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EC number: 946-382-0 | CAS number: -
- 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
In an acute oral toxicity study with PEMP conducted conform OECD guideline 401, the LD50 was calculated as 1085 mg/kg bw for male, 908 mg/kg bw for female and 993 mg/kg bw for male/female. An acute dermal toxicity test was conducted according to OECD/ EC guidelines and GLP principles with PEMP. Based on the results it is concluded that the dermal LD50 of this test substance is > 2000 mg/kg bw. Both studies have Klimisch reliability 1.
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:
- April 4, 1990 - April 26, 1990
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Non-GLP study, however study was conducted in compliance with the Good Laboratory Practice Standards of the Environmental Protection Agency FIFRA, 40 CFR Part 160; the Environmental Protection Agency TSCA, 40 CFR part 792 and the OECD guideline 401.
- Qualifier:
- according to guideline
- Guideline:
- other: Pesticide Assessment Guidelines, subdivision F; Section 81-1, Acute oral Toxicity (Sept 1985)
- Qualifier:
- according to guideline
- Guideline:
- other: TSCA: Section 798.1175 (Sept 1985)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Version / remarks:
- february 24, 1987
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Specific details on test material used for the study:
- The test was performed with PEMP product, the registered substance.
- Species:
- rat
- Strain:
- other: CD (Sprague-Dawley derived)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles river Breeding laboratories, Inc., Wilmington, Massachusetts 01887
- Age at study initiation: Appr. 9-12 weeks
- Weight at study initiation: 273-326 g (males); 236-270 g (females)
- Fasting period before study: yes, o/n prior to dosing (appr. 18 hours)
- Housing: individually housed in suspended, stainless steel cages with wire mesh bottoms
- Diet: ad libitum, Purina Laboratory Chow
- Water: ad libitum, tap water
- Acclimation period: at least 15 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): no information, monitored and recorded twice daily
- Humidity (%): no information, monitored and recorded twice daily
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: April 4, 1990 To: April 26, 1990 - Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- Maximum dose volume applied: 1.1 mL/kg
- Doses:
- 350, 500, 700, 1000 and 1400 mg/kg bw
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations: Twice daily (viability check) and appr. 1, 2 and 4 hours after dosing and daily thereafter (clinical signs)
- Frequency of weighing: prior to fasting, just prior to dosing, day 7 and day 14 (any animal which did not survive for 14 days were weighed at the time of death or at the time that they were found dead)
- Necropsy of survivors performed: yes (all animals except animals used in dose-range finder) - Statistics:
- The LD50 was calculated following the method described by Litchfield and Wilcoxon: "A simplified methods of evaluating dose- effect experiments", J. Pharma.Exp. Ther. 96: 99-113 (1949).
- Preliminary study:
- No mortality was seen up to 500 mg/kg bw. At 1000 mg/kg bw (given with corn oil as vehicle), one animal died. At 1000 mg/kg bw (without vehicle), also one animal died. All animals died at 2500 and 5000 mg/kg bw.
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 700 - <= 1 000 mg/kg bw
- Based on:
- test mat.
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- 1 085 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- >= 883 - <= 1 333
- Remarks on result:
- other: Calculated LD50
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- 908 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- >= 744 - <= 1 109
- Remarks on result:
- other: Calculated LD50
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- 993 mg/kg bw
- Based on:
- test mat.
- 95% CL:
- >= 863 - <= 1 141
- Remarks on result:
- other: Calculated LD50
- Mortality:
- No males died up to 700 mg/ kg bw. One female died at 700 mg/kg bw (at 4 hours post-dose). At 1000 mg/kg bw, 2/5 males died and 3/5 females (at 4 and 5 (males),6, 22 and 22 hours (females) post-dose). At 1400 mg/kg bw, 4/5 males and all females died (at 6 (2 males) and 22 (2 males) hours post-dose; females died after 2 hours (2 females), 6 hours (2 females) and 22 hours post-dose.
- Clinical signs:
- Nasal and oral discharge, fecal staining, abdominal griping and hypoactivity were noted in most groups at the day of dosing. The number of animals affected was dose-related. Additionally, for some animals convulsions, hyperpnea, ocular discharge and urinary staining were observed. Several animals had decreased food intake on the day of dosing (for one female dosed at 1000 mg/ kg bw, this continued until day 9).
After day 9, no further clinical signs were noted in the surviving animals. - Body weight:
- The average weight increase did not change for males exposed up to and including 700 mg/kg bw. At higher doses, the body weight gain decreased. For females, the average body weight gain was similar for females exposed to 350 and 500 mg/ kg bw. The surviving anmals at higher doses showed decreased body weight gain.
- Gross pathology:
- Gross pathology revealed substance-related changes in the lungs (at 700 mg/kg bw discoloration of the lung was seen in female that was found dead; at higher doses red foci in the lung were seen (one male and one female at 1000 mg/kg bw) and discoloration of the lungs (males and females at 1000 and 1400 mg/kg bw). Furthermore, abnormalities in the gastrointestinal tract were found. In animals exposed to 1000 or 1400 mg/kg bw that were found dead, a yellow fluid was found in the intestines. One male in the group dosed at 1400 mg/ kg bw had red fluid in the intestine. Another male in this group had a thickened stomach wall, and a female at this dose had yellow fluid in the stomach.
- Interpretation of results:
- Category 4 based on GHS criteria
- Conclusions:
- In an acute oral toxicity study with PEMP conducted conform OECD guideline 401, an LD50 of 908 mg/kg bw was found.
- Executive summary:
In an oral toxicity study performed in general conformance with OECD guideline 401, PEMP was dosed to male and female rats (5/ sex/ dose) at 350, 500, 700, 1000 and 1400 mg/kg bw. No males died up to 700 mg/kg bw, one female died at 700 mg/kg bw. At 1000 mg/kg bw, 2/5 males died and 3/5 females and at 1400 mg/kg bw, 4/5 males and all females died. All rats died within 24 hours of dosing. Several clinical signs were noted, including nasal and oral discharge, fecal staining, abdominal griping and hypoactivity at the day of dosing. The number of animals affected was dose-related. Additionally, for some animals convulsions, hyperpnea, ocular discharge and urinary staining were observed. Several animals had decreased food intake on the day of dosing (for one female dosed at 1000 mg/kg bw, this continued until day 9). At necropsy, substance-related changes in the lungs at 700 mg/kg bw and above were seen (discoloration and/or red foci in the lung). Furthermore, abnormalities in the gastrointestinal tract were found. In animals exposed to 1000 or 1400 mg/kg bw that were found dead, a yellow fluid was found in the intestines. One male in the group dosed at 1400 mg/kg bw had red fluid in the intestine. Another male in this group had a thickened stomach wall, and a female at this dose had yellow fluid in the stomach.
Based on these data, the oral LD50 for PEMP was determined to be 908 mg/kg bw, the substance is classified for oral toxicity in category 4 according to Regulation (EC) 1272/2008.
Reference
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 908 mg/kg bw
- Quality of whole database:
- Non-GLP study, however study was conducted in compliance with the Good Laboratory Practice Standards of the Environmental Protection Agency FIFRA, 40 CFR Part 160; the Environmental Protection Agency TSCA, 40 CFR part 792 and the OECD guideline 401 (Klimisch 1).
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:
- 25 June - 9 July 1992
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Version / remarks:
- (1981)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.3 (Acute Toxicity (Dermal))
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Date of Inspection 17 March 1992
- Test type:
- standard acute method
- Limit test:
- yes
- Specific details on test material used for the study:
- The test was performed with PEMP product, the registered substance.
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River (UK) Ltd., Manston, Kent, U.K.
- Age at study initiation: appr. 10-14 weeks
- Weight at study initiation: 230-241g (males); 209-227g (females)
- Fasting period before study: No
- Housing: In suspended polypropylene cages, individually during 24-hour exposure period and group-housed with 5 animals per cage thereafter
- Diet: Ad libitum, Rat and Mouse Expanded Diet No. 1, Special Diet Services Limited, Witham, Essex, U.K.
- Water: Ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-23
- Humidity (%): 47-75
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: From: 25 June 1992 To: 9 July 1992 - Type of coverage:
- semiocclusive
- Vehicle:
- unchanged (no vehicle)
- Details on dermal exposure:
- TEST SITE
- Area of exposure: 5 cm * 4 cm
- % coverage: appr. 10% of total body surface area
- Type of wrap if used: surgical gauze held in place by a piece of self-adhesive bandage (HYPERTIE and BLENDERM)
REMOVAL OF TEST SUBSTANCE
- Washing (if done): no, exposure area was wiped with cotton wool moistened with distilled water
- Time after start of exposure: 24 hours
TEST MATERIAL
- Amount applied: 2000 mg/ kg bw - Duration of exposure:
- 24 hours
- Doses:
- 2000 mg/kg bw
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations: 0.5, 1,2 and 4 hours after dosing and subsequently once daily
- Frequency of weighing: prior to application on day 0 and on days 7 and 14
- Necropsy of survivors performed: yes (gross macroscopy)
- Other examinations performed: any adverse dermal reactions were recorded - Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- No mortality occurred.
- Clinical signs:
- No clinical signs were noted during the study.
- Body weight:
- All animals showed expected body weight gain during the study.
- Gross pathology:
- The macroscopic observations did not reveal any abnormalities.
- Other findings:
- Adverse skin reactions were noted for three females: haemorrhage of the dermal capillaries, moderate erythema, keratolysis (glossy skin), small superficial scattered scabs and desquamation. The skin of these treated animals appeared normal 7 days after treatment.
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- An acute dermal toxicity test was conducted according to OECD/ EC guidelines and GLP principles with PEMP. Based on the results it is concluded that the dermal LD50 of this test substance is > 2000 mg/kg bw.
- Executive summary:
An acute dermal toxicity test was conducted according to OECD/ EC guidelines and GLP principles with PEMP. Five male and five female rats were semi-occlusively exposed for 24 hours to 2000 mg/kg bw. No mortality occurred, no clinical signs were noted. Three females were found to have adverse skin reactions, including haemorrhage of the dermal capillaries, moderate erythema, keratolysis (glossy skin), small superficial scattered scabs and desquamation. The skin of these treated animals appeared normal 7 days after treatment.
Based on these data, the dermal LD50 for PEMP was determined to exceed 2000 mg/kg bw, therefore the substance is not classified for dermal toxicity according to Regulation (EC) 1272/2008.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
- Quality of whole database:
- The study was performed according to OECD/EC guidelines and GLP principles.
Additional information
In an oral toxicity study performed in general conformance with OECD guideline 401, PEMP was dosed to male and female rats (5/ sex/ dose) at 350, 500, 700, 1000 and 1400 mg/kg bw. No males died up to 700 mg/kg bw, one female died at 700 mg/kg bw. At 1000 mg/kg bw, 2/5 males died and 3/5 females and at 1400 mg/kg bw, 4/5 males and all females died. All rats died within 24 hours of dosing. Several clinical signs were noted, including nasal and oral discharge, fecal staining, abdominal griping and hypoactivity at the day of dosing The number of animals affected was dose-related. Additionally, for some animals convulsions, hyperpnea, ocular discharge and urinary staining were observed. Several animals had decreased food intake on the day of dosing (for one female dosed at 1000 mg/kg bw, this continued until day 9). At necropsy, substance-related changes in the lungs at 700 mg/kg bw and above were seen (discoloration and/or red foci in the lung). Furthermore, abnormalities in the gastrointestinal tract were found. In animals exposed to 1000 or 1400 mg/kg bw that were found dead, a yellow fluid was found in the intestines. One male in the group dosed at 1400 mg/ kg bw had red fluid in the intestine. Another male in this group had a thickened stomach wall, and a female at this dose had yellow fluid in the stomach. Based on these data, the oral LD50 for PEMP was calculated to be1085mg/kg bwfor maleand 908 mg/kg bw for female.
An acute dermal toxicity test was conducted according to OECD/ EC guidelines and GLP principles with PEMP. Five male and five female rats were semi-occlusively exposed for 24 hours to 2000 mg/kg bw. No mortality occurred, no clinical signs were noted. Three females were found to have adverse skin reactions, including haemorrhage of the dermal capillaries, moderate erythema, keratolysis (glossy skin), small superficial scattered scabs and desquamation. The skin of these treated animals appeared normal 7 days after treatment.
Justification for classification or non-classification
The oral LD50 for PEMP was determined to be 908 mg/kg bw, the substance is classified for oral toxicity in category 4 according to Regulation (EC) 1272/2008.
The dermal LD50 for PEMP was determined to exceed 2000 mg/kg bw, therefore the substance is not classified for dermal toxicity according to Regulation (EC) 1272/2008.
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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