A highly sensitive enzyme immunoassay is described for the detection of atrazine residues in water. Atrazine derivative was conjugated to Bovine Serum Albumin (BSA) to obtain an immunizing antigen and to Horseradish Peroxidase enzyme (POD) to obtain a marker for immunoassay. The formation of these conjugations was confirmed by UV spectroscopy as well as by gel-electrophoresis. Polyclonal antibodies were raised in rabbits by immunization with an atrazine-BSA conjugate containing 29 atrazine residues per BSA molecule. An ELISA on microtitration plates was optimized with peroxidase-atrazine conjugate. The middle of the test (50% B/Bo) was found to be at 90 ng/l, which is well below the maximum concentration permitted by the EC guidelines for drinking water. Detection limits for atrazine of about 1 ng/l could be reached. The assay did not require concentration or cleanup steps for drinking or ground water samples. Validation experiments showed good accuracy and precision. No cross-reactivities were shown by other s-triazines like terbutryn, ametryn, terbuthylazine, des-isopropylatrazine, and de-ethylatrazine except hydroxyatrazine. The latter was present at very low levels that can be calibrated/standardized before analysis or it may be considered as leftover residues of atrazine. Based on these results, it is suggested that this test can be applied to obtain fairly accurate results for atrazine concentration in water samples from different sources.
In-house developed ELISA was standardized to monitor atrazine residues in different environmental samples. The standard curve was linear, indicating an increase in log concentration with decrease in absorbance (%B/B(0)=1.075-0.042 Log C; r= -0.966). The middle of the test was at 75 ng/L and the lowest detection limit at 4 ng/L. ELISA significantly correlated with the high performance liquid chromatography (HPLC) (r=0.990). Internal validation showed good accuracy and precision. Maximum atrazine residues were present in Jehlum River water/sediments and maize/sugarcane plant roots. Most of the food samples were found to be contaminated. ELISA required less clean-up steps than HPLC, but showed matrix effect in soil/colored extracts.
A dipstick format was developed for on-site atrazine monitoring in water samples of different origins. It was derived from an in-house-developed ELISA based on polyclonal antibodies that also cross-react with hydroxyatrazine (30%) and terbuthylazine (17%). Test reagents were evaluated for temperature and pH stabilities and rapidity for field applications. Reagents performed well within a temperature range of 20-30°C and were tolerant to alkaline pH (up to 8.5) of the assay buffering system. Tracer incubation time could be reduced to 40 min. Bovine serum albumin addition (1%) in the assay buffer improved assay performance, giving 50% B/B0 (IC50) of 65 ng/L and the lowest LOD of 2 ng/L at 90 B/B0 (IC10). The dipstick ELISA format was standardized on a membrane support. Nylon membrane, positively charged, was superior to PVDF for qualitative or semiquantitative analysis regarding color intensity and stability. Tracer incubation time was further reduced to 30 min with a lowest LOD of 0.1 µg/L. For real sample screening with dipsticks, acceptable results were obtained for water. Significant correlation was found between dipstick and plate ELISA results. Validation using GC with a nitrogen-phosphorus detector and HPLC indicated that dipstick signals in aged water samples, which were mainly due to hydroxyatrazine, were significantly above European Commission regulations of 0.1 µg/L. However, dipsticks were superior, fast, and cost-effective.
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