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EC number: 219-372-2 | CAS number: 2425-85-6
- 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
Long-term toxicity to fish
Administrative data
- Endpoint:
- fish early-life stage toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- from 2020-06-18 to 2020-07-21
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 021
- Report date:
- 2021
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 210 (Fish, Early-Life Stage Toxicity Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 1-(4-methyl-2-nitrophenylazo)-2-naphthol
- EC Number:
- 219-372-2
- EC Name:
- 1-(4-methyl-2-nitrophenylazo)-2-naphthol
- Cas Number:
- 2425-85-6
- Molecular formula:
- C17H13N3O3
- IUPAC Name:
- 1-(4-methyl-2-nitrophenylazo)-2-naphthol
- Test material form:
- other: Red powder
- Details on test material:
- Test item Hansa Scarlet RNC-IN
Batch number INB 3100014
Purity of main component 98.8% (w/w) (comp. 1)
Chemical name 1-(4-Methyl-2nitrophenylazo)-2-naphtol (EINECS/REACH)
CAS-Name No 2425-85-6
EINECS / EC No 219-372-2
C.I. Index Pigment Red 3 (P.R.3)
Composition Pigment Red 3 98.8% (w/w)
Molecular formula C17H13N3O3
Structure
Particle size D50 = 259 nm
Molecular weight 307.31 g/mol
Density 1.4073 g/cm3
Appearance Red, powder
Water Solubility Approx. 3 µg/L
Expiry date 2021-03-03
Recommended storage Room temperature
Constituent 1
- Specific details on test material used for the study:
- Test item Hansa Scarlet RNC-IN
Batch number INB 3100014
Purity of main component 98.8% (w/w) (comp. 1)
Chemical name 1-(4-Methyl-2nitrophenylazo)-2-naphtol (EINECS/REACH)
CAS-Name No 2425-85-6
EINECS / EC No 219-372-2
C.I. Index Pigment Red 3 (P.R.3)
Composition Pigment Red 3 98.8% (w/w)
Molecular formula C17H13N3O3
Structure
Particle size D50 = 259 nm
Molecular weight 307.31 g/mol
Density 1.4073 g/cm3
Appearance Red, powder
Water Solubility Approx. 3 µg/L
Expiry date 2021-03-03
Recommended storage Room temperature
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- Determination of the test item
The samples were analyzed for the test item dispersed and genuinely dissolved in dilution water with an LC-MS/MS method, implemented under non-GLP and documented finally in the GLP raw data. Samples for determination of the genuinely dissolved test item (dissolved fraction) were centrifuged as specified below prior to analysis. The method was validated.
Sampling schedule
Samples of test media (including control group) were taken from alternating test replicates. The test item Hansa Scarlet RNC-IN and the control were analytically verified twice during 7 days of exposure from freshly prepared test media on study day 0 (start of the exposure), 5, 8, 12, 15, 19, 22, 26, 29 and 33 and from corresponding 24 hours aged test media on study days 1, 6, 9, 13, 16, 20, 23, 27.
Sampling for the analytical monitoring
For each sampling date and sample of test media at least two aliquots were taken after preparation of the test loadings and the control. Dimethyl sulfoxide was added to one replicate. One replicate was taken without addition of solvent. It was centrifuged for 15 minutes at 10000G and analyzed. The remaining replicates were stored at ambient conditions
Test solutions
- Vehicle:
- no
- Details on test solutions:
- Test design
A semi-static test procedure with daily renewal of the test media was performed. Daily renewal was chosen, due to the outcome of the experiments on dispersion stability carried out referring to OECD 318 and Series on the Safety of Manufactured Nanomaterials No. 40 Guidance Document. Eggs were exposed to the test item in test vessels filled with a defined amount of the test media (specifications see below). For the daily renewal of the test media the test organisms were retained in the test vessels whilst a proportion of 75 % of the media was changed. Old test media were gently removed by siphoning with glass tubes. Care was taken not to remove or injure the test organisms. Freshly prepared media were gently added with glass tubes to the test vessels to avoid stressing of the test organisms. Any sedimented test item was daily removed during cleaning as specified below.
Fresh media for water renewals were aerated during renewal procedure for homogenization and to prevent sedimentation of the test item.
Due to the increase of growth of fish during the study, the test vessels were changed once on study day 18 depending on the life-stage and growth of fish.
Loading rates
The study was performed with three nominal loading rates of 10.0, 3.16 and 1.00 mg test item/L (dilution factor √10). According to the guideline the highest loading rate did not exceed 10 mg/L. Three loading rates were tested for profound estimation of the NOELR and LOELR values.
The loading rates are based on the results of a preliminary range finding test (see Annex II).
Preparation of the stock dispersions, application and dispersion treatment
The preparation procedure was carried out referring to UBA Texte 06/2013.
Three stock dispersions were prepared per loading rate with a total volume of 400 mL.
Stock dispersions of 500 mg/L (200 mg / 400 mL), 158 mg/L (63.2 mg / 400 mL) and 50.0 mg/L (20.0 mg / 400 mL) were prepared in dechlorinated tap water in a 500 mL flask. The dispersions were treated with sonication (300 W) for 1 hour. Thereafter, the test loading rates of 10.0, 3.16 and 1.00 mg/L were prepared with a total volume of 20 L by dilution. The total volume of 400 mL of the homogenous dispersions (stock dispersions) were filled up with dilution water to a total volume of 20 L in glass aquaria (500 mg/L for the loading rate of 10.0 mg/L, 158 mg/L for the loading rate of 3.16 mg/L and 50.0 mg/L for the loading rate of 1.00 mg/L).
To achieve homogeneous distribution of the test item and to avoid sedimentation, the prepared loadings were treated with a laboratory blender for about 3 – 5 minutes with 17000 rpm. The water column in the 20L aquaria was agitated by two flow circulation pumps, placed in two transversely opposite bottom corners of the aquaria for approx. 24 ± 2 hours. Thereafter and prior to adding the test loadings to the test vessels (where the eggs/fish were exposed) the loadings were treated again with the laboratory blender for about 3 – 5 minutes with 17000 rpm.
Fresh media for water renewals were aerated during renewal procedure for homogenization and to prevent sedimentation of the test item.
The homogeneous stock dispersions and the test loadings (in 20 L aquaria) were prepared at least 24 ± 2 hours prior to the start of the exposure and daily thereafter until the end of the exposure.
Control Dilution water (without test item)
Test organisms
- Test organisms (species):
- Danio rerio (previous name: Brachydanio rerio)
- Details on test organisms:
- Test organism
Danio rerio (zebrafish) Vertebrata, Gnathostomata, Pisces, Osteichthyes, Teleostei, Cypriniformes, Cyprinidae
Reason for the selection
According to the guideline Danio rerio is recommended for this type of study.
Origin
All fish used in the test were gained at Noack Laboratorien GmbH from a single brood stock (supplier: Umweltbundesamt, Schichauweg 58, D-12307 Berlin, Germany)
Maintenance of brood fish
A breeding stock of unexposed, mature zebrafish with an age of approx. 8 months was used for the egg production. Fish were free of macroscopically discernable symptoms of infection and disease. Spawners were maintained in aquaria with a loading capacity of a minimum of 1 L water per fish.
- Temperature: 25 ± 2 °C
- Dissolved oxygen concentration > 60 % of air saturation value
- pH value: 6 – 8.5
- Photoperiod: 16 h light / 8 h dark cycle
(2 transition periods, 30 minutes each)
- Diffuse light (7 – 750 lux on water surface)
- Food: Artemia salina nauplii, 48 hours old, ad libitum;
Daphnia magna, juvenile and adult daphnids, ad libitum;
dry food sera vipan SERA, ad libitum.
- No disease treatments were administered.
Water Tap water of local origin was used for holding. The water was filtered on activated charcoal and aerated for at least 24 h to remove chlorine.
Nominal water parameters:
Total hardness: 10 – 250 mg CaCO3/L
pH-value: 6.0 – 8.5
Alkalinity: 0.6 mmol/L (recent measurement: 2020-06-17)
Acidity: 0.1 mmol/L (recent measurement: 2020-06-17)
Conductivity: 143 µS/cm (recent measurement: 2020-06-17)
Spawning
15 – 35 adult zebrafish were kept in at least 3 separate aquaria. The fish were healthy with a mortality rate < 5% during the last 7 days before the start of the exposure, and not medically treated during these 7 days. About 15 minutes before start of artificial dawning rectangular dishes covered with a stainless steel mesh and provided with artificial plants (plastic), were introduced into the aquaria. After approximately 1 hour the glass dishes were gently removed. Eggs were checked carefully for abnormalities like fungus infections. These eggs as well as coagulated and not fertilized eggs were discarded. 800 eggs were taken and washed in dilution water. Eggs originated from 2 different spawnings. At least 70% of the eggs appeared healthy.
Start of exposure
The eggs that were used to start exposure were pooled and attributed randomized (eggs were placed in alternating groups into each of the three test groups) to the test groups in crystallization dishes containing test solutions (two dishes per test group, each dish loaded with at least 60 eggs).
Fertilization check
Immediately after exposing the eggs to the test solutions (start of exposure), the eggs were checked for fertilization. Eggs were fully covered with the respective test solutions. Every embryo was checked under a stereo microscope for its stage. Cleavages which form 4, 8, 16 and 32 cell blastomers can be clearly identified by the development of the blastula and were regarded to be fertilized. Eggs with only a 2 cell stage were regarded as not fertilized and were discarded.
Fertilization rate The fertilization rate was 85 %.
Introduction of eggs
Only fertilized eggs with more than 2 cells were placed directly in the test vessels. 20 eggs were introduced by random per replicate (corresponding to 80 eggs per treatment group). Eggs were less than 24 h old at experimental starting. The distribution of eggs to the loading groups was carried out indiscriminately by adding 5 eggs to the first test group, the 2nd 5 eggs to the next test group and so on, until all test groups contain the necessary number of eggs.
Study design
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 33 d
- Remarks on exposure duration:
- 33 days (30 days post hatch), depending on post-hatch day 0 (study day 3)
Test conditions
- Hardness:
- Total hardness of the test media was measured from the control and the highest loading rate of the test item (10.0 mg/L). Total hardness was measured once per week. The mean total hardness was 64 mg CaCO3/L in the control and ranged from 59 to 72 mg CaCO3/L in the control and the highest loading rate of 10.0 mg test item/L (for details, see Table 23).
Total Hardness in the Control and the Loading Rate 10.0 mg/L
Study day Replicate Total hardness [mg CaCO3/L]
Nominal loading rate of the test item [mg/L]
Control 10.0
1 1 62 64
7 2 60 62
14 3 59 64
22 4 70 72
28 1 67 66
Mean 64 66
± SD 4.72 3.85
Min. 59 62
Max. 70 72
Min./Max. = Minimum/Maximum measured hardness - Test temperature:
- Water Temperature
During the exposure the water temperature was recorded continuously (once per hour) with a data logger. The mean temperature was 26.2 °C. The minimum temperature was 25.0 °C and the maximum temperature was 27.3 °C. The water temperature did not differ by more than ± 1.5 °C between successive days during the test. The validity criterion on the parameter temperature was fulfilled.
The mean water temperature measured once per week from all replicates during the exposure period was 26.3 °C for the loading rates 1.00 and 10.0 mg/L and for the control and 26.2 °C for the loading rate 3.16 mg/L. The minimum and maximum measured temperature for all groups were 25.0 and 27.2 °C, respectively.
Water Temperature (Continuous Measuring) of the Control Group
Period of measurements 2020-06-18 to 2020-07-21
Minimum temperature [°C] 25.0
Maximum temperature [°C] 27.3
Mean temperature [°C] 26.2 - pH:
- pH-Values
The mean pH-values in the control and the loading rates 1.00 to 10.0 mg/L were 7.44 to 7.49 and ranged from 7.23 to 7.82 during the exposure period.
pH-Values in the Test Media (Study Day 0 – 22)
Study day Replicate Media pH
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
0 1 Fresh 7.30 7.41 7.40 7.35
2 7.28 7.39 7.37 7.33
3 7.28 7.38 7.33 7.34
4 7.37 7.38 7.32 7.31
1 1 Aged 7.57 7.60 7.70 7.72
2 7.61 7.58 7.66 7.58
3 7.61 7.59 7.65 7.58
4 7.58 7.55 7.68 7.55
7 1 Fresh 7.23 7.28 7.32 7.31
2 7.26 7.26 7.27 7.27
3 7.23 7.24 7.27 7.25
4 7.25 7.26 7.24 7.24
8 1 Aged 7.64 7.51 7.62 7.52
2 7.54 7.51 7.50 7.47
3 7.55 7.56 7.48 7.48
4 7.53 7.59 7.52 7.47
14 1 Fresh 7.35 7.32 7.28 7.34
2 7.34 7.29 7.26 7.31
3 7.29 7.25 7.29 7.26
4 7.27 7.28 7.30 7.28
15 1 Aged 7.24 7.44 7.47 7.45
2 7.29 7.43 7.46 7.42
3 7.36 7.44 7.44 7.43
4 7.39 7.44 7.44 7.40
21 1 Fresh 7.38 7.46 7.48 7.52
2 7.34 7.45 7.46 7.48
3 7.39 7.45 7.47 7.48
4 7.41 7.46 7.49 7.49
22 1 Aged 7.75 7.79 7.80 7.82
2 7.67 7.81 7.78 7.80
3 7.73 7.78 7.79 7.81
4 7.74 7.78 7.82 7.82
Min./Max. = Minimum/Maximum measured pH-value
pH-Values in the Test Media (Study Day 28 – 29)
Study day Replicate Media pH
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
28 1 Fresh 7.34 7.36 7.36 7.33
2 7.33 7.36 7.36 7.32
3 7.34 7.36 7.38 7.33
4 7.34 7.35 7.39 7.35
29 1 Aged 7.56 7.76 7.73 7.62
2 7.68 7.70 7.71 7.64
3 7.71 7.60 7.70 7.66
4 7.69 7.73 7.65 7.69
Mean 7.44 7.48 7.49 7.47
± SD 0.168 0.166 0.174 0.170
Min. 7.23 7.24 7.24 7.24
Max. 7.75 7.81 7.82 7.82
Min./Max. = Minimum/Maximum measured pH value - Dissolved oxygen:
- Dissolved Oxygen
The dissolved oxygen concentrations in the control and the test item groups, expressed in percent saturation, were in the mean 90 to 91% for all test groups and the control and ranged from 61 to 100% during the exposure period.
For more details see window below "Any other information on rsults incl. tables ". - Nominal and measured concentrations:
- The study was performed with three nominal loading rates of 10.0, 3.16 and 1.00 mg test item/L (dilution factor √10).
The samples of the test item Hansa Scarlet RNC-IN and the control were analytically verified twice during 7 days of exposure from freshly prepared test media on study day 0 (start of the exposure), 7, 14, 21 and 28 and from corresponding 24 hours aged test media on study days 1, 8, 15, 22 and 29 (end of the exposure). Freshly prepared test media, which were used for the replacement of about 75% old media, was analyzed weekly. Details of the analytical method are presented in part 11. The test item concentrations of Hansa Scarlet RNC-IN and the control were analytically verified via LC-MS/MS. The freshly prepared stock solutions were analyzed once per week. The medium of the start of the exposure and the corresponding end of the exposure was analytical verified once per week. For all samples the dispersed fraction was analyzed by dilution of the sample with DMSO directly after sampling. Additional the dissolved fraction was analyzed after centrifugation of the samples to remove undissolved test item. For all determinations the geometric mean measured concentrations were calculated.
For further information see field below "Any other information on materials and methods incl. tables " - Details on test conditions:
- Reference item No reference item is recommended for this test according to the guideline.
Test duration 33 days (30 days post hatch), depending on post-hatch day 0 (study day 3)
Replicates, number of eggs
Four replicates per loading rate and control, with 20 eggs each (80 eggs per loading rate and control)
For the whole study 320 eggs/fish were used.
Test vessels Days 0 to 18:
Crystallisation dishes were used. The volume of the test media in the dishes was about 700 mL.
Days 18 to test end:
Glass aquaria (12.5 x 11 x 18 cm) were used. The volume of the test media was about 2.5 L.
Test vessels were covered with transparent lids.
Transfer of juveniles Juveniles were gently transferred to larger aquaria on study day 18.
Loading
A loading rate not exceeding 0.5 g/L wet weight fish per 24 hours and not exceeding 5 g/L of solution at any time was maintained.
Cleaning
The test vessels were siphoned at least once daily (during water renewal) to remove possible sediment of the test item, excess fecal matter and uneaten food, also to minimize microbial growth and biodegradation of the test item. Cleaning started on study day 1 (post hatch day -2).
Aeration
The dilution water used for preparation of the test media was aerated. A gentle aeration was applied for all test vessels.
Dilution water
Same as used for holding.
Feeding of test fish The feeding regime was ad libitum during the whole feeding period (study day 5 to 32).
Feeding started 3 days after the beginning of hatching (on study day 5 (post-hatch day 2)). Larvae were fed with a starter food (ST-1 (AQUA SCHWARZ GMBH, 37081 Göttingen, Germany)) and brine shrimp nauplii (48 h old) until the end of the test (ST-1: 2 – 4 times daily; brine shrimp: 2 – 7 times daily), as well as a suspension of the starter food ST-1 and fine milled brine shrimp nauplii (2 – 5 times daily).
Brine shrimp nauplii origin, breeding conditions:
Artemia salina (Brine shrimp eggs) were purchased from Kessler Zoologiegroßhandel GmbH & Co. KG, D 67122 Altrip, Germany. Fresh cultures were prepared with salt water (NaCl 20 g/L, ca. 2 g eggs to 1 L salt water, gentle aeration for 24 - 48 hours at approx. 22 °C). 24 - 48 h old brine shrimp nauplii were harvested, washed in a stainless steel mesh and resuspended in tap water. Feeding ad libitum was carried out.
Water temperature (target) 26 ± 1.5 °C
Dissolved oxygen Not less than 60% of air saturation value.
Concentration (target)
Light intensity (target) 400 ± 200 Lux
Photoperiod A daily 16 / 8 h photoperiod (light / dark) was maintained throughout exposure.
Type and Frequency of Measurements
Photographic Documentation
During exposure the character of the stock dispersions, test loadings (freshly prepared and aged) and appearance of eggs and embryos (i.e. deposition of the test item) were documented via photographs where appropriate. Attention is paid to the homogeneity of the aqueous media (e.g. sedimentation) and the adhesion of the test item onto the embryonic membrane. Pictures were taken daily during the first 5 days of exposure (time to hatch) and weekly thereafter until the end of the study.
Biological Parameters
All biological parameters were observed daily. Dead larvae/fish and coagulated or dead eggs were removed daily, if observed as described below.
Hatching
The number of hatched larvae was determined daily until study day 5. Eggs were only removed, when mortality of eggs/embryos was observed as specified below.
On study day 3, 96 % of the control larvae had hatched. Therefore, study day 3 was defined as post-hatch day 0 (= PHD 0). For evaluation of hatch, all hatched larvae (even dead ones) were counted.
The cumulative number of hatched larvae was used for evaluation. For further details on evaluation see part 5.
Mortality Criteria for mortality vary according to life stage:
For eggs/embryos: If fungus growth on eggs was observed, these eggs were removed and counted. Mortality as discerned by a distinct change in coloration or a marked loss of translucency and change in coloration, caused by coagulation and/or precipitation of protein, leading to a white opaque appearance and change in coloration was checked daily. Mortality caused by absence of heartbeat was checked, if applicable. Dead eggs/embryos were discarded.
For larvae and juvenile fish: Immobility and/or lack of reaction to mechanical stimulus. Dead larvae or juvenile fish were discarded.
Further effects
Abnormal appearance and behavior were also recorded at adequate intervals.
The number of larvae or fish showing abnormality of body form was recorded. Abnormal animals were only removed from the test vessels on death. Abnormalities, e.g. hyperventilation, uncoordinated swimming, swim-up behavior, atypical quiescence and atypical feeding behavior were recorded by visually inspecting each replicate.
Measurement of fish size
At the end of exposure (post-hatch day 30) the fish were euthanized in a Benzocaine solution and the individual total length of all survivors was measured to the nearest 0.5 mm with graph paper. The total length (from the tip of the snout to the tip of the longer lobe of the caudal fin) was measured.
Measurement of fish wet weight
At the end of exposure (post-hatch day 30) all surviving fish were weighed on replicate basis to the nearest 0.1 mg. Fish were blotted on paper towels to remove excess moisture prior to weighing. The mean wet weight per animal was calculated from the number of surviving fish.
Physical Properties
Water quality measurements were carried out during exposure in the following intervals:
Once per hour Temperature in the dilution water, measured in a separate vessel filled with dilution water
Daily Determination of
- Dissolved oxygen in all replicates of each test group from fresh and old test media
Once per week
Determination of
-pH-value and temperature in all replicates of each test group
from freshly prepared test media at the start of an exposure interval and same measurements from the corresponding interval of the aged test
media
- TOC and Chlorine from the dilution water
- Total hardness in one replicate of the control group and the limit loading rate
The light intensity on the surface of the test aquaria was measured at the start of the exposure and on the day of changing the test vessels (study day 18).
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 33 d
- Dose descriptor:
- NOELR
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- number hatched
- Key result
- Duration:
- 33 d
- Dose descriptor:
- LOELR
- Effect conc.:
- > 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- number hatched
- Key result
- Duration:
- 33 d
- Dose descriptor:
- NOELR
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- length
- Key result
- Duration:
- 33 d
- Dose descriptor:
- LOELR
- Effect conc.:
- > 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- length
- Key result
- Duration:
- 33 d
- Dose descriptor:
- NOELR
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- weight
- Key result
- Duration:
- 33 d
- Dose descriptor:
- LOELR
- Effect conc.:
- > 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- weight
- Key result
- Duration:
- 33 d
- Dose descriptor:
- NOELR
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Post hatch survival
- Key result
- Duration:
- 33 d
- Dose descriptor:
- LOELR
- Effect conc.:
- > 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Post hatch survival
- Key result
- Duration:
- 33 d
- Dose descriptor:
- NOELR
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Overall survival
- Key result
- Duration:
- 33 d
- Dose descriptor:
- LOELR
- Effect conc.:
- > 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Overall survival
- Details on results:
- Egg Fertilization Rate
The egg fertilization rate, determined on study day 0 (start of the exposure) was 85 %.
Eggs were fully covered with the respective test solutions during fertilization check.
126 eggs were introduced in the control media and 21 of these eggs were discarded.
125 eggs were introduced in the loading rate 1.00 mg/L and 20 of these eggs were discarded.
120 eggs were introduced in the loading rate 3.16 mg/L and 14 of these eggs were discarded.
126 eggs were introduced in the loading rate 10.0 mg/L and 19 of these eggs were discarded.
In total 74 eggs of 497 introduced eggs were discarded, resulting in a fertilization rate of 85%.
Hatching and Definition of Post Hatch Day 0
Hatching began on study day 2 in the control and the loading rates 1.00, 3.16 and 10.0 mg/L of the test item and continued until study day 4, where the last hatched larvae in the loading of 1.00 mg/L was observed. Study day 3 was determined to be post hatch day 0 (PHD 0) with a hatching success of 96% in the control and in the loading rates 1.00 and 3.16 mg/L and 90% in the loading rate 10.0 mg/L. Hatching was completed in the loading rate 1.00 mg/L at study day 4 (100% hatching success).
Statistical procedures were applied for the total number of test organisms that have hatched. The Chi2 2x2 Table Test with Bonferroni Correction was performed for statistical analysis of hatching success on study day 3 and 6. No statistically significant difference was found between the control and each loading rate.
The NOELR and the LOELR (nominal loading rate) for this endpoint were determined to be 10 mg/L and > 10 mg/L, respectively.
Hatching Success in the Control and the Loading Rates
Nominal
loading rate
of the test item
[mg/L] Rep. PHD -2 PHD -1 PHD 0 PHD 1
Study day 1 Study day 2 Study day 3 Study day 4
Hatching success [%] per study day
Control 1 0 0 100 100
2 0 0 90 90
3 0 0 100 100
4 0 0 95 95
Mean 0 0 96 96
1.00 1 0 0 100 100
2 0 0 95 100
3 0 0 100 100
4 0 0 90 100
Mean 0 0 96 (-) 100
3.16 1 0 0 85 85
2 0 0 100 100
3 0 0 100 100
4 0 0 100 100
Mean 0 0 96 (-) 96
10.0 1 0 0 100 100
2 0 0 75 75
3 0 0 95 95
4 0 0 90 90
Mean 0 0 90 (-) 90
(-) = No statistically significant difference from control group
Swim-up
Swim-up was observed for a 4 day period from study days 4 to 7. Newly hatched fry began to swim up on study day 4 (PHD 1). On study day 7 (PHD 4), all surviving larvae had swum up, except one larvae in the control, which swam in lateral position, showed coordination disorders and died on study day 11. No statistical analysis of swim-up data was carried out.
Percent Swim-up of Hatched Live Fry of the Control and the Loading Rates
Nominal
loading rate
of the test item
[mg/L] Rep. PHD 0 PHD 1 PHD 2 PHD 3 PHD 4
Study day 3 Study day 4 Study day 5 Study day 6 Study day 7
Swim up [%]
Control 1 0 10 100 100 100
2 0 6 83 94 94
3 0 5 100 100 100
4 0 5 100 100 100
Mean 0 6 96 99 99
1.00 1 0 5 100 100 100
2 0 0 100 100 100
3 0 0 90 100 100
4 0 0 90 100 100
Mean 0 1 95 100 100
3.16 1 0 0 75 100 100
2 0 0 95 100 100
3 0 0 85 95 100
4 0 0 100 100 100
Mean 0 0 89 99 100
10.0 1 0 0 100 100 100
2 0 0 100 100 100
3 0 0 95 100 100
4 0 6 94 100 100
Mean 0 1 97 100 100
Fry Survival (Post-Hatch Survival)
The post-hatch survival in the control replicates met the validity criteria of the guideline (required: ≥ 75%). The fry survival (post-hatch survival) at the end of the study was 78% in the control. The post-hatch survival in the loading rates 1.00 to 10.0 mg/L of the test item was in the range of 76 to 82%.
The Chi2 2x2 Table Test with Bonferroni Correction was performed for statistical analysis of post hatch survival data on study day 33 (PHD 30). No statistically significant differences were found for each loading rate of 10 mg/L.
The NOELR and the LOELR for this endpoint were determined to be 10 and > 10 mg/L (nominal loading rate), respectively.
The LLR0 value for post hatch survival on study day 33 (PHD 30) was determined to be 10 mg/L (nominal limit loading rate).
Post-Hatch Survival on Study Day 33 (PHD 30) of the Control and the Loading Rates
Nominal
loading rate
of the test item
[mg/L] Rep. Eggs introduced on study day 0 Cumulative number of hatched larvae Vital Larvae on
study day 33
(PHD 30)
Post-Hatch survival
on study day 33
[%]
Control 1 20 20 16 80
2 20 18 12 67
3 20 20 18 90
4 20 19 14 74
Mean 20 19 15 78
1.00 1 20 20 15 75
2 20 20 15 75
3 20 20 18 90
4 20 20 13 65
Mean 20 20 15 76 (-)
3.16 1 20 17 13 76
2 20 20 15 75
3 20 20 19 95
4 20 20 16 80
Mean 20 19 16 82 (-)
10.0 1 20 20 15 75
2 20 15 13 87
3 20 19 16 84
4 20 18 13 72
Mean 20 18 14 80 (-)
(-) = No statistically significant difference from control groups
Overall Survival
The overall survival at the end of the exposure, related to the number of eggs introduced on day 0 was 75% in the control group and 71 to 79% in the loading rates 1.00 to 10.0 mg/L of the test item.
The Chi2 2x2 Table Test with Bonferroni Correction was performed for statistical analysis of overall survival data on study day 33 (PHD 30). No statistically significant differences were found for each nominal loading rate.
The NOELR and the LOELR for this endpoint were determined to be 10 and > 10 mg/L (nominal loading rate), respectively.
The LLR0 value for overall survival on study day 33 (PHD 30) was determined to be 10 mg/L (nominal loading rate).
Cumulative Survival and Mortality on Study Day 33 (PHD 30) of the Control and the Limit Loading Rate
Nominal
loading rate
of the test item
[mg/L] Rep.
Vital larvae on study day 33
(PHD 30)
Overall survival [%] Overall mortality [%]
Control 1 16 80 20
2 12 60 40
3 18 90 10
4 14 70 30
Mean 15 75 25
1.00 1 15 75 25
2 15 75 25
3 18 90 10
4 13 65 35
Mean 15 76 24 (-)
3.16 1 13 65 35
2 15 75 25
3 19 95 5
4 16 80 20
Mean 16 79 21 (-)
10.0 1 15 75 25
2 13 65 35
3 16 80 20
4 13 65 35
Mean 14 71 29 (-)
(-) = No statistically significant difference from control groups
Fry Growth
Fry growth, expressed as length and wet weight, was measured on study day 33 (PHD 30) from all survivors.
With the statistical procedures applied for fresh weight data and mean total length of all survivors (Dunnett`s Multiple t-test) all nominal loading rates showed no significant differences for these parameters. Therefore the NOELR and the LOELR for both parameters are 10 mg/L and > 10 mg/L (nominal loading rate).
Biomass Loading
The biomass-loading factor for the study was determined from the fresh weight of the control fish and the fish of the loading rates at the end of the exposur.
The maximum biomass at the end of the exposure was determined in replicate 3 of the loading rate 1.00 mg/L: 557.3 mg total fish weight. The maximum biomass loading based on the 2.5 liter volume of a single growth chamber was 223 mg/L.
Maximum loading rate: biomass/(volume of test solution) = (557.3 mg)/(2.5 L) = 223 mg/L
This loading was well within the requirements to ensure adequate dissolved oxygen levels and to avoid crowding of the fish.
Overview of Fry Growth: Length and Wet Weight on Study Day 33 (PHD 30) of the Control and the Loading Rates
Nominal
loading rate
of the test item
[mg/L] Rep. PHD 30 (End of exposure)
Mean total length per fish
[mm] Mean wet weight per fish
[mg]
Control 1 14.8 26.7
2 15.6 33.4
3 14.4 26.3
4 15.2 31.2
Mean 15.0 29.4
± SD 0.462 3.01
CV [%] 3.09 10.2
1.00 1 15.1 30.4
2 15.1 29.2
3 15.0 31.0
4 14.9 32.4
Mean 15.0 (-) 30.7 (-)
± SD 0.0677 1.18
CV [%] 0.451 3.83
3.16 1 15.0 29.6
2 14.6 29.0
3 13.7 25.0
4 14.5 29.5
Mean 14.4 (-) 28.3 (-)
± SD 0.445 1.91
CV [%] 3.08 6.75
10.0 1 14.9 31.1
2 15.8 36.7
3 14.0 28.5
4 15.7 37.1
Mean 15.1 (-) 33.4 (-)
± SD 0.706 3.68
CV [%] 4.68 11.0
(-) = No statistically significant difference from control groups
Individual Length on Study Day 33 (PHD 30) of the Control and the Loading Rates
Fish No. Nominal loading rate of the test item
[mg/L]
Control 1.00 3.16 10.0
Total length of individual fish in [mm]
1 2 3 4 1 2 3 4 1 2 3 4 1 2 3 4
1 16.5 15.5 14.0 17.5 15.0 15.0 13.0 18.0 15.0 18.5 14.0 14.5 15.0 17.0 11.0 15.0
2 16.0 16.0 13.0 12.0 14.5 16.0 13.0 13.0 16.0 13.0 14.0 14.0 14.0 13.5 15.0 18.0
3 15.0 17.0 15.0 14.5 14.5 16.5 13.0 15.0 15.0 14.5 15.0 13.0 13.0 15.5 14.0 17.5
4 15.0 16.5 17.5 15.0 15.5 17.0 14.5 10.5 16.0 15.0 14.0 14.0 11.0 15.5 12.0 17.0
5 16.5 16.5 17.5 17.0 14.0 12.5 14.5 12.0 16.0 15.0 14.5 11.5 15.5 16.5 12.0 15.0
6 15.0 18.0 17.0 14.5 15.0 15.5 15.0 13.0 15.0 12.0 13.0 15.0 16.5 15.5 14.5 15.0
7 14.0 15.5 13.5 12.5 17.0 15.5 18.0 15.0 13.0 13.0 13.5 15.5 15.0 14.0 15.0 15.0
8 16.5 10.5 10.0 14.0 14.0 13.0 16.0 19.0 10.0 12.0 14.0 16.0 14.0 17.5 13.0 15.5
9 18.0 17.0 12.0 13.0 15.5 14.5 16.5 16.0 12.0 15.5 14.0 12.0 15.5 16.0 10.5 16.0
10 11.0 19.5 16.5 18.0 15.0 16.5 16.0 17.0 14.0 14.5 11.0 14.5 15.5 15.5 16.5 14.0
11 15.5 12.5 16.0 16.0 12.5 17.0 16.0 13.0 17.5 15.0 16.0 15.0 15.0 14.5 17.0 16.0
12 14.0 12.5 15.0 15.5 18.0 14.0 14.5 17.0 18.0 16.0 15.0 14.0 14.5 15.0 16.0 15.0
13 11.0 ̶ 8.0 17.0 19.5 14.0 16.0 15.5 17.0 15.5 10.0 16.5 15.5 19.0 16.0 15.0
14 10.0 ̶ 15.5 16.5 16.5 13.0 15.5 ̶ ̶ 14.0 13.5 15.5 15.0 ̶ 12.0 ̶
15 16.5 ̶ 15.0 ̶ 10.0 16.0 17.0 ̶ ̶ 15.0 15.0 15.5 18.0 ̶ 15.0 ̶
16 15.5 ̶ 15.0 ̶ ̶ ̶ 16.0 ̶ ̶ ̶ 14.0 16.0 ̶ ̶ 15.0 ̶
17 ̶ ̶ 14.5 ̶ ̶ ̶ 14.0 ̶ ̶ ̶ 15.0 ̶ ̶ ̶̶ ̶ ̶
18 ̶ ̶ 13.5 ̶ ̶ ̶ 11.5 ̶ ̶ ̶ 13.5 ̶ ̶ ̶ ̶ ̶
19 ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ 12.0 ̶ ̶ ̶ ̶ ̶
20 ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶ ̶
Mean 14.8 15.6 14.4 15.2 15.1 15.1 15.0 14.9 15.0 14.6 13.7 14.5 14.9 15.8 14.0 15.7
± SD 2.20 2.45 2.42 1.83 2.15 1.45 1.61 2.41 2.17 1.60 1.41 1.37 1.51 1.42 1.96 1.12
CV % 14.92 15.71 16.85 12.02 14.27 9.61 10.72 16.14 14.51 10.99 10.25 9.46 10.2 9.0 14.0 7.1
- = Fish died before end of the study
Pooled Wet Weights on Study Day 33 (PHD 30) of the Control and the Loading Rates
Nominal
loading rate
of the test item
[mg/L] Replicate
Number of fish alive
on study day 33 Pooled
wet weight
per replicate
[mg] Mean
wet weight
per fish
[mg] Mean
[mg] ± SD
CV %
Control 1 16 426.8 26.7 29.4 3.01 10.2
2 12 400.3 33.4
3 18 473.0 26.3
4 14 437.3 31.2
1.00 1 15 455.5 30.4 30.7 1.18 3.83
2 15 437.3 29.2
3 18 557.3 31.0
4 13 421.5 32.4
3.16 1 13 384.5 29.6 28.3 1.91 6.75
2 15 435.0 29.0
3 19 474.4 25.0
4 16 471.4 29.5
10.0 1 15 466.7 31.1 33.4 3.68 11.0
2 13 477.0 36.7
3 16 455.7 28.5
4 13 482.6 37.1
Morphological and Behavioral Effects
No biologically significant morphological and behavioral effects were observed in the nominal loading rate 3.16 mg/L. In the control and the nominal loading rates 1.00 and 10.0 mg/L, isolated events of side position (S), coordination issues (C) and Quiescence (Q) were observed from study day 7 up to study day 21.
Behavioral Effects of the Control and the Nominal Loading Rates 1.00 and 10.0 mg/L (Study Day 7 – 21)
Study Day Control 1.00 mg/L 10.0 mg/L
1 2 3 4 1 2 3 4 1 2 3 4
7 - 1: S - - - - - - - - - -
8 - 1: S - - - - - - - - - -
9 - 1: C - - - - - - - - - -
10 - 1: C - - - - - - - - - -
11 - - - - - - 1: Q - - - - -
12 - - - - - - 1: Q - - - - -
13 - - - - - - 1: Q - - - - -
14 - - - - - - - - - - - -
15 - - - - - - - - - - - -
16 - - - - - - - - - - - -
17 - - - - - - - - - - - -
18 - - - - - - - - 1: Q - 1: Q -
19 - - - - 2: Q - - - 1: Q - 1: Q -
20 - - - - - - - - 1: Q - 1: Q -
21 - - - 1: Q - - - - - - - -
S = Larvae was lying on its side
C = Coordination issues
Q = Quiescence
Any other information on results incl. tables
Dissolved Oxygen
The dissolved oxygen concentrations in the control and the test item groups, expressed in percent saturation, were in the mean 90 to 91% for all test groups and the control and ranged from 61 to 100% during the exposure period.
Dissolved Oxygen in Percent Air Saturation Value in the Test Media (Study Day 0 - 3)
Study day Replicate Media Dissolved oxygen [%]
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
0 1 Fresh 91 89 87 87
2 Fresh 89 88 87 88
3 Fresh 87 87 87 88
4 Fresh 87 87 87 88
1 1 Fresh 93 91 91 91
Aged 89 86 87 86
2 Fresh 93 91 91 89
Aged 89 86 85 81
3 Fresh 92 89 90 91
Aged 89 81 85 82
4 Fresh 91 90 90 90
Aged 86 85 86 81
2 1 Fresh 97 94 94 93
Aged 99 95 91 92
2 Fresh 96 93 93 92
Aged 97 94 92 88
3 Fresh 95 92 93 92
Aged 96 90 90 91
4 Fresh 95 91 93 91
Aged 97 92 91 89
3 1 Fresh 94 92 91 92
Aged 99 93 90 91
2 Fresh 93 92 92 92
Aged 98 92 91 87
3 Fresh 93 91 92 91
Aged 97 82 90 87
4 Fresh 93 91 92 92
Aged 96 87 91 89
Dissolved Oxygen in Percent Air Saturation Value in the Test Media (Study Day 4 - 8)
Study day Replicate Media Dissolved oxygen [%]
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
4 1 Fresh 95 94 92 92
Aged 100 96 93 92
2 Fresh 94 94 94 93
Aged 99 95 93 91
3 Fresh 92 93 92 93
Aged 97 92 92 91
4 Fresh 92 92 92 92
Aged 97 91 92 91
5 1 Fresh 96 92 92 92
Aged 97 94 93 92
2 Fresh 94 92 92 92
Aged 96 92 93 93
3 Fresh 93 91 92 92
Aged 96 90 90 90
4 Fresh 93 92 93 92
Aged 96 92 92 91
6 1 Fresh 95 93 93 91
Aged 95 93 88 90
2 Fresh 93 93 91 91
Aged 91 91 88 89
3 Fresh 92 91 91 89
Aged 91 89 86 83
4 Fresh 92 92 90 89
Aged 92 90 87 85
7 1 Fresh 83 87 90 88
Aged 84 65 80 78
2 Fresh 87 86 88 88
Aged 75 70 78 75
3 Fresh 89 88 88 84
Aged 85 70 71 68
4 Fresh 86 89 89 83
Aged 72 75 76 64
8 1 Fresh 91 90 92 91
Aged 92 85 89 83
2 Fresh 91 90 91 92
Aged 87 88 80 82
3 Fresh 92 91 90 92
Aged 90 90 79 81
4 Fresh 91 91 91 91
Aged 85 91 87 81
Dissolved Oxygen in Percent Air Saturation Value in the Test Media (Study Day 9 - 13)
Study day Replicate Media Dissolved oxygen [%]
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
9 1 Fresh 92 93 94 92
Aged 88 84 87 80
2 Fresh 94 93 92 93
Aged 89 87 86 84
3 Fresh 94 91 92 91
Aged 91 87 85 83
4 Fresh 92 91 93 92
Aged 85 91 83 80
10 1 Fresh 90 94 92 94
Aged 91 89 90 89
2 Fresh 98 93 93 94
Aged 91 88 86 88
3 Fresh 92 90 92 94
Aged 88 86 84 86
4 Fresh 92 91 95 96
Aged 88 88 85 87
11 1 Fresh 93 95 93 95
Aged 97 93 92 92
2 Fresh 94 94 93 95
Aged 96 91 92 93
3 Fresh 95 91 90 95
Aged 96 87 84 90
4 Fresh 95 94 93 96
Aged 94 92 89 91
12 1 Fresh 86 89 92 92
Aged 91 88 91 88
2 Fresh 90 89 90 89
Aged 87 88 90 84
3 Fresh 89 87 89 90
Aged 91 86 88 85
4 Fresh 89 90 89 91
Aged 88 88 90 88
13 1 Fresh 83 91 92 90
Aged 86 90 91 86
2 Fresh 87 90 92 90
Aged 90 90 86 75
3 Fresh 91 83 87 90
Aged 94 85 84 84
4 Fresh 89 88 91 90
Aged 92 90 87 83
Dissolved Oxygen in Percent Air Saturation Value in the Test Media (Study Day 14 - 18)
Study day Replicate Media Dissolved oxygen [%]
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
14 1 Fresh 87 88 87 90
Aged 91 85 87 89
2 Fresh 85 88 87 90
Aged 90 89 87 85
3 Fresh 90 87 90 89
Aged 94 91 81 86
4 Fresh 86 87 88 88
Aged 92 90 84 84
15 1 Fresh 87 88 84 88
Aged 83 86 87 86
2 Fresh 86 90 85 89
Aged 87 88 85 85
3 Fresh 90 90 86 89
Aged 93 90 84 85
4 Fresh 87 87 86 87
Aged 90 88 87 81
16 1 Fresh 90 89 91 90
Aged 92 86 91 88
2 Fresh 89 90 90 86
Aged 87 89 87 86
3 Fresh 90 89 92 86
Aged 92 91 89 85
4 Fresh 86 93 90 87
Aged 87 91 87 86
17 1 Fresh 72 83 90 90
Aged 75 71 67 70
2 Fresh 75 84 87 89
Aged 73 69 74 69
3 Fresh 80 87 89 86
Aged 69 78 75 68
4 Fresh 71 85 84 86
Aged 64 77 65 63
18 1 Fresh 95 92 92 91
Aged 85 85 86 83
2 Fresh 94 91 92 91
Aged 83 86 86 91
3 Fresh 94 92 90 89
Aged 88 84 86 75
4 Fresh 93 92 90 91
Aged 82 85 90 76
Dissolved Oxygen in Percent Air Saturation Value in the Test Media (Study Day 19 - 23)
Study day Replicate Media Dissolved oxygen [%]
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
19 1 Fresh 97 96 92 94
Aged 94 86 82 89
2 Fresh 95 95 91 92
Aged 92 86 84 63
3 Fresh 95 94 93 92
Aged 93 84 79 61
4 Fresh 94 95 92 92
Aged 85 87 88 71
20 1 Fresh 90 92 90 91
Aged 91 94 89 93
2 Fresh 90 92 92 92
Aged 94 93 87 91
3 Fresh 91 91 92 91
Aged 94 91 91 91
4 Fresh 90 91 90 90
Aged 94 94 89 91
21 1 Fresh 84 93 90 93
Aged 89 92 83 91
2 Fresh 87 92 93 93
Aged 88 92 89 92
3 Fresh 90 89 93 95
Aged 91 86 91 93
4 Fresh 89 91 91 93
Aged 91 89 91 91
22 1 Fresh 90 90 90 92
Aged 86 90 84 88
2 Fresh 92 92 92 93
Aged 86 92 90 90
3 Fresh 89 94 91 93
Aged 89 88 89 92
4 Fresh 91 91 91 92
Aged 88 88 92 92
23 1 Fresh 91 100 100 99
Aged 97 100 100 97
2 Fresh 95 100 100 100
Aged 98 100 100 98
3 Fresh 98 100 99 99
Aged 100 100 99 100
4 Fresh 97 99 100 100
Aged 98 99 100 100
Dissolved Oxygen in Percent Air Saturation Value in the Test Media (Study Day 24 - 28)
Study day Replicate Media Dissolved oxygen [%]
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
24 1 Fresh 95 91 92 96
Aged 94 90 84 97
2 Fresh 93 91 93 97
Aged 89 87 87 94
3 Fresh 94 90 94 95
Aged 87 89 90 92
4 Fresh 92 93 94 94
Aged 90 91 90 90
25 1 Fresh 93 92 95 93
Aged 95 94 95 93
2 Fresh 93 93 96 93
Aged 96 96 94 92
3 Fresh 93 92 94 94
Aged 97 96 94 95
4 Fresh 87 91 95 98
Aged 94 91 96 95
26 1 Fresh 90 89 92 91
Aged 88 90 94 87
2 Fresh 89 88 92 86
Aged 90 90 92 81
3 Fresh 87 86 93 92
Aged 87 90 95 93
4 Fresh 85 88 94 93
Aged 83 88 96 86
27 1 Fresh 93 93 96 97
Aged 94 89 94 95
2 Fresh 93 96 96 97
Aged 96 94 94 95
3 Fresh 93 95 97 97
Aged 95 95 95 96
4 Fresh 93 94 96 95
Aged 94 92 94 95
28 1 Fresh 91 95 95 92
Aged 88 86 90 81
2 Fresh 94 93 95 91
Aged 88 89 93 82
3 Fresh 89 90 93 95
Aged 83 90 91 80
4 Fresh 92 95 91 96
Aged 89 92 82 81
Dissolved Oxygen in Percent Air Saturation Value in the Test Media (Study Day 29 - 33)
Study day Replicate Media Dissolved oxygen [%]
Nominal loading rate of the test item [mg/L]
Control 1.00 3.16 10.0
29 1 Fresh 90 96 96 96
Aged 89 96 95 91
2 Fresh 95 97 96 96
Aged 95 93 94 91
3 Fresh 92 93 96 97
Aged 96 88 93 93
4 Fresh 91 95 95 97
Aged 94 95 92 95
30 1 Fresh 95 94 96 95
Aged 94 97 94 92
2 Fresh 96 98 95 96
Aged 94 96 96 92
3 Fresh 95 95 95 97
Aged 94 90 97 95
4 Fresh 93 94 91 97
Aged 91 96 97 93
31 1 Fresh 94 95 95 98
Aged 98 98 97 96
2 Fresh 93 93 95 96
Aged 98 98 98 95
3 Fresh 93 95 96 97
Aged 97 98 99 98
4 Fresh 92 94 96 97
Aged 96 98 95 97
32 1 Fresh 97 95 94 97
Aged 100 99 98 99
2 Fresh 95 95 95 94
Aged 98 99 98 97
3 Fresh 90 94 95 94
Aged 97 99 98 97
4 Fresh 92 94 95 93
Aged 96 98 97 96
33 1 Aged 90 92 89 91
2 Aged 91 91 90 92
3 Aged 92 90 90 92
4 Aged 93 92 89 90
Mean 91 91 91 90
SD 5.31 4.98 5.08 6.53
Min. 64 65 65 61
Max. 100 100 100 100
Min./Max. = Minimum/Maximum measured dissolved oxygen concentration
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Hansa Scarlet RNC-IN caused no adverse effects on Zebrafish in an early life stage toxicity test, 30 days post hatch in comparison to the dilution water control group exposed to a nominal loading rate of 10 mg test item/L.
For the parameter hatching success the NOELR was 10 mg/L. Therefore the LOELR for hatchability was determined to be > 10 mg/L. For the parameters post hatch and overall survival (mortality) the NOELR was 10 mg/L. Therefore, the LOELR for these parameters was determined to be > 10 mg/L. For the parameter fry growth (expressed as length and fresh weight) the NOELR was 10 mg/L. Therefore, the LOELR for these parameters was determined to be > 10 mg/L.
As the test item disperses, the effect values are considered to be based on the nominal loading rates.
Additionally effect levels were given based on the geometric mean measured concentrations of the dispersed fraction of the test item and on the geometric mean measured concentrations of the dissolved fraction of the test item. - Executive summary:
The effects of the test item Hansa Scarlet RNC-IN (Batch-No. INB 3100014) to the early-life stage of fish (Danio rerio / Zebrafish) were determined at the test facility according to OECD Guideline 210 from 2020-06-18 to 2020-07-21.
Hansa Scarlet RNC-IN is a red powder with a water solubility of approximately 3 µg/L. Three loading rates were tested for profound estimation of the NOELR and LOELR values. According to the guideline the highest loading rate did not exceed 10 mg/L.
With regard to the specific properties of the test item (particles, poorly water soluble, pigment), the study was carried out with dispersions of the test item (i.e. in excess of water solubility). The preparation of the dispersions include ultra-sonication and vigorous mixing to disperse the test item in water, followed by low energy mixing with circulating pumps to prevent sedimentation.
The study was conducted as a semi-static test and daily renewal of the test media. Daily renewal was chosen, due to the outcome of the preliminary experiments on dispersion stability carried out referring to OECD 318 and Series on the Safety of Manufactured Nanomaterials No. 40 Guidance Document.
The test was started by placing fertilized eggs into the test vessels and it lasted 33 days (30 days post-hatch). 80 eggs of Danio rerio / zebrafish were exposed to each loading rate and the control (4 replicates with 20 eggs each).
The water quality parameters pH-value, oxygen concentration, temperature and total hardness were within the acceptable limits.
On study day three, 96 % of the control larvae had hatched. Therefore, study day 3 was defined as post hatch day 0 (= PHD 0).
Different toxicological endpoints were determined: hatching success, time to hatch, fry growth (expressed as length and fresh weight), morphological and behavioral effects, post-hatch survival and overall survival (mortality).
Specific analysis of each loading rate of Hansa Scarlet RNC-IN and the control was carried out via LC-MS/MS. The dispersed fraction of the test item was determined after addition of DMSO directly after sampling. The dissolved fraction was determined after centrifugation of the water samples, to remove undissolved test item. The concentrations were analytically verified twice during 7 days of exposure from freshly prepared test media on study day 0 (start of the exposure), 7, 14, 21 and 28 and from corresponding 24 hours aged test media on study days 1, 8, 15, 22 and 29.
As the test item disperses, the effect values are considered to be based on the nominal loading rates. Additionally, the specific analysis determined the ratio of truly dissolved and particulate test item.
Therefore all effect values are given based on the nominal limit loading rate of the test item. Additionally effect levels were given based on the geometric mean measured concentrations of the dispersed fraction of the test item and on the geometric mean measured concentrations of the dissolved fraction of the test item. In the samples, the sedimentated fraction was not included. However, this fraction was also present in the test vessels.
Findings and Observations
The results of the parameters hatching success, time to hatch, fry growth (expressed as weight and length), post-hatch survival and overall survival were checked for statistically significant differences.
No statistically significant differences were detected between the dilution water control and the each loading rate of the test item. In conclusion under the conditions of this test the test item did not affect early-life stages of the zebrafish at a nominal loading rate of 10 mg/L.
The effect values NOELR and LOELR were determined based on the statistical results. The results are presented in the tables below:
NOELR and LOELR Values of Hatching Success and Fry Growth
Parameter Hatching Success Fry Growth
expressed as:
Length Weight
Nominal test item loading [mg/L]
NOELR
[mg/L] 10 10 10
LOELR
[mg/L] > 10 > 10 > 10
geometric mean measured concentrations
of the dispersed fraction of the test item [mg/L]
NOELR
[mg/L] 3.27 3.27 3.27
LOELR
[mg/L] > 3.27 > 3.27 > 3.27
geometric mean measured concentrations
of the dissolved fraction of the test item [mg/L]
NOELR
[mg/L] 0.00581 0.00581 0.00581
LOELR
[mg/L] > 0.00581 > 0.00581 > 0.00581
NOELR and LOELR Values of Post Hatch Survival and Overall Survival
Parameter Post hatch survival Overall survival
Nominal test item loading [mg/L]
NOELR
[mg/L] 10 10
LOELR
[mg/L] > 10 > 10
geometric mean measured concentrations
of the dispersed fraction of the test item [mg/L]
NOELR
[mg/L] 3.27 3.27
LOELR
[mg/L] > 3.27 > 3.27
geometric mean measured concentrations
of the dissolved fraction of the test item [mg/L]
NOELR
[mg/L] 0.00581 0.00581
LOELR
[mg/L] > 0.00581 > 0.00581
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