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EC number: 202-196-5 | CAS number: 92-84-2
- 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 somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1998
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well perfomed GLP study according to standard NTP protocols.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: standard NTP protocol
- Deviations:
- not specified
- GLP compliance:
- yes
- Remarks:
- According to the NTP-website only GLP-studies are accepeted for publication (http://ntp.niehs.nih.gov/files/Specifications_2006Oct1.pdf)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Phenothiazine
- EC Number:
- 202-196-5
- EC Name:
- Phenothiazine
- Cas Number:
- 92-84-2
- Molecular formula:
- C12H9NS
- IUPAC Name:
- 10H-phenothiazine
- Details on test material:
- - Test item: phenothiazine
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- - The NTP has specific requirements for the testing laboratories to comply with the Laboratory Animal Welfare Act of 1966 and adhere to the principles enunciated in the "Guide for the Care and Use of Laboratory Animals" NRC, 1996.
- URL: http://ntp.niehs.nih.gov/go/type
- At the end of the study animals were killed by CO2 overdose
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Corn oil
- Duration of treatment / exposure:
- - 3 treatments
- Treatments are administered in 24hr intervals
- Sample collection time 24hrs after last treatment - Frequency of treatment:
- - 3 treatments
- Post exposure period:
- - 24hrs after last treament (sample collection time) animals were killed by CO2 overdose
Doses / concentrations
- Remarks:
- Doses / Concentrations:
625 mg/kg, 1250 mg/kg, 2500 mg/kg
Basis:
actual ingested
Doses extend up to the maximum tolerated dose
- No. of animals per sex per dose:
- 5 males per dose
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - Cyclophosphamide
- Dose: 25 mg/kg
- No of animals: 4 males
Examinations
- Tissues and cell types examined:
- - Bone marrow is flushed from the femurs and spread onto slides
- 24hrs after last exposure about 50% of the erythrocytes in the bone marrow are immature, newly formed erythrocytes, and these are the cell types that are checked for presence of micronuclei - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
- Doese extend up to the maximum tolerated dose
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
- 3 treatments in 24hr intervals
- sampling time 24hrs after last treatment
DETAILS OF SLIDE PREPARATION:
- Bone marrow is flushed from the femurs and spread onto slides
- Slides are air dried, fixed and stained with a fluorescent DNA-specific stain (acridine orange) that illuminates any micronuclei that may be present
METHOD OF ANALYSIS:
- 2000 polychromatic erythrocytes (PCEs, reticulocytes; immature erythrocytes) are scored per animal for frequency of micronucleated cells
- This is done for each of 5 animals per dose group
- In addition, the %PCEs among the total erythrocyte population in the bone marrow is scored for each dose group as an indicator of chemical-induced toxicity
- In non-treated healthy mice and rats, the %PCE in bone marrow is usually around 50-60%
- If a chemical interferes with the production of erythrocytes in the bone marrow, then the %PCE in the bone marrow may decline from the typical normal level
- Conversely, if erythrocyte production is stimulated by chemical exposure, then a higher percentage of immature erythrocytes may be observed - Evaluation criteria:
- - See details in section "Any other information on materials and methods incl. tables" below
- Statistics:
- - See details in section "Any other information on materials and methods incl. tables" below
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- not specified
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- - Please find the study results summarised (and in detail) in the section "Remarks on results including tables and figures" below
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): no
- Ratio of PCE/NCE (for Micronucleus assay): dose dependent, between 0.30 to 0.90 with test item and 11.88 with positive control
- Appropriateness of dose levels and route: doses were extended up to maximum tolerated dose, route of adminstration is according to NTP protocol and considered relevant for the test item
- Statistical evaluation: is included in the results tables in the section "Remarks on results incl. tables and figures" below
Any other information on results incl. tables
Study Summary: Bone Marrow
Study ID |
Result |
|
Male |
Female |
|
A12280 |
Negative |
Not Tested |
Start Date |
Sample Collection Time |
Sex |
Cell |
Dosing Regimen |
Route |
Trend Test P-Value |
01/20/1998 |
24 Hours |
Male |
PCE |
GAV x 3, 72 Hours |
Gavage |
0.305 |
|
Dose (mg/kg) |
Number of Animals Scored |
Mean MN-PCE/1000 PCE ± SEM |
Pairwise P |
||
Vehicle Control |
Corn Oil |
0 |
5 |
0.90 ± 0.19 |
||
Test Chemical |
Phenothiazine |
625 |
5 |
0.30 ± 0.12 |
0.958 |
|
1250 |
5 |
0.70 ± 0.34 |
0.692 |
|||
2500 |
5 |
0.90 ± 0.53 |
0.500 |
|||
Positive Control |
Cyclophosphamide |
25 |
4 |
11.88 ± 1.56 |
< 0.0001 |
Detailed results: Bone Marrow
|
Dose |
Animal |
Polychromatic Erythrocytes |
||||
No. Examined |
Total MN Cells |
Percent PCE |
MN Cells |
||||
Vehicle Control |
CRNO |
0 |
20 |
2000 |
1 |
47.5 |
0.5 |
|
0 |
41 |
2000 |
2 |
38.0 |
1.0 |
|
|
0 |
47 |
2000 |
1 |
30.0 |
0.5 |
|
|
0 |
55 |
2000 |
2 |
54.0 |
1.0 |
|
|
0 |
65 |
2000 |
3 |
56.0 |
1.5 |
|
Average ± SEM |
|
45.10 ± 4.91 |
0.90 ± 0.19 |
||||
|
|||||||
Test Chemical |
625 |
38 |
2000 |
0 |
49.5 |
0.0 |
|
|
625 |
44 |
2000 |
1 |
51.5 |
0.5 |
|
|
625 |
50 |
2000 |
0 |
34.0 |
0.0 |
|
|
625 |
57 |
2000 |
1 |
38.0 |
0.5 |
|
|
625 |
62 |
2000 |
1 |
49.0 |
0.5 |
|
Average ± SEM |
|
44.40 ± 3.51 |
0.30 ± 0.12 |
||||
Pairwise P |
|
0.958 |
|||||
|
|||||||
Test Chemical |
1250 |
14 |
2000 |
1 |
47.0 |
0.5 |
|
|
1250 |
42 |
2000 |
1 |
31.0 |
0.5 |
|
|
1250 |
48 |
2000 |
1 |
41.0 |
0.5 |
|
|
1250 |
59 |
2000 |
4 |
49.0 |
2.0 |
|
|
1250 |
67 |
2000 |
0 |
37.0 |
0.0 |
|
Average ± SEM |
|
41.00 ± 3.29 |
0.70 ± 0.34 |
||||
Pairwise P |
|
0.692 |
|||||
|
|||||||
Test Chemical |
2500 |
39 |
2000 |
1 |
57.5 |
0.5 |
|
|
2500 |
46 |
2000 |
0 |
45.0 |
0.0 |
|
|
2500 |
52 |
2000 |
6 |
23.5 |
3.0 |
|
|
2500 |
543 |
2000 |
1 |
42.5 |
0.5 |
|
|
2500 |
64 |
2000 |
1 |
55.0 |
0.5 |
|
Average ± SEM |
|
44.70 ± 6.02 |
0.90 ± 0.53 |
||||
Pairwise P |
|
0.500 |
|||||
|
|||||||
Positive Control |
CPA |
25 |
37 |
2000 |
18 |
20.5 |
9.0 |
|
25 |
45 |
2000 |
32 |
16.5 |
16.0 |
|
|
25 |
53 |
2000 |
25 |
1.0 |
12.5 |
|
|
25 |
58 |
0 |
0 |
0 |
0.0 |
|
|
25 |
61 |
2000 |
20 |
2.0 |
10.0 |
|
Average ± SEM |
|
10.00 ± 4.98 |
11.88 ± 1.56 |
||||
Pairwise P |
|
< 0.0001 |
|||||
|
|||||||
Abbreviations: |
|||||||
CRNO = Corn Oil |
|||||||
CPA = Cyclophosphamide |
|||||||
MN = Micronucleated Cells |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Under the conditions described the test item phenothiazine is not inducing any micronuclei. - Executive summary:
Following the standard NTP protocol for the assessment of in vivo micronuclei induction (which is similar to recent OECD TG), phenothiazine is not increasing the number of micronucleated cells and hence considered to be non-genotoxic.
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