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EC number: 216-133-4 | CAS number: 1506-02-1
- 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

Endpoint summary
Administrative data
Description of key information
The dermal and oral toxicity of AHTN are determined by a number of studies. Based on the lowest reliable LD50 for AHTN, the classification of category 4 of the acute oral toxicity applies (Harmful if swallowed).
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 9 August 1985 - 23 August 1985
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted in accordance with GLP requirements and OECD 401 method.
- Reason / purpose for cross-reference:
- reference to other study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- yes
- Remarks:
- The variation in volume of dosing; that recommendation was not part of that guideline.
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Cpb:Wu;Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Young adult, SPF—bred albino rats (Cpb:Wu;Wistar random) were used. They were obtained from the Central Institute for the Breeding of Laboratory Animals TNO, Zeist, the Netherlands. The body weights of the males varied from 245 to 283 g, those of the females from 162 to 187 g. The rats were kept under the environmental conditions of the Institute’s animal house for 1 week prior to the test.
Species: albino ratis, male: weight 245-283 g and female: weight 162-187 g.Test conditions: temperature: 22 =/-2 degreesCelsius. Relative humidity; 40-60 % 12 hours light/12 hours dark. Food: cereal-based diet. - Route of administration:
- oral: gavage
- Vehicle:
- other: isopropyl myristate (IPM)
- Doses:
- 17.5% Tonalid in IPM. Dose: 4.00, 4.80, 5.76, 6.91, 8.29 ml/kg body weight euivalent to 700, 840, 1008, 1209, 1451 g/kg body weight.
- No. of animals per sex per dose:
- 10 (5 male and 5 female)
- Control animals:
- no
- Statistics:
- The LD5O was calculated according to the method of Weil, C.W., Biometrics 8 (1952) 249-263
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- 920 mg/kg bw
- 95% CL:
- > 795 - < 1 066
- Mortality:
- Deaths occurred between 6 hours and 8 days after dosing.
- Clinical signs:
- other: Within a few hours after dosing the rats showed sluggishness and piloerection. - Later on haematuria was observed until 2 days after treatment. After a few days, moreover, encrustations around eyes and nostrils, and signs of’ emaciation were observed. The
- Gross pathology:
- Macroscopic examination at autopsy of the rats that died in the first few post—treatment days revealed blood—stained urine in the bladder of all rats. In the rats that died thereafter and in those that survived the observation period no treatment—related gross alterations were found.
- Interpretation of results:
- Category 4 based on GHS criteria
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- After treatment, the rats showed sluggishness, piloerection, haematuria, encrustations around eyes and nostrils & signs of emaciation. Deaths occurred between 6 hours and 8 days after treatment. The oral LD50 of Tonalid was found to be 920 mg per kg body weight with 795 and 1066 as the 95% confidence limits.
- Executive summary:
Groups of five male and five female young adult albino rats were administered by gavage 4.00, 4.80, 5.76, 6.91 or 8.29 ml/kg bw of a 17.5% (w/v) solution of AHTN (Tonalid®; purity =98%; equivalent to doses of 700, 840, 1008, 1209 and 1451 mg/kg bw AHTN) in isopropyl myristate and observed for 14 days. Within a few hours, signs of sluggishness and piloerection were seen. Later on haematuria, encrustrations around eyes and nostrils and signs of emaciation were observed. Death occurred between 6 hours and 8 days of dosing at which time survivors recovered gradually looking healthy at the end of the observation period. Macroscopic examination at autopsy of the rats that died in the first few days revealed blood stained urine in the bladder. No other treatment-related gross alterations were seen in these or other animals. An LD50 of 920 mg/kg bw was calculated.
Source: EU Risk Asssessment Report AHTN, Luxembourg, Office for Official Publications of the European Communities, ECB (May 2008)
Reference
Table 1 Body weight and mortality rate in rats after a single oral dose administration in rats
Bodyweights on day (g) | Mortality | |||||||
Dose | Males | Females | Males | Females | ||||
mg/kg bw | 0 days | 7 days | 14 days | 0 days | 7 days | 14 days | ||
700 | 268 | 280 | 315 | 172 | 171 | 191 | 1/5 | 0/5 |
840 | 254 | 212 | 273 | 170 | 157 | 170 | 4/5 | 0/5 |
1008 | 266 | 235 | 287 | 178 | 150 | 196 | 3/5 | 4/5 |
1209 | 257 | 250 | 304 | 174 | 152 | 175 | 4/5 | 3/5 |
1451 | 260 | - | - | 173 | - | - | 5/5 | 5/5 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 920 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 7 June 1977 - 12 August 1977
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: This study was conducted prior to GLP and OECD guidelines, but was according to acceptable procedures at that time.
- Principles of method if other than guideline:
- Sprague-Dawley rats were administered AHTN in absolute ethanol (or undiluted) by dermal application to the shaved skin, and were observed for mortality and clinical effects immediately after the dosing at 1, 4, and 24 hours, and also once daily thereafter for a total of 7 days.
- GLP compliance:
- not specified
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- Initial body weight ranged from 108 to 197 grams, and the animals were fasted overnight prior to dosing.
- Type of coverage:
- not specified
- Vehicle:
- ethanol
- Details on dermal exposure:
- AHTN was administered by gentle inunction to the shaved skin of 5 groups of five female rats
- Duration of exposure:
- single administration of dose
- Doses:
- 0.5 to 10 g/kg
- No. of animals per sex per dose:
- 5 (5 groups of 5 animals)
- Control animals:
- no
- Statistics:
- Mortality data was analyzed statistically, utilising the tables of Horn, H.J., Biometrics 12, 311, 1956.
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- 7 940 mg/kg bw
- 95% CL:
- 4 890 - 12 900
- Remarks on result:
- other: Assuming all dead at 21500 mg/kg.
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- LD 50 AHTN = 7940 mg/kg, which is larger than the upper limit for classification dermal toxicity (i.e. 2000 mg/kg).
- Executive summary:
Groups of 5 female rats were fasted overnight prior to the experiment, and the test material in absolute ethanol was applied to the shaved skin of the animals. Observations for mortality and clinical effects were conducted immediately after the dosing at 1, 4, and 24 hours, and also once daily thereafter for a total of 7 days. Gross necropsy was conducted on all animals (those that died or were sacrificed at the end of the study). The LD50 value was 7.94 g/kg. Animals found dead exhibited the effects expected at their respective stages of autolysis; all other animals exhibited no remarkable necropsy findings.
Reference
Major necropsy findings: animals found dead exhibited the effects expected at their respecive stages of autolysis; all other animals exhibited no remarkable necroscopy findings.
Table 1: Mortality data and toxic effects of Fixolide tested on acute dermal toxicity on rats.
Dose | Concentration | Time of death | ||
g/kg bw | % in ethanol | Immediate | 1-24 h. | 24-48h. |
0.464 | 10 | 0/5 | 0/5 | 0/5 |
1.000 | 10 | 0/5 | 0/5 | 1/5 |
2.150 | 10 | 0/5 | 0/5 | 0/5 |
4.640 | 20 | 0/5 | 0/5 | 1/5 |
10.000 | 40 | 0/5 | 0/5 | 3/5 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 7 940 mg/kg bw
Additional information
AHTN should be classified as "Harmful if swallowed" according to Table 3.1.2 of the CLP regulation (EC 1272/2008). The EU Risk Assessment report mentioned LD50 of an oral intubation study from Minner [1] of 825 mg/kg, while an intraperitoneal study in the same report showed the lowest LD50 of 79 mg/kg. Nevertheless, the latter study is very old, not conducted according to an OECD method and not conducted by a GLP accredited company.
An intraperitoneal GLP study on mice was performed by Gudi [2] showing a LD50 of ca. 2000 mg/kg. Three tests from Spanjers (1985) showed similar LD50 values and all three concluded that AHTN should be classified as harmful if swallowed. The lowest LD50 (oral) obtained from the key studies was selected to carry forward in the risk assessment (Spanjers 1985a).
The three oral toxicity studies from Spanjers (1985) show steep dose response curves (see attachment "figure acute toxicity mortality rats"). The key study used in determining the LC50 shows a LOAEL of around 700 mg/kg bw. The mortality rate in the Spanjers 1985b curve starts already at 40% for the lowest dose in that study. The curves in the study Spanjers 1985b and 1985c have shifted towards higher concentrations. The mortality rate in the Spanjers 1985b study is already 40% at the lowest concentration. The study of Spanjers 1985c confirms the study of Spanjers 1985a even though it contains one outlier in the dose-response curve.
Loss in weight has been described extensively in several studies, also in other toxicity studies. However, this weight loss is fully reversible after the exposure period and although this is a sub-lethal adverse effect, only the acute toxicity for a single exposure is considered here.
AHTN should not be used for human ingestion and exposure is purely of accidental nature.
Based on the three studies, taking the LOAEL of the most conservative curve (Spanjers 1985a), the LOAEL can be converted into a NOAEL by applying an assessment factor of 3.
Referenced in EU Risk Assessment Report AHTN, ECB (May 2008)
[1] Minner and Foster, Comparative acute toxicity studies in the female rat with five synthetic musk chemicals, 1977
Justification for classification or non-classification
The test substance has to be classifiedas category 4 for acute oral toxicity according to Regulation (EC) No 1272/2008, based on the acute oral toxicity test (Spanjers 1985a).
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