Zeranol, a semi-synthetic oestrogenic growth promoter, was banned in the EU in 1988. The ability of Member States to police the ban on zeranol has been hampered by suggestions from New Zealand and from this laboratory that zeranol may be formed by the in vivo metabolism of naturally occurring Fusarium spp. toxins. The present study demonstrates that zeranol is formed from alpha-zearalenol and zearalenone in vivo and is detected in bovine bile following the oral administration of these compounds. However, it is not detected following administration of beta-zearalenol. These data suggest that hydrogenation of alpha-zearalenol, probably in the rumen, is responsible for the appearance of zeranol. The present study shows that environmental contamination with Fusarium spp. toxins is widespread in Northern Ireland. Fusarium spp. toxins were present in 32% (n = 422) of all bovine bile samples tested for zeranol during 1995. Zeranol itself was confirmed in 6.6% (n = 28) of the samples. However, the mean alpha-zearalenol and beta-zearalenol concentrations in the bile of zeranol-positive animals were 12 and 9 times higher, respectively, than those in the zeranol-negative animals. The alpha-zearalenol concentration always exceeded the zeranol concentration by at least 5:1. This may, in the future, permit differentiation between zeranol abuse and natural contamination.

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In this study, a version of the "quick, easy, cheap, effective, rugged, and safe" (QuEChERS) method was modified to use ethyl acetate (EtOAc) rather than acetonitrile (MeCN) for extraction in the determination of multiple pesticide residues in fruits and vegetables. EtOAc is better suited than MeCN for gas chromatographic (GC) analysis with electron capture detection (ECD) and nitrogen-phosphorus detection (NPD). The method entailed extraction of 30 g chopped sample plus 5 g NaHCO(3) and 30 g anhydrous Na(2)SO(4) with 60 mL EtOAc using a probe blender. After a centrifugation step, removal of residual water and cleanup were performed using dispersive solid-phase extraction (dispersive-SPE) with MgSO(4) and primary secondary amine (PSA) sorbent. (14)C-labeled chlorpyrifos with liquid scintillation counting was used to assist in optimizing and characterizing the method, and GC-ECD and GC-NPD were used for analysis of 24 selected pesticides. The method was validated using tomato, apple and frozen green bean matrices spiked at 0.05, 0.5, and 5 mg/kg. For 22 of the analytes, recoveries averaged 93% for all three commodities over the validation range with a relative standard deviation of 10% (n = 1182). Lower recoveries of dichlorvos were obtained with the method and iprodione determination was compromised in the green beans by an interfering peak. Typical limits of detection were 0.005-0.01 mg/kg with the method.