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EC number: 267-051-0 | CAS number: 67774-74-7
- 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:
- key study
- Study period:
- Nov 1999 to Mar 2000
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 201 (Alga, Growth Inhibition Test)
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- yes
- Details on test solutions:
- Acetone was used as a solvent (1 mL/L).
- Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Source: Ecotoxicology Dpt. of Centro Nacional de Sanidad Ambiental. Instituto de Salud Carlos lll 28220. Majadahonda (Madrid) - Test type:
- not specified
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Hardness:
- (Ca + Mg) ≤ 0.6 mmol /L
- Test temperature:
- 22 ± 1
- pH:
- 7.1 ± 0.1
- Nominal and measured concentrations:
- - Nominal concentrations: 25, 50 and 100 µg/L.
- Measured concentrations: 23, 25 and 98 µg/L respectively. - Details on test conditions:
- - Initial cells density: 1.0E+04
- Determination of cell concentrations: Coulter Counter
- No. of vessels pre treatment: 3
- No. of vessels pre controls: 2 - 5
- The composition of algae mediumis provide in Table 1 in "Any other information on materials and methods incl. tables". - Reference substance (positive control):
- no
- Key result
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 50 µg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 µg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- LOEC
- Effect conc.:
- 100 µg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Details on results:
- An overview of the results is provided in Table 2 to Table 7 in "Any other information on results incl. tables"
- No effects were found for LAB C10 - C13 at 50 µg/L (solubility as measured in study for C12 LAB: 37.6 µg/L).
- EC50 values were above 100 µg/L for all the tested substances. - Validity criteria fulfilled:
- yes
- Conclusions:
- Based on the findings, the 72-hr NOErC was determined to be ≥50 µg/L and ErC50 values were > 100 µg/L for all substances tested. This is higher than the measured solubility limit for C12 LAB of 37.6 µg/L.
- Executive summary:
This study examined the toxicity of linear alkyl benzenes to aquatic algae, Scenedesmus subspicatus. The study was conducted according to OECD TG 201 and in compliance with GLP. The algae was exposed to concentrations of 25, 50 and 100 µg/L of test substance for 72 hrs. During this time, readings of the growth rate were taken. Tests were also done on C10, C12, and C14 linear alkyl benzenes in addition to commercial LAB. Based on the findings, the 72-hr NOErC was determined to be ≥ 50 µg/L and ErC50 values were > 100 µg/L for all substances tested. This is higher than the measured solubility limit for C12 LAB of 37.6 µg/L.
Reference
Table 2. Results of cell concentration s for LAB CAS 67774 -74 -7
Cell concentrations for LAB CAS 67774-74-7 Time 72 hours Replicates 3 Controls 6 Nº 1.0E+04 cell/mL Threshold 8 Cell Diameter 3.340 µm Cell Volume 19.48 µm3 |
|||||||||||
Controls |
|||||||||||
C - 1 |
C – 2 |
C – 3 |
C – 4 |
C – 5 |
C - 6 |
||||||
198 |
207 |
244 |
211 |
208 |
247 |
||||||
220 |
210 |
217 |
224 |
210 |
233 |
||||||
201 |
205 |
245 |
221 |
230 |
235 |
||||||
206 |
207 |
235 |
220 |
216 |
238 |
||||||
F = 2000 x = 220 S=13.6 N = 4.4 x 105 µ = 1.30 |
|||||||||||
LAB – CAS 67774-74-7 |
|||||||||||
|
1 |
x |
2 |
x |
3 |
x |
|
||||
|
267 |
|
281 |
|
259 |
|
x = 269 |
||||
25 ppb |
273 |
278 |
261 |
269 |
268 |
260 |
N=5.4x105 |
||||
|
294 |
|
265 |
|
254 |
|
µ = 1.33 |
||||
|
288 |
|
292 |
|
254 |
|
x= 272 |
||||
50 ppb |
277 |
278 |
292 |
288 |
237 |
250 |
N=5.4x105 |
||||
|
268 |
|
280 |
|
260 |
|
µ = 1.33 |
||||
|
230 |
|
204 |
|
191 |
|
x=216 |
||||
100 ppb |
259 |
245 |
206 |
206 |
191 |
198 |
N=4.3x105 |
||||
|
245 |
|
209 |
|
211 |
|
µ = 1.25 |
Table 3. Results of cell concentrations for LAB C10
Cell concentrations for LAB C10 Time 72 hours Replicates 2 Controls 2 Nº 1.0E+04 cell/mL Threshold 8 Cell Diameter 3.340 µm Cell Volume 19.48 µm3
|
|||||
Control |
|||||
C-1 |
C-2 |
||||
335 |
356 |
||||
341 |
353 |
||||
375 |
381 |
||||
350 |
363 |
||||
F= 2000; X= 357; S= 9.19; N= 7.1 E+05; µ = 1.42 |
|||||
LAB – C10 |
|||||
ppb |
1 |
Mean |
2 |
Mean |
|
25 |
212 |
224 |
267 |
272 |
x = 248 µ = 1.30 N = 5E+05 |
222 |
274 |
||||
238 |
274 |
||||
50 |
282 |
256 |
284 |
252 |
x = 254 µ = 1.30 N = 5.1 E+05 |
229 |
234 |
||||
258 |
238 |
||||
100 |
261 |
245 |
183 |
215 |
x = 230 µ = 1.27 N = 4.6E+05 |
228 |
239 |
||||
248 |
223 |
Table 4. Results of cell concentrations for LAB C12
Cell concentrations for LAB C12 Time 168 hours (Prolonged) Replicates 3 Controls 5 Nº 1.0E+04 cell/mL Threshold 8 Cell Diameter 3.340 µm Cell Volume 19.48 µm3
|
|||||||||||
Control |
|||||||||||
C -1 |
C - 2 |
C - 3 |
C - 4 |
C - 5 |
|||||||
4033 |
2469 |
2251 |
3241 |
2551 |
|||||||
4168 |
2499 |
2115 |
3309 |
2619 |
|||||||
4347 |
2469 |
2243 |
3392 |
2661 |
|||||||
4182 |
2479 |
2203 |
3314 |
2610 |
|||||||
Annuled F= 2000; X= 2651; S= 573.12; N= 5.3 E+06; µ = 0.89 |
|||||||||||
LAB – C12 |
|||||||||||
ppb |
1 |
Mean |
2 |
Mean |
3 |
Mean |
|
||||
25 |
2357 |
2440 |
2616 |
2609 |
3359 |
3359 |
x = 2802 µ = 0.9 N = 5.6E+06 |
||||
2439 |
2532 |
3396 |
|||||||||
2525 |
2679 |
3322 |
|||||||||
50 |
2378 |
2432 |
2119 |
2223 |
2235 |
2285 |
x = 2313 µ = 0.87 N = 4.6E+06 |
||||
2510 |
2210 |
2320 |
|||||||||
2410 |
2341 |
2302 |
|||||||||
100 |
2562 |
2482 |
3191 |
3183 |
3196 |
3079 |
x = 2914 µ = 0.9 N = 5.8E+06 |
||||
2452 |
3188 |
3069 |
|||||||||
2423 |
3172 |
2973 |
Table 5. Results of cell concentrations for LAB C14
Cell concentrations for LAB C14 Time 72 hours Replicates 3-2 Controls 5 Nº 1.0E+04 cell/mL Threshold 8 Cell Diameter 3.340 µm Cell Volume 19.48 µm3
|
|||||||||||
Control |
|||||||||||
C -1 |
C - 2 |
C - 3 |
C - 4 |
C - 5 |
|||||||
785 |
620 |
726 |
721 |
739 |
|||||||
784 |
708 |
669 |
793 |
784 |
|||||||
716 |
678 |
649 |
786 |
756 |
|||||||
761 |
668 |
681 |
766 |
760 |
|||||||
F= 2000; X= 727; S= 48.38; N= 1.45 E+06; µ = 1.65 |
|||||||||||
LAB – C14 |
|||||||||||
ppb |
1 |
Mean |
2 |
Mean |
3 |
Mean |
|
||||
25 |
743 |
717 |
821 |
842 |
|
|
x = 779 µ = 1.6 N = 1.5E+06 |
||||
717 |
859 |
|
|||||||||
692 |
847 |
|
|||||||||
50 |
741 |
728 |
750 |
753 |
|
|
x = 740 µ = 1.6 N = 1.48E+06 |
||||
710 |
728 |
|
|||||||||
735 |
783 |
|
|||||||||
100 |
705 |
718 |
645 |
620 |
807 |
819 |
x = 719 µ = 1.6 N = 1.4E+06 |
||||
719 |
611 |
854 |
|||||||||
740 |
604 |
798 |
|||||||||
Table 6. Results of growth inhibition for LAB CAS 67774 -74 -7
Inhibition of growth rate |
|
Sample : Commercial LAB CAS Nº 67774-74-7 |
|
Concentration ppb |
Inhibition % |
25 |
-2.3 |
50 |
-2.3 |
100 |
3.8 |
Table 7. Results of growth inhibition for LAB-C10, LAB-C12, LAB-C14
Inhibition of growth rate |
|||
Samples: LAB-C10, LAB-C12, LAB-C14 |
|||
Concentration ppb |
Inhibition % |
||
|
LAB-C10 |
LAB-C12 |
LAB-C14 |
25 |
8.4 |
-1.1 |
3.1 |
50 |
8.4 |
2.2 |
3.1 |
100 |
10.5 |
-1.1 |
3.1 |
Description of key information
All available data was assessed and the key study was condisered to be the worst-case and selected for CSA. The other study was included as supporting information.
A 72-hour short-term toxicity test of the test subtsance to freshwater algae (Scenedesmus subspicatus) was conducted according to OECD Guideline No. 201. The NOErC was determined to be ≥ 50 µg/L and ErC50 value was > 100 µg/L.
Key value for chemical safety assessment
- EC10 or NOEC for freshwater algae:
- 50 µg/L
Additional information
The key study examined the toxicity of
various LABs to aquatic algae. Tests were also done on C10,
C12, and C14
linear alkyl benzenes in addition to the commercial LAB.
Scenedesmus subspicatus was exposed to the test substances for 72 hours.
During this time, readings of the growth rate were taken. The nominal
concentrations tested were 25, 50 and 100 µg/L, with corresponding
measured concentrations of 23, 25, and 98 µg/L, respectively, for the C12-LAB.
The 72-hr EC50 values for all substances were >100 µg/L (nominal), which
is higher than the measured solubility limit for C12-LAB
(37.6 µg/L).
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