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EC number: 204-616-2 | CAS number: 123-30-8
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 03-09-2010 to 25-09-2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP and OECD guideline followed
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.19 (Estimation of the Adsorption Coefficient (KOC) on Soil and Sewage Sludge Using High Performance Liquid Chromatography (HPLC))
- GLP compliance:
- yes
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
- Radiolabelling:
- no
- Test temperature:
- The column temperature during the study was monitored every 2 min by a data logger. Details are given in Table 1.
Table 1: Temperature range
Determination at pH 7 Determination at pH 3
Min. Temperature 19.9 °C 20.0 °C
Max. Temperature 20.3 °C 20.2 °C
Mean Value 20.0 °C 20.1 °C - Details on study design: HPLC method:
- Analyses of 4-Aminophenol were carried out by high performance liquid chromatography (HPLC) with an analytical column packed
with cyanopropyl (CN-) solid phase. The test item was dissolved in acetonitrile and then diluted in mobile phase and injected into the HPLC where the test item interacted with the stationary phase while passing through the column.
CONDITIONS OF ANALYSIS
Injection volume: 100 µL
Mobile phase 1) 50 % acetonitrile : 50 % pH 7 buffer [(HPO42-/H2PO4-) 0.01 mol/L] (v/v)
2) 50 % acetonitrile : 50 % pH 3 buffer [(HPO42-/PO43-) 0.01 mol/L] (v/v)
Column temperature 20 °C
Flow 1 mL/minute
Wavelength 1) 240 nm for analysis at pH 7
2) 220 nm and 275 nm for analysis at pH 3
Run time 15 miniutes
Calibration The method was calibrated by determination of the retention times tR of the reference items for soil and for sewage sludge.
UV using DAD (PDA) detector
HPLC-column YMC-Pack Cyano, serial no. 70823 11353, 250 x 4.0 mm,
batch 6703, YMC EUROPE GMBH
TEST ITEM 4-Aminophenol
Stock solutions 100 mg/L in acetonitrile (separate solutions for pH 3 and pH 7)
Test concentration 2 mg/L
Dilution With acetonitrile and buffer to mobile phase ratio
Replicates Triplicates (three injections)
REFERENCE ITEMS Reference items as specified in part 3. NaNO3 was used for determination of the dead time.
Stock solutions 100 mg/L each in acetonitrile
100 mg/L in mobile phase for NaNO3
Test concentrations 2 mg/L (nominal) of each reference item in separate solution
Dilution In mobile phase
Replicates Two injections (one before and one after the analysis of the
test item)
Three injections for NaNO3 at the beginning of the sample set.
A threefold determination of the dead time to was performed with a solution of 2 mg/L NaNO3 in mobile phase. Mean value was calculated.
Determination of the retention times tR of the eight reference items. Each reference item was analysed separately before and after analysis of the test item.
The retention time tR of the test item was determined with three injections.
Evaluation and plotting of the calibration graph log Koc vs. log k’ of six reference items for soil / sewage sludge.
Recording of the temperature during the whole study. - Computational methods:
- Capacity factor :The capacity factor k’ was calculated according to equation (1): k'= (tR-t0) / t0
tR Retention time [min]
t0 Dead time [min]
k’ Capacity factor
Adsorption coefficient: By means of the adsorption coefficient values (KOC) and the corresponding capacity factors of the reference items calibration graphs of log KOC, soil versus log k’ and log KOC,sewage sludge versus log k’ were plotted. - Type:
- log Koc
- Remarks:
- soil
- Value:
- 0.59
- Temp.:
- 20 °C
- Remarks on result:
- other: pH 7; undissociated form
- Type:
- Koc
- Remarks:
- soil
- Value:
- 3.85
- Temp.:
- 20 °C
- Remarks on result:
- other: ph 7;undissociated form
- Type:
- log Koc
- Remarks:
- sewage sludge
- Value:
- 0.51
- Temp.:
- 20
- Remarks on result:
- other: ph 3; undissociated form
- Type:
- Koc
- Remarks:
- sewage sludge
- Value:
- 3.22
- Temp.:
- 20 °C
- Remarks on result:
- other: pH 7; undissociated form
- Details on results (HPLC method):
- The estimated values of log KOC and KOC for pH 3 (dissociated form):
Soil Sewage Sludge
log KOC, soil KOC, soil log KOC, sewage sludge KOC, sewage sludge
-1.27 0.054 -1.17 0.068
According to the Mc Call classification scheme the dissociated form of the test item is classified as very high mobile in soil.
• The calculated values for log KOC of the injections for the test item did not differ more than ± 0.25. - Validity criteria fulfilled:
- yes
- Conclusions:
- The estimated values of log KOC and KOC for pH 7 (undissociated form):Soil- log KOC 0.59, Sewage Sludge log KOC 0.51. According to the Mc Call classification scheme the undissociated form of the test item is classified as very high mobile in soil.
The estimated values of log KOC and KOC for pH 3 (dissociated form):Soil- log KOC -127, Sewage Sludge log KOC -1.17 . According to the Mc Call classification scheme the dissociated form of the test item is classified as very high mobile in soil.
Reference
Table2: Dead Time of the HPLC-System
Serial No. |
Determination at pH 7 |
Determination at pH 3 |
t0 |
t0 |
|
1 |
1.741 |
2.278 |
2 |
1.740 |
2.278 |
3 |
1.739 |
2.279 |
Mean ± SD |
1.740±0.001 |
2.278±0.001 |
SD = Standard deviation
Table5: Retention Times, Capacity Factors (k’)
and Adsorption Coefficient (KOC) of
4-Aminophenolfor Soilat pH 7
|
tR |
k' |
log k' |
KOC, soil |
logKOC, soil |
∆ logKO, soil |
4-Aminophenol |
2.705 |
0.555 |
-0.2557 |
3.85 |
0.586 |
0.00 |
2.705 |
0.555 |
-0.2557 |
3.85 |
0.586 |
||
2.706 |
0.555 |
-0.2557 |
3.85 |
0.586 |
||
Mean |
2.705 |
0.555 |
-0.2557 |
3.85 |
0.59 |
|
SD |
0.000 |
0.000 |
0.0020 |
0.003 |
0.00 |
|
CI 95% |
|
0.15 to 1.02 |
|
tR= Retention time; SD = Standard deviation; CI = Confidence Interval
Table6: Retention Times, Capacity Factors (k’)
and Adsorption Coefficient (KOC) of
4-Aminophenolfor Sewage Sludgeat pH 7
|
tR |
k' |
log k' |
KOC, sewage sludge |
logKOC, sewage sludge |
∆ logKOC, sewage sludge |
|
4-Aminophenol |
2.705 |
0.555 |
-0.2557 |
3.22 |
0.508 |
0.00 |
|
2.705 |
0.555 |
-0.2557 |
3.22 |
0.508 |
|||
2.706 |
0.555 |
-0.2557 |
3.22 |
0.508 |
|||
Mean |
2.705 |
0.555 |
-0.2557 |
3.22 |
0.51 |
|
|
SD |
0.000 |
0.000 |
0.0020 |
0.003 |
0.00 |
||
CI 95% |
|
-0.29 to 1.30 |
|
|
tR= Retention time; SD = Standard deviation; CI = Confidence Interval
Table7: Retention Times, Capacity Factors (k’)
and Adsorption Coefficient (KOC) of
4-Aminophenolfor Soil at pH 3
|
tR |
k' |
log k' |
KOC, soil |
logKOC, soil |
∆ logKO, soil |
4-Aminophenol |
2.568 |
0.127 |
-0.8962 |
5.61×10-2 |
-1.251 |
0.02 |
2.566 |
0.126 |
-0.8996 |
5.35×10-2 |
-1,272 |
||
2.565 |
0.126 |
-0.8996 |
5.35×10-2 |
-1.272 |
||
Mean |
2.566 |
0.126 |
-0.8995 |
5.44×10-2 |
-1.27 |
|
SD |
0.000 |
0.001 |
0.0020 |
1.50×10-3 |
0.01 |
|
CI 95% |
|
-2.25 to -0.29 |
|
tR= Retention time; SD = Standard deviation; CI = Confidence Interval
Table8: Retention Times, Capacity Factors (k’)
and Adsorption Coefficient (KOC) of
4-Aminophenolfor Sewage Sludge at pH 3
|
tR |
k' |
log k' |
KOC, sewage sludge |
logKOC, sewage sludge |
∆ logKOC, sewage sludge |
|
4-Aminophenol |
2.568 |
0.127 |
-0.8962 |
6.97×10-2 |
-1.157 |
0.02 |
|
2.566 |
0.126 |
-0.8996 |
6.64×10-2 |
-1.178 |
|||
2.565 |
0.126 |
-0.8996 |
6.64×10-2 |
-1.178 |
|||
Mean |
2.566 |
0.126 |
-0.8995 |
6.75×10-2 |
-1.17 |
|
|
SD |
0.000 |
0.001 |
0.0020 |
1.91×10-3 |
0.01 |
||
CI 95% |
|
-2.93 to 0.59 |
|
|
tR= Retention time; SD = Standard deviation; CI = Confidence Interval
Description of key information
log Koc=0.59 for soil and log Koc=0.51 for sewage sludge for pH 7 (undissociated form).
Key value for chemical safety assessment
- Koc at 20 °C:
- 3.85
Other adsorption coefficients
- Type:
- log Kp (solids-water in effluent sewage sludge)
- Value in L/kg:
- 0.51
Additional information
From a key study the substance has a log Koc of 0.59 for soil and log Koc of 0.51 for sewage sludge at a pH of 7 (undissociated form). These findings indicate that it is unlikely that this substance will significantly adsorb to sediments and soils.
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