The aim of this work was to develop an immunoassay-based lateral flow dipstick for the rapid detection of aflatoxin B(1) in pig feed. The test consisted of three main components: conjugate pad, membrane, and absorbent pad. The membrane was coated with two capture reagents, that is, aflatoxin B(1)-bovine serum albumin conjugate and rabbit anti-mouse antibodies. The detector reagent consisted of colloidal gold particles coated with affinity-purified monoclonal anti-aflatoxin B(1) antibodies, which saturated the conjugate pad. A comparison of several extraction methods for the pig feed matrix is presented. A mixture of methanol/water (80:20, v/v) gave the best recoveries. After sample extraction and dilution, the dipstick was put in the sample solution at the conjugate pad side and developed for 10 min. Analyte present in the sample competed with the aflatoxin B(1) immobilized on the membrane for binding to the limited amount of antibodies in the detector reagent. Thus, the line color intensity of an aflatoxin B(1)-positive dipstick is visually distinguishable from that of an aflatoxin B(1)-negative sample. The visual detection limit for aflatoxin B(1) is 5 microg/kg. The major advantages of this one-step striptest are that results can be obtained within 10 min and that all reagents are immobilized on the lateral flow dipstick.

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Ochratoxin A is a common feed contaminant, which may impair animal health and may lead to residues in edible tissues of slaughter animals. To simulate field conditions, broiler chicks were exposed to a total of 0.5 mg ochratoxin A per week for each of 4 weeks. Plasma toxin levels and tissue residues were measured by high-performance liquid chromatography (HPLC) and microplate enzyme-linked immunosorbent assay (ELISA). Results indicate an accumulation in plasma and wide distribution into all organs, with high levels in the liver and the kidney. Microscopical changes that could primarily be associated with toxin exposure were glomerulonephrosis, tubulonephrosis, focal tubular epithelial cell proliferation and multiple, adenoma-like structures in the renal parenchyma. The HPLC and ELISA methods gave similar results for both tissue distribution and depletion. Differences in absolute tissue toxin concentrations obtained by the two methods might be attributed to the different extraction and clean-up procedures, along with antibody specificity. The findings indicate that the dose applied causes subclinical tissue lesions and measurable tissue residues.

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A direct, competitive enzyme-linked immunosorbent assay (ELISA) with monoclonal antibody has been developed for quantitative determination of ochratoxin A (OA) in different cereals. A dichloromethane/citric acid mixture was used for extraction of cereals. This cleanup procedure proved to be as effective for ochratoxin A extraction as protocols using strong acids. The mean withinassay and interassay coefficients of variation for the standard curve was <10%. The range of this test is 1-10 ng/g, with a detection limit of 0.5 ng/g OA. The toxin recovery from cereals infected with 5-100 ng/mL OA varied between 90 and 130%.

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A membrane-based flow-through enzyme immunoassay (patent application pending) for the detection of ochratoxin A (OA) in roasted coffee was developed. First, an extraction and solid-phase cleanup method was developed. A high partition coefficient for OA in the mobile phase was achieved by using methanol/5% aqueous NaHCO(3) as the sample extraction and cleanup solvent. The solid-phase (aminopropyl) cleanup was developed to chromatographically elute OA but retain cross-reacting compounds. Without using aminopropyl cleanup, cross-reacting compounds resulted in 100% false positives for both flow-through enzyme immunoassay and HPLC methods. However, after cleanup with aminopropyl, no false positives were observed. The flow-through results were visually evaluated. The sensitivity achieved for the flow-through was 4 microg kg(-1) in spiked roasted coffee. The assay was used to screen roasted coffee samples. Results were confirmed with HPLC with a detection limit of 1 microg kg(-1).