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On September 9th, 2002, two goods trains collided in Bad Münder, Lower Saxony, causing the release of more than 40 metric tonnes of epichlorohydrin (1-chloro-2,3-epoxypropane) into the environment. A human biomonitoring study was performed to evaluate the accidental exposure to epichlorohydrin and to assess the possible long-term, i.e. carcinogenic health effects. This was done on the basis of a biochemical effect monitoring using the N -(3-chloro-2-hydroxypropyl)valine and the N -(2,3-dihydroxypropyl)valine haemoglobin adducts of epichlorohydrin in blood to respond to missing ambient monitoring immediately after the crash. N -(3-chloro-2-hydroxypropyl)valine adduct levels above the LOQ (25 pmol/g globin) ranged from 32.0 to 116.4 pmol/g globin in 6 out of 628 samples. The N -(2,3-dihydroxypropyl)valine adduct was not detected above the LOD (10 pmol/g globin) in any of the blood samples. Based on the quantified N -(3-chloro-2-hydroxypropyl)valine adduct values, the body doses after two days of exposure were estimated to be in the range of 1.7–6.2 nmol/kg body weight. The reverse estimation of the external exposure leads to cumulative additional lifetime cancer risks ranging from 2.61 × 10 −8 to 9.48 × 10 −8 . The estimated excess lifetime cancer risks have to be assessed as extremely low. Our biomonitoring study facilitated the dialogue between individuals and groups concerned and authorities, because suspected or occurred exposures and risks to human health could be quantified and interpreted in a sound manner. [ABSTRACT FROM AUTHOR]

Arsenic is a human carcinogen that occurs ubiquitously in soil and water. Based on epidemiological studies, a benchmark dose (lower/higher bound estimate) between 0.3 and 8 μg/kg bw/day was estimated to cause a 1 % increased risk of lung, skin and bladder cancer. A recently published study by EFSA on dietary exposure to inorganic arsenic in the European population reported 95th percentiles (lower bound min to upper bound max) for different age groups in the same range as the benchmark dose. For toddlers, a highly exposed group, the highest values ranged between 0.61 and 2.09 µg arsenic/kg bw/day. For all other age classes, the margin of exposure is also small. This scenario calls for regulatory action to reduce arsenic exposure. One priority measure should be to reduce arsenic in food categories that contribute most to exposure. In the EFSA study the food categories 'milk and dairy products,' 'drinking water' and 'food for infants' represent major sources of inorganic arsenic for infants and also rice is an important source. Long-term strategies are required to reduce inorganic arsenic in these food groups. The reduced consumption of rice and rice products which has been recommended may be helpful for a minority of individuals consuming unusually high amounts of rice. However, it is only of limited value for the general European population, because the food categories 'grain-based processed products (non rice-based)' or 'milk and dairy products' contribute more to the exposure with inorganic arsenic than the food category 'rice.' A balanced regulatory activity focusing on the most relevant food categories is required. In conclusion, exposure to inorganic arsenic represents a risk to the health of the European population, particularly to young children. Regulatory measures to reduce exposure are urgently required. [ABSTRACT FROM AUTHOR]