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EC number: 263-179-6 | CAS number: 61791-46-6
- 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
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Endpoint summary
Administrative data
Description of key information
Short-term toxicity to aquatic invertebrates:
In the acute immobilisation test according to OECD guideline 202 the 48 hours acute median Effective Loading Rate (EL50) of Humectol LYS MOD on Daphnia magna is 0.0815 mg/L, the 95% confidence interval with lower limit of 0.0696 mg/L and upper limit of 0.0954 mg/L. No Observed Effect Loading Rate (NOELR) and Lowest Observed Effect Loading Rate (LOELR) over the 48 hours exposure period are 0.021 and 0.047 mg/L of Humectol LYS MOD respectively.
Toxicity to aquatic algae and cyanobacteria:
In a 72 hours Growth Inhibition Test on Pseudokirchneriella subcapitata according to OECD guideline 201 an ErL50 (growth rate) and EyL50 (yield) of Humectol LYS MOD of >100 mg/L was determined, respectively. The 72 hours No Observed Effect Loading Rate (NOELR) and the Lowest Observed Effect Loading Rate (LOELR) is >100 mg/L of Humectol LYS MOD, respectively.
Additional information
Short-term toxicity to aquatic invertebrates:
The test item Humectol LYS MOD was evaluated
for acute toxicity on Daphnia magna according to OECD Guideline No. 202.
The acute toxicity study of Humectol LYS MOD on Daphnia magna was
performed to determine the 48 hours Effective concentration (EL50) and
to determine Lowest Observed Effect Nominal Loading Rate (LOELR) and No
Observed Effect Nominal Loading Rate (NOELR). Daphnids were exposed for
the test item by aqueous exposure (treatment) under semi-static
condition. Daphnids were observed at 24 and 48 hours for signs of
toxicity and immobilization.
Based on the results of a dose range finding study, main study was
conducted at the nominal loading rates of 0.010, 0.021, 0.047, 0.103,
0.227 and 0.500 mg/L of Humectol LYS MOD of test medium along with
control. No clinical signs of toxicity were observed in control and at
the nominal loading rate of 0.010 mg/L during the 48 hours observation
period. Clinical signs of daphnids localized on bottom of container and
lethargy was observed at the nominal loading rates of 0.021, 0.047,
0.103 and 0.227 mg/L during the 48 hours observation period. Clinical
signs of daphnids localized on bottom of container and lethargy was
observed at the nominal loading rates of 0.500 mg/L during the 24 hours
observation period. The immobilization percentages of 0, 10, 35, 60, 80
and 100% were observed at the nominal loading rates of 0.010, 0.021,
0.047, 0.103, 0.227 and 0.500 mg/L respectively during the 48 hours
observation period.
Based on the above results of the experiment and under experimental
conditions employed, it is concluded that the 48 hour acute median
effective concentration (EL50) of Humectol LYS MOD on Daphnia magna is
0.0815 mg/L; the 95 % confidence interval with lower limit of 0.0696
mg/L and upper limit of 0.0954 mg/L. NOELR and LOELR over the 48 hours
exposure period are 0.021 and 0.047 mg/L of Humectol LYS MOD,
respectively.
Toxicity to aquatic algae and cyanobacteria:
The test item Humectol LYS MOD was assessed for Growth Inhibition on Pseudokirchneriella subcapitata according to OECD Guideline 201.
A dose range finding study was conducted
with six nominal loading rates of 0.01, 0.1, 1.0, 10.0, 50.0 and 100.0
mg/L along with control. Each loading rate contains 2 replicates except
control possessing 3 replicates. The algal growth (cell density) was
assessed at 24, 48 and 72 hours of post-exposure during the test. During
the dose range finding study, exponentially growing cells (5709
cells/mL) were exposed to range of selected nominal loading rates. A
growth rate inhibition of 0.36, 0.08, 0.48, 0.02, -0.23 and -0.45%, was
observed at the tested nominal loading rates of 0.01, 0.1, 1.0, 10.0,
50.0 and 100.0 mg/L of Humectol LYS MOD respectively as compared with
the control. Percent inhibition in yield of 1.8, 0.4, 2.4, 0.1, 2.8 and
-2.2% was observed at the tested nominal loading rates of 0.01, 0.1,
1.0, 10.0, 50.0 and 100.0 mg/L of Humectol LYS MOD respectively as
compared with the control.
Based on the results of dose range finding study, a limit test was
conducted at the nominal loading rate of 100 mg/L along with control
having 6 replicates. The algal growth (cell density) was assessed at 24,
48 and 72 hours post-exposure. Exponentially growing alga cells (5462
cells/mL) were exposed to the limit nominal loading rate. A growth rate
inhibition of 0.01 % was observed at the nominal loading rate of 100
mg/L as compared with the control. Similarly, inhibition in yield of
0.1% was observed at the nominal loading rate of 100 mg/L as compared
with the control.
From the experiment conducted under standard experimental conditions,
the 72 hours ErL50 (growth rate) and EyL50 (yield) of Humectol LYS MOD
on Pseudokirchneriella subcapitata is >100 mg/L. The 72 hours No
Observed Effect Loading Rate (NOELR) and the Lowest Observed Effect
Loading Rate (LOELR) is >100 mg/L of Humectol LYS MOD.
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