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EC number: 849-290-8 | CAS number: 9001-97-2
- 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 highest concentration (undiluted concentrate) of 1,4-alpha-glucan branching enzyme, batch PPY 27209 did not cause any adverse changes in any of the investigated parameters in the sub-chronic toxicity study in rats. Therefore, the no-observed-adverse-effect level (NOAEL) for 1,4-alpha-glucan branching enzyme, batch PPY 27209 was considered to be 1128 mg Dry matter/kg bw/day for both sexes.
Key value for chemical safety assessment
- Toxic effect type:
- dose-dependent
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 06 July 2007 to 13 March 2008
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- This assessment of sub-chronic systemic toxicity (according to OECD TG 408) has been performed due to data requirements from the European Food Safety Authority (EFSA), as this enzyme also comply with the regulatory system of FIAP [REGULATION (EC) No 1331/2008 and EFSA CEF guidance from 2009/2013]. Moreover; it has been generated in accordance with Directive 2010/63/EU.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Version / remarks:
- Adopted 21st September 1998.
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland, Sulzfeld, Germany
- Females nulliparous and non-pregnant: Yes
- Age at study initiation: approximately 6 week
- Weight at study initiation: Weighed 135.2 g (mean for females) and 179.6 g (mean for males)
- Fasting period before study: None
- Housing: In Macrolon cages (480 x 375 x 210 mm) with sterilized wood shavings (Lignocel, Type 3/4) as bedding material and strips of paper (Enviro-dri) as environmental enrichment.
- Diet: Rat & Mouse No. 3 Breeding Diet, RM3; pelleted
- Water: Ad libitum. Water, taken from the public supply.
- Acclimation period: 13 days
ENVIRONMENTAL CONDITIONS
- Temperature : 20-24°C
- Humidity : 40-70% RH
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- water
- Remarks:
- and purified water for the other control
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Dilutions of the test substance in the vehicle were prepared weekly and stored in closed vials (one vial per group per day) in a freezer at < -18ºC.
VEHICLE
- The vehicle for dosing the controls was stored as described above.
- Amount of vehicle (if gavage): constant volume 10 mL/kg body weight/day. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Samples of formulations prepared for administration on one occasion in Week 1 and 13 were taken for content check analysis. The results of these analyses indicated values close and acceptable to the intended enzyme activity.
- Duration of treatment / exposure:
- 13 weeks
- Frequency of treatment:
- Daily
- Dose / conc.:
- 113 mg/kg bw/day (nominal)
- Remarks:
- Concentration is in mg Enzyme concentrate dry matter.
- Dose / conc.:
- 372 mg/kg bw/day (nominal)
- Remarks:
- Concentration is in mg Enzyme concentrate dry matter.
- Dose / conc.:
- 1 128 mg/kg bw/day (nominal)
- Remarks:
- Concentration is in mg Enzyme concentrate dry matter.
- No. of animals per sex per dose:
- 20
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The highest dose (100%) is the maximum practical dose and represents administration of the enzyme, as received, at a volume dosage of 10 mL/kg body weight.
- Positive control:
- Not included
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: At least twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Individual observations of all animals were also recorded before and after dosing on each day of treatment as indicated below. The timing of these observations were performed to establish and confirm any pattern of signs.
BODY WEIGHT: Yes
- Time schedule for examinations: The weight of each animal was recorded during the acclimatisation period, on the day that treatment commenced, at weekly intervals throughout the treatment period and before necropsy.
FOOD CONSUMPTION: Yes
- The weight of food supplied to each cage, that remaining and an estimate of the amount spilled was recorded for each week throughout the treatment period. From these records the mean weekly consumption per animal was calculated for each cage.
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: Were made prior to the start of treatment in all rats, and in the last week of the treatment period in all rats of the control group and the high-dose group.
- Dose groups that were examined: Observations were bilateral unless otherwise indicated.
HAEMATOLOGY: Yes
- Time schedule for collection of blood: Week 13
Differential leucocyte counts were determined automatically by counting the numbers of lymphocytes, neutrophils, monocytes, eosinophils, basophils and large unstained cells in the instrument sample.
CLINICAL CHEMISTRY: Yes
The concentration of each protein fraction was determined by reference to the percentage value and to the total protein concentration. Albumin to globulin (A/G) ratios were calculated from the percentage values before conversion to absolute concentrations. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes
ORGAN WEIGHTS: Yes - Statistics:
- The main tests used were analysis of covariance (ANOVA), Shapiro-Wilks test, Dunnett's multiple comparison test, Kruskal-Wallis non-parametric analysisi, Pearson chisquare analysis, and Fisher's Exact Probability test. Significant differences between the groups compared were expressed at the 5% (p<0.05) level.
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- Only a significantly lower mean corpuscular haemoglobin concentration (MCHC) in high-dose males were observed. This change was not seen in females and was not estimated to be test item related.
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- no effects observed
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Description (incidence and severity):
- The following statistically significant differences in organ weights were observed compared to controls: 1) Absolute brain weight was significantly lower in males of the high-dose group, 2) Relative liver weight was significantly higher in males of the high-dose group and 3) Absolute and relative weight of the epididymides was significantly lower in the mid-dose group. None of these observations were considered test item related.
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- A statistically significantly increased incidence of renal basophilic tubules was observed in mid-dose males. Since basophilic tubules are part of common background pathology in (particularly male) rats with rather large variations in incidence, and a comparable finding was not observed in high-dose males or treated females, this finding was not considered to be related to the test-substance.
- Histopathological findings: neoplastic:
- no effects observed
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- >= 1 128 mg/kg bw/day (nominal)
- Based on:
- other: Enzyme concentrate dry matter
- Sex:
- male/female
- Basis for effect level:
- other: No adverse effects were seen so NOAEL was the highest dose administered.
- Critical effects observed:
- no
- Conclusions:
- Undiluted concentrate of 1,4-alpha-glucan branching enzyme, batch PPY 27209 did not cause any adverse changes in any of the investigated parameters in the sub-chronic toxicity study in rats. Therefore, the no-observed-adverse-effect level (NOAEL) for 1,4-alpha-glucan branching enzyme, batch PPY 27209 was considered to be 1128 mg Enzyme concentrate dry matter/kg bw/day for both sexes.
- Executive summary:
The objective of this study was to provide data on the possible sub-chronic toxicity of 1,4-alpha-glucan branching enzyme, batch PPY 27209 in rats of both sexes upon daily oral administration by gastric gavage for 13 consecutive weeks. Rats were exposed to 113, 372, 1128 mg Enzyme concentrate dry matter/kg bw/day.
Clinical observations, neurobehavioural testing, growth, food and water consumption, ophthalmoscopy, haematological and clinical chemistry parameters, gross examination at necropsy, organ weights and microscopic examination of various organs and tissues were used as criteria for disclosing possible harmful effects.
No indication of toxicity of the test substance was observed after oral adminitration in rats, since none of the parameters investigated showed any treatment-related or toxicologically relevant changes.
In conclusion, undiluted concentrate of 1,4-alpha-glucan branching enzyme, batch PPY 27209 did not cause any adverse changes in any of the investigated parameters in the sub-chronic toxicity study in rats. Therefore, the no-observed-adverse-effect level (NOAEL) for 1,4-alpha-glucan branching enzyme, batch PPY 27209 was considered to be 1128 mg Enzyme concentrate dry matter/kg bw/day for both sexes.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 128 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
Additional information
Justification for classification or non-classification
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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