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EC number: 221-424-4 | CAS number: 3089-17-6
- 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
Acute Toxicity: inhalation
Administrative data
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 16 January 2007 to 16 March 2007
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.2 (Acute Toxicity (Inhalation))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.1300 (Acute inhalation toxicity)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: JMAFF Test data for Registration of Agricultural Chemicals, Test Guidelines, Acute Inhalation Toxicity, 12 NohSan No. 8147, November 2000
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Study in compliance with Swiss Ordinance relating to GLP, which is based on OECD Principles of GLP
- Test type:
- standard acute method
- Limit test:
- no
Test material
- Reference substance name:
- 5,12-dihydro-2,9-dimethylquino[2,3-b]acridine-7,14-dione
- EC Number:
- 213-561-3
- EC Name:
- 5,12-dihydro-2,9-dimethylquino[2,3-b]acridine-7,14-dione
- Cas Number:
- 980-26-7
- Molecular formula:
- C22H16N2O2
- IUPAC Name:
- 2,9-dimethyl-5,12-dihydroquino[2,3-b]acridine-7,14-dione
- Test material form:
- solid: nanoform
- Details on test material:
- name of test material (as cited in study report): Hostaperm Pink E
batch: DEB2018126
analytical purity: 98.44 % (w/w) C.I. Pigment Red 122
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Strain specifics: HanBrl:WIST(SPF)
- Source: RCC Ltd, Laboratory Animal Services, Füllinsdorf, Switzerland
- Age at study initiation: males: 9 weeks, females: 10 weeks
- Weight at study initiation: males: 232.1-261.6 g, females: 210.0-221.9 g
- Housing: Animals of the same sex were housed in groups of five in Makrolon type IV cages with wire mesh tops and standard softwood bedding
- Diet (e.g. ad libitum): standard rat maintenance diet, ad libitum, except during the treatment period
- Water (e.g. ad libitum): community tap water ad libitum, except during the treatment period
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19.5-20 °C
- Humidity (%): 30-72%
- Air changes (per hr): 10-15
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- nose only
- Remarks:
- flow-past exposure
- Vehicle:
- other: unchanged (no vehicle)
- Mass median aerodynamic diameter (MMAD):
- >= 2.64 - <= 2.83 µm
- Geometric standard deviation (GSD):
- >= 3.93 - <= 4.04
- Remark on MMAD/GSD:
- MMAD (two measurements)
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Similar to the system originally described by Sachsse et al. (1973, 1976) and Cannon et al. (1983)
- Method of holding animals in test chamber: restraint tubes
- Source and rate of air: total airflow: 34 l/min, airflow of the aerosol arriving at the animal ports: 1 l/min per animal port
- System of generating particulates/aerosols: dust aerosol generated from the test item using a rotating brush aerosol generator connected to a micronising jet mill. The aerosol generated was then discharged into the exposure chamber through a 63Ni charge neutraliser.
- Method of particle size determination: gravimetrically (see below)
- Temperature, humidity, oxygen concentration in air chamber: measured on test atmosphere samples collected from the feed tubes in the breathing zone of the animals
TEST ATMOSPHERE
- Brief description of analytical method used: gravimetric (weighing the generator cylinder containing the test item before and after the exposure to determine the quantity of test item used. The total weight used during the exposure was then divided by the total airflow volume to give the nominal concentration.
- Samples taken from breathing zone: yes (gravimetric using Millipore filters)
TEST ATMOSPHERE (if not tabulated)
- Particle size distribution: measured gravimetrically twice during each exposure using a 7 stage cascade a Mercer Impactor
- MMAD (Mass median aerodynamic diameter) / GSD (Geometric st. dev.): calculated on the basis of the results with the Mercer Impactor
For results, see below
References:
Sachsse, K., L. Ullmann, G. Voss and R. Hess: Measurements of Inhalation Toxicity of Aerosols in Small Laboratory Animals. In: Proceedings of the Europ. Soc. for the Study of Drug Toxicity, Vol. XV, pp. 239-251, Zürich, June 1973.
Sachsse, K., L. Ullmann, K. Zbinden: Toxikologische Prüfungen von Aerosolen im Tierexperiment, "Chemische Rundschau" 29 (1976), No. 38, p. 1.
Cannon, W.C., E.F. Blanton and K.E. McDonald: The Flow-Past Chamber: An Improved Nose-Only Exposure System for Rodents, Am. Ind. Hyg. Assoc. J., 44 (12): 923-928, 1983 - Analytical verification of test atmosphere concentrations:
- yes
- Remarks:
- see above
- Duration of exposure:
- 4 h
- Remarks on duration:
- Approx. 2 h after the start, exposure was interrupted for 3 min (cleaning the exposure system and changing the piston cylinder). Nevertheless, animals were exposed for a total of 4 hours.
- Concentrations:
- Nominal concentration: 4.419 mg/l
Actual concentration: 3.055 mg/l (± 0.068 mg/l, n = 5), MMAD (two measurements): 2.83 µm (GSD 4.04) and 2.64 µm (GSD 3.93)
Rationale: A target concentration of 3 mg/l air (actual concentration of test item in air) corresponds to the maximum technically feasible aerosol concentration as determined in technical trials. - No. of animals per sex per dose:
- 5 males and 5 females
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 15 days beginning on the day of exposure
- Frequency of observations and weighing: daily for mortality and clinical signs, weiging on days 1 (before exposure), 4, 8 and 15 (day of necropsy)
- Necropsy of survivors performed: yes (all animals)
- Other examinations performed:
clinical signs included, but were not limited to: changes in behaviour, somatomotor activity, body position, respiratory and circulatory effects, autonomic effects such as salivation, central nervous system effects, e.g. tremors or convulsions, reactivity to handling or sensory stimuli, altered strength, alteration of the skin, fur, nose, eyes and mucous membranes - Statistics:
- The LOGIT model was not used as only one group was exposed.
Results and discussion
Effect levels
- Key result
- Sex:
- male/female
- Dose descriptor:
- LC0
- Effect level:
- 3.055 mg/L air (analytical)
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: mean analytical concentration of five measurements
- Mortality:
- No mortality, all animals were sacrificed as scheduled on test day 15.
- Clinical signs:
- other: All animals showed rales, decreased spontaneous activity, hunched posture, tachypnea and ruffled fur on the day of exposure and the two following days in individually variable extent. These signs were not noted from day 4 onwards.
- Body weight:
- Four females showed a slight transient body weight loss between Day 1 and Day 4. All other animals gained body weight as expected.
- Gross pathology:
- There were no macroscopic pathology findings in any of the animals. No macroscopically visible coloration of the lungs by Hostaperm Rosa E was detected.
- Other findings:
- Temperature, relative humidity and oxygen concentration during exposure were considered to be satisfactory for this type of study.
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- No mortality was observed after nose-only inhalation exposure to the test item (Pigment Red 122) of male and female rats at the highest technically achievable aerosol concentration of 3.055 mg/L for 4 hours. Based on the lack of lethal effects, severe clinical symptoms indicating a life-threatening or moribund state, and gross morphological abnormalities, it may be reasonably assumed that the LC50 for the test item is greater than 5 mg/l air and that the test item has not to be classified as acutely toxic by the inhalation route according to Regulation (EC) No 1272/2008.
- Executive summary:
The purpose of this study was to assess the acute inhalation toxicity of the test item when administered to rats for a single 4-hour period.
One group of five male and five female albino rats [HanBrl:WIST(SPF)], was exposed by nose-only, flow-past inhalation to the test item at mean aerosol concentrations of 3.055 ± 0.068 (n=5) mg/L air (gravimetrically determined). Two gravimetric measurements of particle size distribution during the exposure produced mass median aerodynamic diameters and geometric standard deviations (GSD) of 2.83 µm (GSD 4.04) and 2.64 µm (GSD 3.93), respectively.
All animals were observed for clinical signs and mortality during and following the inhalation exposure, i.e. over a 15-day observation period. Body weights were recorded prior to exposure on test day 1, and during the observation period on test days 4, 8 and 15. All animals were sacrificed and necropsied on day 15.
The ranges of temperature, relative humidity, oxygen content and particle size measured during the exposure were satisfactory for a study of this type.
There were no spontaneous deaths.
All animals showed rales, decreased spontaneous activity, hunched posture, tachypnea and ruffled fur on the day of exposure and the two following days in individually variable extent.
Four females showed a slight transient body weight loss between Day 1 and Day 4. All other animals gained body weight as expected.
There were no macroscopic pathology findings in any of the animals.
In conclusion, at the highest technically achievable aerosol concentration of the test item of 3.055 mg/L air, none of the ten exposed animals died (LC0 = 3.055 mg/L). Based on the lack of lethal effects or severe clinical symptoms indicating a life-threatening or moribund state, it may be reasonably assumed that the LC50 for the test item is likely to be greater than 5 mg/L air.
Therefore, the test item has not to be classified as acutely toxic by the inhalation route according to Regulation (EC) No 1272/2008.
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