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EC number: 415-890-1 | CAS number: 142770-42-1 QUANTACURE CPTX
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Genetic toxicity: in vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in bacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Setptember - October 1991
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 991
- Report date:
- 1991
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- GLP compliance:
- yes
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- 1-chloro-4-(n-propoxy)-5-thioxanthen-10-one
- EC Number:
- 415-890-1
- EC Name:
- 1-chloro-4-(n-propoxy)-5-thioxanthen-10-one
- Cas Number:
- 142770-42-1
- Molecular formula:
- C16H13ClO2S
- IUPAC Name:
- 1-chloro-4-propoxy-9H-thioxanthen-9-one
Constituent 1
Method
- Target gene:
- Histidine
Species / strainopen allclose all
- Species / strain / cell type:
- S. typhimurium TA 1538
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Metabolic activation system:
- Mixed function oxidase systems in the livers of a group of rats (SD male rats) were stimulated by Aroclor 1254, administered as a single intra-peritoneal injection in Arachis oil at a dosage of 500 mg/kg bw. On the fifth day after injection, following an overnight starvation, the rats were killet and their livers aseptically revomed.
The following steps were arried out at 0-4°C under aseptic conditions. The livers were placed in 0.15 M KCl before being trasnferred to an Ultra-Turrax homogeniser. Following preparation, the homogenates were centrifuged at 9000 g for 10 minutes. The supernatant fraction (S9 fraction) was dispensed into aliquots and stored at -80°C until required. The S9-fraction was tested with two carcinogens before use.
S9 mix contained : S9 fraction (10% v/v), MgCl2 (8 mM), KCl (33 mM), sodium phosphate buffer pH 7.4 (100 mM), glucose-6-phodphate (5mM), NADP (4 mM). All the cofactors were filter-sterilised before use. - Vehicle / solvent:
- DMSO
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Details on test system and experimental conditions:
- Preliminary toxicity test :
Four concentrations of test substance were assessed for toxicity using the five tester strains. The highest concentration was 50 mg/ml of test substance in the chosen solvent, which provided a final concentration of 5000 µg/plate. Three 10-fold serial dilutions of the highest concentration were also tested. The chosen solvent was used as the negative control.
An aliquot of 0.1 ml of a 10 hour bacterial culture and 0.5 ml S9-mix or 0.5 ml 0.1 M phosphate buffer (pH 7.4) were placed in glass bottles. An aliquot of 0.1 ml of the test substance solution was added followed, immediately, by 2 ml of histidine deficient agar. The mixture was thoroughly shaken and overlaid onto previously prepared petri dishes containing 25 ml minimal agar. A single petri dish was used for each dose level. Plates were also prepared without the additionof bacteria in order to assess the sterility of the test substance, S9 mix and phosphate buffer. All plates were incubated at 37°C for 3 days. After this period the appearance of the background bacterial lawn was examined. Revertant colonies were counted.
Main test
The test substance was added to cultures of the five tester strains at five concentrations. The highest concentration of CPTX used was 5000 µg/plate.
The main test was repeated using the same concentrations of test substance. - Evaluation criteria:
- The mean number of revertant colonies for all treatment groups is compared with those obtained for solvent control groups. The mutagenic activity of a test material is assessed by applying the following criteria :
-If treatment with a test material produces an increaase in revertant colony numbers of at least twice the concurrent solvent controls, with some evidence of a positive dose-relationshp in two separate experiments, with any bacterial strain either in the presence or absence of S9 mix, it is considered to show evidence of mutagenic activity in this test system. No statistical analysis is performed.
-If treatment with a test material does not produce reproducible increases of at least 1.5 times the concurrent solvent controls, at any dose level with any bacterial strain, it is considered to show no evidence of mutagenic activity in this test system. No statistical analysis is performed.
-If the results obtained fail to satisfy the criteria for a clear positive or negative response, repeat test and/or use statistics are recommanded. - Statistics:
- see Evaluation criteria
Results and discussion
Test resultsopen allclose all
- Species / strain:
- S. typhimurium TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- True negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 98
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- True negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 1538
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- True negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 1537
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- True negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 1535
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not applicable
- True negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- CPTX was not toxic towards the tester strains in the preliminary toxicity test, therefore 5000 µg/plate was chosen as the top dose in the mutation tests.
In the mutation tests, no substantial increases in revertant colony numbers of any of the tester strains were observed following treatment with CPTX at any dose level, either in the presence or absence of S9 mix.
Applicant's summary and conclusion
- Conclusions:
- It is concluded that CPTX was not mutagenic in the bacterial test system.
- Executive summary:
Mutagenic potential of CPTX was evaluated in an Ames test. Histidine dependent auxotrophic mutants of Salmonella typhimurium (strains TA1535, TA1537, TA1538, TA98, TA100) were exposed to the test material, diluted in DMSO which was also used as a negative control. Two independent mutation tests were performed, in the presence and absence of liver preparations from Arochlor 1254-induced rats.
In the preliminary dose range finding study with dose levels of up to 5000 µg/plate, no toxicity was observed. A top dose level of 5000 µg/plate was chosen for the subsequent mutation study. Other dose levels used in the mutation assays were 1500, 5000, 150 and 50 µg/plate.
No evidence of mutagenic activity was seen at any dose level of CPTX in either mutation test. The concurrent positive control compounds demonstrated the sensitivity of the assay and the metabolising activity of the liver preparations.
It is concluded that CPTX was not mutagenic in the bacterial test system.
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