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EC number: 238-270-9 | CAS number: 14324-55-1
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian cell study: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Remarks:
- Comparable to guideline study, published in peer-reviewed literature, no restrictions, fully adequate for assessment.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Mirsalis J C and Butterworth B E (1980) Detection of unscheduled DNA synthesis in hepatocytes isolated from rats treated with genotoxic agents. An in vivo-in vitro assay for potential mutagens and carcinogens. Carcinogenesis 1, 621-625
- Deviations:
- no
- GLP compliance:
- not specified
- Type of assay:
- unscheduled DNA synthesis
Test material
- Reference substance name:
- Zinc bis(diethyldithiocarbamate)
- EC Number:
- 238-270-9
- EC Name:
- Zinc bis(diethyldithiocarbamate)
- Cas Number:
- 14324-55-1
- Molecular formula:
- C10H20N2S4Zn
- IUPAC Name:
- zinc bis(diethyldithiocarbamate)
- Details on test material:
- - Name of test material (as cited in study report): ZDEC
- Physical state: fine (aggregative) white powder
- Purity: at least 98%
- Impurities (identity and concentrations): ZDBC (1000 ppm) and TETD (56 ppm)
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
Administration / exposure
- Route of administration:
- oral: unspecified
- Vehicle:
- - Vehicle(s)/solvent(s) used: corn oil
- Duration of treatment / exposure:
- In experiment 1, all rats were killed 2 hours after dosing.
In experiment 2, all rats were killed 16 hours after dosing. - Frequency of treatment:
- Single dose
Doses / concentrationsopen allclose all
- Dose / conc.:
- 500 mg/kg bw (total dose)
- Dose / conc.:
- 1 000 mg/kg bw (total dose)
- Dose / conc.:
- 1 500 mg/kg bw (total dose)
- No. of animals per sex per dose:
- 4 males/dose
- Control animals:
- yes
- Positive control(s):
- MMS (methylmethanesulfonate)
2-AAF (2-acetyl aminofluorene)
- Route of administration: oral
- Doses / concentrations: 500 mg/kg for MMS and 200 mg/kg for 2-AAF
Examinations
- Tissues and cell types examined:
- liver (hepatocytes)
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
in preliminary toxicity trials, a maximum dose of 2000 mg/kg was employed end for ZDEC, this proved highly toxic.
METHOD OF ANALYSIS:
Hepatocytes were isolated by liver perfusion and cultured in medium supplemented with tritiated thymidine. The amount of unscheduled DNA synthesis was assessed by autoradiography using standard techniques: 50 cells/slide from each of two slides/animal were evaluated. Nuclear grain count (NG), cytoplasmic grain count (CG) and net nuclear grain count (NNG: calculated as NG minus CG) were determined for each scored cell. - Statistics:
- The results from ZDEC treated animals were compared statistically to those from concurrent vehicle controls using Student's t-test.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- ambiguous
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- Most rats dosed with ZDEC showed diarrhoea, and most killed 16 hr post-dose showed weight loss. Hepatocyte viabilities after isolation were high (6993%), and did not differ markedly between test and control groups. A total of four treated rats killed 16 hr post-dose (three dosed at 1000 mg/kg, one each at 500 and 1500 mg/kg) showed small increases in NNG such that their individual values for this parameter exceeded 1.0 (a threshold for consideration of a positive result in the liver UDS assay). These rats also showed increased numbers of cells undergoing DNA synthesis (cells in repair: %IR) so that %IR was between 18 and 32%. However only one of these animals showed NNG greater than 0 on both of the replicate slides scored for grain count; in addition, no dose-relationship or other response pattern was evident, and (most importantly) evaluation on a group basis found no significant effect of ZDEC treatment at any dose (see statistical analysis, Table 1). It was concluded that this study had produced no conclusive evidence of induction of UDS by ZDEC: the study was considered to have shown an equivocal result.
Any other information on results incl. tables
Table 1: Rat hepatocyte UDS assay. Grain counts 2 hours and 16 hours after animal treatment:group means±standard deviation four rats/ group
ZDEC: Hepatocytes taken 2 hours post-dose |
||||
Treatment: ZDEC (mg/kg) |
Nuclear grain count |
Cytoplasmic grain count |
Net nuclear grain count |
% cells in repair |
0 (corn oil) |
3.58±0.59 |
5.38±0.87 |
-1.80±0.40 |
1.75 |
500 |
3.15±0.35 |
5.04±0.48 |
-1.88±0.60 |
7.25 |
1000 |
3.49±0.48 |
4.96±0.94 |
-1.47±0.91 |
2.25 |
1500 |
4.16±1.09 |
5.70±0.74 |
-1.54±1.30 |
3.00 |
MMS: 500 |
9.13±0.85** |
4.23±0.69 |
4.90±0.85** |
40.33 |
ZDEC: Hepatocytes taken 16 hours post-dose |
||||
Treatment: ZDEC (mg/kg) |
Nuclear grain count |
Cytoplasmic grain count |
Net nuclear grain count |
% cells in repair |
0 (corn oil) |
4.75±1.21 |
6.86±1.05 |
-2.11±1.24 |
5.5 |
500 |
6.73±2.09 |
8.22±1.55 |
-1.49±2.10 |
7.5 |
1000 |
7.65±2.13 |
7.26±0.85 |
-0.40±2.77 |
17.25 |
1500 |
6.60±2.06 |
7.94±1.55 |
-1.34±1.94 |
8 |
2-AAf: 200 |
12.77±2.11** |
6.16±1.92 |
6.61±0.98** |
55.75 |
MMS= positive control 1(methylmethanesulfonate).Data from three rats/group only in ZDEC study
2-AAF= positive control 2 (2-acetyl aminofluorene)
Significant difference fromvehicle controls: *test group>controls, 0.01 < P < 0,05; **test group>controls, P<0.01
Typical historicalcontrol values forthe testing laboratory were between -3 and -6.
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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