Environmental risk assessment of musk ketone and musk xylene in The Netherlands in accordance with the EU-TGD.

An environmental risk assessment has been carried out for musk ketone and musk xylene according to the EU Technical Guidance Document for Environmental Risk Assessment for New and Existing Substances [1]. Musk ketone and musk xylene are used in fragrances for cosmetics and household products. For the fragrance industry these are important fragrance ingredients because of their excellent substantivity as well as for their unique smell, which determines largely the odor of a product. The initial environmental risk assessment is based on information provided by the fragrance industry as represented in the Netherlands by its association NEA, by the Research Institute for Fragrance Materials (RIFM) and data reported in the international open literature. The risk assessment includes and evaluation of the risks for aquatic organisms in surface water and sediment and for soil organisms in soil after application of sewage sludge. Secondary poisoning of fish-eating birds and mammals is considered as well. For each compartment the Predicted Environmental Concentration (PEC) is compared to the Predicted No Effect Concentration (PNEC) to obtain PEC/PNEC ratios. Since monitoring data are available in water, sediment and fish, similar ratios are obtained with measured concentrations instead of the predicted ones. For both substances, PEC/PNEC ratios are at or below 0.1 for organisms in the aquatic environment, including sediment organisms. PEC/PNEC ratios for fish-eating predators are 0.01. Ratios based on monitoring data are below 0.01 for all of these organisms. For soil organisms the PEC/PNEC ratio is 0.5 for musk ketone and 1.3 for musk xylene. Although in the Netherlands (as well as in some other European countries), sewage sludge presently finds no application as fertilizer on agricultural soil, the aim of environmental policy is to upgrade the sludge quality to enable future applications on agricultural and grassland. The reliability of the predicted soil concentrations can be greatly improved by obtaining experimental data on fate and behaviour of musk ketone and musk xylene in digested sludge and soil. The risk assessment provides reassurance for the aquatic compartment while pointing the way for obtaining additional data for the soil compartment.

Lethal body burden of triphenyltin chloride in fish: preliminary results.

1. Guppies exposed to several triphenyltin chloride (TPTC) concentrations in water died as soon as a body burden of 20 +/- 10 nmol/g fish was reached. 2. Accumulation of TPTC during exposure in acute toxicity experiments can be predicted by using the kinetic parameters of TPTC. 3. The lethal body burden is two orders of magnitude lower than for narcotic organic compounds such as chlorobenzenes.

Neural and non-neural acetylcholine in the rat diaphragm.

The compartmentation of acetylcholine (ACh) and of choline acetyltransferase in the rat diaphragm was analysed by measuring their contents in muscle segments containing endplates (e.p.) and endplate-free segments (non-e.p.) at different times following section of the phrenic nerve. In addition ACh release was determined before and after denervation. Freshly dissected hemidiaphragms contained about 125 pmol of ACh; more than 90% of this was localized in the e.p. portion. Between 10 and 18 h after denervation the ACh content of the e.p. portion decreased by 80% and its ACh concentration became approximately equal to that in the non-e.p. region, whose ACh content did not change. Spontaneous release of ACh was reduced by denervation and ACh release evoked by 50 mM KC1 was practically abolished. Choline acetyltransferase activity in freshly dissected preparations was about 30 nmol of ACh per gram per hour, Km 0.5 mM. About 65% of the enzyme disappeared in the first 24 h and the remaining 35% between 24 and 50 h after denervation. A different enzyme capable of ACh synthesis was found in the muscle fibres; its activity did not decrease after denervation. It is concluded that about 70% of the ACh in the diaphragm is contained in the motor nerve terminals, about 10% in the intramuscular nerve fibres and the remainder in the muscle fibres, and that about 65% of choline acetyltransferase is in the motor terminals and 35% in the nerve fibres.