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EC number: 219-210-0 | CAS number: 2387-03-3
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Short term toxicity to aquatic invertebrates
During determination of the acute effect of test substance LUMOGEN GB 0790 ST. BER. 100 % (Chemical Name: 2-hydroxynaphthalene-1-carbaldehyde [(2-hydroxy-1-naphthyl)methylene]hydrazone) on the swimming ability of the water flea Daphnia magna STRAUS in a 48-hour static test according to OECD Guideline 202 resulted in EC0= ≥100 mg/L;EC50 >100 mg/L and EC100 > 100 mg/L .Thus on the basis of results from BASF lab study report (Sustainability Support Service (Europe) AB, report no. 01/0031/50/1, 2001),the substance can be classified as non- hazardous as per the criteria of CLP regulation.
Toxicity to aquatic algae and cyanobacteria
Various studies of predicted data for the target chemical C.I. Pigment Yellow 101(CAS no 2387-03-3) were reviewed to summarize the following information:
72 hrs aquatic toxicity study (SSS QSAR prediction model, 2016) was conducted to assess toxic effects of the test compound C.I. Pigment Yellow 101(CAS no 2387-03-3) and the results were predicted. The study was based on the effects of the test compound on the Scenedesmus subspicatus in a static fresh water system. The predicted data suggests the effective concentration (EC50) for the test compound C.I. Pigment Yellow 101was estimated to be 2.7442 mg/L on the basis of growth rate.Thus, based on the EC50 value, test substance can be classified as aquatic chronic category 2 as per the criteria of CLP regulation.
72 hrs aquatic toxicity study (Danish (Q)SAR Database, 2016) was conducted to assess toxic effects of the test compound C.I. Pigment Yellow 101(CAS no 2387-03-3) and the results were predicted. The study was based on the effects of the test compound on Pseudokirchnerella subcapitata in a static fresh water system. The predicted data suggests the effective concentration (EC50) for the test compoundC.I. Pigment Yellow 101(CAS no 2387-03-3) was estimated to be 9.832 mg/L on the basis of growth rate.Thus based on this value it can be concluded that the substance can be classified as aquatic chronic category 2 as per the criteria of CLP regulation.
Based on the overall reported results of predicted data of toxicity to aquatic algae and cyanobacteria for target substance, it can be concluded that the substance can be classified as aquatic chronic category 2 as per the CLP criteria.
Toxicity to microorganisms:
Toxicity to micro-organism study for Target CAS no. 2387-03-3 -C.I. Pigment Yellow 101: Summarized as fallowed:
Study report (Sustainability Support Service (Europe) AB, report no. 01/0031/50/1, 2001):Assessment of the inhibitory effect of a test substance LUMOGEN GB 0790 ST. BER. 100% (chemical name: 2-hydroxynaphthalene-1-carbaldehyde [(2-hydroxy-1-naphthyl)methylene]hydrazone) on the oxygen consumption rate of aerobic micro-organisms (activated sludge) after short-term exposure (30 or 180min) was conducted.
The effective concentration i.e EC20; EC50 and EC80 in the activated sludge respiration inhibition test when mciroorganisms were exposed to LUMOGEN GB 0790 ST. BER. 100% (Chemical name: 2-hydroxynaphthalene-1-carbaldehyde [(2-hydroxy-1-naphthyl)methylene]hydrazone) was found to be >1000 mg/L during test duration of 180 minutes.
In a supporting studyof authorVanya B. Kurteva et. al, 2011:Toxicity to micro-organisms study was conducted on 10 different gram positive and gram negative bacteria.
Antimicrobial studies were carried out by the agar-cup diffusion test against the test bacteria.
Stock solutions of test substance was freshly prepared by dissolving each chemical in dimethyl sulfoxide (DMSO). The conc. of test chemical used for the study was 12500 mg/l (12.5 mg/ml).
10 different test organisms were used for the study. They include -B. subtilis ATCC 6633,Bacillus idosusB241,B. megat.NRRL 1353895,Bacillus mycoidesDSMZ 274,Bacillus cereusATCC 11778,Acinetob. johnst.ATCC 17909,Staph. aureusNRRL B 313,Sarcina luteaATCC 9341,Microc. luteusATCC 9631 andE. coliATCC 8739, respectively.
The bacterial strains were grown in nutrient agar for 24 h at 37°C.
Suspensions of the test microorganisms were inoculated into sterile melted nutrient agar media and poured into Petri dishes. Six per dish wells, each 8 mm in diameter, were prepared. Fifty microliter of each test sample in dimethylsulfoxide (DMSO) (25 mg/ml) was added to the appropriate well. For pre-diffusion the Petri dishes were placed at 4°C for 2 h. The antimicrobial activity was estimated by the diameter of inhibitory zones (mm) in the agar layer. Control experiments were carried out with the pure solvent.Streptomycin was used as a reference substance for the study.
Based on growth inhibition of test organism, the LOEC value was found to be 12500 mg/l.
In a supporting study on similar substance (CAS no. 708-06-5) [Binnur Μericli Yapici, et. al (2005)]:
1) Toxicity to micro-organisms study was conducted on 14 different bacteria.
Antimicrobial studies were carried out by the agar-disc diffusion method against the test bacteria.
Test solutions were prepared by dissolving the test substance in DMF solvent. The conc. of test chemical used for the study was 200 mg/l (200 ppm).
14 different bacteria were used for study. They include-
1. Corynobacterium xerosisCCM 2824
2. Proteus vulgarisATCC 6897
3. Staphylococcus epidermidisNRRL B-4877 10.0
4. Staphylococcus aureusATCC 6538 Ρ
5. Enterobacter aerogenesATCC 13048
6. Salmonella thyphimuriumCCM 5445
7. Pseudomonas aeruginosaATCC 27853
8. Escherichia coliATCC 11230
9. Escherichia coliATCC 23998
10. Bacillus cereusATCC 7064
11. Bacillus cereusATCC 99
12. Bacillus subtilisATCC 6633
13. Yersininiaspp. and
14. Neisseria canis.
Test microorganisms were obtained from the culture collection of Ege University Faculty of Science, Basic and Industrial Microbiology Department.
Bacterial cultures were suspended in 7-8 ml brain heart infusion broth (Oxoid). The bacteria were incubated at 37 ± 0.1 °C for 24 hours.Prepared bacterial suspensions were inoculated at 10 μl into Muller Hilton agar. Microbial cultures were separated with L bags and all Petri dishes after inoculation were allowed to dry for 15-20 minutes at room temperature. The concentration of test chemical used was 200 ppm in DMF solvent. These chemicals were impregnated into 6 mm diameter discs at 10 μl. All discs were dried at 50°C and placed into the Petri dishes containing the bacteria. Inhibition zone diameters were measured after 24-48 hours using the agar-disc diffusion method.
Based on growth inhibition of test organism, the LOEC value was found to be 200 mg/l.Thus based on this value it can be concluded that the substance can be classified as non- hazardous as per the criteria of CLP regulation.
2) Toxicity to micro-organisms study was conducted on 8 different filamentous fungi.
Antimicrobial studies were carried out by the agar-disc diffusion method against the filamentous fungi.
Test solutions were prepared by dissolving the test substance in DMF solvent. The conc. of test chemical used for the study was 200 mg/l (200 ppm).
8 different filamentous fungi were used for the study. They are-
1. Aspergillus niger
2. A. fumigates,
3. A. versicolor,
4. A. flavus,
5. A. parasiticus,
6. Penicillium granulatum,
7. P. chrysogenum,and
8. P. herque
Test microorganisms were obtained from the culture collection of Ege University Faculty of Science, Basic and Industrial Microbiology Department.
The solutions of OHNA were added to Petridishes to 100 μl. The sterilized medium at 45-50°C was poured into 90 mm diameter Petri dishes. All Petri dishes were allowed to dry for 15- 20 minutes at room temperature. Spore suspensions of filamentous fungi were inoculated onto malt extract agar at 105cfu/ml by plate dilution techniques using Thomas slides. The evaluation of filamentous fungi was carried out by means of reproduction on the medium and reduction of colony numbers at the end of a 7-day period.
As no inhibitory effect on growth of test organisms were observed, the NOEC value was found to be 200 mg/l.Thus based on this value it can be concluded that the substance can be classified as non- hazardous as per the criteria of CLP regulation.
On the basis of the above results, the substance can be classified as non- hazardous as per the criteria of CLP regulation.
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