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EC number: 232-730-2 | CAS number: 9012-33-3
- 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
Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Data waiving:
- other justification
- Justification for data waiving:
- other:
Reference
Description of key information
The solubility of enzymes is generally between 0.5 and 250 g/L in tap water (moderate salinity at pH 7 or just below). Increasing pH generally leads to higher solubility.
Key value for chemical safety assessment
- Water solubility:
- 125 g/L
- at the temperature of:
- 25 °C
Additional information
The solubility of beta-N-acetylhexosaminidases purified water at pH 7 is between 0.5 and 250 g/L.
The degree of solubility at a given pH is depending on several factors, e.g. temperature, the amino acid sequence and structure of the enzyme and other components in the system such as salts. The amino acid sequence and structure affect the polarity, including the isoelectric point (pI) of the enzyme, which is an important factor for solubility. Thus, the difference in solubility is a reflection of the variation in the amino acid sequence. In addition, post translational modifications influence solubility, where the most important is glycosylation, which typically increases the solubility. The influence of pH and salt concentration on protein stability has been investigated (Carbannaux et al., 1995; Green, 1933; Guilloteau et al., 1992; Hofmeister, 1888). The effects of anions and cations on protein solubility in general are described by the Hofmeister series (Hofmeister, 1888). All indicate that the solubility of proteins like enzymes is dependent on the conditions in a given environment.
Enzymes generally have the lowest solubility when the pH is close to pI (+/- 1 pH unit) and the solubility increases when pH is shifting away from pI, as long as the pH is not denaturing the enzyme. The pI of beta-N-acetylhexosaminidases ranges from 6.63-7.9 (http://www.brenda-enzymes.info/). Studies on different enzymes covering alpha-amylases (Faber et al., 2007) and proteases (HERA, 2007)* show high solubility (60 -100 g/L) at pH between 6 to 8.
The conclusion is that the water solubility differs between different enzymes within the same class, due to difference in amino acid sequence and presence of post translational modifications. Water solubility is also highly dependent on the aqueous environment, i.e. pH, salts present, temperature and stabilizing agents, and it is thus not possible to give one water solubility value for all industrial produced enzymes but only a range. Industrial enzymes are produced in submerged fermentation followed by downstream purification. The final product is a mixture of the enzyme, other constituents from the fermentation and stabilizing agents that are added in the downstream processing. In general, solubility data are based either on finished products or enzymes purified in buffer and salts and not in purified water alone.
References:
Carbonnaux C, Riès-Kautt M, Ducruix A. (1995). Protein Science, 4(10):2123 -2128.
Green AA. (1932). Physical Chemistry of Proteins. 10:47-66.
Guilloteau J P, Riès-Kautt M, Ducruix A. (1992). Variation of lysozyme solubility as a function of temperature in the presence of organic and inorganic salts. J. Crystal Growth, 122(1 -4):223-230.
Hofmeister F. (1888); Archiv für experimentelle Pathologie und Pharmakologie, 24, 247 -260.
Faber C, Hobley TJ, Mollerup J, Thomas ORT and Kaasgaard SG. (2007). Study of the Solubility of a Modified Bacillus licheniformis α-Amylase around the Isoelectric Point. J. Chem. Eng. Data, 52:707-713
HERA (Human & Environmental Risk Assessment) on ingredients of household cleaning products, (2007); Subtilisins (Protease) CAS No: 9014-01-1, 1395-21-7, 9073-77-2, 9001-92-7, 79986-26-8, 95979-76-3, 68909-17-1. *NOTE: Data published in HERA 2007 as “> 1 kg/L”, but has to be corrected to “> 100 g/L”.
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