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EC number: 209-795-0 | CAS number: 593-51-1
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data from peer review journal
- Justification for type of information:
- Data from peer review journal
- Qualifier:
- according to guideline
- Guideline:
- other: as per mentioned below
- Principles of method if other than guideline:
- Short term toxicity to Microcystis aeruginosa study was carried out for 24 hrs.
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Methylamine hydrochloride
- Molecular formula (if other than submission substance): CH5N.Cl H
- Molecular weight (if other than submission substance): 67.5184 g/mol
- Smiles notation (if other than submission substance): C[NH3+].[ClH-]
- InChl (if other than submission substance): 1S/CH5N.ClH/c1-2;/h2H2,1H3;1H
- Substance type: Organic
- Physical state: Solid - Analytical monitoring:
- not specified
- Details on sampling:
- - Concentrations: 20 mg/l (nominal concentrations)
- Sampling method: Test chemical was prepared in stock solutions and aliquots added to individual cultures to give the desired concentrations. - Vehicle:
- not specified
- Test organisms (species):
- Microcystis aeruginosa
- Details on test organisms:
- TEST ORGANISM
- Common name: Blue-Green Algae
- Age of inoculum (at test initiation): Exponential Growth Phase (Log)
- Method of cultivation: The algae was grown in 125 ml Erlenmeyer flasks with 75 ml of a modified Chu No. 10 solution under continuous florescent illumination and at a temperature of approx. 22ᵒC, respectively. - Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 24 h
- Test temperature:
- 22°C
- Nominal and measured concentrations:
- nominal concentrations
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyer flask
- Material, size, headspace, fill volume: Erlenmeyer flasks of 125 ml was used as a test vessel.
- Initial cells density: 1,000,000 to 2,000,000 cells/ml
GROWTH MEDIUM
- Detailed composition if non-standard medium was used: The composition of the nutrient solution in gm/l was as follows-
NaNO3, 0.124; K2HPO4.3H2O, 0.013; MgSO4.7H2O, 0.025; Na2CO3, 0.020; Na2SiO3.9H2O, 0.058; CaCl2.2H2O, 0.036; ferric citrate, 0.003; and citric acid, 0.003.
OTHER TEST CONDITIONS
- Light intensity and quality: continuous florescent illumination
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- Determination of cell concentrations: Microscopic examination of the cells were carried out for determining the extent of their disintegration after 24 hr period.
- Other: The failure of treated cultures to grow in subcultures was used for determining the minimum lethal dosages.
TEST CONCENTRATIONS
- Test concentrations: 20 mg/l - Reference substance (positive control):
- not specified
- Duration:
- 24 h
- Dose descriptor:
- EC100
- Effect conc.:
- 20 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Validity criteria fulfilled:
- not specified
- Conclusions:
- For chemical Methylamine hydrochloride, based on the effect on growth rate of the test organism Microcystis aeruginosa, the 24 hr EC100 value was determined to be 20 mg/l, respectively.
- Executive summary:
Short term toxicity to Microcystis aeruginosa study was carried out for 24 hrs.The study was based on the effects of the test compound Methylamine hydrochloride (CAS no. 593 -51 -1) on Microcystis aeruginosa in a static fresh water system at a temperature of 22ᵒC. Microcystis aeruginosa was used as a test organism. The algae was grown in 125 ml Erlenmeyer flasks with 75 ml of a modified Chu No. 10 solution under continuous florescent illumination and at a temperature of approx. 22ᵒC, respectively. Test chemical conc. used for the study was 20 mg/l(nominal concentrations). Test chemical was prepared in stock solutions and aliquots added to individual cultures to give the desired concentrations. Test was performed in a 125 ml Erlenmeyer flasks under continuous florescent illumination at a temperature of 22ᵒC. Initial cell of the organism used for the study was 1,000,000 to 2,000,000 cells/ml, respectively. Microscopic examination of the cells were carried out for determining the extent of their disintegration after 24 hr period. The failure of treated cultures to grow in subcultures was used for determining the minimum lethal dosages. Based on the effect on growth rate of the test organism Microcystis aeruginosa, the 24 hr EC100 value was determined to be 20 mg/l, respectively. Thus, based on the EC100 value, it can be concluded that the substance Methylamine hydrochloride can be considered as toxic to aquatic organisms. Since, the chemical Methylamine hydrochloride is readily biodegradable in nature, Methylamine hydrochloride can be considered as non-toxic to aquatic organisms and thus cannot be classified as hazardous as per the CLP classification criteria.
Reference
Table: Effect of test chemical Methylamine hydrochloride on the growth of Microcystis aeruginosa.
Chemical |
Conc. (mg/l) |
Kill (%) |
Methylamine.HCl |
20 |
100 |
Description of key information
Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance methanaminium chloride (CAS no. 593 -51 -1) according to OECD Guideline 201 (ABITEC study report, Sustainability Support Services (Europe) AB, Report no. 715/16, 2016) . The stock solution (300 mg/L) was prepared by dissolving white powder in OECD growth medium. Test solutions of required concentrations were prepared by mixing the stock solution of the test sample with OECD growth medium and inoculum culture. Conc. of test chemical used for the study was 0, 60, 90, 132, 201 and 300 mg/L, respectively. The test was performed under static conditions in a static fresh water system at a temp. of 23±2°C. Initial cell density of test organism used was 5x10(3) cells/ml. Determination of cell counting involve the use of electronic particle counter. ErC50 was calculated using non-linear regression by the software Prism 4.0. The median effective concentration (EC50) for the test substance methanaminium chloride in Desmodesmus subspicatus was determined to be 971.6 mg/L on the basis of effects on growth rate in a 72 hour study. Thus, based on this value, test chemical methanaminium chloride can be considered as non-toxic to aquatic organisms and thus can be considered to be not classified as per the CLP classification criteria.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 971.6 mg/L
Additional information
1 experimental key study alongwith the supporting datafor the target chemical methanaminium chloride(CAS no. 593-51-1)were reviewed for the toxicity to aquatic algae and cyanobacteria end point which are summarized as below:
In an experimental key study (ABITEC study report, Sustainability Support Services (Europe) AB, Report no. 715/16, 2016), Freshwater algal growth inhibition test was carried out on Desmodesmus subspicatus with the substance methanaminium chloride (CAS no. 593 -51 -1) according to OECD Guideline 201. The stock solution (300 mg/L) was prepared by dissolving white powder in OECD growth medium. Test solutions of required concentrations were prepared by mixing the stock solution of the test sample with OECD growth medium and inoculum culture. Conc. of test chemical used for the study was 0, 60, 90, 132, 201 and 300 mg/L, respectively. The test was performed under static conditions in a static fresh water system at a temp. of 23±2°C. Initial cell density of test organism used was 5x10(3) cells/ml. Determination of cell counting involve the use of electronic particle counter. ErC50 was calculated using non-linear regression by the software Prism 4.0. The median effective concentration (EC50) for the test substance methanaminium chloride in Desmodesmus subspicatus was determined to be 971.6 mg/L on the basis of effects on growth rate in a 72 hour study. Thus, based on this value, test chemical methanaminium chloride can be considered as non-toxic to aquatic organisms and thus can be considered to be not classified as per the CLP classification criteria.
In a supporting data (Fitzgerald,G.P., G.C. Gerloff, and F. Skoog, 1952) of short term toxicity to Microcystis aeruginosa for the test compound Methylamine hydrochloride (CAS no. 593 -51 -1) was carried out for 24 hrs in a static fresh water system at a temperature of 22ᵒC. Microcystis aeruginosa was used as a test organism. The algae was grown in 125 ml Erlenmeyer flasks with 75 ml of a modified Chu No. 10 solution under continuous florescent illumination and at a temperature of approx. 22ᵒC, respectively. Test chemical conc. used for the study was 20 mg/l(nominal concentrations). Test chemical was prepared in stock solutions and aliquots added to individual cultures to give the desired concentrations. Test was performed in a 125 ml Erlenmeyer flasks under continuous florescent illumination at a temperature of 22ᵒC. Initial cell of the organism used for the study was 1,000,000 to 2,000,000 cells/ml, respectively. Microscopic examination of the cells were carried out for determining the extent of their disintegration after 24 hr period. The failure of treated cultures to grow in subcultures was used for determining the minimum lethal dosages. Based on the effect on growth rate of the test organism Microcystis aeruginosa, the 24 hr EC100 value was determined to be 20 mg/l, respectively. Thus, based on the EC100 value, it can be concluded that the substance Methylamine hydrochloride can be considered as toxic to aquatic organisms. Since, the chemical Methylamine hydrochloride is readily biodegradable in nature, Methylamine hydrochloride can be considered as non-toxic to aquatic organisms and thus cannot be classified as hazardous as per the CLP classification criteria.
Thus, based on the overall reported results for target chemicalmethanaminium chloride(from ABITEC study report and peer reviewed journal), it can be concluded that the test substance methanaminium chloride can be considered as non-toxic to aquatic environment and can be considered to be not classified as per the CLP classification criteria.
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