Dioxin contamination in food. Bayreuth, Germany, from September 28 to October 1, 2000.

Dioxin and PCB monitoring programs for food and feeding stuff in most countries of the world, including many European Countries are currently inadequate. Better control of food production lines and food processing procedures is needed to minimize entry of dioxin to the food chain and will help to avoid dioxin contamination accidents. This would also improve the ability to trace back a possible contamination to its source. European guidelines for monitoring programs should be established to ensure comparable and meaningful results. These guidelines should define the minimum requirements for the design of monitoring programs, analytical methods, and quality assurance. Though data from Northern Europe shows that the general population exposure to dioxin and PCB has decreased during the last ten years these compounds continue to be a risk of accidental contamination of the food chain. The most prominent recent example is the Belgian dioxin contamination of feeding stuff in 1999. The Belgian dioxin contamination was not detected due to dioxin monitoring programs but by their direct biological effects seen in animals. Four other cases of dioxin contamination have been detected in Europe since 1997 due to local monitoring programs. One of them (citrus pulp pellets 1998) was in a much larger scale than the Belgian dioxin contamination. The general population's exposure to dioxins and PCBs is still in the same range (1-4 pg WHO-TEQ/kg body weight and day) as the recently revised WHO tolerable daily intake (TDI). There is concern that short-term high level exposure to dioxins, furans, and PCB may cause biological effects on the human fetal development and further research is required. Further actions to control sources building on considerable advances already made in many countries may need to be supplemented by measures to prevent direct contamination of feeding stuff or food to reduce general population exposure further.

Levels of toxaphene congeners in fish from Danish waters.

The levels of toxaphene congeners, in addition to PCB congeners and organochlorine pesticides, were determined in various fish samples from different Danish waters. While PCB-153 and p,p'-DDE show different levels depending on the fishing area, with highest levels in fish from the Western Baltic Sea, toxaphene was detected in all the samples investigated at a more constant level. The distribution of the three toxaphene congeners Parlar #26, #50 and #62 depends on the fishing area, with the Western Baltic Sea being different from the other waters by having almost equal levels of toxaphene congeners #26 and #50.

Direct determination of copper and iodine in milk and milk powder in alkaline solution by flow injection inductively coupled plasma mass spectrometry.

The development and evaluation of a flow injection inductively coupled plasma mass spectrometric (FI-ICP-MS) method for the determination of copper and iodine in milk and milk powder has been described. The sample preparation is based simply on the dilution of the sample by an alkaline solution containing 0.05 mol/l potassium hydroxide and 0.07 mol/l tetramethylammonium hydroxide. Possible matrix interferences on the determination of copper were alleviated by the use of standard addition calibration. Detection limits (3s) were 0.94 microg l(-1) and 0.45 microg l(-1) for copper and iodine, respectively. Four different certified milk powder reference materials were analysed and the concentrations found were in a good agreement with the certified values indicating that the method is unbiased. Due to the simplicity of the method a high sample throughput is possible, approximately 90 samples can be analysed in one day. More than 100 samples of Danish raw milk were analysed and median values of 0.050 mg kg(-1) of Cu and 0.084 mg kg(-1) of I were found.

Mutagenic metabolites in rat urine after dermal exposure to 1,3-diaminobenzene.

Amberlite XAD-2 purified urine extracts from rats treated dermally with 1,3-diaminobenzene were fractionated by HPLC and the metabolites were identified by GC-MS. Mutagenic activity in Salmonella typhimurium TA 98 was equally distributed between the two fractions, none of which contained the parent amine. The first fraction, eluted between 2-7 minutes, contained only a very small amount of presently unidentified metabolites, while the second fraction eluted between 14-19 minutes contained N,N'-diacetyl-1,3-diaminobenzene. Both fractions showed minor, but still significant activity even without metabolic activation. A non-mutagenic fraction, eluted between 10-12 minutes contained N-acetyl -acetyl-1,3-diaminobenzene and N,N'-diacetyl-2,4-diaminophenol.