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EC number: 244-848-1 | CAS number: 22224-92-6
- 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:
- 2000-05-25 to 2000-09-15
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 001
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Version / remarks:
- adopted May 12 1981
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.1300 (Acute inhalation toxicity)
- Version / remarks:
- August 1998
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- traditional method
- Limit test:
- no
Test material
- Reference substance name:
- Fenamiphos
- EC Number:
- 244-848-1
- EC Name:
- Fenamiphos
- Cas Number:
- 22224-92-6
- Molecular formula:
- C13H22NO3PS
- IUPAC Name:
- {ethoxy[3-methyl-4-(methylsulfanyl)phenoxy]phosphoryl}(propan-2-yl)amine
- Test material form:
- solid: crystalline
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Remarks:
- SPF bred Wistar rats, strain Hsd Cpb:WU
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan-Winkelmann GmbH, Borchen (Germany)
- Females nulliparous and non-pregnant: yes
- Age at study initiation: approx. 8 weeks
- Weight at study initiation: females: 163.0 - 175.4 g, males: 171.6 - 204.6 g
- Housing: housed singly in conventional Makrolon® Type II cages, with type BK 15 low-dust wood granulate
- Historical data: available
- Diet (ad libitum): standard fixed-formula diet (Altromin® 1324 pellets maintenance diet for rats and mice, Altromin GmbH, Lage)
- Water (ad libitum): tap water
- Acclimation period: at least 5 days
- Microbiological status when known: SPF
- Method of randomisation in assigning animals to test and control groups: A computerized list of random numbers served the purpose to assign animals at random to the treatment groups.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 2
- Humidity (%): approx. 50
- Air changes (per hr): approx. 10
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- nose only
- Vehicle:
- other: a mixture consisting of polyethylene glycol 400 (PEG) and ethanol (1:1; w/v)
- Mass median aerodynamic diameter (MMAD):
- 1.31 - 1.44
- Geometric standard deviation (GSD):
- 2.12 - 2.28
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Plexiglas exposure tubes applying a directed-flow nose-only exposure principle
- Exposure chamber volume:
The aluminum inhalation chamber has the following dimensions: inner diameter = 14 cm, outer diameter = 35 cm (two-chamber system), height = 25 cm (internal volume = about 3.8 L).
- Method of holding animals in test chamber:
Tubes were chosen that accommodated the animals size. These tubes were designed so that the rat's tail remained outside the tube, thus restrained-induced hyperthermia can be avoided.
- Source and rate of air (airflow):
During the exposure period air flows were monitored continuously and, if necessary, readjusted to the conditions required. Air flows were measured with calibrated flow-meters and/or soap bubble meter (Gilibrator, Strb'hlein Instruments, Kaarst) and were checked for correct performance at regular intervals.
- Method of conditioning air:
Compressed air was supplied by Boge compressors and was conditioned (i.e. freed from water, dust, and oil) automatically by a VIA compressed air dryer. Adequate control devices were employed to control supply pressure.
- System of generating aerosols:
Under dynamic conditions the test substance was nebulized into a baffle (pre-separator) from which the substance was conveyed into the intake of the cylindrical inhalation chamber. The test substance was nebulized using a binary nozzle with conditioned compressed air (15L/min; dispersion pressure approximately 600 kPa; for details see Table 1, result section). The solution was fed into the nozzle by a digitally controlled Hamilton Microlab pump.
- Method of particle size determination: Gravimetric analyses
- Treatment of exhaust air:
The exhaust air was purified via cotton-wool/HEPA filters. These filters were disposed of by Bayer AG.
- Temperature, humidity, pressure in air chamber:
Temperature and humidity measurements were made using a computerized system
(Hydra, Fluke-Philips). The values were recorded at intervals of 5 min (computerized
recording). The test atmosphere temperature and humidity were measured at the exposure location. Humidity and temperature were measured using a FTF-sensor (Elka-Elektronik, Liidenscheid). The sensor was calibrated using saturated salt solutions according in a two-point calibration at 33% (MgCI2) and at 75% (NaCI) relative humidity. The calibration of the temperature sensor is also checked at two temperatures using a reference thermometer. The measured values were evaluated using a spread-sheet software.
TEST ATMOSPHERE
- Brief description of analytical method and equipment used: BERNER-TYPE AERAS lowpressure critical orifice cascade impactor (Hauke, Gmunden, Austria).
- Samples taken from breathing zone: yes
- Time needed for equilibrium of exposure concentration before animal exposure: not specified
VEHICLE
- Composition of vehicle: a mixture consisting of polyethylene glycol 400 (PEG) and ethanol (1:1; w/v)
- Justification of choice of vehicle: The solvent in this vehicle promotes the formation of smaller particles due to its evaporation.
TEST ATMOSPHERE
- Particle size distribution: in the respirable range
- MMAD (Mass median aerodynamic diameter) / GSD (Geometric st. dev.): 1.4 / 2.2 - Analytical verification of test atmosphere concentrations:
- yes
- Duration of exposure:
- 4 h
- Concentrations:
- 0, 63.6, 64.7, 92.1, 243.1, 510.8 mg/m3 (males and females);
- No. of animals per sex per dose:
- 5 animals/ sex
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Body weights were measured before exposure, on days 3 and 7, and weekly thereafter. Individual weights are also recorded at death, if applicable. The period of observation was for 2 weeks.
The appearance and behavior of each rat were examined carefully several times on the day of exposure and at least once daily thereafter. Weekend assessments were made once a day (morning). Assessments from restraining tubes were made only if unequivocal signs occurred.
- Necropsy of survivors performed: yes
- Other observations: The rectal temperatures were measured directly after cessation of exposure (approximately within 14hour after the end of exposure) using a Digimed digital thermometer with a rectal probe for rats. - Statistics:
- yes
Results and discussion
Effect levels
- Key result
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- 74 mg/m³ air
- Based on:
- act. ingr. (total fraction)
- 95% CL:
- 67 - 85
- Exp. duration:
- 4 h
- Mortality:
- Mortalitiy was observed in males at and above 63.6 mg/m3 air, in females at and above 64.7 mg/m3.
- Clinical signs:
- other: Please refer to "Any other information on results incl. tables"
- Body weight:
- Decreased body weights were observed in both sexes.
- Gross pathology:
- Lung less collapsed, dark-red discolorations, intestine bloated, parenchymatous organs pale, corneal opacity.
- Other findings:
- RECTAL TEMPERATURE
The rats exposed to the test substance experienced a statistically significant decrease in body temperature.
Any other information on results incl. tables
CLINICAL SIGNS
Piloerection, hair-coat ungroomed, bradypnea, labored breathing pattern, dyspnea, irregular breathing pattern, motility reduced, limp, tremor, fasciculations, giddiness, high-legged gait, prostration (lying on belly), exophthalmos, miosis, corneal opacity, chromodacryorrhea, nostrils: red encrustations, salivation, pallor, emaciation, periorbicular red stains.
Table 1: Results summary
Atmosphere concentration | Toxicological | Duration | Time | Mortality |
male rats | ||||
0 | 0/0/5 | -- | -- | -- |
63.6 | 1/4/5 | 0 d – 9 d | 0 d | 20 |
64.7 | 2/3/5 | 0 d – 7 d | 0 d | 40 |
92.1 | 5/-‘/5 | -- | < 4 h | 100 |
243.1 | 5/-/5 | -- | < 4 h | 100 |
510.8 | 5/-/5 | -- | < 4 h | 100 |
female rats | ||||
0 | 0/0/5 | -- | -- | -- |
63.6 | 0/5/5 | 0 d – 6 d | -- | -- |
64.7 | 1/4/5 | 0 d – 7 d | 0 d | 20 |
92.1 | 4/2/5 | 0 d – 6 d | 0 d, 1 d | 80 |
243.1 | 5/-/5 | -- | < 4 h | 100 |
510.8 | 5/-/5 | -- | < 4 h | 100 |
LC50 males & females: 74 mg/m³ air |
# 1st number = number of dead animals
2nd number = number of animals with clinical signs
3rd number = number of animals used rats died during the exposure period
Applicant's summary and conclusion
- Interpretation of results:
- Category 2 based on GHS criteria
- Conclusions:
- The aerosolized test substance (liquid aerosol) proved to have a high acute inhalation toxicity. The LC50 inhalation of the test item in rats was 65 – 79 mg/m3 for 4 h (aerosol) exposure in males and females, respectively.
- Executive summary:
A study on the acute inhalation toxicity of the test substance on rats has been conducted in accordance with OECD Guideline No. 403, Directive 92/69/EEC and OPPTS 870.1300. Groups of rats were nose-only exposed to mean liquid aerosol concentrations of 64, 65, 92, 243, and 511 mg/m3 air. This concentration was chosen to meet the limit concentration defined by the OPPTS 870.1300 testing guideline. Attempts were made so that aerosol generated was respirable to rats. In all groups of rats exposed to the test substance a concentration-dependent mortality occurred on the day of exposure.
The following clinical signs were observed: piloerection, hair-coat ungroomed, bradypnea, labored breathing pattern, dyspnea, irregular breathing pattern, motility reduced, limp, tremor, fasciculations, giddiness, high-legged gait, prostration (lying on belly), exophthalmos, miosis, corneal opacity, chromodacryorrhea, nostrils: red encrustations, salivation, pallor, emaciation, periorbicular red stains, hypothermia, decreased reflexes, decreased body weights. Signs occurred in a concentrationdependent manner and subsided almost entirely up to the end of the first postexposure week. Necropsy findings were suggestive of increased bronchial secretions. All findings are consistent with the pathomechanism of a cholinesterase inhibitor. With respect to the respirability of the aerosol generated internationally recognized recommendations such as of SOT (1992) were fulfilled i.e. the average MMAD was «1.4 urn (GSD «2.2).
In summary, the aerosolized test substance (liquid aerosol) proved to have a high acute inhalation toxicity. The LC50 inhalation of the test item in rats was 65 – 79 mg/m3 for 4 h (aerosol) exposure in males and females, respectively.
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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