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Diss Factsheets

Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Administrative data

Link to relevant study record(s)

Reference
Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: data from the EU Risk Assessment DODMAC (2002)
Justification for type of information:
The primary component of all substances provide complete coverage of 68334-33-8. 68334-33-8 shares high structural similarity with 61789-80-8, 68783-78-8, 107-64-2, and 112-02-7. As 68334-33-8 is a UVCB its components encapsulate the other substances except for the counter ion (Cl-). In solution, the counter ions will dissociate from the parent structures. Therefore, we are comparing substances of equivalent nature. CAS 107-64-2 represents the C18 boundary of the 61789-80-8. Ignoring the salt component CAS 61789-80-8 is equivalent to CAS 68334-33-8. 68783-78-8 is a worst case of both 68334-33-8 and 61789-80-8 since it is unsaturated and the SP2 carbon-carbon bonds are of higher reactivity and a more likely site of metabolic activation. The primary component of CAS 112-02-7 is a substructure of all the other substances. Additional documentation, provided within the IUCLID Assessment Reports section, supports the read-across approach.
Reason / purpose for cross-reference:
read-across: supporting information
Qualifier:
no guideline followed
Principles of method if other than guideline:
Algae were tested in river water and laboratory water.
GLP compliance:
not specified
Analytical monitoring:
not specified
Test organisms (species):
Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
Test type:
not specified
Water media type:
freshwater
Total exposure duration:
5 d
Hardness:
20 mg/L CaCO3 (Laboratory water)
299 mg/L CaCO3 (White River)
pH:
7.3 (White River)
Details on test conditions:
68 mg/L suspended solids
0.2 μg/L MBAS
Duration:
5 d
Dose descriptor:
NOEC
Effect conc.:
0.062 mg/L
Nominal / measured:
nominal
Conc. based on:
act. ingr.
Basis for effect:
cell number
Remarks on result:
other: Water from White river: pH 7.3, 299 mg/L CaCO3, 68 mg/L suspended solids
Duration:
5 d
Dose descriptor:
NOEC
Effect conc.:
0.078 mg/L
Nominal / measured:
nominal
Conc. based on:
act. ingr.
Basis for effect:
cell number
Remarks on result:
other: Laboratory water: 20 mg/L CaCO3
Conclusions:
5-day NOEC: 0.062 mg/L (cell number; river water)
5-day NOEC: 0.078 mg/L (cell number; laboratory water)
Executive summary:

The influence of different test media on the sensitivity of Selenastrum capricornutum towards DHTDMAC (71.4% active ingredient) was investigated. Laboratory water with a hardness of 20 mg/L CaCO3 (no further characterization) and algae nutrient enriched White River water (Indiana) of the following quality prior to autoclaving were used: pH = 7.3, total hardness = 299 mg/L CaCO3, 68 mg/L suspended solids, 0.2 μg/L MBAS) In laboratory water a NOEC of 0.078 mg/L and an algistatic concentration of 0.228 mg/L were derived for the reduction of cell number after 5 days (nominal concentrations of active ingredient). The corresponding values for the river water were: NOEC = 0.062 mg/L and algistatic concentration = 0.708 mg/L. The table shows that results for Microcystis aeruginosa are similar (cited in EU Risk Assessment).

 

Selenastrum capricornutum

5d NOEC

0.078 mg/L

DHTDMAC

Laboratory water

EG & G

Bionomics,

1981

5 d EC100

0.228 mg/L

DHTDMAC

Laboratory water

5d NOEC

0.062 mg/L

DHTDMAC

River water

5 d EC100

0.708 mg/L

DHTDMAC

River water

 

Microcystis aeruginosa

5d NOEC

0.13 mg/L

DHTDMAC

Laboratory water

EG & G

Bionomics,

1981

5 d EC100

0.32 mg/L

DHTDMAC

Laboratory water

5d NOEC

0.078 mg/L

DHTDMAC

River water

5 d EC100

0.21 mg/L

DHTDMAC

River water

 

Description of key information

Key value for chemical safety assessment

EC50 for freshwater algae:
0.48 mg/L
EC10 or NOEC for freshwater algae:
0.062 mg/L

Additional information