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EC number: 204-826-4 | CAS number: 127-19-5
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Epidemiological data
Administrative data
- Endpoint:
- epidemiological data
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- restrictions: low number of workers in cohort, only 21 workers in high exposure group; no exposure data of control group reported [minor restriction]
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Monitoring acrylic fiber workers for liver toxicity and exposure to dimethylacetamide 2. Serum clinical chemistry results of dimethylacetamide-exposed workers
- Author:
- Spies GJ, Rhyne RH, Evans RA, Emmonds Wetzel K, Ragland DT, Turney HG, Leet TL, Oglesby JL
- Year:
- 1 995
- Bibliographic source:
- J Occup Environ Med 37: 1102-1107
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1995
Materials and methods
- Study type:
- cohort study (prospective)
- Endpoint addressed:
- basic toxicokinetics
- repeated dose toxicity: inhalation
- repeated dose toxicity: dermal
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The study was conducted to investigate the relationship between occupational DMAC exposure and hepatotoxicity. As part of the study, a biological monitoring of urinary levels of DMAC, N-methylacetamide (NMAC), and acetamide in humans after occupational inhalation (and dermal) exposure was done.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- N,N-dimethylacetamide
- EC Number:
- 204-826-4
- EC Name:
- N,N-dimethylacetamide
- Cas Number:
- 127-19-5
- Molecular formula:
- C4H9NO
- IUPAC Name:
- N,N-dimethylacetamide
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- - Name of test material: dimethylacetamide (DMAC)
No details available.
Method
- Type of population:
- occupational
- Ethical approval:
- not specified
- Details on study design:
- Study subjects were male employees in an acrylic fiber manufacturing facility, who worked in two departments using DMAC: solution preparation and spinning; employees worked fixed 12-hour schedules (2 days on, 2 off, 3 on, 3 off, 2 on, 2 off, etc.) in 4 shifts (each shift employed 27 workers); during the 1-year study period, a total of 127 DMAC-exposed workers were participants of the study.
In-plant control consisted of 217 employees working in 6 departments of the plant during the study period with no current or previous contact with DMAC.
At least once during the 1-year study period, a blood sample for serum clinical chemistry assessment was obtained from all study participants; additional blood samples may have been drawn from certain participants. The serum biochemistry tests were not coordinated with exposure monitoring. Additional serum clinical chemistry testing was conducted if a worker's biomonitoring result exceeded one of the "trigger" values established for the study: 60 mg N-methylacetamide (NMAC)/g creatinine (Cr) or 136 mg DMAC equivalent (DMAC Eq)/g Cr. These blood samples for clinical chemistry determination were immediately requested of "confirmed exposure" employees and subsequent blood samples were obtained 1 week and 2 weeks after the first (to investigate the rise or fall of serum biochemistry results).
Clinical chemistry
Serum clinical chemistry tests were used to measure liver injury; blood samples were collected by standard phlebotomy and analyzed for total bilirubin (TBILI), AST, ALT, alkaline phosphatase (ALKPHOS), and y-glutamyltranspeptase (GGTP). 490 sets of serum clinical chemistry results were obtained from 127 workers in the 2 "DMAC departments" and from the 217 workers in the control group. Log-transformed serum clinical chemistry results were used in all subsequent analyses.
The null hypothesis that there is no correlation between the serum biochemistry and biomonitoring results in the high-exposure group was investigated by multiple regression, with a random selection of one of the three postbiomonitoring serum biochemistry results as the dependent variable and one of the postshift biomonitoring results, urinary NMAC or acetamide, or urinary DMAC Eq, and the confounding variables, alcohol consumption and age, as the independent variables.
Toxicokinetics
Personal air monitoring for DMAC und biological monitoring for levels of DMAC, NMAC, and acetamide in spot urine samples. - Exposure assessment:
- measured
- Details on exposure:
- 60 out of the 127 workers who worked in two departments using DMAC were monitored bimonthly (employees participated in air and biological monitoring). Air and biological monitoring was targeted toward those job classes for which previous air monitoring had suggested a higher potential for DMAC exposure; effort was made to sample the same person each month for job classes in which virtually everyone was monitored (potential exposure), such as dope prep, utility, and jet room (28 persons).
During the first 10 months, full-shift air and post-shift biological monitoring was conducted on the second consecutive workday after the 3-day break. During the last 2 months of the 1-year study period, air and biological monitoring was conducted both on the first and the second day.
DMAC in air was sampled with 3M passive dosimeters and analyzed by gas chromatography. Post-shift urine samples were collected for DMAC, MMAC, and acetamine (ACET) and analysed by gas chromatography. - Statistical methods:
- Geometric Mean (GM), Geometric Standard Deviation (GSD), and t- Test
Scheffe's test
Level of significance: p<0.05.
Results and discussion
- Results:
- Biomonitoring results from 21 of 127 workers (in the 2 DMAC departments) participating in the air and biological monitoring study exceeded one of the biomonitoring trigger values (formed a high-exposure group), leaving 106 individuals in an unspecified-exposure group. All 217 controls formed a no-exposure group.
DMAC in air, and NMAC and DMAC Eq in urine results for each exposure group were compared (t-test) and for all exposure indexes, the mean result from the high-exposure group exceeded the mean from the unspecified group (see Table below).
Serum clinical chemistry data were available from 127 DMAC exposed workers plus the 217 controls (clinical chemistry results from 9 workers without data on alcohol consumption were excluded as well as the result of one control with diagnosed liver condition).
The exposure indexes tested - urinary ACET, urinary NMAC, and urinary DMACEq - were not correlated with the serum biochemistry results.
None (0 of 21) of the high exposure group individuals had an abnormal serum biochemistry result during the study period; in both replicates of the analysis, only one (1 of 106) of the unspecified exposure group and four (4 of 217) of the no-exposure group individuals had abnormal clinical chemistry values.
Toxicokinetics:
- Personal air monitoring for DMAC und biological monitoring for levels of DMAC, NMAC, and acetamide in spot urine samples.
- Biological monitoring of urinary levels of DMAC, N-methylacetamide (NMAC), and acetamide was conducted in humans after occupational inhalation (and dermal) exposure. Male workers in two departments of an acrylic fiber manufacturing facility, where DMAC was used, were examined. Each shift employed 27 workers in seven job classes; Data on 97 workers were available for monitoring.
The workers were whole body exposed (via respiratory tract and skin) to the vapour. Employees worked fixed 12-hour schedules (2 days on, 2 days off, 3 days on, 3 days off, 2 days on, 2 days off, etc.) in four shifts (A, B, C, and D). Worker exposure to DMAC was measured over a 1-year study period. 93 workers of the plant were monitored on the second consecutive workday after at least 3 days off for the first 10 months of the study and on both the first and second days during the study's final 2 months. Personal air monitoring was performed for DMAC und biological monitoring for levels of DMAC, NMAC, and acetamide in spot urine samples. An air concentration of 6.7 ppm (12-hour time-weighted average (TWA)) corresponded to an urine NMAC level of 62 mg/g creatinine in a postshift spot urine sample obtained after the second consecutive workday. NMAC and acetamide were identified as metabolites in urine.
Conclusion: A level of 35 mg NMAC/g creatinine in a postshift spot urine sample (12-h shift) was recommended as a biomonitoring index. DMAC demethylation metabolic mechanisms did not become saturated at the threshold limit value.
- Details on Excretion: An air concentration of 6.7 ppm (12-hour time-weighted average (TWA)) corresponded to an urine NMAC level of 62 mg/g creatinine in a postshift spot urine sample obtained after the second consecutive workday.
- Metabolites identified: NMAC and acetamide in urine - Confounding factors:
- Sufficiently considered:
1) Age (capable of confounding serum clinical chemistry results)
2) Alcohol consumption (data from medical questionnaire; alcohol consumption categories 0-3)
3) Liver disease (data from plant physician) - Strengths and weaknesses:
- Low number of exposed workers
Any other information on results incl. tables
Exposure indices in high and unspecified exposure groups
High exposure if one biomonitoring result exceeded one of the trigger values (see details of study design)
Geometric means ± geometric standard deviation (SD)
Exposure index |
Exposure group |
Number of samples |
Mean ± SD |
DMAC concentration in air, 12 h TWA |
High |
96 |
1.9 ± 2.6 |
Unspecified |
294 |
1.3 ± 2.1 |
|
Urinary NMAC concentration (mg/g creatinine) |
High |
98 |
26.7 ± 2.7 |
Unspecified |
295 |
13.5 ± 2.3 |
|
Urinary DMAC Eq (mg/g creatinine) |
High |
98 |
81.2 ± 2.2 |
Unspecified |
295 |
43 ± 1.8 |
TWA: time weighted average
Clinical chemistry results versus exposure group
Geometric means ± geometric standard deviation (SD); abbreviation see text
Clinical chemistry parameter |
Non-exposure group (n = 217) |
Unspecified exposure group (n = 106) |
High-exposure group (n = 21) |
TBILI |
0.52 ± 1.48 |
0.45 ± 1.58 |
0.37 ± 1.35* |
AST |
25.8 ± 1.37 |
24.7 ± 1.36 |
24.8 ± 1.25 |
ALT |
27.0 ± 1.49 |
25.1 ± 1.48 |
25.5 ± 1.48 |
ALKPHOS |
81.8 ± 1.30 |
76.6 ± 1.27 |
85.3 ± 1.31 |
GGTP |
19.1 ± 1.64 |
16.8 ± 1.62 |
16.1 ± 1.55# |
*: significantly different from non-exposure and
unspecified exposure group
#: significantly different from non-exposure group
Applicant's summary and conclusion
- Conclusions:
- There was no liver injury in workers exposed to DMAC and excreting > 60 mg N-methylacetamide/g creatinine (trigger value) via the urine (2-fold BEI value).
- Executive summary:
Exposure of workers to N,N-dimethylacetamide (DMAC) in an acrylic fiber plant was measured over a 1-year study period, by full-shift (12 h) personal air monitoring of DMAC and biological monitoring for levels of DMAC, N-methylacetamide (NMAC) and acetamide in post-shift spot urine samples. Evidence of liver toxicity was assessed by serum clinical chemistry tests (total bilirubin, aspartate aminotransferase, alanine aminotransferase, alkaline phosphatase, and y-glutamyl transpeptidase) at least once during the study period for all 127 male workers in the 2 study departments and for 217 male in-plant controls with no previous or current exposure to DMAC. Additional serum clinical chemistry tests were conducted at weekly intervals for 3 weeks in workers showing increased DMAC (>132 mg/g creatinine) or NMAC (>60 mg/g creatinine) levels in urine (trigger values). DMAC-exposed workers were classified as either high exposure (if one biomonitoring result exceeded one of the trigger values), or unspecified exposure (trigger value not reached). Control employees were classified as no-exposure. Mean DMAC levels in air differed for the high- and unspecified exposure group (mean DMAC in air levels of 1.9 and 1.3 ppm, 12-hour time-weighted average, respectively) as well as mean urinary NMAC values (26.7 vs 13.5 mg/g creatinine). No DMAC exposure related trends in hepatic serum clinical chemistry results were detected. None (0 of 21) of the high exposure group had an abnormal serum biochemistry result during the study period.
A level of 35 mg NMAC/g creatinine in a postshift spot urine sample (12-h shift) was recommended as a biomonitoring index.
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