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EC number: 270-659-9 | CAS number: 68475-76-3 A complex combination of finely divided inorganic particles separated from the exit gases formed during the manufacture of Portland cement. The flue dust consists of uncalcined raw materials along with partially calcined materials. Some Portland cement clinker is usually included. The major constituents of kiln dust are calcium carbonate, clays, shales, quartz and sulfate salts. The following materials may also be present:@Dolomite@Ca(OH)2@Feldspars@CaSO4@Fly ash@KCl@Iron oxides@K2CO3@CaF2@K2SO4@CaO@Na2SO4@Glasses of SiO2, Al.s@Portland cement chemicals [659
- 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:
- 2010-03-12 to 2010-03-29
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP study, according to the OECD 207 technical guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 207 (Earthworm, Acute Toxicity Tests)
- Version / remarks:
- and ISO 11268-1 (1997)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Details on sampling:
- No analytical monitoring
- Vehicle:
- yes
- Details on preparation and application of test substrate:
- - Method of mixing into soil (if used):
The test item amount (i.e. 2400 mg) for the limit concentration was weighed out and mixed thoroughly with quartz sand (10 g per replicate). The treated quartz sand was given to the artificial soil. Demineralised water (439 g) was added to adjust the humidity of the artificial soil to a moisture of 54 % of the maximum water holding capacity.
Subsequently, the test medium was thoroughly mixed to ensure a homogenous distribution and about 555 g soil dry weight were filled to each test vessel.
- Controls: Artificial soil with the addition of quartz sand and moistened with demineralised water without test item was used as control medium.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): Quartz sand
- Concentration of vehicle in test medium (stock solution and final test solution): 10 g per replicates
- Evaporation of vehicle before use: Not necessary - Test organisms (species):
- Eisenia fetida
- Animal group:
- annelids
- Details on test organisms:
- TEST ORGANISM
- Common name: Earthworm Eisenia fetida Savigny 1826
- Source: Own breeding
- Weight at test initiation (mean and range, SD): 0.47 +/- 0.09
ACCLIMATION
- Acclimation period: 2 days
- Acclimation conditions (same as test or not): same as test
- Health during acclimation (any mortality observed): No mortality observed - Study type:
- laboratory study
- Substrate type:
- artificial soil
- Limit test:
- yes
- Total exposure duration:
- 14 d
- Post exposure observation period:
- No
- Test temperature:
- 18 - 22 °C
- pH:
- Nominal test item
concentration
[mg/kg soil dry weight]
pH-value
day 0 day 14
Control 5.93 6.51
1000 6.17 6.49 - Moisture:
- Nominal test item
concentration
[mg/kg soil dry weight] Moisture [%] of dry weight
day 0 day 14
Control 34.6 33.0
1000 33.9 32.7 - Details on test conditions:
- TEST SYSTEM
- Test container (material, size): Glass dishes, volume 1.5 L, covered with perforated plastic film
- Amount of soil or substrate: 555 g (dry weight)
- No. of organisms per container (treatment): 10 per replicate
- No. of replicates per treatment group: 4
- No. of replicates per control: 4
SOURCE AND PROPERTIES OF SUBSTRATE (if soil)
- Composition (if artificial substrate):
- Organic carbon (%): 10 % peat
- Maximum water holding capacity (in % dry weigth): 64
- Storage (condition, duration): under test conditions for 9 days
OTHER TEST CONDITIONS
- Photoperiod: 24 h
- Light intensity: 564 +/- 78 lx
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
The live weight of the earthworms was measured individually at the day of application (day 0) and at day 14.
Mortality, behaviour and morphological changes of the earthworms were recorded 7 and 14 days after application.
VEHICLE CONTROL PERFORMED: no
TEST CONCENTRATIONS
- Spacing factor for test concentrations: none
- Range finding study
Range Finding Test (14 d): Mortality and Change of Live Weight [%]
Concentration Mortality Change of Live weight
[mg test item/kg soil dry weight] [%] [%]
Control 0 2
10 0 0
100 0 4
1000 0 2 - Nominal and measured concentrations:
- Nominal: 1000 mg/kg soil DW
- Reference substance (positive control):
- yes
- Remarks:
- 2-Chloroacetamide
- Duration:
- 14 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 1 000 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Remarks:
- loss of body weight, other symptoms
- Details on results:
- - Mortality at end of exposure period: No mortality was seen at the test item concentration 1000 mg/kg soil DW after 14 days of exposure
- Changes in body weigth of live adults (% of initial weight) at end of exposure period:
During the test the biomass loss of the earthworms was below 20 % in the controls. After 14 days of exposure the earthworm biomass was not statistically significant different at the limit test item concentration of 1000 mg/kg soil dry weight compared to the control
- Behavioural abnormalities: No earthworm showed any symptoms or behavioural changes in the control as well as in the limit test item concentration of 1000 mg/kg soil dry weight
- Other biological observations: None - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Relevant effect levels:
NOEC and LC-Values after 14 d for 2-Chloroacetamide
LC-Values /
NOEC Concentration[mg/kg soil dry weight] 95% -Confidence Interval
[mg/kg soil dry weight]
LC50 47.5 42.7 - 52.8
NOEC 20.0 – - Reported statistics and error estimates:
- A t-test was carried out for the determination of statistically significant differences compared to the control. A Normality Test and an Equal Equal Variance Test were conducted prior to the
t-test. P-values for both Normality and Equal Variance Test are 0.05. The -value (acceptable probability of incorrectly concluding that there is no difference) is =0.05. - Validity criteria fulfilled:
- yes
- Conclusions:
- No mortality as well as no pathological symptoms or changes in the earthworm behaviour were observed at the limit test item concentration of 1000 mg/kg soil dry weight after 14 days of exposure to Flue Dust T. Compared to the control the biomass of earthworms exposed to Flue Dust T at the limit test item concentration of 1000 mg/kg soil dry weight was not statistically significantly reduced at test end.
Consequently, the No Observed Effect Concentration (NOEC) of Flue Dust T with respect to mortality, loss of body weight and other symptoms was determined to be at 1000 mg/kg soil dry weight. - Executive summary:
The acute effects of Flue Dust T(Batch: 12-2009) on the earthworm Eisenia fetidawere determined according to the OECD Guideline 207 and DIN ISO 11268-1 at Dr.U.Noack-Laboratorien in 31157 Sarstedt, Germany from March 12th to March 29th, 2010with the definitive exposure phase from March 12th to March 26th, 2010. The study was conducted with a limit test item concentration of 1000 mg/kg soil dry weight for 14 days. Artificial soil without test item was used as control. 40 test organisms with an initial individual weight between 0.3 - 0.6 g, divided into four replicates, were tested at the limit test item concentration and control in artificial soil containing 10 % peat.
No mortality as well as no pathological symptoms or changes in the earthworm behaviour were observed in the control and at the limit test item concentration of 1000 mg/kg soil dry weight after 7 and 14 days of exposure (Table 1). Compared to the control, the biomass of the earthworms at the limit test item concentration was not statistically significantly reduced at test end.
Consequently, the no observed effect concentration (NOEC) with respect to mortality, loss of biomass and other symptoms was determined to be at 1000 mg/kg soil dry weight (Table 1).
All validity criteria of the test guideline were fulfilled.
Summary of all Effects
Effects
Flue Dust T
[mg/kg soil dry weight]
LOEC
Mortality
> 1000
LOEC
Loss of body weight
> 1000
LOEC
Behaviour and pathological symptoms
> 1000
NOEC
Mortality, loss of body weight, other symptoms
1000
Flue Dust T did not induce effects on mortality and biomass of adult earthworms
at the nominal limit test item concentration of 1000 mg/kg soil dry weight.
Reference
Earthworm Mortality in [%] after 7 and 14 Days of Exposure
Mortality [%] |
||||||||||
Nominal test item concentration |
||||||||||
Day 7 |
Day 14 |
|||||||||
[mg/kg soil dry weight] |
1 |
2 |
3 |
4 |
MV |
1 |
2 |
3 |
4 |
MV |
Control |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1000 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Earthworm Behaviour and Pathological Symptoms after 7 and 14 Days of Exposure
Nominal test item concentration |
Effect |
Day 7 Replicate |
Day 14 Replicate |
||||||
[mg/kg soil dry weight] |
1 |
2 |
3 |
4 |
1 |
2 |
3 |
4 |
|
Control |
a) |
10/10 |
10/10 |
10/10 |
10/10 |
10/10 |
10/10 |
10/10 |
10/10 |
1000 |
a) |
10/10 |
10/10 |
10/10 |
10/10 |
10/10 |
10/10 |
10/10 |
10/10 |
Mean Biomass and Mean Loss of Body Weight
Mean live weight |
Comparison versus Control |
||||
Nominal test item concentration |
Test start MV ± SD |
Test end MV ± SD |
Test end CV |
Loss |
Significance |
[mg/kg soil dry weight] |
[g/worm] |
[g/worm] |
[%] |
[%] |
|
Control |
0.473 ± 0.09 |
0.446 ± 0.09 |
20.2 |
6 |
– |
1000 |
0.473 ± 0.09 |
0.449 ± 0.09 |
22.3 |
5 |
No |
Description of key information
The substance is not toxic to soil macroorganisms, due to a Klimisch 1 study result. The substance did not induce effects on mortality and biomass of adult earthworms at the nominal limit test item concentration of 1000 mg/kg soll dry weight.
Key value for chemical safety assessment
- Short-term EC50 or LC50 for soil macroorganisms:
- 1 000 mg/kg soil dw
Additional information
The acute effects of Flue Dust T (Batch: 12-2009) an the earthworm Eisenia fetida were determined according to the OECD Guideline 207 and DIN ISO 11268-1. The study was conducted with a limit test item concentration of 1000 mg/kg soil dry weight for 14 days. Artificial soil without test item was used as control. 40 test organisms with an initial individual weight between 0.3 - 0.6 g, divided into four replicates, were tested at the limit test item concentration and control in artificial soil containing 10 % peat. No mortality as well as no pathological symptoms or changes in the earthworm behaviour were observed in the control and at the limit test item concentration of 1000 mg/kg soil dry weight after 7 and 14 days of exposure. Compared to the control, the biomass of the earthworms at the limit test item concentration was not statistically significantly reduced at test end. Consequently, the no observed effect concentration (NOEC) with respect to mortality, loss of biomass and other symptoms was determined to be at 1000 mg/kg soll dry weight.
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