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EC number: 236-337-7 | CAS number: 13308-51-5
- 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 soil macroorganisms except arthropods
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil macroorganisms except arthropods: long-term
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 14 Apr - 09 Jun 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 222 (Earthworm Reproduction Test (Eisenia fetida/Eisenia andrei))
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Ministerium für Arbeit, Integration und Soziales des Landes Nordrhein-Westfalen
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on preparation and application of test substrate:
- - Method of mixing into soil (if used): As the test item is insoluble in water and easily evaporating organic solvents, the quantity of test item required to obtain the desired concentrations was applied to quartz sand by grinding. The spiked quartz sand was distributed on the soil and mixed thoroughly. The test substrate was prorated to each test container.
- Controls: yes - Test organisms (species):
- Eisenia andrei
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Source: Regenwurmfarm Tacke, Borken, Germany
- Age at test initiation (mean and range, SD): 2 - 12 months
- Weight at test initiation (mean and range, SD): 250 - 600 mg
ACCLIMATION
- Acclimation period:6 days
- Acclimation conditions (same as test or not): The worms were conditioned in the artificial soil before use. The same food which was also used in the test was given in a sufficient amount.
- Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- no
- Total exposure duration:
- 56 d
- Test temperature:
- 18 - 22°C
- pH:
- test start: 6.2 - 6.5
test end: 5.9 - 6.2 - Details on test conditions:
- TEST SYSTEM
- Test container (material, size): plastic containers (area of 17x12 cm, height of 6 cm); containers were covered with perforated transparent plastic caps
- Amount of soil or substrate: 500 - 650 g dry mass of artificial soil
- No. of organisms per container (treatment): 10
- No. of replicates per treatment group: 4
- No. of replicates per control: 8
- other: One day after addition of the worms, an amount of 5 g air dried finely ground cow manure per test container was spread on the soil surface and moisten with water. Once a week, during the first four weeks, the adult earthworms were fed according to their food consumption.
SOURCE AND PROPERTIES OF SUBSTRATE (if soil)
- Composition (if artificial substrate): Sphagnum peat, air-dried, finely ground 10 %, Kaolinite, air-dried 20 %, Industrial quartz sand, air-dried 70 %
- Pretreatment of soil: The test substrate was wetted with deionised water to a water content of between 40 % and 60 % by mass of the total water-holding capacity. The pH of the substrate was adjusted to 6.0 ± 0.5 (1 mol/L KCl) by adding pulverized calcium carbonate (CaCO3).
OTHER TEST CONDITIONS
- Photoperiod: light/dark cycle 16 h : 8 h
- Light intensity: 732 - 764 lx
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): mortality and weight change after 28 days, offspring number after 56 days - Nominal and measured concentrations:
- Nominal: control, 62.5, 125, 250, 500 and 1000 mg TI/kg dry mass soil
- Reference substance (positive control):
- yes
- Remarks:
- carbendazim
- Duration:
- 56 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 500 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: weight change
- Duration:
- 28 d
- Dose descriptor:
- EC0
- Effect conc.:
- 750 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: weight change
- Details on results:
- - Mortality at end of exposure period: ≤ 5%
- Total mass of adults at beginning of test: see "Any other information on results"
- No. of offspring produced: see "Any other information on results" - Results with reference substance (positive control):
- - Results with reference substance valid?
- Relevant effect levels: EC10 = 0.9 mg/kg for weight change; EC10 = 2.0 mg/kg for reproduction (results for reproduction are in agreement with the range of 1 - 5 mg carbendazim per kg (OECD 222); weight change and mortality are in agreement with experience in test facikity)
- Other: - Validity criteria fulfilled:
- yes
Reference
Living earthworms after 28 days. Single values of the parallel test pots [Individuals].
TI = Test item; DM = Dry mass; Concentrations given as nominal values.
|
replicate |
Control |
62.5 mg TI |
125 mg TI |
250 mg TI |
500 mg TI |
1000 mg TI |
Living earthworms [Ind.] |
1 |
9 |
10 |
9 |
10 |
10 |
9 |
2 |
10 |
9 |
10 |
10 |
9 |
10 |
|
3 |
10 |
10 |
10 |
9 |
10 |
10 |
|
4 |
9 |
10 |
9 |
10 |
10 |
9 |
|
5 |
10 |
|
|
|
|
|
|
6 |
10 |
|
|
|
|
|
|
7 |
10 |
|
|
|
|
|
|
8 |
8 |
|
|
|
|
|
Biomass of the earthworm batches at test start and after 28 days.Single values of the parallel test pots [g FM].
TI = Test item; FM = Fresh mass; DM = Dry mass; Concentrations given as nominal values.
|
replicate |
Control |
62.5 mg TI |
125 mg TI |
250 mg TI |
500 mg TI |
1000 mg TI |
Test start |
1 |
3.588 |
3.062 |
3.131 |
3.187 |
3.408 |
3.752 |
2 |
3.302 |
2.977 |
3.554 |
3.295 |
2.962 |
3.313 |
|
3 |
3.064 |
3.257 |
3.378 |
3.069 |
3.002 |
3.327 |
|
4 |
2.965 |
3.408 |
3.272 |
3.080 |
3.076 |
3.426 |
|
5 |
3.441 |
|
|
|
|
|
|
6 |
3.364 |
|
|
|
|
|
|
7 |
3.409 |
|
|
|
|
|
|
8 |
3.524 |
|
|
|
|
|
|
28 d |
1 |
4.885 |
4.917 |
4.696 |
4.911 |
5.098 |
3.898 |
2 |
4.995 |
4.063 |
5.237 |
5.247 |
4.227 |
4.364 |
|
3 |
4.664 |
4.749 |
5.251 |
4.325 |
4.839 |
4.684 |
|
4 |
4.211 |
4.966 |
4.652 |
4.801 |
4.692 |
4.152 |
|
5 |
5.223 |
|
|
|
|
|
|
6 |
5.061 |
|
|
|
|
|
|
7 |
5.267 |
|
|
|
|
|
|
8 |
4.175 |
|
|
|
|
|
Weight change at test end. Weight change compared to the start value [%] and compared to the control [%].
TI = Test item; DM = Dry mass; *: significant when compared with control (Williams test, one-sided); Concentrations given as nominal values.
Test species |
Control |
62.5 mg TI |
125 mg TI |
250 mg TI |
500 mg TI |
1000 mg TI |
|||||||
compared to start value [%] |
45 |
47 |
49 |
53 |
52 |
24 |
|||||||
compared to control [%] |
|
6 |
9 |
18 |
15 |
-45 * |
Reproduction. Single values of the parallel test pots [Individuals]and mean values at the end of the study (56 d) [Individuals].
TI = Test item; DM = Dry mass; CV = Coefficient of variation; Concentrations given as nominal values.
|
Replicate |
Control |
62.5 mg TI |
125 mg TI |
250 mg TI |
500 mg TI |
1000 mg TI |
Juveniles [Ind.] |
1 |
120 |
142 |
79 |
120 |
112 |
94 |
2 |
116 |
140 |
87 |
112 |
89 |
57 |
|
3 |
127 |
143 |
143 |
48 |
134 |
126 |
|
4 |
48 |
129 |
82 |
83 |
114 |
111 |
|
5 |
97 |
|
|||||
6 |
69 |
||||||
7 |
118 |
||||||
8 |
129 |
||||||
Mean Juveniles [Ind] |
|
103 |
139 |
98 |
91 |
112 |
97 |
Description of key information
Key value for chemical safety assessment
Additional information
One experimental study was conducted investigating the effects of Boron orthophosphate (CAS 13308-51-5) on mortality, body weight and reproduction of Eisenia andrei. Until now preliminary results are available.
The test was performed according to OECD 222 with nominal concentrations of 62.5, 125, 250, 500 and 1000 mg/kg. After 4 weeks mortality of adults was ≤ 5%, resulting in a NOEC ≥ 1000 mg/kg soil dw. For weight change a NOEC (4 wks) of 500 mg/kg soil dw was calculated. After an additional 4 weeks the influence of the test substance on reproductive output of parent animals was recorded. No effects on the number of juveniles were found resulting in a NOEC (8 wks) ≥ 1000 mg/kg soil dw. Thus, the relevant endpoints mortality and reproduction did not result in any effects up to a nominal concentration of 1000 mg/kg soil dw.
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