Phycotoxins in seafood--toxicological and chromatographic aspects

Revolutionizing Food Safety with Quantum Dot-Polymer Nanocomposites: From Monitoring to Sensing Applications

The present review article investigates the prospective utilisation of quantum dot-polymer nanocomposites in the context of ensuring food safety. The text pertains to the advancement of nanocomposites, encompassing their distinctive optical and electrical characteristics, and their prospective to transform the detection and perception of food safety risks. The article explores diverse methodologies for producing nanocomposites and underscores their potential utility in identifying impurities, microorganisms, and harmful substances in food. The article provides an overview of the challenges and limitations associated with the utilisation of nanocomposites in food safety applications, encompassing concerns regarding toxicity and the necessity for standardised protocols. The review article presents a comprehensive examination of the present research status in this area and underscores the potential of quantum dots-polymer nanocomposites in transforming food safety monitoring and sensing.

Intriguing differences in the gas-phase dissociation behavior of protonated and deprotonated gonyautoxin epimers

The aim of this study was to investigate the unusual gas-phase dissociation behavior of two epimer pairs of protonated gonyautoxins (GTX) following electrospray ionization in comparison to their deprotonated counterparts. The chemical structures of the investigated GTX1-4 variants vary in their substitution pattern at N-1 and the stereochemical orientation of the hydroxysulfate group at C-11 (11α for GTX1/2 versus 11β for GTX3/4). The direct comparison of mass spectra in positive and negative ion modes illustrated two distinct features: first, an intriguing difference between protonated 11α and 11β species, where 11α conformations exhibited almost complete dissociation of [M + H](+) ions via facile SO(3) elimination, while 11β species remained mostly intact as [M + H](+); and second, the lack of such differences for the deprotonated counterparts. In this study, we propose an acid-catalyzed elimination mechanism from density functional theory calculations, initiated by a proton transfer of a guanidinium proton to the hydroxysulfate group with simultaneous SO(3) release, which is only possible for the 11α conformation based on intramolecular distances. The same mechanism explains the lack of a comparable SO(3) loss in the negative ion mode. CID experiments supported this proposed mechanism for GTX1 and GTX2. Computational modeling of product ions seen in the CID spectra of GTX3 and GTX4 established that the lowest energy dissociation pathway for the 11β epimers is elimination of water with the possibility for further SO(3) release from the intermediate product. Experimental data for structurally analogous decarbamoyl gonyautoxins confirmed the evidence for the GTX compounds as well as the proposed elimination mechanisms.

Determination of okadaic acid, dinophysistoxin-1 and related esters in Greek mussels using HPLC with fluorometric detection, LC-MS/MS and mouse bioassay

An approach involving both chemical and biological methods was undertaken for the detection and quantification of the marine toxins okadaic acid (OA), dinophysistoxin-1 (DTX-1) and their respective esters in mussels from different sampling sites in Greece during the period 2006-2007. Samples were analyzed by means of a) high performance liquid chromatography with fluorometric detection (HPLC-FLD), using 9-athryldiazomethane (ADAM), as a pre-column derivatization reagent, b) liquid chromatography coupled with tandem mass spectrometry (LC-MS/MS) and c) the mouse bioassay. Free OA and DTX-1 were determined by both HPLC-FLD and LC-MS/MS, while their respective esters were determined only by LC-MS/MS after alkaline hydrolysis of the samples. The detection limit (L.O.D.) and quantification limit (L.O.Q.) of the HPLC-FLD method were 0.015 microg/g HP and 0.050 microg/g HP, respectively, for OA. The detection limit (L.O.D.) and quantification limit (L.O.Q.) of the LC-MS/MS method were 0.045 microg/g HP and 0.135 microg/g HP, respectively, for OA. Comparison of results between the two analytical methods showed excellent agreement (100%), while both HPLC-FLD and LC-MS/MS methods showed an agreement of 97.1% compared to the mouse bioassay.

Detection of okadaic acid and related esters in mussels during diarrhetic shellfish poisoning (DSP) episodes in Greece using the mouse bioassay, the PP2A inhibition assay and HPLC with fluorimetric detection

An approach involving chemical, functional and biological techniques was taken for the detection and quantification of the marine toxin okadaic acid (OA) in mussels from Thermaikos and Saronikos Gulfs, Greece, during DSP episodes that occurred in 2006-2007. Samples were analyzed using the mouse bioassay, high performance liquid chromatography with fluorimetric detection (HPLC-FLD), using l-bromoacetylpyrene (BAP), as a precolumn derivatisation reagent, and the protein phosphatase 2A inhibition assay (PP2AIA) using a commercially available kit. Okadaic acid (OA) and its polar and non-polar esters were detected and quantified by HPLC-FLD, after hydrolysis of the samples during preparation. The detection limit of the HPLC method for OA was 5.86 microg OA/kg, which permits this method to be used for the regulatory control of these toxins in shellfish. Comparison of the results by all three methods revealed excellent consistency.

Determination of paralytic shellfish poisoning toxins in cultured microalgae by high-performance liquid chromatography with fluorescence detection

A novel method for the determination of paralytic shellfish poisoning (PSP) toxins using high-performance liquid chromatography with fluorescence detection was developed. The fluorescent derivates of neosaxitoxin (neoSTX), saxitoxin (STX), gonyautoxins 1 and 4 (GTX1+4), and gonyautoxins 2 and 3 (GTX2+3) were separated on a muBondapak NH2 column (300 mm x 3.9 mm, 10 microm) using water and acetate buffer (pH 6.5) as the mobile phase (1.00 mL min(-1)) in gradient mode with fluorescence detection at 390 nm (excitation at 330 nm). The linear ranges of neoSTX, STX, GTX1+4 and GTX2+3 were 3.31-331, 0.952-95.2, 3.78-378 and 0.124-12.4 ng mL(-1), respectively. The detection limits of neoSTX, STX, GTX1+4 and GTX2+3 were 1.10, 0.32, 1.26 and 0.041 ng mL(-1), respectively. The method was successfully applied to the determination of PSP toxins in microalgae. The recoveries ranged from 88+/-2% to 107+/-4% and the relative standard deviations were 0.16% to 4.4%. The procedure is also environmentally friendly because no organic solvent is used in the mobile phase.

Overview of key phytoplankton toxins and their recent occurrence in the North and Baltic Seas

The frequency and intensity of harmful algal blooms (HABs) appear to be on the rise globally. There is also evidence of the geographic spreading of toxic strains of these algae. Consequently, methods had to be established and new ones are still needed for the evaluation of possible hazards caused by increased algal toxin production in the marine food chain. Different clinical effects of algae-related poisoning have attracted scientific attention; paralytic shellfish poisoning, diarrhetic shellfish poisoning, and amnesic shellfish poisoning are among the most common. Additionally, cyanobacteria (blue-green algae) in brackish waters often produce neurotoxic and hepatotoxic substances. Bioassays with mice or rats are common methods to determine algal and cyanobacterial toxins. However, biological tests are not really satisfactory because of their low sensitivity. In addition, there is growing public opposition to animal testing. Therefore, there has been increasing effort to determine algal toxins by chemical methods. Plankton samples from different European marine and brackish waters were taken during research cruises and analyzed on board directly. The ship routes covered marine areas in the northwest Atlantic, Orkney Islands, east coast of Scotland, and the North and Baltic seas. The first results on the occurrence and frequency of harmful algal species were obtained in 1997 and 1998. During the 2000 cruise an HPLC/MS coupling was established on board, and algal toxins were measured directly after extraction of the plankton samples. In contrast to earlier cruises, the sampling areas were changed in 2000 to focusing on coastal zones. The occurrence of toxic algae in these areas was compared to toxin formation during HABs in the open sea. It was found that the toxicity of the algal blooms depended on the prevailing local conditions. This observation was also confirmed by monitoring cyanobacterial blooms in the Baltic Sea. Optimal weather conditions, for example, during the summers of 1997 and 2003, favored blooms of cyanobacteria in all regions of the Baltic. The dominant species regarding the HABs in the Baltic was Nodularia spumigena. However, in addition to high concentrations of Nodularia spumigena in coastal zones, other blue-green algae are involved in bloom formation, with changes in plankton communities influencing both toxin profiles and toxicity.

Application of solid phase microextraction in the determination of paralytic shellfish poisoning toxins

A SPME-HPLC-post-column fluorescent derivatization method for the direct determination of saxitoxin (STX), the most potent paralytic shellfish poisoning (PSP) toxin, in water has been developed. Commercially available SPME devices with 50 microm Carbowax templated resin (CW/TPR) coating was found to be able to pre-concentrate STX from aqueous media. A special pre-conditioning treatment of soaking the SPME coating in 0.1 M NaOH solution significantly improved the extraction efficiency. The optimal pH for the SPME process is 8.1 and the equilibration time is 40 min. The partition coefficient, K, of the distribution of STX between the SPME coating and the aqueous media was measured to be 2.99 +/- 0.04 x 10(3). Extracted toxin on the SPME stationary phase was difficult to be desorbed by the HPLC mobile phase under dynamic desorption mode. A static ion-pairing desorption technique using a desorption solvent mixture of 20 mM sodium 1-heptanesulfonate in 30% aqueous acetonitrile acidified with 50 mM sulfuric acid was developed to overcome this problem. The method detection limit and repeatability achieved by this SPME-HPLC method were 0.11 ng ml(-1) and 3.7%, respectively, with a sample volume of just 5 ml of water. This analytical method is adequate for the monitoring of the PSP toxin in fresh/drinking waters. However, serious interference was observed when this technique was applied to saline water samples. This is probably due to competition of sodium ions with the cationic STX for absorption into the SPME stationary phase.

Gas-phase dissociation reactions of protonated saxitoxin and neosaxitoxin

The aim of this study was to investigate the behavior of the protonated paralytic shellfish poisons saxitoxin (STX) and neosaxitoxin (NEO) in the gas-phase after ion activation using different tandem mass spectrometry techniques. STX and NEO belong to a group of neurotoxins produced by several strains of marine dinoflagellates. Their chemical structures are based on a tetrahydropurine skeleton to which a 5-membered ring is fused. STX and NEO only vary in their substituent at N-1, with STX carrying hydrogen and NEO having a hydroxyl group at this position. The collision-induced dissociation (CID) spectra exhibited an unusually rich variety and abundance of species due to the large number of functional groups within the small skeletal structures. Starting with triple-quadrupole CID spectra as templates, linked ion-trap MSn data were added to provide tentative dissociation schemes. Subsequent high-resolution FTICR experiments gave exact mass data for product ions formed via infrared multiphoton dissociation (IRMPD) from which elemental formulas were derived. Calculations of proton affinities of STX and NEO suggested that protonation took place at the guanidinium group in the pyrimidine ring for both molecules. Most of the observed parallel and consecutive fragmentations could be rationalized through neutral losses of H2O, NH3, CO, CO2, CH2O and different isocyanate, ketenimine and diimine species, many of which were similar for STX and NEO. Several exceptions, however, were noted and differences could be readily correlated with reactions involving NEO's additional hydroxyl group. A few interesting variations between CID and IRMPD spectra are also highlighted in this paper.

A rapid and sensitive assay for paralytic shellfish poison (PSP) toxins using mouse brain synaptoneurosomes

A membrane potential assay using mouse brain synaptoneurosomes was evaluated for the determination of paralytic shellfish poison (PSP) toxin content of mussels and other bivalve species important to the shellfish industry. The assay relies on the ability of PSP toxins to block veratridine-induced depolarization of synaptoneurosomes. Changes in the membrane potential of synaptoneurosomes were monitored using the voltage-sensitive fluorescent probe rhodamine 6G. Standard saxitoxin was found to be a potent inhibitor of the membrane depolarizing effects of the sodium channel activator veratridine (I(50) ca. 4 nM). Likewise, shellfish extracts containing PSP toxins inhibited veratridine-induced depolarization. Neither saxitoxin or shellfish extracts had any discernible effect on the resting membrane potential of synaptoneurosomes. When synaptoneurosomal results for extracts of mussels (n=120) and other shellfish (n=29) were correlated with official mouse toxicity assay data there was very good agreement (r(2)=0.84 and 0.86, respectively), indicating that the in vitro assay has utility for a variety of commercially relevant shellfish species. Our investigation suggests that the mouse synaptoneurosome assay is of similar sensitivity to the official CD1 mouse toxicity assay. The synaptoneurosome fraction can be prepared quickly (approx. 40 min) and an individual assay takes less than 7 min. Since 20 such assays can be performed using material from a single CD1 mouse brain, there is considerable opportunity for reducing the number of animals required in conventional PSP monitoring while retaining the same animal system.

Matrix effect and correction by standard addition in quantitative liquid chromatographic-mass spectrometric analysis of diarrhetic shellfish poisoning toxins

An evaluation of the feasibility of liquid chromatography-mass spectrometry (LC-MS) with atmospheric pressure ionization was made for quantitation of four diarrhetic shellfish poisoning toxins, okadaic acid, dinophysistoxin-1, pectenotoxin-6 and yessotoxin in scallops. When LC-MS was applied to the analysis of scallop extracts, large signal suppressions were observed due to coeluting substances from the column. To compensate for these matrix signal suppressions, the standard addition method was applied. First, the sample was analyzed and then the sample involving the addition of calibration standards is analyzed. Although this method requires two LC-MS runs per analysis, effective correction of quantitative errors was found.

Pectenotoxins--an issue for public health: a review of their comparative toxicology and metabolism

Pectenotoxins (PTXs) are a group of toxins associated with diarrhetic shellfish poisoning (DSP) and isolated from DSP toxin-producing dinoflagellate algae. Consumption of shellfish contaminated with PTXs has been associated with incidences of severe diarrhetic illness resulting in hospitalisation. Concern has been raised for public health following the discovery that these toxins are not only hepatotoxic and can cause diarrhetic effects in mammals, but that they are potently cytotoxic to human cancer cell lines and have been found to be tumour promoters in animals. With advances in knowledge and technology, more PTXs are being identified, but little is known of their toxicology and the potential impact these toxins may have on public health in the long term. Without such information, adequate health-risk assessments for the consumption of shellfish contaminated with PTXs cannot be performed. This review gives a brief introduction to diarrhetic shellfish toxins, details the known toxicology and metabolism of PTXs in animals, and discusses known incidences of PTX poisoning in humans.

Derivatization of thymine and thymine photodimers with 4-bromomethyl-7-methoxycoumarin for fluorescence detection in high-performance liquid chromatography

Exposure of DNA to utraviolet radiation results in the formation of a number of photoproducts, including thymine photodimers. A sensitive and selective analytical method based on high-performance liquid chromatography (HPLC) and fluorescent labeling with 4-bromomethyl-7-methoxycoumarin has been developed to quantify both thymine and thymine photodimers. The identity of the thymine and thymine dimer derivatives were determined by HPLC-electrospray ionization mass spectrometry. The derivatization reaction yield was maximized by optimizing several reaction variables. The limit of detection for HPLC method was 1.0 pmol thymine and 0.4 pmol thymine dimer for S/N = 3.

Use of immunoaffinity columns for clean-up of diarrhetic toxins (okadaic acid and dinophysistoxins) extracts from shellfish prior to their analysis by HPLC/fluorimetry

Diarrhetic Shellfish Poisoning (DSP) is a severe gastro-intestinal disease caused by consumption of seafood contaminated by microalgal toxins, mainly okadaic acid (OA) and structurally related toxins, dinophysistoxins (DTXs). Regulatory monitoring is generally based on rodent bioassays which, however, present some technical and ethical disadvantages. The most promising technique of analysis of these toxins involves an HPLC separation with spectrofluorimetric detection after derivatization of the toxins with a fluorescent reagent. The lack of specificity of the extraction procedure (liquid-liquid partition), and the presence of interfering compounds in the matrix, does not allow the determination and the quantification of low amounts of toxins in seafood. In this paper, the authors report the development and the characterization of immunoaffinity columns (IAC), which were elaborated using anti-okadaic acid monoclonal antibodies, for a specific retention of the OA group of toxins. The coupling yield and the stability of these columns were investigated as well as their capacity to remove interfering compounds. Cross-reactivity was observed between the antibodies and the DTX-1 and the DTX-2, allowing the detection of the different toxins in a single analysis. Different spiked (1 microgram OA/g) or naturally-contaminated (mussel digestive gland: 2 micrograms OA/g; algae: 165 micrograms OA/g) matrices were tested. The recovery for OA varied from 55 to 95% according to the matrices. The IAC purification was then included as a step of a global [IAC/HPLC/spectrofluorimetric detection] method and the performance of the method was evaluated. Estimations of the linearity and the accuracy (percentages of the presumptive response for OA in the range +101% to +114%) were satisfactory in accordance with the method validation criteria.

Improvement on sample clean-up for high-performance liquid chromatographic-fluorimetric determination of diarrhetic shellfish toxins using 1-bromoacetylpyrene

Okadaic acid (OA) and dinophysistoxin-2, two of the main diarrhetic shellfish toxins, can be determined by high-performance liquid chromatography coupled to fluorimetry as pyrenacyl esters. Toxin fluorescent derivatives were obtained after quantitative derivatization with 1-bromoacetylpyrene in acetonitrile. An efficient improvement in the silica gel clean-up procedure of the pyrenacyl derivatives is reported. The clean-up cartridge is washed with hexane-dichloromethane (1:1, v/v), dichloromethane-ethyl acetate (8:2, v/v), and finally the pyrenacyl esters were eluted with dichloromethane-methanol (9:1, v/v). We compare this procedure with other methods already described. Good results were obtained with mussels, scallops and clams. The clean-up procedure showed good robustness when checked against silica and solvents activity. Using samples of mussel hepatopancreas with an OA concentration ranging from 0 to 2 micrograms OA/g hepatopancreas, the inter-assay relative standard deviation ranged from 5.5 to 12.6%.

Determination of okadaic acid by micellar electrokinetic chromatography with ultraviolet detection

Micellar electrokinetic chromatography (MEKC) with ultraviolet (UV) detection was applied for the determination of non-derivatized phycotoxins associated with diarrhoetic shellfish poisoning. A detection limit for 40 pg of okadaic acid (OA) was achieved. The UV intensities of this toxin measured at 200 nm showed good linearity in the range 40-640 pg. OA was detected in mussels spiked with 10 ng/g whole tissue. The presence of OA and dinophysistoxin-2 was observed in the crude extract of the dinoflagellate Prorocentrum lima.

High-performance liquid chromatographic methods for determination of marine biotoxins

Paralysing and diarrhetic shellfish poisonings (PSP and DSP) are important intoxications caused by the consumption of shellfish, mainly bivalve molluscs, contaminated by certain species of toxic dinoflagellates present in the marine phytoplankton. Their appearance and massive reproduction take place in some periods of the year, causing the phenomenon commonly known as 'red tide'. This causes significant problems to health and to the economy of the Galician region. The AOAC mouse bioassay is the most commonly used method of analysis for these toxic compounds, being the official method in most countries. Owing to the lack of sensitivity and selectivity of the biological assay, HPLC methods were developed as an alternative methodology. In this paper work carried out on the improvement of the chromatographic conditions in order to achieve accurate information about the PSP and DSP compounds present in the studied samples is reported.

Isolation of dinophysistoxin-2 and the high-performance liquid chromatographic analysis of diarrhetic shellfish toxins using derivatisation with 1-bromoacetylpyrene

The rare diarrhetic shellfish toxin, dinophysistoxin-2 (DTX-2), was isolated from the digestive glands of mussels (Mytilus edulis). This was achieved by chromatography on silica and Sephadex LH-20 followed by reversed-phase solid phase extraction and semi-preparative high-performance liquid chromatography (HPLC) with an Ultremex C18 column. Using 1-bromoacetylpyrene (BAP), as a precolumn derivatisation reagent, the diarrhetic shellfish toxins, okadaic acid (OA), dinophysistoxin-1 (DTX-1) and DTX-2, were determined by HPLC with fluorimetric detection. Derivatisation using BAP was compared with 9-anthryldiazomethane (ADAM) and, although the latter exhibited a four-fold better sensitivity, the BAP method gave fewer artefact peaks from reagent decomposition. The limits of detection of OA and DTX-2 were 0.4 ng on-column using BAP, which permits this method to be used for the regulatory control of these toxins in shellfish.

Automatic high-performance liquid chromatographic method for the determination of diarrhetic shellfish poison

A rapid HPLC method with fluorescence detection for the determination of okadaic acid (OA) and dinophysistoxin-1 (DTX-1) in mussels and mussel products is presented. For fluorescence labelling of OA and DTX-1, 9-anthryldiazomethane (ADAM) is used. HPLC with a column-switching system is proposed to avoid time-consuming clean-up procedures after derivatization of sample extracts with ADAM. The column-switching system as well as the chromatographic conditions and detection are described.

Applications of liquid chromatography-mass spectrometry interfacing systems in food analysis: pesticide, drug and toxic substance residues

This paper reviews applications of different LC-MS techniques for the determination of xenobiotic substances in foods. Specific examples of contaminants discussed are pesticides, herbicides, insecticides and drugs; concerning toxic substances, mycotoxins, phycotoxins, cyanobacterial toxins, mutagenic and heterocyclic amines and beta-carbolines, arsenic, tin and inorganic halogen compounds, packaging materials and various epoxy resins are considered. Advantages and limitations are outlined for the different LC-MS interfacing systems (particle beam, thermospray, atmospheric pressure ionization with electrospray, ionspray and heated pneumatic nebulizer). The impact of developments in instrumental analysis on methodology and the limitations of the various LC-MS methods are discussed. Further, the coupling of LC with element-selective detection systems such as inductively coupled plasma mass spectrometry is discussed, with emphasis on speciation of trace toxic elements in foods.

Two formats of enzyme immunoassay for the detection of saxitoxin and other paralytic shellfish poisoning toxins

A competitive direct enzyme-linked immunofiltration assay for the detection of saxitoxin was developed, using polyclonal antibodies against saxitoxin and a saxitoxin-horseradish peroxidase conjugate. The test was performed in an eight-well plastic test device, in which antibody-coated nylon membranes were pressed tightly to an absorbent cellulose layer. Saxitoxin standard or sample extract solution, saxitoxin-conjugate, and enzyme substrate/chromogen solution were sequentially added on to the membrane. The test was evaluated visually by comparing the intensity of the resulting coloured (blue) dot with that of a negative control. The detection limits for saxitoxin in buffer solution and in shellfish tissue were 4 ng/ml and 80 ng/g respectively, with an assay time of less than 15 min. Under the conditions of the immunofiltration assay, decarbamoyl-saxitoxin, gonyautoxin 2/3, and neosaxitoxin standards (in buffer) gave a positive response at concentrations of about 10 ng/ml, 40 ng/ml, and 80 ng/ml, respectively. The relative cross-reactivity of the antibody to these PSPs was similar when determined using both direct and indirect (using a saxitoxin-bovine serum albumin conjugate) competitive enzyme immunoassays in microtitre plate format. In competitive direct microtitre plate assays, the 50% binding values found for saxitoxin, decarbamoyl-saxitoxin, gonyautoxin 2/3 and neosaxitoxin were 15 pg/ml, 47.5 pg/ml, 163.5 pg/ml, and 510 pg/ml respectively. In competitive indirect microtitre assay, the respective values were 138 pg/ml, 404 pg/ml, 1582 pg/ml, and 6982 pg/ml.

Investigation of derivatization reagents for the analysis of diarrhetic shellfish poisoning toxins by liquid chromatography with fluorescence detection

Several derivatization reagents for the conversion of okadaic acid and related DSP toxins to fluorescent derivatives for analysis by liquid chromatography have been examined, viz: 9-anthryldiazomethane (ADAM), 1-pyrenyldiazomethane (PDAM), 4-diazomethyl-7-methoxycoumarin (DMMC), 4-bromomethyl-7-methoxycoumarin (BrMMC), 4-bromomethyl-7,8-benzcoumarin (BrMBC), 4-bromomethyl-7-acetoxycoumarin (BrMAC), and 4-bromomethyl-6,7-dimethoxycoumarin (BrDMC). The ADAM reagent provides the greatest selectivity and sensitivity, but its application on a routine basis has been limited by its instability and cost. Improvement of this method was achieved through the production of ADAM in situ from the stable 9-anthraldehyde hydrazone. A detection limit of 30 ng/g hepatopancreas (equivalent to 6 ng/g whole tissue) was achieved. The other aryldiazomethane reagents were found to have insufficient reactivity. Of the bromomethylcoumarin reagents, BrDMC was found to have the greatest promise. The reagent is inexpensive and has excellent stability and purity. Quantitative derivatization may be achieved in a 2 hour reaction at 45 degrees C with N,N-diisopropylethylamine as a catalyst. Unfortunately, the lower reaction selectivity of BrDMC compared to that of ADAM limits its application to isolated toxins, plankton samples, and shellfish tissues with high levels of DSP toxins. The use of BrDMC for the determination of how toxin levels in shellfish tissues will require development of a more extensive clean-up prior to derivatization. Successful application of the ADAM and coumarin derivatization methods to real-world samples has been demonstrated.