the labeling. This occurs primarily through not observing label of withdrawal
times as well as extra-label use of drugs.
The microbial residues mostly mycotoxins, metabolites of toxigenic molds (fungi)
are present in feedstuffs. During the course of evolution organisms have accustomed
themselves to certain toxic contents in foods. However, the direct consumption
of mycotoxin-contaminated cereal grains is much more probable than exposure
to residues in foods of animal origin because livestock and poultry have the
ability to dilute or detoxify these chemicals (Michael and
Buck, 1987; Van Zytveld et al., 1970; Sims
et al., 1970).
Detection of Residues in Meat and Meat Products
A number of analytical techniques such as colorimetric method, Thin Layer
Chromatography (TLC), High Performance-Thin Layer Chromatography (HP-TLC), Gas
Liquid Chromatography (GLC), Gas Chromatography-Mass Spectrometry (GC-MS), High
Performance Liquid Chromatography (HPLC), Liquid Chromatography-Mass Spectrometry-Mass
Photometry (LC-MS-MS) etc., are established for detection and quantification
of pesticide residues in animal tissues (Argauer et al.,
1995; Bogialli et al., 2003; Pecorelli
et al., 2004). However, colorimetric and TLC method are limited only
for qualitative determination due to its low sensitivity. GLC or GC-MS though
normally used for determination of non-volatile compounds (organochlorine and
organophosphorus pesticides), but also effectively utilized for determination
of thermo-labile compounds such as synthetic pyrethroid and N-methyl carbamate
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 (Choi et al.,
2001; Andres and Narayanaswamy, 1997). Biosensors
based on enzyme inhibition although sensitive, are not selective and cannot,
therefore, be used for quantification of either an individual or a class of
pesticides. But introduction of recombinant enzyme for biosensor applications
can solve the problem. The organophosphorus hydrolase (OPH) 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 (Mulchandani et al., 2001). In
a different approach, biosensors based on immunological assays have been developed
with limit of detection of 0.1 μg L-1. Mallat
et al. (2001) 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. 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-1.
However, there are very limited applications of biosensor detection of pesticide
compounds in meat system.
For determination of veterinary drug residues in foods, currently, 6 types
of detection methods are commonly used. These include microbial growth inhibition
assays, microbial receptor assays, enzymatic colorimetric assays, receptor binding
assays, chromatographic methods and immunoassays. But microbial growth inhibition
assays and later 2 methods are popular for monitoring of antimicrobial residues
in meat and meat products as are capable of detecting a broad range of these
drugs (Mitchell et al., 1998; Biswas
et al., 2007). Korsrud et al. (1998)
evaluated a number of common bacterial inhibition test for screening antimicrobial
drug residues in tissues. They found that screening for tetracycline was excellent
with German three-plate test, the European Union four-plate test and new Dutch
kidney test instead of Swab Test On Premises (STOP), Calf Antibiotic and Sulfa
Test (CAST) and the Fast Antibiotic Screen Test (FAST).
Most of the biosensors developed are aimed at determining them in biological
or food samples. The Surface Plasmon Resonance (SPR) technique has been developed
and demonstrated for on-line/at-line detection of veterinary drug residues in
milk, porcine bile and bovine urine, including a commercial handling robot.
This sensor operates in real time and it may detect up to 8 different veterinary
drugs simultaneously with a throughput of up to 600 samples day-1.
The SPR techniques are having a major impact on the development of new optical
biosensors. Sulfamethazine has been determined by Akkoyun
et al. (2000) with an optical immunosensor in animal urine. Hansen
and Sorensen (2000) presented three different reporters gene systems from
V. fischeri, E. coli and Aequorea victoria all combined
with a tetracycline inducible 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
(Setford et al., 1999) or tetracyclines (Hansen
and Sorensen, 2000), both in milk.
Conventional and Modern Methods
The TLC and HP-TLC is regularly used for determination of micotoxins in
foods. However, a great number of specific sensors for bacterial toxins and
mycotoxins have been developed for food and environmental control (Delehanty
and Ligler, 2002). 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 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 (Kumar et al.,
1994). 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 has 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-1.
Residues and Health Risk
Among all residues, pesticides receiving most interest worldwide in recent
years. Though violative level of pesticides are relatively uncommon, a low violation
rate even remain an important public health consideration because of their wide
spread use in meat and poultry production, their persistence in environment
and varying toxicity. The United Nations has estimated that about 2 million
poisoning and 10, 000 deaths occur each year from pesticides, with about three-fourth
of this occurring in developing countries. The acute and malicious consumption
involving higher dose results in death whereas, chronic insidious intake lead
to elevated cancer risk and disruption of bodys reproductive, immune,
endocrine and nervous system (Horrigan et al., 2002).
The carcinogenicity of organochlorine (OC) pesticides has been studied in a number of laboratory animals including non-human primates. Lifetime or limited period of time treatment of mice with DDT induced liver tumors including malignant metastasizing hepatoblastomas. DDT also increased incidences lung tumors and lymphoma in mice, liver tumors in rats and adrenal adenomas in hamster. However, DDT did not induce DNA damage in bacteria or cultured rodent and human cells. It induced chromosomal aberration in mouse but not in rat bone marrow cells. DDT and its metabolites inhibited gap-junctional intracellular communication.
Other areas of concerns are childhood brain cancer and cancers of nervous system. Studies suggest an increase in risk in brain cancer, leukemia, Wilms tumors, Ewings sarcoma and germ cell tumors associated with paternal occupational exposure to pesticides prior to and during pregnancy. However, maternal occupational exposure during pregnancy was less frequent but was also associated leukemia, Wilms tumors and germ cell tumors. Pesticides can suppress immune system, as epidemiological evidence shows an association between pesticide exposure and increase incidence of human disease, particularly those disease to which immuno-compromised individuals are especially prone. The endocrine disrupter includes atrazine and alachlor. However, there is strong need of sufficient data for complete health hazard evaluation in this context.
In contrast to pesticides, exposure from veterinary drug residues rather most
common as are directly injected or fed to the animals. The overuse of antimicrobials
such as tetracyclines, sulfonamides, amino glycosides, β-lactam derivatives
etc. in animal production or their residues in food system pose potential allergic
reactions in sensitized individuals, but sub therapeutic and therapeutic levels
may perturb human gut micro flora (Paige et al.,
1997). The tetracyclines are incompletely absorbed from the gastrointestinal
tract; they reach readily high concentrations in the intestine, producing perturbations
of the intestinal microflora within 48 h of daily treatment. Experience with
tetracyclines in human medicine indicates that therapeutic levels of tetracyclines
can perturb the intestinal microflora by inducing emergence of resistant strains
and altering the metabolic activity of the microflora, its resistance to colonization
by pathogenic, opportunistic or resistant microorganism barrier effect and its
ecological balance, without any identified deleterious effect. Immunodepression
and phototoxicity may also occur in animals and human beings besides superinfections
related to tetracyclines. Treatment with oxytetracycline during the second month
of pregnancy presents a teratogenic risk to the foetus (Czeizel
et al., 1998; Czeizel and Rockenbauer, 2000).
As an undesirable side effect, OTC not only discolours the primary and permanent
teeth but also causes hypoplasia in developing teeth when administered to the
infants, mothers during last two trimesters of pregnancy and children under
12 years of age. However, unwanted risk is highest when OTC is given to neonates
and babies prior to the first dentition (Tanase et al.,
1998). Sulfonamides (sulfadimidine and sulfamethoxazole) can induce thyroid,
adenoma and hyperplasia in laboratory animals. It has also potential carcinogenic
character. To reduce bacteria resistance to sulfonamides to get synergistic
effect, pyrimethamines such as trimethoprim and oriprim are used in combination.
The National Research Council and Institute of Medicine have noted a link between
the use of antibiotics in food animals and the development of bacterial resistance
to these drugs causing human diseases. Similarly, scientist at Center for Disease
Control and Prevention (CDC) began tracking a new type of Salmonella
called Newport 9+ which is resistant to nine antibiotics including ceftriaxone,
one of the few drugs that kill most bacteria and the drug of choice for children
when Salmonella enter the blood stream. Nonetheless, toxicity of these
antimicrobial chemicals includes aplasia of bone marrow, the emergence of resistant
bacteria within animals and the transfer of antibiotic resistance gene to human
pathogens. The appearance of resistance among pathogenic organisms such as Salmonella
DT-104 and Campylobacter is of more concern (Glynn
et al., 1998). E. coli is an opportunist pathogen capable
of infecting people via the food chain and causing enteric infections in young
children and travelers as well as range of other infections. Enteric infections
with Salmonella, E. coli or Campylobacter rarely warrant
antibiotic treatment and so one might argue that the problem is not nearly as
important as Methicillin Resistant Staphylococcus aureus (MRSA) or other
major human resistance problems. However, treatment failure has been reported
(Smith et al., 1999; Fey
et al., 2000) and the livestock industries can not ignore the problem.
Enterococci have only been thought of as food borne organisms since discovery
of Vancomycin Resistant Enterococci (VRE) in pigs and poultry and there is some
dispute that their spread occurs from animals to people.
Similarly, uses of hormonal compound like DES in meat production known to have
strong carcinogenic effects and are banned from use for food producing animals
(Lee et al., 2001). On the other hand, beta-adrenergic
agonist (clenbuterol, salbuterol, cimeterol) act through binding to receptor
on target cells and act by repartitioning energy from fat to lean meat production.
This compound in excessive amount leaves residues in meat and thereby adverse
reaction in consumers requiring hospital treatment. Thus, health risks of veterinary
medicinal products and their metabolites are very difficult to define and their
presence of above the violative level is illegal and subject to financial penalties
in many countries (Paige et al., 1997).
The health implications from heavy metals lead to kidney damage, cardiovascular diseases, induction of hypertension, growth inhibition, interference in haeme synthesis, irreversible changes in brain and nerve cells and also some of these residues are known to be carcinogenic in nature. The pulmonary and nervous systems and skins are the main target organs of arsenic contamination. Cadmium associated with kidney damage and lead considered to has been associated with learning deficits in children. Copper and zinc are essential micronutrients but in higher amount may impact metallic taste to the product resulting unacceptability of the product.
Like other residues mycotoxin also mutagenic, carcinogenic, teratogenic or hepatotoxic to most experimental and domestic animals and man. Aflatoxin B1 the most important mycotoxin in view of occurrence and toxicity, is a potential hepatocarcinogen in various species of laboratory animals tested, among which are fish, birds, rodents and monkey.
In 1979, a US General Accounting Office (GAO) report identified 143 drugs
and pesticides as likely to leave residues in raw meat and poultry. Of these,
42 are known to cause or are suspected to causing cancer, 20 are suspected teratogens
and 6 are suspected mutagens (Shull and Chuke, 1983).
In the ensuing 24 years these numbers have probably risen.
The regulation of residues handled by each country throughout the world has a tendency towards uniform approach. But much greater enforcement has been seen with the passage of WTO and sanitary and phytosanitary measures. In the United States, pesticide use is regulated under FIFRA (US, Federal Insecticide, Fungicide and Rodenticide Act) on the basis of risk-benefit standard. This balancing takes into account the economic, social and environmental cost as well as potential benefits of the use of any pesticide in relation to its efficacy, inherent toxicity to mammals, wild-life and plants. A given pesticide may have many different uses, but required individual approval by the U.S. Environmental Protection Agency (EPA) under FIFRA. In fact, in the United States, pesticide regulation is under auspices of three government agencies, the Environmental Protection Agency (EPA), the Food and Drug Administration and the United States Department of Agriculture-Food Safety Inspection Services (USDA-FSIS). The FDA and USDA-FSIS are responsible for monitoring pesticide residues in foods based on level set by the EPA. The FSIS is responsible for meat and poultry products and FDA covers all other types of raw commodities and processed food products. However, regulation of pesticides in European Union is done on the basis of their toxicological properties. The council directive of the European Economic Community 91/414/EEC specified criteria for plant protection products in relation to Acceptable Daily Intake (ADI) for man, Acceptable Operator Exposure Level (AOEL), acute reference dose and maximum admissible concentration in water. The international organizations such as Codex Alimentarius Commission (CAC) have also set their standards using the term Maximum Residue Limits (MRLs) and Acceptable Daily Intake (ADI) levels of various pesticide residues in meat and meat products.
In contrast to pesticides, the USDA-FSIS and the FDA are responsible for monitoring
meat and poultry products for animal drug residues. The USDA-FSIS conducts the
National Residue Programme (NRP) to prevent animals containing violative amounts
of drug residues from market samples through extensive on-site sampling technique
(FSIS-USDA, 1998). The samples are also sent to FSIS field
laboratories for further testing. The FDA Center for Veterinary Medicine (CVM)
is responsible for approving new animal drugs, setting tolerances and enforcement
action depends on results of FSIS findings (FSIS-USAD, 1999).
Other international organizations include the European Agency for the evaluation
of medicinal products (EMEA), Office International des Epizootics (OIE) and
Consultation Mondiale de I' Industrie de la Sante Animale (COMISA). Many countries
have specialist groups involved such as FDA in USA, the Bureau of Veterinary
Drugs in Canada and the Veterinary Products Committee of Ministry of Agriculture,
Fisheries and Foods in the United Kingdom. The essential parameters required
for dietary exposure assessment at the national/international level are: (a)
food consumption data, (b) food chemical data, (c) methods for estimating dietary
exposure, (d) priority setting function of dietary exposure methods and (e)
extent of over estimation, uncertainty and variability.
Statutory Limits/Risk Assessment of Residues
International Organization such as Codex Alimentarius Commission have taken
initiation of harmonization of chemical residues in food through establishment
of statutory limitations viz., Maximum Residue Limits (MRLs), Acceptable Daily
Intake (ADI) levels, acute reference dose (ARfD), No Observed Adverse Effect
Levels (NOAEL) etc. However all these statutory limitations are important principles
for risk assessment of residues in foods including meat. For statutory limits
of residues, the terms tolerances or Maximum Residue Limits (MRLs) are frequently
used by regulatory agencies. But both the term tolerances and MRLs are synonymous;
former is used in United States other countries, while later is used in Canada
and the European Union. The term MRL may be defined as the maximum concentration
of marker residue (e.g., parent compound, metabolites etc.), expressed in parts
per million (ppm) or parts per billion (ppb) on fresh weight basis, that is
legally permitted or recognized as acceptable in or on food. The MRLs are established
on the basis of package of toxicology and residue data and these are referred
to as safety file and the residue file. The toxicology data are used not only
to characterize the biological properties of the molecules, but also to identify
a suitable No Observed Effect Levels (NOELs), which in turn is used to calculate
an Acceptable Daily Intake (ADI), the quantity, which if consumed over a human
lifetime will have no adverse effect on consumer health. This in turn expressed
on body weight basis and can be considered the safety standard for that compound.
The MRL is then elaborated from this ADI along with knowledge of the depletion
kinetics of the residues in the animal or its meat and with reference to standard
intake values for particular types of food. The identification of NOELs, the
calculation of ADI values and the establishment of MRLs is a complex scientific
process involving toxicology, pharmacology, microbiology, residue kinetics and
analytical chemistry but the MRL is established at a magnitude which ensures
that the ADI will not be exceeded by the consumer when eating food of animal
origin (Hartzell, 1996). Another Term Total Residue
Levels (TRL) refers to the safe concentration of total residues that corresponds
to the MRL.
The term Acceptable Operator Exposure Level (AOEL) and acute reference dose
(ARfD) also practiced most commonly by European Union. The AOEL is defined as
the maximum amount of active substance to which the operator may be exposed
without any adverse health effect and is based on the highest level at which
no adverse effect is observed in tests in the most sensitive relevance animal
species. The AOEL is expressed as mg of chemical/kg body weight of the operator.
On the other hand, the ARfD of a chemical is an estimate of the amount of substance
in food or drinking water, expressed on the body weight basis, that can be ingested
over a short period of time, usually during 1 meal or 1 day, without appreciable
health risk to the consumer, based on all the known fact at the time of evaluation.
This calculated reference dose is compared to an estimate or measurement of
exposure in the risk assessment process.
1: Akkoyun, A., V.F. Kohen and U. Bilitewski, 2000. Detection of sulphamethazine with an optical biosensor and anti-idiotypic antibodies. Sens. Actuators B, 70: 12-18.
2: Andres, R.T. and R. Narayanaswamy, 1997. Fibre-optic pesticide biosensor basedon covalently immobilized acetylcholinesterase and thymol blue. Talanta, 44: 1335-1352.
3: Argauer, R.J., K.I. Eller, M.A. Ibrahim and R.J. Brown, 1995. Determining propoxur and other carbamates in meat using HPLC fluorescence and gas chromatography/ion trop mans spectrometry after supercritical fluid extraction. J. Agric. Food Chem., 43: 2774-2778.
CrossRef | Direct Link |
4: Biswas, A.K., G.S. Rao, N. Kondaiah, A.S.R. Anjaneyulu and J.K. Malik, 2007. Simple multiresidue method for monitoring of trimethoprim and sulfonamide residues in buffalo meat by high-performance liquid chromatography. J. Agric. Food Chem., 55: 8845-8850.
CrossRef | PubMed | Direct Link |
5: Bogialli, S., R. Curini, A.D. Corciad, M. Nazzari and M.L. Polci, 2003. Rapid confirmation assay for determining 12 sulfonamide antimicrobials in milk and eggs by matrix solid-phase dispersion and liquid chromatography mass spectrometry. J. Agric. Food Chem., 51: 4225-4232.
CrossRef | Direct Link |
6: Choi, J.W., Y.K. Kim, I.H. Lee, J. Min and W.H. Lee, 2001. Optical organophosphorus biosensor consisting of acetylcholinesterase/viologen hetero Langmuir-Blodgett film. Biosensors Bioelectronics, 16: 937-943.
7: Czeizel, A.E. and M. Rockenbauer, 2000. A population-based case-control teratologic study of oral OTC treatment during pregnancy. Eur. J. Obstetrics Gynaecol. Reprod. Biol., 88: 27-33.
8: Czeizel, A.E., M. Rockenbauer and J. Olsen, 1998. Use of antibiotics during pregnancy. Eur. J. Obstetrics Gynaecol. Reprod. Biol., 81: 1-8.
9: Delehanty, J.B. and F.S. Ligler, 2002. A microarray immunoassays for simultaneous detection of proteins and bacteria. Anal. Chem., 74: 5681-5687.
CrossRef | Direct Link |
10: FSIS-USDA, 1998. National Residue Program Report. USDA, Washington DC
11: FSIS-USDA, 1999. The Impact of Pathogen Reduction/HACCP on Food Animal Production Systems. USDA, Washington DC
12: Fey, P.D., T.J. Safranek, M.E. Rupp, E.F. Dunne and E. Ribot et al., 2000. Ceftriaxone-resistant Salmonella infection acquired by a child from cattle. N. Engl. J. Med., 432: 1242-1249.
CrossRef | PubMed | Direct Link |
13: Glynn, M.K., C. Bopp, W. Dewitt, P. Dabney, M. Mokhtar and F.J. Angulo, 1998. Emergence of multidrug resistant Salmonella enterica serotype typhimurium DT104 infection in the United States. N. Engl. J. Med., 19: 1333-1338.
PubMed | Direct Link |
14: Hansen, L.H. and S.J. Sorensen, 2000. Detection and quantification of tetracyclines by whole cell biosensors. FEMS. Microbiol. Lett., 190: 273-278.
Direct Link |
15: Hartzell, G.E., 1996. Overview of combustion toxicology. Toxicology, 115: 7-23.
16: Horrigan, L., S.L. Robert and P. Walker, 2002. How sustainable agriculture can address the environmental and human health harms of industrial agriculture. Environ. Health Perspect., 110: 445-456.
CrossRef | PubMed | Direct Link |
17: Korsrud, G.O., J.O. Boison, J.F.M. Nouws and J.D. MacNeil, 1998. Bacterial inhibition tests used to screen for antimicrobial veterinary drug residues in slaughtered animals. J. AOAC Int., 81: 21-24.
Direct Link |
18: Kumar, P., J.T. Colston, J.P. Chambers, E.D. Rael and J.J. Valdes, 1994. Detection of botulinum toxin using an evanescent wave immunosensor. Biosens. Bioelectron., 9: 57-63.
PubMed | Direct Link |
19: Lee, M.H., H.J. Lee and P.D. Ryu, 2001. Public health risks: Chemical and antibiotic residues. Rev. Asi. Aust. J. Anim. Sci., 14: 402-413.
Direct Link |
20: MOHFW., 2004. Contaminants in foods: Prevention of food adulterationContaminants in foods: Prevention of food adulteration Act 1954, (Ammendment 2004). Ministry of Health and Family Welfare.
21: Mallat, E., C. Barzen, R. Abuknesha, G. Gauglitz and D. Barcelo, 2001. Fast determination of paraquat residues in water by an optical immunosensor and validation using capillary electrophoresis-ultraviolet detection. Anal. Chim. Acta, 427: 165-171.
22: Michael, L.B. and W.W.B. Buck, 1987. Chemical contaminants: Their metabolisms and their residues. J. Food Prot., 50: 1058-1073.
23: Mitchell, J.M., M.W. Griffiths, S.A. McEwen, W.B. McNab and A.E. Yee, 1998. Antimicrobial drug residues in milk and meat: Causes, concerns, prevalence, regulations, tests and test performance. J. Food Prot., 61: 742-756.
PubMed | Direct Link |
24: Mulchandani, A., W. Chen, P. Mulchandani, J. Wang and K.P. Rogers, 2001. Biosensors for direct determination of organophosphate pesticides. Biosens. Bioelectron., 16: 225-230.
PubMed | Direct Link |
25: Paige, J.C., L. Tollefson and M. Miller, 1997. Public health and drug residues in animal tissues. Vet. Hum. Toxicol., 30: 162-169.
PubMed | Direct Link |
26: Pecorelli, I., R. Bibi, I. Fioroni and R. Galarini, 2004. Validation of a confirmatory method for the determination of sulfonamides in muscle according to the European Union regulation 20002/657/EC. J. Chromatogr. A, 1032: 23-29.
PubMed | Direct Link |
27: Setford, S.J., E.R.M. Van, Y.J. Blankwater and S. Kroger, 1999. Receptor binding protein amperometric affinity sensor for rapid β-lactam quantification in milk. Anal. Chim. Acta, 398: 13-22.
28: Shull, L.R. and P.R. Chuke, 1983. Effect of synthetic and natural toxicants as livestock. J. Anim. Sci., 57: 330-354.
Direct Link |
29: Sims, W.M. Jr., D.C. Kelley and P.E. Sandford, 1970. A study of aflatoxicosis in laying hens. Poult. Sci., 49: 1082-1084.
PubMed | Direct Link |
30: Smith, K.E., J.M. Besser, C.W. Hedberg, F.T. Leano and J.B. Bender et al., 1999. Quinolone-resistant Campylobacter jejuni infections in Minnesota, 1992-1998. N. Engl. J. Med., 340: 1525-1532.
PubMed | Direct Link |
31: Tanase, S., H. Tsuchiya, J. Yao, S. Ohmoto, N. Takagi and S. Yoshida, 1998. Reverse-phase ion-pair chromatographic analysis of tetracycline antibiotics: Application to discoloured teeth. J. Chromatogr. B Biomed. Sci. Appl., 706: 279-285.
32: Van Wendel de Joode, B., C. Wesselling, H. Kromhout, P. Moge, M. Garcia and D. Mergler, 2001. Chronic nervous system effects of long-term occupational exposure to DDT. Lancet, 357: 1014-1016.
33: Van Zytveld, W.A., D.C. Kelley and S.M. Dennis, 1970. Aflatoxicosis: The presence of aflatoxins or their metabolites in livers and skeletal muscle of chickens. Poult. Sci., 49: 1350-1356.
PubMed | Direct Link |