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CYP 450 enzyme induction by chronic oral musk xylene in adult and developing rats.

Developmental and adult toxicity of musk xylene was studied in Long Evans (LE) rats fed with chow containing musk xylene (MX) in food pellets in concentrations of 1 mg, 10 mg, 33 mg, 100 mg and 1000 mg MX per 1 kg chow corresponding to a daily intake of 0.07-0.08 mg MX/kg up to 70-80 mg MX/kg body weight. Adult male and female rats were MX exposed for a minimum of 10 weeks before mating. Exposure continued throughout pregnancy, birth and lactation. The effects of MX on CYP1A1/1A2 were studied in liver microsomes by EROD (7-ethoxyresorufin-rosomes deethylase) for CYP1A1 and by MROD (methoxyresorufin-o-demethylase) for CYP1A2 activity and by Western blotting. MX induced these enzymes dose dependently in adult and developing rats at PN (postnatal day) 1 and 14. The lowest effective maternal dose was 2-3 mg MX/kg/day. Western blot data of CYP2B and CYP3A indicated the induction of both P450 enzyme proteins in developing rats at PN 14 at the higher dose of 70-80 mg MX/kg/day. In contrast, upon high MX exposure CYP2B but not CYP3A was found to be induced in adult first generation male and female rats, indicating differential sensitivity to MX in development.

Administration, Oral↗

Dermal absorption and disposition of musk ambrette, musk ketone and musk xylene in human subjects.

Musk ambrette, musk ketone and musk xylene have a long history of use as fragrance ingredients, although musk ambrette is no longer used in fragrances. As part of the review of the safety of these uses, it is important to consider the systemic exposure that results from these uses. Since the primary route of exposure to fragrances is on the skin, dermal doses of carbon-14 labelled musk ambrette, musk ketone and musk xylene were applied to the backs (100 cm2) of healthy human volunteers (two to three subjects) at a nominal dose level of 10-20 microg/cm2 and excess material removed at 6 h. Means of 2.0% musk ambrette, 0.5% musk ketone and 0.3% musk xylene were absorbed based on the amounts excreted in urine and faeces during 5 days. Most of the material was excreted in the urine with less than 10% of the amount excreted being found in faeces. No radioactivity was detected in any plasma sample, consistent with low absorption, and no radioactivity was detected (<0.02% dose) in skin strips taken at 120 h. Analysis of urine samples indicated that all three compounds were excreted mainly as single glucuronide conjugates. The aglycones were chromatographically different, but of similar polarity, to the major rat metabolites excreted in bile also as glucuronides.

Adult↗

Genotoxicity of nitro musks in the micronucleus test with human lymphocytes in vitro and the human hepatoma cell line Hep G2.

The nitro musk compounds musk xylene (1-tert.-butyl-3,5-dimethyl-2,4,6-trinitrobenzene), musk ketone (4-tert.-butyl-3,5-dinitro-2,6-dimethylacetophenone), musk ambrette (1-tert.-butyl-4-methyl-6-methoxy-3,5-dinitrobenzene), musk moskene (1,1,3,3,5-pentamethyl-4,6-dinitroindane) and musk tibetene (1-tert.-butyl-3,4,5-trimethyl-2,6-dinitrobenzene) were tested for their genotoxic activity in the micronucleus test (MN) with human lymphocytes in vitro and the human hepatoma cell line Hep G2. Compound concentrations were employed up to cytotoxic doses. Musk xylene, musk ketone, musk ambrette, musk moskene and musk tibetene revealed no genotoxicity in the micronucleus test with human lymphocytes and with the human hepatoma cell line Hep G2.

Adult↗

Testing of SOS induction of artificial polycyclic musk fragrances in E. coli PQ37 (SOS chromotest).

Synthetic fragrances are widespread in the environment. Residues were found in animals, human tissues and breast milk. Therefore, six artificial polycyclic musk fragrances--Galaxolide, Tonalide, Celestolide, Phantolide, Cashmeran and Traseolide--were tested for SOS induction using the Escherichia coli PQ37 genotoxicity assay (SOS chromotest) in the presence (+S9) and absence (-S9) of an exogenous metabolizing system. All compounds tested exhibited no SOS inducing potency with the SOS chromotest. These results could be rated as one indicator of the biological inactivity of this group of compounds with respect to genotoxicity.

Alkaline Phosphatase↗

Toxicity of nitromusks in early lifestages of South African clawed frog (Xenopus laevis) and zebrafish (Danio rerio).

Musk xylene (MX), musk ketone (MK) and musk moskene (MM) are synthetic nitro-containing fragrances. Due to their inherent lipophilicity and environmental persistence, they are frequently detected in environmental samples and especially in aquatic ecosystems. Despite this, the current environmental toxicity database of nitromusks is limited. Although nitromusks have been shown to accumulate in aquatic organisms, little is known about their potential developmental effects in the respective aquatic species. To investigate the developmental toxicity of these compounds to amphibians and fish, early lifestages of xenopus (Xenopus laevis) and zebrafish (Danio rerio) were exposed to three nitromusks for 96 h to examine the developmental effects of these compounds in the two species. Nitromusk body concentration measurements were carried out in parallel for correlation with potential developmental effects. No increased mortality, malformation or growth inhibition was observed in either species following 96-h exposure to 400 microg/l MX, MK and MM. However, an approximately 20% reduced viability was observed in xenopus larvae when exposed to 400 microg/l MX, MK and MM for 11 days. Xenopus and zebrafish exposed to 10, 153, 871 and 1637 microg/l 14C-MX for 96 h resulted in whole-body concentrations of 0.7 +/- 0.1, 11.1 +/- 1.1, 38.7 +/- 1.9 and 76.3 +/- 18.3 microg/g, and 4.3 +/- 0.6, 73.3 +/- 11.8, 440.0 +/- 72.7 and 664.0 +/- 47.7 microg/g wet body weight, respectively. Exposure of xenopus larvae to 400 microg/l MX, MK and MM for 11 days, resulted in whole body concentrations (extrapolated from gas chromatographic determinations) of 4700 +/- 5000, 1300 + 300 and 4600 + 4800 microg/g wet weight for MX, MK and MM, respectively. The latter toxicity results, in conjunction with the fact that the concentrations used for the above experiments were between 400- and 10000-fold higher than those detected in the environment, suggest that environmental concentrations of nitromusks are not hazardous for early lifestages of fish and amphibians.

Abnormalities, Drug-Induced↗

Interactions of nitromusk parent compounds and their amino-metabolites with the estrogen receptors of rainbow trout (Oncorhynchus mykiss) and the South African clawed frog (Xenopus laevis).

Nitromusks, musk xylene (MX), musk ketone (MK) and musk moskene (MM) are synthetic fragrances. 4-Amino-MX (4X), 2-amino-MX (2X) and 2-amino-MK (2K) are nitromusk metabolites formed during the sewage treatment process and have been detected in effluent and surface water at concentrations four to 40 times higher than their parent compounds. To date, data to the aquatic toxicity of nitromusk compounds are limited to the parent compounds and the determination of acute and subacute effects in aquatic organisms. No data are available regarding the potential endocrine modulating effects of these compounds and/or their metabolites in aquatic organisms. Therefore, the competitive binding capability of nitromusks and their metabolites to the estrogen receptors (ER) in rainbow trout and xenopus was investigated. No binding of MX, MK and MM to the ER of either species was observed. In contrast, binding to the ER was observed for 4X, 2X and 2K in both species. The IC50 (competitive binding at the ER) of 2X in rainbow trout was 1.3 +/- 1.1 mM. In contrast, 4X, 2X and 2K bound to the xenopus ER with an IC50 of 30.8 +/- 28.5, 12.9 +/- 10.3 and 70.1 +/- 88.3 microM, respectively.

Animals↗

Environmental risk assessment for the polycyclic musks AHTN and HHCB in the EU. I. Fate and exposure assessment.

For the environmental exposure assessment of the fragrance ingredients 7-acetyl-1,1,3,4,4,6-hexamethyl-1,2,3,4-tetrahydronaphthalene (AHTN) and 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethylcyclopenta-gamma-2-ben zopyran (HHCB) the following properties were determined: vapour pressure 0.0682 and 0.0727 Pa; water solubility 1.25 and 1.75 mg/l; log K(ow) 5.7 and 5.9; log K(oc) 4.80 and 4.86; bioconcentration factor in fish: 597 and 1584 (fresh weight) for AHTN and HHCB, respectively. Both substances are degraded to more polar metabolites in fish, in soil and during sewage treatment. A review is made of concentrations measured in sludge, in freshwater and marine systems including suspended matter, sediment and fish. The 90th-percentile in more than 200 surface water samples is 0.3 microg/l for AHTN and 0.5 microg/l for HHCB. The 90th-percentile of the concentrations in fish is 0.12 mg/kg fresh weight for both substances (n = 27). These concentrations are lower by a factor of 5-15 than predicted on the basis of the yearly use volumes in Europe, 585 tonnes for AHTN and 1482 tonnes for HHCB. Concentrations in sludge-amended soils and in earthworms are predicted based on concentrations measured in sludge. For AHTN, the predicted values are: PECsoil, 0.029 mg/kg and PECworm, 0.065 mg/kg while for HHCB the corresponding figures are 0.032 and 0.099 mg/kg. These concentrations assume a biodegradation half-life in the soil of 180 days based on preliminary soil biodegradation data.

Animals↗

Environmental risk assessment for the polycyclic musks, AHTN and HHCB. II. Effect assessment and risk characterisation.

Reports of the polycyclic musks AHTN and HHCB in surface water and fish, primarily in Europe, have prompted studies of their environmental effects. These effects then are used, along with the predicted environmental concentrations in a risk assessment according to the approach developed under European Union Regulation 793/93, in line with the Technical Guidance Document for risk assessment of new and existing chemicals. In 72-h studies with algae (Pseudokirchneriella subcapitata), NOECs were 0.374 mg/l (AHTN) and 0.201 mg/l (HHCB). In 21-day reproductive tests with daphnia (Daphnia magna) NOECs were 0.196 (AHTN) and 0.111 mg/l (HHCB). In 21-day growth tests with bluegill sunfish (Lepomis macrochirus), NOECs were 0.067 (AHTN) and 0.068 mg/l (HHCB). And, finally 35-day early life stage tests with fathead minnows (Pimephales promelas) resulted in NOECs of 0.035 (AHTN) and 0.068 mg/l (HHCB). These results lead to Predicted No Effect Concentrations (PNEC) of 3.5 microg/l (AHTN) and 6.8 microg/l (HHCB) for aquatic organisms. For the soil compartment, 8-week studies with earthworms (Eisenia fetida) resulted in NOECs of 105 (AHTN) and 45 mg/kg (HHCB) and 4-week studies with springtails (Folsomia candida) resulted in a NOECs of 45 mg/kg for both substances. These values lead to a PNEC of 0.32 mg/kg dw for both materials. Using mammalian studies, PNECs for fish or worm eating predators of 10 mg/kg fw (AHTN) and 100 mg/kg fw (HHCB) can be derived. For sediment dwelling organisms, PNECs were derived by equilibrium partitioning using the aquatic PNECs. Comparing PNECs with the measured or predicted environmental exposures leads to risk characterisation ratios as follows: aquatic species: AHTN 0.086, HHCB 0.074; sediment organisms: AHTN 0.44, HHCB 0.064; soil organisms: AHTN 0.091, HHCB 0.10; fish eating predators: AHTN 0.012, HHCB 0.001; worm eating predators: AHTN 0.007, HHCB 0.001.

Animals↗

Dermal absorption and disposition of musk ambrette, musk ketone and musk xylene in rats.

Dermal doses of carbon-14 labelled musk ambrette (MA), musk ketone (MK) or musk xylene (MX) to male Sprague-Dawley CD rats were applied at a nominal dose level of 0.5 mg/kg (11 microg/cm2 of skin) and excess material removed at 6 h. Means of about 40, 31 and 19% of the applied doses of MA, MK and MX, respectively, were absorbed. Most of the absorbed material was excreted within 5 days with only 1-2% of the applied dose remaining in the animal at this time. Tissue concentrations of radiolabel were similar for all three compounds with peak concentrations occurring at 6-8 h. In general, fat and liver contained the highest concentrations at around 0.2 microg nitromusk equivalents/g but concentrations in fat declined fairly rapidly to around 0.005 microg equiv./g at 120 h. Most of the absorbed dose was eliminated in bile mainly in the form of polar conjugated metabolites. Structural characterisation of the major aglycones for MA and MX indicated that they were hydroxylated analogues formed by oxidation of the ring methyl. Repeated daily dosing for 14 days resulted in little bioaccumulation for musk xylene and accumulation of about three-fold for musk ketone.

Animals↗

Effects of musk xylene and musk ketone on rat hepatic cytochrome P450 enzymes.

The purpose of the present work was to characterize the effect of musk xylene (MX) and musk ketone (MK) treatment on rat hepatic cytochrome P450 enzymes. Male F344 rats were dosed orally with MX (10, 50 or 200 mg/kg) or MK (20, 100 or 200 mg/kg) for 7 days, after which CYP1A, 2B and 3A enzyme activities and protein levels were determined. MX treatment resulted in a two- to four-fold increase in the activity of CYP1A, 2B and 3A enzymes. For CYP1A and 3A, these changes were consistent with small increases in immunoreactive proteins. However, for CYP2B, despite only a three-fold increase in enzyme activity, protein levels were increased nearly 50-fold relative to control. This induction occurred by transcriptional activation of the CYP2B1 gene as evidenced by increased steady state CYP2B1 mRNA levels. In contrast to MX, MK treatment increased CYP2B activity, protein and mRNA levels. However MK treatment also increased CYP1A enzyme activity nearly 30-fold higher than control rats, a profile that was markedly different from MX, and very different from its effects in mice (Stuard, S.B., Caudill, D., Lehman-Mc-Keeman, L.D., 1997. Characterization of the effects of musk ketone on mouse cytochrome P450 enzymes. Fund. Appl. Toxicol. 40, 264-271). These results indicate that in rats, MX is an inducer of CYP2B enzymes, but these enzymes are not functionally active. In contrast, MK also induces CYP2B enzymes, with no concurrent inactivation. MK also exhibits a unique pattern of cytochrome P450 induction by increasing both CYP1A and CYP2B in rats.

Animals↗

CYP 450 enzyme induction by chronic oral musk xylene in adult and developing rats.

Developmental and adult toxicity of musk xylene was studied in Long Evans (LE) rats fed with chow containing musk xylene (MX) in food pellets in concentrations of 1 mg, 10 mg, 33 mg, 100 mg and 1000 mg MX per 1 kg chow corresponding to a daily intake of 0.07-0.08 mg MX/kg up to 70-80 mg MX/kg body weight. Adult male and female rats were MX exposed for a minimum of 10 weeks before mating. Exposure continued throughout pregnancy, birth and lactation. The effects of MX on CYP1A1/1A2 were studied in liver microsomes by EROD (7-ethoxyresorufin-o-deethylase) for CYP1A1 and by MROD (methoxyresorufin-o-demethylase) for CYP1A2 activity and by Western blotting. MX induced these enzymes dose dependently in adult and developing rats at PN (postnatal day) 1 and 14. The lowest effective maternal dose was 2-3 mg MX/kg/day. Western blot data of CYP2B and CYP3A indicated the induction of both P450 enzyme proteins in developing rats at PN 14 at the higher dose of 70-80 mg MX/kg/day. In contrast, upon high MX exposure CYP2B but not CYP3A was found to be induced in adult first generation male and female rats, indicating differential sensitivity to MX in development.

Administration, Oral↗

The systemic exposure to the polycyclic musks, AHTN and HHCB, under conditions of use as fragrance ingredients: evidence of lack of complete absorption from a skin reservoir.

7-Acetyl-1,1,3,4,4,6-hexamethyl-1,2,3,4-tetrahydronaphthalene (AHTN) and 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexa-methylcyclopenta-gamma-2-be nzopyran (HHCB) are two large volume fragrance ingredients widely used in consumer products. As part of the risk evaluation, the systemic exposures to these materials was determined in rats under occlusion and in humans under simulated conditions of exposure. Ring 14C-labeled AHTN or HHCB were applied dermally in alcoholic solutions to rats at doses of 4.5 mg/kg and occluded for 6 h. Urine, feces and air were collected for up to 120 h and analyzed for radioactivity. Pairs of rats were sacrificed periodically for analysis of tissues and organs. The total amount absorbed was approximately 19% for AHTN and 14% for HHCB. In both cases, significant amounts diffused into the skin, most of which was further absorbed but a significant amount of which was lost to surface dressing by reverse diffusion and/or desquamation. Ring 14C-labeled AHTN or HHCB were applied in alcoholic solutions without occlusion to three male volunteers at concentrations approximating that which might be encountered in a typical cologne type product. After a 6-h period, all material was removed from the surface of the skin. Blood, feces and urine were collected over a 5-day period. For both materials, levels in blood and plasma were below limits of detection at all times. Based on excretion, primarily in the urine, the total absorbed dose was approximately 1 and 0.1% for AHTN and HHCB, respectively. However, over the 5-day period, 14.5% of AHTN and 19.5% of HHCB was recovered from the skin in dressings over the site of application indicating that a 'reservoir' had formed in the skin but the material in the reservoir was lost, by desquamation and/or by reverse absorption, and not available systemically. A mean of 24% (AHTN) and 22% (HHCB) was shown to evaporate under the conditions of exposure.

Animals↗

Evaluation of the oral subchronic toxicity of HHCB (1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethylcyclopenta-gamma-2 -benzopyran) in the rat.

1,3,4,6,7,8-Hexahydro-4,6,6,7,8,8-hexamethylcyclopenta-gamma-2-ben zopyran (HHCB) is used in a wide variety of fragrances in consumer products. Because of the widespread exposure to this material, a 90-day oral feeding study in accordance with OECD guidelines No. 408, with 4-week recovery periods for selected rats, was conducted. HHCB was added to the diet of rats at levels calculated to result in mean daily doses of 5, 15, 50 or 150 mg HHCB/kg. On completion of the treatment period, three males and three females from the high dose and control groups were maintained for a treatment free period of 4 weeks. No adverse effects were revealed from clinical examination or following extensive histopathological examinations. There were no significant findings at any dose level; a NOAEL of 150 mg/kg per day was concluded. As a supplement to the main study, histopathological examination of the prostate, seminal vesicles, mammary gland and testes of males and ovaries, mammary gland, uterus and vagina of females was undertaken on all animals in all test groups. This examination did not reveal any evidence of hormonal effects.

Administration, Oral↗

Acute hepatotoxicity of the polycyclic musk 7-acetyl-1,1,3,4,4,6-hexamethyl-1,2,3,4-tetrahydronaphtaline (AHTN).

Synthetic musks are present in fine fragrances, cosmetics, soaps and laundry detergents. One of the most important synthetic musks is 7-acetyl-1,1,3,4,4,6-hexamethyl-1,2,3,4-tetrahydro-naphthaline+ ++ (AHTN; annual production: about 1500 metric tons). An increasing number of studies show that AHTN accumulates in surface water and fish and can be detected in human adipose tissue, as well in human milk. In the present report it is shown that a single high dose of AHTN leads to acute hepatic damage in rats, characterized by single cell necrosis, inflammation, swelling of liver parenchymal cells, and the presence of cytoplasmic condensations in the hepatocytes, while at the ultrastructural level disorganization of the rough endoplasmic reticulum and mitochondria as well as focal cytolysis is evident. Furthermore, evidence is presented that AHTN is not genotoxic, does not induce peroxisome proliferation, and does not lead to the induction of drug-metabolizing enzymes as phenobarbital and 3-methylcholanthrene do.

Animals↗

AHTN and HHCB show weak estrogenic--but no uterotrophic activity.

The ubiquitous presence of the polycyclic musks AHTN (6-acetyl-1,1,2,4,4,7-hexamethyltetraline) and HHCB (1,2,4,6,7,8-hexahydro-4,6,6,7,8-hexamethylcyclopenta-gamma-2-b enzopyreen) in surface waters and their identification in human milk fat together with their polycyclic nature, which makes them potential candidates for interference with estrogen receptors, prompted us to assess these compounds for their potential estrogenic effects. We therefore investigated the effects of AHTN and HHCB in ERalpha- and ERbeta-dependent gene transcription assays with Human Embryonal Kidney 293 (HEK293) cells, which have proven to be very suitable to estimate the estrogenic activity of compounds with low binding activity (Kuiper, G.G., Lemmen, J.G., Carlsson, B., Corton, J.C., Safe, S.H., Van der Saag, P.T., Van der Burg, B., Gustafsson, J.A., 1998. Interaction of estrogenic chemicals and phytoestrogens with estrogen receptor beta. Endocrinology 139, 4252-4264). Both AHTN and HHCB were found to induce a slight but dose-dependent stimulation of transcriptional activity in the transiently ERalpha transfected HEK293 cells. This weak estrogenic response was not observed in the ERbeta transiently transfected cells. However, these cells were less responsive to estradiol than the ERalpha transfected HEK293 cells. Also, no significant increase in transcriptional activity was observed in HEK293 cell lines, permanently expressing the same estrogen-responsive reporter gene construct and either ERalpha or ERbeta. In the classical uterine weight assay performed in juvenile Balb/c mice, no uterotrophic activity of AHTN and HHCB was noted at relatively high dietary exposure levels up to 50 and 300 ppm, respectively, at which levels an increase in liver weight was evident. Also the vitellogenin production by carp hepatocytes, a sensitive marker of estrogenic activity, was not affected by these two fragrance materials (Smeets, J.M.W., Rouhani Rankouhi, T., Nichols, K.M., Komen, H., Kaminsky, N.E., Giesy, J.P., Van den Berg, M., 1999. In vitro vitellogenin production by carp (Cyprimus carpio) hepatocytes as a screening method for determining (anti-) estrogenic activity of xenobiotics. Toxicol. Appl. Pharmacol., 157, 68-76). Therefore it is concluded that these compounds have very weak estrogenic potency, too weak to induce estrogenic effects in wildlife species or humans at the current levels of exposure. These results give further support to the promiscuity of estrogen receptors.

Animals↗

Developmental toxicity studies of four fragrances in rats.

Four fragrances, 6-acetyl-1,1,2,4,4,7-hexamethyltetraline (AHTN), 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethylcyclopenta-gamma-2-ben zopyran (HHCB), musk ketone and musk xylene were tested for developmental toxicity in Sprague-Dawley rats (25/group, 3 groups/fragrance, 2 fragrances/corn oil control). Dosages tested were HHCB: 50, 150, 500 mg/kg per day; AHTN: 5, 15, 50 mg/kg per day; musk ketone: 15, 45, 150 mg/kg per day; musk xylene: 20, 60, 200 mg/kg per day. All dosages tested exceeded multiples of the estimated maximal daily human dermal exposure. Treatment (gavage, 5 ml/kg) occurred on GDs 7-17 and Caesarean-sectioning on GD 20. Based on the results of these studies, none of the four fragrances tested were more toxic in the conceptuses than in the dams. Maternal NOAELs were 50, 5, 15 and 20 mg/kg per day for HHCB, AHTN, musk ketone and musk xylene, respectively (150, 50, 45 and 60 mg/kg per day caused clinical signs and reduced weight gain and feed consumption). Developmental NOAELs were 150, 50, 45 and 200 mg/kg per day for HHCB, AHTN, musk ketone and musk xylene, respectively. No adverse effects on embryo-fetal viability, growth or morphology occurred at the highest dosages of AHTN (50 mg/kg per day) or musk xylene (200 mg/kg per day). Developmental toxicity occurred at the high-dosages of HHCB (axial skeletal malformations at 500 mg/kg per day) and musk ketone (increased postimplantation loss and reduced fetal body weight at 150 mg/kg per day). The results of this study indicate that under conditions of normal use, the tested fragrances do not pose a risk to human conceptuses.

Animals↗

Subchronic inhalation studies of complex fragrance mixtures in rats and hamsters.

Users of consumer products are invariably and intentionally exposed to complex mixtures in such products. With finished fragrance products, these mixtures may represent 100 or more fragrance raw materials (FRMs). The objective of the described studies was to evaluate the safety of finished fragrance products via the inhalation route. In total, the finished products contained approximately 100 FRMs at concentrations of 1% or greater. Major FRMs evaluated included benzyl acetate, coumarin, hydroxycitronellal, musk ketone, 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethyl-cyclopenta-gamma-2-be nzopyran (HHCB) and phenyl ethyl alcohol. Groups of rats or hamsters were exposed by inhalation (whole body) to the mixtures at 5, 9 or 50 mg/m3 for 4 h per day, 5 days per week for 6 or 13 weeks. For each of the fragrance products, the doses used generally represented a ten- to 100-fold exaggeration of levels expected to be achieved during typical use by consumers. With one exception, the fragrances were aerosolized prior to introduction into the inhalation chamber. The exception product was formulated with a propellant, packaged in a pressurized container and expelled with an automated actuator. In all studies, chamber concentrations of fragrance were monitored. Particle sizes ranged from 0.5 to 7.5 microm, depending on the study. Subchronic exposure to all fragrance mixtures resulted in no toxicologically significant effects on animal survival, behavior, body weights or weight gains, organ weights, or in hematology, clinical chemistry, or urinalysis parameters. No gross pathological or histopathological findings related to test material exposures were observed. These studies support the conclusions that the fragrance mixtures would not pose a hazard to product users based on repeated and exaggerated inhalation exposures of animals.

Administration, Inhalation↗

Musk xylene and musk ketone amino metabolites in the aquatic environment.

The monoamino metabolites of the nitro musk fragrances musk xylene (MX) and musk ketone (MK) were analysed simultaneously with their parent compounds by GC/ECD, GC/PND and GC/EI/MS in the various compartments of the aquatic environment. In this review the data of the metabolites 4-NH2-MX, 2-NH2-MX, and 2-NH2-MK in five river water and seven sewage samples, six sediment samples and in a total of 33 biota samples are summarized and discussed. In the effluents of two municipal sewage plants low nitro musk concentrations and comparatively high levels of the amino metabolites (maximum concentrations: 34 ng 4-NH2-MX/L, 250 ng 2-NH2-MK/L) were analysed indicating that besides adsorption to the sludge the metabolization pathway plays an important role in the sewage plant. In water samples from the river Elbe the transformation products were the dominant compounds as well. In general, in water samples the concentrations of 2-NH2-MK exceeded those of the main MX metabolite 4-NH2-MX significantly. In biota samples 4-NH2-MX seems to be the main metabolite, very often its contents were higher than those of the parent compound. Maximum concentrations of 4-NH2-MX were found in tenches from a sewage pond (3600 microg/kg lipid), a species dependent bioaccumulation was discussed. The bioconcentration of 2-NH2-MK in biota samples is relatively low. There are only few toxicological studies on the mixed amino nitroaromatics, whose data indicate the relevance of the monoamino metabolites in environmental analysis and toxicology and the urgent need of further investigations.

Fresh Water↗