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EC number: 249-636-2 | CAS number: 29450-45-1
- 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
Biodegradation in soil
Administrative data
- Endpoint:
- biodegradation in soil, other
- Remarks:
- Aerobic and unaerobic transformation in soil
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 07.06.2005 - 25.06.2005
- Reliability:
- 1 (reliable without restriction)
Cross-reference
- Reason / purpose for cross-reference:
- read-across source
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 005
- Report date:
- 2005
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 307 (Aerobic and Anaerobic Transformation in Soil)
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- laboratory
Test material
- Reference substance name:
- (4-chloro-2-methylphenoxy)acetic acid
- EC Number:
- 202-360-6
- EC Name:
- (4-chloro-2-methylphenoxy)acetic acid
- Cas Number:
- 94-74-6
- Molecular formula:
- C9H9ClO3
- IUPAC Name:
- (4-chloro-2-methylphenoxy)acetic acid
- Reference substance name:
- Water
- EC Number:
- 231-791-2
- EC Name:
- Water
- Cas Number:
- 7732-18-5
- Molecular formula:
- H2O
- IUPAC Name:
- water
- Reference substance name:
- 4-chloro-o-cresol
- EC Number:
- 216-381-3
- EC Name:
- 4-chloro-o-cresol
- Cas Number:
- 1570-64-5
- Molecular formula:
- C7H7ClO
- IUPAC Name:
- 4-chloro-2-methylphenol
- Test material form:
- solid
Constituent 1
impurity 1
impurity 2
- Radiolabelling:
- no
Study design
Soil propertiesopen allclose all
- Soil no.:
- #1
- Soil type:
- loamy sand
- % Clay:
- 16
- % Silt:
- 19
- % Sand:
- 65
- % Org. C:
- 6.1
- pH:
- 6.8
- CEC:
- 22.2 other: cmol/kg
- Bulk density (g/cm³):
- 1.02
- Soil no.:
- #2
- Soil type:
- silt loam
- % Clay:
- 6
- % Silt:
- 76
- % Sand:
- 18
- % Org. C:
- 1.7
- pH:
- 6.1
- CEC:
- 8 other: cmol/kg
- Bulk density (g/cm³):
- 1.18
- Soil no.:
- #3
- Soil type:
- loamy sand
- % Clay:
- 10
- % Silt:
- 21
- % Sand:
- 69
- % Org. C:
- 1.4
- pH:
- 5.7
- CEC:
- 3.3 other: cmol/kg
- Bulk density (g/cm³):
- 1.46
- Soil no.:
- #4
- Soil type:
- Silt
- % Clay:
- 21
- % Silt:
- 76
- % Sand:
- 3
- % Org. C:
- 1.4
- pH:
- 7
- CEC:
- 11.5 other: cmol/kg
- Bulk density (g/cm³):
- 1.18
Results and discussion
Half-life / dissipation time of parent compoundopen allclose all
- Key result
- Soil No.:
- #1
- DT50:
- 3.7 d
- Type:
- (pseudo-)first order (= half-life)
- Temp.:
- >= 18 - <= 22 °C
- Remarks on result:
- other:
- Remarks:
- soil #1
- Key result
- Soil No.:
- #2
- DT50:
- 6.5 d
- Type:
- (pseudo-)first order (= half-life)
- Temp.:
- >= 18 - <= 22 °C
- Remarks on result:
- other:
- Remarks:
- soil #2
- Key result
- Soil No.:
- #3
- DT50:
- 7.1 d
- Type:
- (pseudo-)first order (= half-life)
- Temp.:
- >= 18 - <= 22 °C
- Remarks on result:
- other:
- Remarks:
- soil #3
- Key result
- Soil No.:
- #4
- DT50:
- 5.4 d
- Type:
- (pseudo-)first order (= half-life)
- Temp.:
- >= 18 - <= 22 °C
- Remarks on result:
- other:
- Remarks:
- soil #4
- Transformation products:
- yes
Identity of transformation products
Reference
- Reference substance name:
- Unnamed
- IUPAC name:
- 4-chloro-2-methylphenol
- Inventory number:
- InventoryMultipleMappingImpl [inventoryEntryValue=EC 216-381-3]
- CAS number:
- 1570-64-5
- Identity:
- 4-chloro-o-cresol
- Identity:
- Phenol, 4-chloro-2-methyl-
- Molecular formula:
- C7H7ClO
- Molecular weight:
- 142.583
- SMILES notation:
- Cc1cc(Cl)ccc1O
- InChl:
- InChI=1/C7H7ClO/c1-5-4-6(8)2-3-7(5)9/h2-4,9H,1H3
Any other information on results incl. tables
The concentrations of MCPA in the soil samples obtained during the experiment are presented in Tables
Table 1. MCPA TECHNICAL - aerobic transformation in soil concentration of MCPA in soil I during the experiment
Day |
Concentration |
concentration |
SD |
RSD [%] |
Percent of the |
Decrease in relation to the initial concentration [%] |
0 |
13.55 |
|
|
|
|
|
24.05.2005 |
|
14.03 |
0.55 |
4.9 |
100.0 |
0.0 |
14.53 |
||||||
1 |
10.77 |
|
|
|
|
|
25.05.2005 |
|
11.11 |
0.38 |
4.30 |
79.1 |
20.9 |
11.45 |
||||||
3 |
7.16 |
|
|
|
|
|
27.05.2005 |
|
7.07 |
0.10 |
1.74 |
50.3 |
49.7 |
6.98 |
||||||
6 |
2.38 |
|
|
|
|
|
30.06.2005 |
|
2.39 |
0.02 |
0.86 |
17.0 |
83.0 |
2.41 |
||||||
9 |
<0.1 |
|
|
|
|
|
2.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
||||||
12 |
<0.1 |
|
|
|
|
|
5.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
||||||
16 |
<0.1 |
|
|
|
|
|
9.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
||||||
20 |
<0.1 |
|
|
|
|
|
13.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
||||||
32 |
<0.1 |
|
|
|
|
|
25.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
Table 2. MCPA TECHNICAL - aerobic transformation in soil concentration of MCPA in soil II during the experiment
Day |
Concentration |
concentration |
SD |
RSD [%] |
Percent of the |
Decrease in relation to the initial concentration [%] |
0 |
12.43 |
|
|
|
|
|
24.05.2005 |
|
12.12 |
0.36 |
3.70 |
100.0 |
0.0 |
11.80 |
||||||
1 |
10.58 |
|
|
|
|
|
25.05.2005 |
|
10.73 |
0.17 |
1.96 |
88.5 |
11.5 |
10.88 |
||||||
3 |
8.12 |
|
|
|
|
|
27.05.2005 |
|
8.43 |
0.34 |
5.11 |
69.5 |
30.5 |
8.73 |
||||||
6 |
4.41 |
|
|
|
|
|
30.06.2005 |
|
4.40 |
0.01 |
0.28 |
36.3 |
63.7 |
4.40 |
||||||
9 |
2.13 |
|
|
|
|
|
2.06.2005 |
|
2.21 |
0.09 |
5.24 |
18.2 |
81.8 |
2.29 |
||||||
12 |
1.02 |
|
|
|
|
|
5.06.2005 |
|
1.11 |
0.10 |
11.43 |
9.1 |
90.9 |
1.20 |
||||||
16 |
0.12 |
|
|
|
|
|
9.06.2005 |
|
0.12 |
0.01 |
8.92 |
0.9 |
99.1 |
0.11 |
||||||
20 |
<0.1 |
|
|
|
|
|
13.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
||||||
32 |
<0.1 |
|
|
|
|
|
25.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
Table 3. MCPA TECHNICAL - aerobic transformation in soil concentration of MCPA in soil III during the experiment
Day |
Concentration |
concentration |
SD |
RSD [%] |
Percent of the |
Decrease in relation to the initial concentration [%] |
0 |
12.81 |
|
|
|
|
|
24.05.2005 |
|
13.10 |
0.32 |
3.09 |
100.0 |
0.0 |
13.39 |
||||||
1 |
9.98 |
|
|
|
|
|
25.05.2005 |
|
10.03 |
0.06 |
0.70 |
76.5 |
23.5 |
10.08 |
||||||
3 |
7.22 |
|
|
|
|
|
27.05.2005 |
|
7.09 |
0.14 |
2.41 |
54.1 |
419 |
6.97 |
||||||
6 |
4.94 |
|
|
|
|
|
30.06.2005 |
|
4.95 |
0.01 |
0.36 |
37.7 |
62.3 |
4.96 |
||||||
9 |
4.25 |
|
|
|
|
|
2.06.2005 |
|
4.19 |
0.07 |
1.99 |
31.9 |
68.1 |
4.13 |
||||||
12 |
3.42 |
|
|
|
|
|
5.06.2005 |
|
3.32 |
0.11 |
4.19 |
25.3 |
74.7 |
3.22 |
||||||
16 |
2.43 |
|
|
|
|
|
9.06.2005 |
|
2.42 |
0.01 |
0.42 |
18.4 |
81.6 |
2.41 |
||||||
20 |
1.67 |
|
|
|
|
|
13.06.2005 |
|
1.50 |
0.20 |
16.32 |
11.4 |
88.6 |
1.33 |
||||||
32 |
0.15 |
|
|
|
|
|
25.06.2005 |
|
0.15 |
0.00 |
0.89 |
1.1 |
98.9 |
0.14 |
Table 4. MCPA TECHNICAL - aerobic transformation in soil concentration of MCPA in soil IV during the experiment
Day |
Concentration |
concentration |
SD |
RSD [%] |
Percent of the |
Decrease in relation to the initial concentration [%] |
0 |
15.51 |
|
|
|
|
|
24.05.2005 |
|
15.23 |
0.32 |
2.62 |
100.0 |
0.0 |
14.95 |
||||||
1 |
12.92 |
|
|
|
|
|
25.05.2005 |
|
12.76 |
0.19 |
1.84 |
83.7 |
16.3 |
12.59 |
||||||
3 |
9.97 |
|
|
|
|
|
27.05.2005 |
|
9.98 |
0.01 |
0.15 |
65.5 |
34.5 |
9.99 |
||||||
6 |
3.85 |
|
|
|
|
|
30.06.2005 |
|
4.02 |
0.19 |
6.05 |
26.3 |
73.7 |
4.19 |
||||||
9 |
1.76 |
|
|
|
|
|
2.06.2005 |
|
1.93 |
0.20 |
1.28 |
12.6 |
87.4 |
2.11 |
||||||
12 |
0.24 |
|
|
|
|
|
5.06.2005 |
|
0.18 |
0.07 |
4.77 |
1.1 |
98.9 |
0.12 |
||||||
16 |
<0.1 |
|
|
|
|
|
9.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
||||||
20 |
<0.1 |
|
|
|
|
|
13.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
||||||
32 |
<0.1 |
|
|
|
|
|
25.06.2005 |
|
<0.1 |
- |
- |
- |
- |
<0.1 |
The concentrations of 4-chloro-2-metylophenol in the soil samples obtained during the experiment are presented in Tables
Table 5. aerobic transformation in soil concentration of 4-chloro-2-metylophenol in soil I during the experiment
Day |
Concentration in mg/kg d.w. |
Mean concentration |
SD |
RSD |
0 |
<0.05 |
|
|
|
24.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
1 |
<0.05 |
|
|
|
25.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
3 |
<0.05 |
|
|
|
27.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
6 |
0.12 |
|
|
|
30.06.2005 |
|
0.11 |
0.00 |
0.00 |
0.11 |
||||
9 |
<0.05 |
|
|
|
2.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
12 |
0.25 |
|
|
|
5.06.2005 |
|
0.28 |
0.04 |
0.01 |
0.31 |
||||
16 |
<0.05 |
|
|
|
9.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
20 |
<0.05 |
|
- |
- |
13.06.2005 |
|
<0.05 |
|
|
<0.05 |
||||
32 |
<0.05 |
|
|
|
25.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
Table 6. aerobic transformation in soil concentration of 4-chloro-2-metylophenol in soil II during the experiment
Day |
Concentration in mg/kg d.w. |
Mean concentration |
SD |
RSD |
0 |
<0.05 |
|
|
|
24.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
1 |
<0.05 |
|
|
|
25.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
3 |
<0.05 |
|
|
|
27.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
6 |
0.09 |
|
|
|
30.06.2005 |
|
0.09 |
0.00 |
0.00 |
0,09 |
||||
9 |
<0.05 |
|
|
|
2.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
12 |
<0.05 |
|
|
|
5.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
16 |
<0.05 |
|
|
|
9.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
20 |
<0.05 |
|
|
|
13.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
32 |
<0.05 |
|
|
|
25.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
Table 7. aerobic transformation in soil concentration of 4-chloro-2-metylophenol in soil III during the experiment
Day |
Concentration in mg/kg d.w. |
Mean concentration |
SD |
RSD |
0 |
<0.05 |
|
|
|
24.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
1 |
<0.05 |
|
|
|
25.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
3 |
<0.05 |
|
|
|
27.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
6 |
<0.05 |
|
|
|
30.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
9 |
<0.05 |
|
|
|
2.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
12 |
<0.05 |
|
|
|
5.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
16 |
0.13 |
|
|
|
9.06.2005 |
|
0.15 |
0.02 |
15.42 |
0.16 |
||||
20 |
0.19 |
|
|
|
13.06.2005 |
|
0.18 |
0.01 |
5.27 |
0.17 |
||||
32 |
0.16 |
|
|
|
25.06.2005 |
|
0.17 |
0.02 |
13.71 |
0.09 |
Table 8. aerobic transformation in soil concentration of 4-chloro-2-metylophenol in soil IV during the experiment
Day |
Concentration in mg/kg d.w. |
Mean concentration |
SD |
RSD |
0 |
<0.05 |
|
|
|
24.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
1 |
<0.05 |
|
|
|
25.05.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
3 |
0.09 |
|
|
|
27.05.2005 |
|
0.09 |
0.00 |
0.00 |
0.09 |
||||
6 |
0.09 |
|
|
|
30.06.2005 |
|
0.08 |
0.01 |
12.5 |
0.08 |
||||
9 |
0.09 |
|
|
|
2.06.2005 |
|
0.09 |
0.00 |
0.00 |
0.09 |
||||
12 |
<0.05 |
|
|
|
5.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
16 |
<0.05 |
|
|
|
9.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
20 |
<0.05 |
|
|
|
13.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
||||
32 |
<0.05 |
|
|
|
25.06.2005 |
|
<0.05 |
- |
- |
<0.05 |
Taking into account the obtained results it was assessed that MCPA TECHNICALwas degraded, and the DT50is 3.7, 6.5, 7.1 and 5.4 days for loamy sand (soil I), silt loam (soil II), loamy sand (soil III) and silt (soil IV), respectively.
Applicant's summary and conclusion
- Conclusions:
- Taking into account the obtained results it was assessed that degradation of MCPA TECHNICAL in aerobic conditions depended on the parameters of soils, used in the experiment. However, DT50 values for MCPA in tested soils did not exceeded 8 days.
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