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We present a comprehensive overview of recent developments in analytical chemistry for the most environmentally important groups of chemicals of emerging concern (CECs), including pharmaceuticals and personal-care products, pesticides, steroid hormones, perfluorinated compounds, alkylphenolethoxylates, bisphenol A and phthalates. Due to both the typically very low concentrations at which CECs occur and environmental samples being complex matrices demanding extensive extraction and clean-up procedures, very specific, sensitive analytical procedures are needed. In this context, we discuss state-of-the-art instrumentation for sample preconcentration, analyte separation and detection. We could observe several prominent trends: the common use of liquid chromatography (LC) to allow separation of CECs (instead of gas chromatography); the development and the application of multi-class methods; and, the increasing popularity of high-resolution, full-scan analysis, combined with a trend towards the use of sub-2-μm-particle sizes and high flow rates (ultra-high-performance LC). Overall, due to the recent advances in instrumentation, we could see significant progress in the analytical chemistry of CECs in environmental matrices.

An ultra-high performance liquid chromatography tandem mass spectrometry multi-residue method for the determination of 34 anabolic steroids (10 estrogens including stilbenes, 14 androgens and 10 gestagens) in meat of bovine origin is reported. The extraction and clean-up procedure involved homogenization with methanol, defatting with hexane, liquid/liquid extraction with diethylether and finally SPE clean-up with coupled Si and NH(2) cartridges. The analytes were separated on a 1.9 μm Hypersil Gold column (100×2.1 mm) and quantified on a triple quadrupole mass spectrometer (TSQ Vantage) operating simultaneously in both positive and negative atmospheric pressure chemical ionisation (APCI) modes. This analytical procedure was subsequently validated according to EU criteria (CD 2002/657/EC), resulting in decision limits and detection capabilities ranging between 0.04 and 0.88 μg kg(-1) and 0.12 and 1.9 μg kg(-1), respectively. The method obtained for all, natural and synthetic steroids, adequate precisions and intra-laboratory reproducibilities (relative standard deviation below 20%), and the linearity ranged between 0.991 and 0.999. The performance characteristics fulfill the recommended concentrations fixed by the Community Reference Laboratories. The developed analysis is sensitive, and robust and therefore useful for confirmation and quantification of anabolic steroids for research purposes and residue control programs.

Organic micropollutants such as pharmaceuticals, perfluorinated compounds (PFCs), and pesticides, are important environmental contaminants. To obtain more information regarding their presence in marine organisms, an increasing demand exists for reliable analytical methods for quantification of these micropollutants in biotic matrices. Therefore, we developed extraction procedures and new analytical methods for the quantification of 14 pesticides, 10 PFCs, and 11 pharmaceuticals in tissue of marine organisms, namely blue mussels (Mytilus edulis). This paper presents these optimized analytical procedures and their application to M. edulis, deployed at five stations in the Belgian coastal zone. The methods consisted of a pressurized liquid extraction and solid-phase extraction (SPE) followed by ultra high-performance liquid chromatography coupled to triple quadrupole mass spectrometry for pharmaceuticals and pesticides, and of a liquid extraction using acetonitrile and SPE, followed by liquid chromatography coupled to time-of-flight mass spectrometry for PFCs. The limits of quantification of the three newly optimized analytical procedures in M. edulis tissue varied between 0.1 and 10 ng g−1, and satisfactory linearities (≥0.98) and recoveries (90106%) were obtained. Application of these methods to M. edulis revealed the presence of five pharmaceuticals, two PFCs, and seven pesticides at levels up to 490, 5, and 60 ng g−1, respectively. The most prevalent micropollutants were salicylic acid, paracetamol, perfluorooctane sulfonate, chloridazon, and dichlorvos.

The biochemicals utilized in the Charm MRL -Lactam test (8 min test) were applied to faster flowing lateral components to create a new 3 min, one-step -lactam test called Charm MRL-3 (Charm Sciences Inc., Lawrence, MA). This new test was validated at T&V-ILVO according to Commission Decision 2002/657/EC. The following analytical parameters were checked: test specificity, detection capability, and test robustness (impact of deviation of the test protocol, and impact of the milk composition, batch differences of reagents). Further, the suitability of the Charm MRL-3 to screen heat-treated milk or milk from animal species other than the cow was also tested. Finally, the test was integrated in the monitoring of dairy samples to check the occurrence of false-negative or false-positive results, and the test was also included in a national ring trial and an international proficiency study. The results proved that the Charm MRL-3 is a fast, simple, and reliable cows' milk test that can be used at the farm level in order to prevent tanker milk contamination, or at the entrance of the dairy plant to screen tanker milk for the presence of -lactam antibiotics.

Adequate glazing (6-10%) of fish fillets prior to frozen storage protects the final product from dehydration, oxidation and quality loss. Excessive glazing (>12%) on the other hand may significantly affect the economic value and end user satisfaction of frozen fish fillets. This paper describes the optimization, validation and application of a gravimetric procedure for the quantification of the ice-glaze content of frozen fish fillets (accredited under ISO 17025). This procedure has been utilized to determine the glazing percentage of multiple batches (n=50) of 11 different fish species sampled from 2005 until 2009. Average glazing percentages were 8.7+/-2.0% for the pooled samples (n=712), and ranged between 6.6+/-2.2% (salmon/cod) and 10.6+/-1.6% (plaice). The lower threshold value of 6% glazing for sufficient protection was violated in only one batch, whereas none of the batches exceeded the 12% excessive glazing threshold. The annual market place value of one %-point glazing is estimated at 1 million Euro in a low to moderate fish consumption market like Belgium. The large variability of glazing, combined with this technology's possible implications with respect to end-product-quality and economic value urges for technology improvement, monitoring and more controlled application of the glazing process in the frozen fish industry.

The use of anabolic steroids as growth promoting agents in food production is prohibited under European Union legislation, but there is currently no internationally accepted method for detecting the abuse of the anabolic steroid nandrolone in the porcine. Therefore, an analytical biomarker approach based on gas chromatography-tandem mass spectrometry (GC-MS-MS) analysis of the major urinary free fraction nandrolone metabolite 19-noretiocholanolone was developed and validated. The lower and upper limits of quantification of the assay were 25 and 3,000 pg mL−1 respectively. The limit of detection was calculated as 13.2 pg mL−1, which is significantly lower than previously reported methods. When applied to a population of untreated animals, 19-noretiocholanolone distributions in boars and gilt were bimodal, with a small number of concentrations in each sex at around the 1,000 pg mL−1 region and the majority of concentrations closer to the lower end of the calibration range. Statistical analysis of the data was carried out in order to suggest screening and confirmatory threshold approaches for this steroid in the urine of boars and gilts. The adopting of particular screening thresholds would be at the discretion of the individual regulating authorities, but at a false non-compliance rate of 1 in 10,000 of the normal population, the suggested confirmatory thresholds (7,501.6 pg mL−1 for boars and 19,200.4 pg mL−1 in gilts) are able to detect the abuse of nandrolone for several weeks following administration of this steroid.

A liquid chromatographic tandem mass spectrometric method for the determination of sulfa drugs in beeswax was developed. When performing residue control on beeswax intended for the fabrication of wax foundations, residues of sulfonamides were found. A migration test was set up to study whether sulfonamide-containing beeswax could lead to the contamination of honey. The higher the concentration of sulfamethazine doped in the wax, the higher was the concentration of sulfamethazine found in the honey. The maximum transfer was 15.6, 56.9, and 29.5% of the initial amount spiked in the wax foundation. In a second experiment, the percentage of sulfamethazine migrating from medicated winter feed to beeswax in relation to the concentration in the syrup and the contact time was studied. The maximum transfer of sulfamethazine from medicated sucrose syrup to beeswax was 3.1%.

Boldenone (17-hydroxy-androsta-1,4-diene-3-one, Bol) and boldione (androst-1,4-diene-3,17-dione, ADD), are currently listed as exogenous anabolic steroids by the World Anti-Doping Agency. However, it has been reported that these analytes can be produced endogenously. Interestingly, only for Bol a comment is included in the list on its potential endogenous origin. In this study, the endogenous origin of ADD in human urine was investigated, and the potential influence of phytosterol consumption was evaluated. We carried out a 5-week in vivo trial with both men (n=6) and women (n=6) and measured alpha-boldenone, beta-boldenone, boldione, androstenedione, beta-testosterone and alpha-testosterone in their urine using gas chromatography coupled to multiple mass spectrometry (GC-MS-MS). The results demonstrate that endogenous ADD is sporadically produced at concentrations ranging from 0.751 ng mL(-1) to 1.73 ng mL(-1), whereas endogenous Bol could not be proven. We also tested the effect of the daily consumption of a commercially available phytosterol-enriched yogurt drink on the presence of these analytes in human urine. Results from this study could not indicate a relation of ADD-excretion with the consumption of phytosterols at the recommended dose. The correlations between ADD and other steroids were consistently stronger for volunteers consuming phytosterols (test) than for those refraining from phytosterol consumption (control). Excretion of AED, bT and aT did not appear to be dependent on the consumption of phytosterols. This preliminary in vivo trial indicates the endogenous origin of boldione or ADD in human urine, independent on the presence of any structural related analytes such as phytosterols.

A selective and sensitive method for the simultaneous determination of five avermectins (abamectin, ivermectin, doramectin, emamectin and eprinomectin) and one milbemycin (moxidectin) in porcine liver, bovine meat and fish tissue was developed. The method involved extraction with acetonitrile and purification by C18 solid-phase extraction. Detection was carried out using liquid chromatography coupled to multiple mass spectrometry (LC–MS2) equipped with APCI in the negative mode. This method was validated according to the requirements of Commission Decision EC/2002/657 (Implementing Council Directive 96/23/EC concerning the performance of analytical methods and the interpretation of results. Off J Eur Commun. L221: 8–36.). In addition to the linear response (R 2 between 59 and 97%), good repeatability (CV between 20 and 35%), reproducibility (CV between 20 and 35%) and detection (CCα) and quantification (CCβ) limits were obtained for all compounds in all matrices considered.

17alpha-ethinylestradiol (EE2), the active compound of the contraceptive pill, is a recalcitrant estrogen, which is encountered at ng/l levels in wastewater treatment plant (WWTP) effluents and rivers and can cause feminization of aquatic organisms. The aim of this study was to isolate micro-organisms that could remove such low EE2 concentrations. In this study, six bacterial strains were isolated from compost that co-metabolize EE2 when metabolizing estrone (E1), 17beta-estradiol (E2) and estriol (E3). The strains belong to the alpha, beta and gamma-Proteobacteria. All six strains metabolize E2 over E1, at microg/l to ng/l concentrations. In 4 days, initial concentrations of 0.5 microg E2/l and 0.6 microg EE2/l were degraded to 1.8 +/- 0.4 ng E2/l and 85 +/- 16 ng EE2/l, respectively. No other metabolites besides E1, E2, E3 or EE2 were detected, suggesting that total degradation and cleavage of the aromatic ring occurred. This is the first study describing that bacteria able to metabolize E2, can subsequently co-metabolize EE2 at low microg/l levels.

Ion suppression, a matrix effect that affects quantitative mass spectrometry, is one of the main problems encountered in liquid chromatography/tandem mass spectrometry. Two different clean-up steps for the multi-residue analysis of beta-agonists in urine were evaluated with respect to minimisation of ion suppression, namely, a mixed-phase solid phase extraction (SPE) column, i.e., clean screen Dau (CSD), and a molecular imprinted polymer (MIP) SPE column. Ion suppression experiments revealed that CSD sample clean-up can lead to false negative results for some beta-agonists, and that clean-up using MIP columns is more selective for beta-agonists than the use of CSD columns.

During their first period of development, the liquid chromatography–mass spectrometry techniques were met with great enthusiasm from most end-users. An extended application range, the needlessness of derivatisation step prior to injection, the possibility of reduced sample preparation and high throughput analysis were some of the arguments given in favor of these techniques. Few years and more than thousands applications later, more attention is paid to their adverse aspects and limitations, especially regarding the existence of matrix effects. Such problems are well known for many years and may concern various detection techniques. But ion suppression appears as a kind of matrix effect specifically linked to mass spectrometry that probably represents one of the main source of pitfalls in liquid chromatography–mass spectrometry (LC–MS n ). In the actual tendency to promote these techniques for control purposes in the field of residue analysis, it was thought necessary to highlight one of their possible side-effect which may have critical consequences for the analytical results. In this context, the objectives of the present article, which is based on a literature review and additional experiments, were to present the origins and mechanisms of ion suppression, to expose several case studies illustrating its consequences in the field of residue analysis, and finally to propose and comment on some solutions that may overcome this problem.

Current evidence suggests that the biocide tributyltin (TBT) causes the development of imposex, a state of pseudohermaphrodism in which females exhibit functional secondary male characteristics, by altering the biotransformation or elimination of testosterone. Imposex in gastropods following TBT exposure is the most complete example of the effects of an endocrine disrupter on marine invertebrates. Previous studies have demonstrated that the estuarine mysid Neomysis integer converts testosterone into multiple polar and nonpolar metabolites resulting from both phase I and phase II biotransformations. In this study, the effects of TBT chloride (TBTCl) on the phase I and II testosterone metabolism of N. integer were evaluated. The TBTCl was highly toxic to N. integer (96-h median lethal concentration [LC50] of 164 ng/L). To assess the effects on testosterone metabolism, mysids were exposed for 96 h to different concentrations of TBTCl (control, 10, 100, and 1,000 ng/L), and testosterone elimination as polar hydroxylated, nonpolar oxido-reduced, and glucose- and sulfate-conjugated metabolites was examined. The TBTCl differentially affected testosterone metabolism. The effect of TBTCl on phase I metabolism was unclear and has been shown to vary among species, likely depending on the inducibility or presence of certain P450 isozyme families. Reductase activity and metabolic androgenization were induced in the 10-ng/L treatment, whereas higher concentrations resulted in a reduction of sulfate conjugation. The exact mechanisms underlying TBT-induced imposex and alterations in the steroid metabolism need to be further elucidated.

According to the European Commission Decision 2001/699/EC and 2001/705/EC certain fishery and aquaculture products, imported from China, Vietnam or Indonesia and intended for human consumption, must be subjected to a test in order to ensure the absence of chloramphenicol residues. For that reason an analytical method has been developed and validated based on ELISA for screening and gas chromatography–tandem mass spectrometry (GC–MS2) or liquid chromatography–tandem mass spectrometry (LC–MS2) for confirmation. The chloramphenicol ELISA was carried out directly on an aqueous extract of the shrimps or after an extraction with ethyl acetate. Confirmation of suspect samples was performed after extraction with ethyl acetate and defatting with n-hexane. The clean-up was based on solid phase extraction using C18 cartridges or reversed phase HPLC. After derivatisation with N-methyl-N-(trimethylsilyl)trifluoroacetamide (MSTFA), the final extracts were analysed by GC–MS2 in the negative ion chemical ionisation mode. Confirmation of chloramphenicol was also possible with LC–MS2 after the same clean-up. Both selective techniques made it possible to detect chloramphenicol residues at the 0.1 μg kg−1 level starting from 20 g of matrix for enzyme-linked immunosorbent assay (ELISA) with organic solvent extraction, or from 5 g of matrix for ELISA with aqueous extraction.

A rapid and easy-to-perform method for the screening and confirmation of estrogens, gestagens and androgens (EGAs) in kidney fat has been developed. In this investigation only 5 g of fat was needed. After extraction with acetonitrile the steroid phase was defatted using n -hexane. Followed by a saponification step, the sample extract was purified by solid phase extraction. After derivatisation as trimethylsilyl ether derivatives, the steroids in the final extract were analysed using gas chromatography-tandem mass spectrometry (GC-MS 2 ). With this method the Belgian National Minimum Required Performance Limits (National MRPLs) for EGAs could be fulfilled.

Testosterone metabolism by Neomysis integer (Crustacea; Mysidacea) was assessed to obtain initial data on its metabolic capacity. N. integer were exposed to both testosterone and [(14)C]testosterone. Identification of testosterone metabolites and endogenous steroids was performed using thin-layer chromatography and liquid chromatography with multiple mass spectrometry. Endogenous production of testosterone in mysids was detected for the first time. N. integer were exposed to testosterone and metabolized administered testosterone extensively. At least 11 polar testosterone metabolites (R(f,metabolite) < R(f,testosterone)), androstenedione, dihydrotestosterone, and testosterone were produced in vivo by N. integer. A sex-specific testosterone metabolism was also observed, although this observation requires further confirmation. The anabolic steroid beta-boldenone was also identified for the first time in invertebrates. The metabolic pathway leading to the formation of beta-boldenone remains unknown, since the steroidal precursor androstadienedione could not be detected. These results reveal interesting similarities in enzyme systems in invertebrate and vertebrate species. Alterations in steroid hormone metabolism may be used as a new biomarker for the effects of endocrine disruptors in invertebrates.

The use of identification points (IPs) is a new approach to set up quality criteria for the identification of organic residues and contaminants: a laboratory is allowed to use any molecular spectrometric technique or combination of techniques in order to earn a minimum number of points. The system of IPs balances the identification power of the different analytical techniques and has the advantage that new techniques can be introduced very easily. © 2001 Elsevier Science B.V. All rights reserved.

In previous work (Le Bizec et al., Rapid Commun. Mass Spectrom. 2000; 14: 1058), it was demonstrated that a boar meal intake could lead to possible false accusations of abuse of 17beta-nortestosterone in antidoping control. The aim of the present study was to identify and quantify endogenous 19-norsteroids in boar edible tissue at concentrations that can alter the steroid urinary profile in humans, and lead to excretion of 19-norandrosterone (19-NA) and 19-noretiocholanolone (19-NE). The samples were analysed in two laboratories. The methodologies used for extraction and detection (GC/MS(EI) and LC/MS/MS(APCI+)) are compared and discussed. 19-Norandrostenedione (NAED), 17beta- and 17alpha-nortestosterone (bNT, aNT), and 17beta- and 17alpha-testosterone (bT, aT) were quantified. The largest concentrations of NAED and bNT were observed in testicles (83 and 172 microg/kg), liver (17 and 63 microg/kg) and kidney (45 and 38 microg/kg). A correlation between the bNT and NAED content of a typical meal prepared with boar parts and the excreted concentrations of 19-NA and 19-NE in human urine was demonstrated.

A combination of three plates, seeded with strains of Micrococcus luteus, Bacillus cereus or Escherichia coli, can be used for detection of residues of beta-lactam antibiotics, tetracyclines and fluoroquinolones. The sensitivity of each plate is optimal for only one of these groups, resulting in detection limits (LOD) lower than the corresponding maximum residue limits (MRL) and in distinct inhibition patterns typical for each antibiotic family. Beta-lactam antibiotics such as penicillin G, ampicillin and amoxicillin give only inhibition zones on the plate with M. luteus. Tetracyclines are detected up to the MRL level with B. cereus, and fluoroquinolones with E. coli. The LODs of the antibiotics tested were as follows: penicillin G (PENG) 0.9 ng, ampicillin (AMPI) 0.6 ng and amoxicillin (AMOX) 1.0 ng on the plate with M. luteus; tetracycline (TET) 4 ng, oxytetracycline (OXY) 3 ng, doxycycline (DOX) 0.6 ng, and chlortetracycline (CHL) 0.3 ng on the plate with B. cereus; enrofloxacin (ENRX) 1.5 ng, ciprofloxacin (CIPX) 0.5 ng and flumequine (FLUM) 1.5 ng on the plate with E. coli. The combination of plates enables the laboratory to select appropriate chromatographic techniques for identification and quantification of the residues. On the other hand, the three groups can also be detected on one plate seeded with Bacillus subtilis, although the limits of detection are higher: PENG 0.4 ng, AMPI and AMOX 3 ng, TET 5 ng, OXY 8 ng, DOX 1 ng, CHL 0.5 ng, ENRX 4 ng, CIPX 10 ng and FLUM 4 ng. The test was applied to 228 broiler fillets and to 27 turkey thighs, originating from different poultry slaughterhouses. Nineteen broiler fillets contained inhibiting substances. The positive results of the inhibition tests were confirmed with a chromatographic technique. Doxycycline residues were found in 16 samples and amoxicillin in two.

For the first time in the field of steroid residues in humans, demonstration of 19-norandrosterone (19-NA: 3alpha-hydroxy-5alpha-estran-17-one) and 19-noretiocholanolone (19-NE: 3alpha-hydroxy-5beta-estran-17-one) excretion in urine subsequent to boar consumption is reported. Three male volunteers agreed to consume 310 g of tissues from the edible parts (meat, liver, heart and kidney) of a boar. The three individuals delivered urine samples before and during 24 h after meal intake. After deconjugation of phase II metabolites, purification and specific derivatisation of target metabolites, the urinary extracts were analysed by mass spectrometry. Identification was carried out using measurements obtained by gas chromatography/high resolution mass spectrometry (GC/HRMS) (R = 7000) and liquid chromatography/tandem mass spectrometry (LC/MS/MS) (positive electrospray ionisation (ESI+)). Quantification was realised using a quadrupole mass filter. 19-NA and 19-NE concentrations in urine reached 3.1 to 7.5 microg/L nearby 10 hours after boar tissue consumption. Levels returned to endogenous values 24 hours after. These two steroids are usually exploited to confirm the exogenous administration of 19-nortestosterone (19-NT: 17beta-hydroxyestr-4-en-3-one), especially in the antidoping field. We have thus proved that eating tissues of non-castrated male pork (in which 17beta-nandrolone is present) might induce some false accusations of the abuse of nandrolone in antidoping.

The use of corticosteroids in combination with other hormonal substances has long been known to result in increased mass gain with bovines. Practice has demonstrated, however, that even the single use of a glucocorticoid may result in growth promoting effects. In addition to the popular dexamethasone, more recently other corticosteroids have also been misused for fattening purposes. The first part of this study deals with the detection of two of them, namely betamethasone and triamcinolone acetonide. Betamethasone was administered orally to a cow at a dose of 50 mg d-1 for 5 d, then later the same cow was injected intramuscularly with a dose of 50 mg of betamethasone dipropionate. Excretion in urine and faeces was followed with both HPLC-enzyme immunoassay and a previously described method based on negative chemical ionization mass spectrometry (NCI-MS) after oxidation. For the triamcinolone acetonide study a cow was treated with 50 mg d-1 of the drug during a 7 d period. Excretion in faeces was followed with GC-NCI-MS. As triamcinolone acetonide is resistant to the previously described oxidation procedure, however, a hydrolysis step had to be introduced prior to oxidation. In addition to this specific modification necessary for triamcinolone acetonide, in a subsequent part of this study the original oxidation procedure with pyridinium chlorochromate was re-investigated especially to shorten the procedure. With the introduction of potassium dichromate the reaction time could be decreased from 3 h to 10 min.

European legislation forbids the use of beta-agonists as growth-promoting substances in cattle raised for human consumption. However, the use of beta-agonists is allowed as a therapeutic treatment of tocolysis for female cattle during calving and of respiratory diseases and tocolysis for horses not raised for human consumption. A maximum residue limit (MRL) of 0.5 microgram kg-1 for clenbuterol in the liver of cattle and horses is proposed by law. Residues of beta-agonists in liver are identified with LC-MS-MS. Using ion trap technology, it was possible to identify each analyte without the need to resolve completely the chromatographic peaks. For each analyte, specific fragment ion spectra were obtained. The coeluting or incompletely resolved peaks were separated mass spectrometrically. For tulobuterol, bromobuterol and mabuterol, qualitative information was obtained. All beta-agonists could be detected up to a concentration of 0.1 microgram kg-1. For clenbuterol, a limited quantitative validation was performed. A working range was defined for which the method was applicable. Quantification was based on the integration of the response of the analytes in spiked blank liver samples. The mean recovery was 15%. The relative standard deviation (RSD) values at different concentrations were below the maximum allowed RSD. The limit of detection of clenbuterol was 0.11 microgram kg-1. The limit of quantification was 0.21 microgram kg-1. It was possible to quantify clenbuterol below one-half of the MRL. The advantage of this method is the ease of use of the mass spectrometric separation to qualify and quantify the presence of four beta-agonists in liver.

Qualitative methods are used for illegal drugs (e.g. hormones) which have a so-called zero tolerance (i.e. the presence of even a very small amount is not tolerated). In practice a limit of determination is used to prove the presence or absence of an analyte. Quantitative analysis is necessary especially for residues with a maximum residue limit (MRL). The method used in this case must have a limit of quantification (much) lower than the MRL. In any case, quality criteria must be fulfilled before quantification. In this investigation the pro's and con's of different strategies towards the use of qualitative and quantitative methods are discussed from the point of view and the daily experience of routine control in two field laboratories and one national reference laboratory.

In all EU member states, the use in livestock farming of certain substances having a hormonal action is prohibited. Clenbuterol, the beta-adrenergic agonist, has some growth promoting characteristics. Screening for clenbuterol can be carried out by an immunoassay. Gas chromatography-mass spectrometry (GC-MS) is very valuable for confirmatory purposes. In full scan MS it is impossible to fulfil the EU criteria of four diagnostic ions with one single ionisation mode. Some alternative possibilities are: (1) the use of two different ionisation modes, (2) the use of different derivatization methods or (3) the use of tandem MS. Each derivatisation or ionisation mode on its own did not give a sufficient number of ions. By combining these different possibilities we were able to obtain four ions, fulfilling the EU criteria.

A more sensitive method was developed using the hyphenated technique of gas chromatography-mass spectrometry (GC-MS) supplementary to the official high-performance thin-layer chromatography (HPTLC) method. Even combined with less efficient extraction and clean-up methods, GC-MS is able to lower the detection limit to less than 50 ppb. The powerful technique of GC-MS-MS is tried out to reduce the detection limit even more, in combination with simplified extraction methods. This time-saving approach combined with the increase in sensitivity is of great importance for a routine technique.

Intramuscularly administered, many anabolic residues are present in injection sites in an esterified form. Routine high-performance thin-layer chromatography (HPTLC) results show different spots recognizable as the esters of a certain anabolic compound, e.g., testosterone or estradiol, without giving the exact identity of the ester. Hydrolysis of the extract and respotting on HPTLC plates can confirm these spots to be esters owing to the absence of such spots on the plate after hydrolysis. The residues are then seen in their unesterified form. Identification is possible after respotting on reversed phase plates. As this method is complex and time consuming, an alternative method was tried out using gas chromatography–mass spectrometry (GC–MS). GC–MS analysis of injection site extracts is not only an independent method to confirm HPTLC results, but also provides the opportunity to identify the specific ester of the anabolic steroid. Identification is only possible when a standard of the ester is available for comparing the respective mass spectra. This report presents the mass spectra of some esters of testosterone, estradiol and nortestosterone found during the confirmation analysis of 35 injection sites by using GC–MS.

The bee diseases American and European foulbrood and nosemosis can be treated with anti-infectious agents. However, in the EU and the USA the use of these agents in beekeeping is strictly regulated due to the lack of tolerance (e.g. Maximum Residue Limit) for residues of antibiotics and chemotherapeutics in honey. This article reviews the literature dealing with antimicrobials of interest in apiculture, stability of these antimicrobials in honey, and disposition of the antimicrobials in honeybee hives.

In this paper, the past, present, and (possible) future of the European analytical criteria for residues are described. The elaboration of the revision of Commission Decision 93/256/EC was a long process starting in 1996 and ending with the formation of a European Commission (EC) working group in 1998. This working group took account of developments in scientific and technical knowledge at that time and produced a draft version of the revision within 6 months. The revision, finally published in 2002 (2002/657/EC), includes new ideas on the identification of analytes and the criteria for performance assessment as well as validation procedures. Currently (2009), the evolution in analytical equipment and progress in scientific research, accompanied by recent European regulatory changes, demands an update or revision of the 2002/657/EC.

The presence of both pharmaceuticals and pesticides in the aquatic environment has become a well-known environmental issue during the last decade. An increasing demand however still exists for sensitive and reliable monitoring tools for these rather polar contaminants in the marine environment. In recent years, the great potential of passive samplers or equilibrium based sampling techniques for evaluation of the fate of these contaminants has been shown in literature. Therefore, we developed a new analytical method for the quantification of a high number of pharmaceuticals and pesticides in passive sampling devices. The analytical procedure consisted of extraction using 1:1 methanol/acetonitrile followed by detection with ultra-high performance liquid chromatography coupled to high resolution and high mass accuracy Orbitrap mass spectrometry. Validation of the analytical method resulted in limits of quantification and recoveries ranging between 0.2 and 20 ng per sampler sheet and between 87.9 and 105.2%, respectively. Determination of the sampler-water partition coefficients of all compounds demonstrated that several pharmaceuticals and most pesticides exert a high affinity for the polydimethylsiloxane passive samplers. Finally, the developed analytical methods were used to measure the time-weighted average (TWA) concentrations of the targeted pollutants in passive samplers, deployed at eight stations in the Belgian coastal zone. Propranolol, carbamazepine and seven pesticides were found to be very abundant in the passive samplers. These obtained long-term and large-scale TWA concentrations will contribute in assessing the environmental and human health risk of these emerging pollutants.

International audience; Corticosteroids are hormonal substances widely used in human and veterinary medicine for their anti-inflammatory properties. Among the numerous existing artificial corticosteroids, dexamethasone remains the most commonly used, mainly throughout esterified forms such as acetate or phosphate. An experimental study was designed to assess its drug residue levels in urine and feces, as well as its fixation in bovine hair following a single administration of 0.15 mg/kg b.w. dexamethasone acetate and 0.12 mg/kg b.w. dexamethasone sodium phosphate. Different analytical methods based on GC-MS or LC-MS/MS were used for measuring dexamethasone and its esterified forms, which were implemented in 3 different European laboratories in the field that collaborated for this study. The obtained results confirmed the high and rapid urinary excretion rate of dexamethasone, with a maximal concentration (267 mu g/L) measured one day after administration and 98% elimination within 3 days. The concentrations obtained with the GC-NCI-MS procedure (using chemical oxidation as derivatization) were found significantly higher than the ones obtained with LC-ESI-MS/MS, indicating a possible contribution of dexamethasone phase I and/or II metabolites to the monitored signal. Fecal elimination was also found rapid (95% elimination within 3 days) with a maximum concentration level (28.5 mu g/kg) observed one day after administration. Detectable levels of dexamethasone in hair appeared on day 2 (11.5 mu g/kg), reached a maximum around one week, and could be identified until 22 days upon treatment, establishing the suitability of hair as a biological matrix for medium to long-term residue controls of dexamethasone. (C) 2010 Elsevier Inc. All rights reserved.

Nosema apis spore hatching was examined in different salt solutions. Best results were obtained in 0.5 M NaCl + 0.5 M NaHCO3 at pH 6. No differences could be detected between sodium and potassium salts. The differences in efficacy between monovalent anions were more obvios, and a rank order could be formed: Cl- > Br- > F- > I-. The carbohydrate content of ungerminated and germinated spores was measured by GC-MS analysis. Only a very small shift in the ratio αα-trehalose/ d -glucose was found. Scanning electron microscopy of extruded spores was done. No convincing images of released sporoplasms were obtained.

Knowledge of the presence of micropollutants such as pharmaceuticals, in coastal areas, is very limited; therefore, the main objective of this study was to optimize and validate a new analytical method for the quantitative analysis of 13 multiclass pharmaceuticals in seawater. Target compounds included antibiotics, non-steroidal anti-inflammatory drugs, beta-blockers, lipid regulators and one psychiatric drug. A combination of solid-phase extraction and liquid chromatography coupled with multiple mass spectrometry enabled their detection at the low nanogram per litre level. The limits of quantification varied between 1 and 50 ng L(-1), for most components the linearities were more than 0.99 and the recoveries obtained in seawater (95-108%) were satisfactory. This method was applied to seawater and estuarine water samples collected in the Belgian coastal zone, to assess the prevalence of common pharmaceuticals in this marine environment. Seven phar-maceuticals, including compounds of which the presence in marine environments had not been reported earlier, were detected, with salicylic acid and carbamazepine being the most abundant, in concentrations up to 855 ng L(-1).

Flow-through reactors with manganese oxides were examined for their capacity to remove 17 alpha-ethinylestradiol (EE2) at microg L(-1) and ng L(-1) range from synthetic wastewater treatment plant (WWTP) effluent. The mineral MnO(2) reactors removed 93% at a volumetric loading rate (B(V)) of 5 microg EE2 L(-1) d(-1) and from a B(V) of 40 microg EE2 L(-1) d(-1) on, these reactors showed 75% EE2 removal. With the biologically produced manganese oxides, only 57% EE2 was removed at 40 microg EE2 L(-1) d(-1). EE2 removal in the ng L(-1) range was 84%. The ammonium present in the influent (10 mg N L(-1)) was nitrified and ammonia-oxidizing bacteria (AOB) were found to be of prime importance for the degradation of EE2. Remarkably, EE2 removal by AOB continued for a period of 4 months after depleting NH(4)(+) in the influent. EE2 removal by manganese-oxidizing bacteria was inhibited by NH(4)(+). These results indicate that the metabolic properties of nitrifiers can be employed to polish water containing EE2 based estrogenic activity.

As part of the Endis-Risks project, the current study describes the occurrence of the chlorotriazine pesticides atrazine, simazine and terbutylazine in water, sediment and suspended matter in the Scheldt estuary (B-Nl) from 2002 to 2005 (3 samplings a year, 8 sampling points). Atrazine was found at the highest concentrations, varying from 10 to 736 ng/l in water and from 5 up to 10 ng/g in suspended matter. Simazine and terbutylazine were detected at lower concentrations. Traces of the targeted pesticides were also detected in sediments, but these were below the limit of quantification. As part of an ecotoxicological assessment, we studied the potential effect of atrazine on molting of Neomysis integer (Crustacea:Mysidacea), a resident invertebrate of the Scheldt Estuary and a proposed test organism for the evaluation of endocrine disruption. Following chronic exposure ( approximately 3 weeks), atrazine did not significantly affect mysid molting at environmentally relevant concentrations (up to 1 microg/l).

A multi-residue liquid chromatography/tandem mass spectrometry method (LC/MS2) was developed for the detection of the non-steroidal anti-inflammatory drugs acetylsalicylic acid (via the marker residue salicylic acid), flunixin, phenylbutazone, tolfenamic acid, meloxicam and ketoprofen, in bovine muscle. After extraction of the bovine muscle with acetonitrile, the cleanup was performed using a Oasis HLB column. The evaporated eluate was reconstituted and analysed by LC/MS2. To obtain optimal detection of salicylic acid and phenylbutazone, the ion trap mass spectrometric parameters activation q and maximum ion injection time, respectively, were optimised. The activation q for salicylic acid was increased to obtain reliable detection of both salicylic acid and its product ion. The maximum ion injection time for the time segment containing phenylbutazone was decreased since there were not enough scans across the chromatographic peak of this compound. The multi-residue method was able to detect the different analytes below or at the maximum residue limit (MRL) or minimum required performance limit (MRPL) or, in the case of phenylbutazone and ketoprofen, at 100 and 20 microg kg(-1), respectively.

An analytical procedure enabling routine analysis of four environmental estrogens at concentrations below 1 ng L–1 in estuarine water samples has been developed and validated. The method includes extraction of water samples using solid-phase extraction discs and detection by gas chromatography (GC) with tandem mass spectrometry (MS–MS) in electron-impact (EI) mode. The targeted estrogens included 17 alpha- and 17 beta-estradiol (aE2, bE2), estrone (E1), and 17 alpha-ethinylestradiol (EE2), all known environmental endocrine disruptors. Method performance characteristics, for example trueness, recovery, calibration, precision, accuracy, limit of quantification (LOQ), and the stability of the compounds are presented for each of the selected estrogens. Application of the procedure to water samples from the Scheldt estuary (Belgium – The Netherlands), a polluted estuary with reported incidences of environmental endocrine disruption, revealed that E1 was detected most frequently at concentrations up to 7 ng L–1. aE2 was detected once only and concentrations of bE2 and EE2 were below the LOQ

The use of estrogens, gestagens and androgens (EGAs) in animal fattening is prohibited in the European Community. Based on the general detection capabilities of Belgian laboratories, National Minimum Required Performance Limits (National MRPLs) for a number of EGAs have been imposed by the inspection services. Selective hyphenated techniques, e.g. GC-MS and GC-MS2, with high detection capability are needed. Beta-trenbolone, which is meant to be a "problem" molecule for GC-MS, can be detected at the 2 microg/kg level using GC-MS2. Based on the National MRPLs in different matrices, our laboratory has divided the EGAs into a class system. In this set-up, analysis of EGAs in kidney fat and meat is discussed.

Helium is considered to be the ideal carrier gas for gas chromatography/mass spectrometry (GC/MS) in general, and for use with an ion trap in particular. Helium is an inert gas, can be used without special precautions for security and, moreover, it is needed as a damping gas in the trap. A disadvantage of helium is the high viscosity resulting in long GC run times. In this work hydrogen was tested as an alternative carrier gas for GC in performing GC/MS analyses. A hydrogen generator was used as a safe source of hydrogen gas. It is demonstrated that hydrogen can be used as a carrier gas for the gas chromatograph in combination with helium as make-up gas for the trap. The analysis time was thus shortened and the chromatographic performance was optimized. Although hydrogen has proven useful as a carrier gas in gas chromatography coupled to standard detectors such as ECD or FID, its use is not mentioned extensively in the literature concerning gas chromatography-ion trap mass spectrometry. However, it is worth considering as a possibility because of its chromatographic advantages and its advantageous price when using a hydrogen generator.

In the European Union, the use of growth promoting substances such as thyreostats, anabolics (products with estrogenic, androgenic or gestagenic action) and beta-agonists in animal fattening is forbidden. Corticosteroids, such as dexamethasone, although considered catabolic substances, have been administered to food producing animals in order to achieve mass gains. For the analysis of injection sites and of suspect cocktails (found at the farm), a number of HPTLC and HPLC methods are used. However, in injection sites and also in cocktails found at the farm, sometimes many unknown substances are found. In this investigation, a multiple mass spectrometric (MSn) method was developed. The method is based on rapid extraction of the matrix with methanol and direct infusion of the extract into the interface of the mass spectrometer. Tables that summarise the masses of corticosteroids and their possible esters are presented.

In addition to methods for the determination of residues, there is an important need for knowledge of the fate and excretion of growth promoting substances in fattening animals. In court, often simple questions are asked, such as, over what period of time can the drug be detected?, is it possible to find residues after 2 months, etc. These questions can only be answered by conducting animal experiments. Data on excretion and distribution of thiouracils in cows are rather scarce. At the beginning of the 1980s, animal experiments with methylthiouracil (MTU) were carried out in the Laboratory of Chemical Analysis. These experiments showed that treatment of cows with MTU results in the rapid appearance of the drug in plasma, urine and milk, whereas MTU selectively accumulates in the thyroid gland. The results of these experiments were only published in media with limited access (thesis, abstracts) and also there has been a considerable improvement in data handling with computer programs in the last 15 years. This investigation reinterprets the ‘old’ analytical data from animal experiments using a pharmacokinetic software package.

Residues of the tetracycline group of antibiotics were quantified in pork and chicken muscle tissue that had previously been screened with a microbiological inhibition test and an immunological method. Pieces of frozen pork and chicken meat were screened on a pH 6 culture medium seeded with Bacillus subtilis. An aqueous extract of the inhibitor-positive samples was then screened with a group-specific commercial ELISA kit, able to detect levels of oxytetracycline, chlortetracycline, tetracycline and doxycycline corresponding with the European MRL or lower. The cut-off value of the ELISA was set at a B/B0 value of 75%. Finally, confirmation and quantification were performed using a validated HPLC method with fluorescence detection. The fluorescence was induced by complexation of the tetracyclines with the zirconium cation which is added post-column to the HPLC eluate. This fluorescence makes it possible to quantitate residues below one-half of the MRL. To gain additional qualitative information some samples were also analysed with LC-MS-MS. ELISA analysis demonstrated the presence of residues of tetracyclines in 12 out of 19 inhibitor-positive pork samples and in 19 out of 21 inhibitor-positive chicken samples. Doxycycline was detected with HPLC in 10 of these 12 pork samples and in 18 out of 19 chicken samples. The two other ELISA positive pork samples contained oxytetracycline, while no tetracyclines were found in one ELISA positive chicken meat sample. The correlation between the ELISA B/B0 values and the actual levels determined with the HPLC method was poor, whereas a better correlation was observed between the inhibition zones and the doxycycline levels. Our results indicate that an inhibition test with a medium at pH 6 and B. subtilis as test organism is well suited to screen pork and chicken muscle tissue for residues of tetracycline antibiotics. Since many positive samples contained doxycycline levels below the MRL, a confirmatory method is necessary to quantify the residues.

Within several regional field laboratories and the national reference laboratory a harmonised methodology for the analysis of anabolic residues in faecal samples was developed. The method consists of a liquid–liquid and a solid-phase extraction step, followed by a high-performance liquid chromatography purification step. Using gas chromatography-mass spectrometry, currently illegally used anabolic steroids can be detected in faeces at the ppb level. Within this context acidification, followed by centrifugation under cooling, allows efficient, practical and rapid defatting of faecal samples. Furthermore, a combination of a silica and an aminopropyl solid-phase extraction column was found to give the best results as regards the sample purification process.

For several years, the misuse of dexamethasone and its esters in livestock production has been clearly demonstrated. The first part of the present study deals with the elaboration of a sensitive and specific method for the determination of residues of dexamethasone in excreta at the ppb level. Sample preparation for urine and faeces, including high-performance liquid chromatography (HPLC) fractionation, was carried out. The detection was based on established methodology employing negative chemical ionization–mass spectrometry (NCI–MS) after oxidation of the dexamethasone. In comparison with previous literature, the yield of oxidized dexamethasone was substantially improved and the oxidation procedure was made more simple and robust. In the second part of the study, the relationship between the dose of dexamethasone administered and the levels of the drug in excreta was investigated using this method, as was the ratio between drug levels in urine and faeces. Treatment was carried out for 7 d with an oral dose of 50 mg d–1, the maximum levels found in urine and faeces were 980 and 744 ppb, respectively. While the elimination via faeces responded much slower at the start and the end of treatment, the final part of both excretion profiles were very similar and a level of 1 ppb was reached in both matrices 9 d after the end of treatment. Gas chromatography–mass spectrometry (GC–MS) results obtained for the urine samples were compared with those obtained with direct enzyme immunoassay.

Since the late 1980s all of the laboratories involved in high-performance thin-layer chromatography (HPTLC) control of hormonal residues in kidney fat, have occasionally detect a green fluorescent spot with similar RF values and colour to those observed for methyltestosterone (MT). This spot (product) could lead to false positive results for MT and was thus named 'le faux méthyl' (the false methyl) by a french speaking colleague. All of the samples with a false methyl spot also contained a relatively high concentration of progesterone. Differentiation of this product from methyltestosterone can be performed in three ways: firstly, extra HPTLC on reversed-phased plates, secondly, extra purification of the extract with HPLC prior to HPTLC and thirdly, gas chromatography--mass spectrometry. This interference was identified as 20 beta-hydroxyprogesterone, a by-product of progesterone. The problem of the false methyl was not only linked with the TLC characteristics of MT but also to the progesterone used as standard. Some laboratories used an analytical-reagent grade standard and others used commercial progesterone powders as standards (e.g., obtained in crude form from pharmaceutical companies). The commercial-grade progesterones showed two spots in comparison with the analytical standard that showed just one spot. As the false methyl was observed not only in kidney fat and meat samples, but also in illegal hormone cocktails, it was concluded that we had detected a by-product of an illegally used 'natural progesterone'.

A diverse set of reference compounds suspected of having an endocrine-disrupting mode of action (i.e., testosterone, flutamide, ethinylestradiol, precocene, nonylphenol, fenoxycarb, and methoprene) were tested for acute toxicity to the estuarine mysid Neomysis integer (Crustacea: Mysidacea). Neomysis integer was very sensitive to all tested compounds, with 96-h median lethal concentrations in a narrow range between 0.32 and 1.95 mg/L. The pesticides methoprene and fenoxycarb, both synthetic insect juvenile hormone analogs, were most toxic to N. integer. In addition, the short-term sublethal effects of methoprene and nonylphenol (an estrogen agonist) on the energy and steroid metabolism of N. integer were evaluated. Both compounds significantly affected energy and testosterone metabolism of N. integer at concentrations below acute toxicity levels. Energy consumption in methoprene- and nonylphenol-exposed mysids was significantly induced at 100 µg/L, resulting in a lower cellular energy allocation in these animals. Testosterone phase I metabolism was affected at 10 µg/L, whereas glycosylation was the most important phase II pathway affected in mysids exposed to 100 µg/L of both compounds. Methoprene exposure resulted in a concentration-dependent increase in the metabolic androgenization ratio. Mysids exposed to nonylphenol at 10 µg/L had a significantly higher metabolic androgenization ratio. The present study indicates that energy and testosterone metabolism of mysids, as endpoints, are able to detect endocrine-disruptive activity of chemicals after short-term exposure to environmentally realistic levels of endocrine disruptors.

When residues of nortestosterone (NT) were found in the urine of cattle, racehorses or bodybuilders, exogenic administration was thought to be proven. In previous literature, no records were found of the endogenic presence of this molecule. In the horse-racing world, Houghton and Courthot found that NT is normally present in the urine of the stallion. Belgian and Dutch researchers found that NT is also present in the urine and edible parts of the intact boar. Vandenbroeck et al. (1991) suggested the endogenous presence of NT (in the beta form) in the pregnant cow. Meyer (1992) reported the presence of NT (in the alpha form) in relatively high amounts in the urine of the cow peri-partum and the neo-natal calf. These observations may have important consequences for veterinary meat inspection in the EU. Therefore, in Belgium a large scale experiment was set up in co-operation with the EU Community Reference Laboratory (RIVM). In this paper the present state of the results in this area is presented. A large number of urine samples (50) of pregnant non-treated cows were collected and analysed by gas chromatography-mass spectrometry (GC-MS) in 4 different laboratories. Further samples (100) were taken, but only analysed in one laboratory. The results proved clearly that NT may indeed be detectable in the alpha form in the urine of pregnant cows, from at least 2 months, but most probably from 4-5 months before partus.

The reproducibility and sensitivity of the radiochemical assay of fatty acids, described by R. J. Ho, can be enhanced by replacing the centrifugation step with absorption of water by anhydrous sodium sulfate.