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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 232-623-0 | CAS number: 9001-66-5
- 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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- sensitisation (respiratory tract)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- sensitisation (respiratory tract)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DMEL (Derived Minimum Effect Level)
- Value:
- 60 ng/m³
- Most sensitive endpoint:
- sensitisation (respiratory tract)
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- sensitisation (respiratory tract)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
Worker DMEL, acute short-term as well as long-term inhalation exposure:
Potential occupational exposure to levels of enzyme, which is toxicologically relevant, is unrealistic due to the stringent work practices and adherence to the voluntary Occupational Exposure Guidelines at or below the established ACGIH (www.acgih.org, the American Conference of Governmental Industrial Hygienists) exposure limit value of 60 ng/m3, based on pure enzyme protein for the benchmark enzyme Subtilisin.
Worker DMEL has been discussed and concluded by the involved industry in a recent publications (see reference list) and a limit of 60 ng/m3, expressed in pure enzyme protein, was suggested (Basketter et al, 2010) in line with the established ACGIH threshold limit value.
Worker DNEL, acute short-term as well as long-term dermal exposure:
Investigations of percutaneous absorption of peptides, proteins and other molecules of large size revealed that percutaneous absorption of proteins is extremely low and of no toxicological relevance (Basketter et al, 2012 a and b). This is further supported by the physico-chemical data of monoamine oxidase. This substance is a protein with a molecular weight above 50,000 D, has a low logPow value (<0), indicating that it has no bioaccumulation potential and can be anticipated to be readily biodegraded. Thus, systemic exposure following enzyme exposure at occupational exposure levels is without toxicological significance. Non-proteases, such as monoamine oxidase, lack the potential to be skin and eye irritants.
References
Basketter, D., Berg, N., Broekhuizen, C., Fieldsend, M., Kirkwood, S., Kluin, C., Mathieu, S. and Rodriguez, C., 2012a. Enzymes in cleaning products: an overview of toxicological properties and risk assessment/management. Regulatory Toxicology and Pharmacology, 64(1), pp.117-123.
Basketter, D., Berg, N., Kruszewski, F.H., Sarlo, K. and Concoby, B., 2012b. The toxicology and immunology of detergent enzymes. Journal of immunotoxicology, 9(3), pp.320-326.
Basketter, D.A., Broekhuizen, C., Fieldsend, M., Kirkwood, S., Mascarenhas, R., Maurer, K., Pedersen, C., Rodriguez, C. and Schiff, H.E., 2010. Defining occupational and consumer exposure limits for enzyme protein respiratory allergens under REACH. Toxicology, 268(3), pp.165-170.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- sensitisation (respiratory tract)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- sensitisation (respiratory tract)
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DMEL (Derived Minimum Effect Level)
- Value:
- 15 ng/m³
- Most sensitive endpoint:
- sensitisation (respiratory tract)
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- sensitisation (respiratory tract)
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
Consumer DMEL, acute short-term as well as long-term inhalation exposure, systemic and local:
The risk to consumers is considered very low and regarded as toxicologically insignificant (Basketter et al, 2010, Basketter et al, 2012 a and b). Consumer DMEL has been discussed among the enzyme allergy specialists from enzyme and detergent manufacturers and it was concluded by the involved industry partners in a recent publication and the limit of 15 ng/m3 was suggested (Basketter et al, 2010).
Consumer DNEL, acute short-term as well as long-term dermal exposure:
Investigations of percutaneous absorption of peptides, proteins and other molecules of large size revealed that percutaneous absorption of proteins is extremely low and of no toxicological relevance (Basketter et al, 2012 a and b). This is further supported by the physico-chemical data of monoamine oxidase. This substance is a protein with a molecular weight above 50,000 D, has a low logPow value (<0), indicating that it has no bioaccumulation potential and can be anticipated to be readily biodegraded. Thus, systemic exposure following enzyme exposure at occupational exposure levels is without toxicological significance. Non-proteases, such as monoamine oxidase, lack the potential to be skin and eye irritants.
Consumer DNEL, acute short-term as well as long-term systemic oral exposure:
CDX-616 has not been engineered for gastric stability and would be digested/hydrolyzed when ingested. Like all proteins, enzymes that have not been engineered for low pH and/or gastric stability, will denature or degrade into amino acids.
References
Basketter, D.A., Broekhuizen, C., Fieldsend, M., Kirkwood, S., Mascarenhas, R., Maurer, K., Pedersen, C., Rodriguez, C. and Schiff, H.E., 2010. Defining occupational and consumer exposure limits for enzyme protein respiratory allergens under REACH. Toxicology, 268(3), pp.165-170..
Basketter, D., Berg, N., Broekhuizen, C., Fieldsend, M., Kirkwood, S., Kluin, C., Mathieu, S. and Rodriguez, C., 2012a. Enzymes in cleaning products: an overview of toxicological properties and risk assessment/management. Regulatory Toxicology and Pharmacology, 64(1), pp.117-123..
Basketter, D., Berg, N., Kruszewski, F.H., Sarlo, K. and Concoby, B., 2012b. The toxicology and immunology of detergent enzymes. Journal of immunotoxicology, 9(3), pp.320-326.
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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