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Diss Factsheets

Administrative data

Endpoint:
partition coefficient
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Study conducted to GLP and in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do no effect the quality of the relevant results.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2007
Report date:
2007

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
EU Method A.8 (Partition Coefficient)
Deviations:
no
GLP compliance:
yes (incl. QA statement)
Type of method:
shake-flask method to: flask method
Partition coefficient type:
octanol-water

Test material

Reference
Name:
Unnamed
Type:
Constituent
Test material form:
solid: particulate/powder
Remarks:
migrated information: powder

Study design

Analytical method:
photometric method

Results and discussion

Partition coefficient
Type:
log Pow
Partition coefficient:
< -4.37
Temp.:
23 °C
pH:
7
Details on results:
The partition coefficient of the test material has been determined to be <4.31 x 10-5 at 23.0 ± 0.5 degC, log10 Pow <-4.37.

Any other information on results incl. tables

Results

Preliminary estimate

Approximate solubility in n-octanol: 9.2 x 10 -3 g/l

Approximate solubility in water:       >515 g/l
Approximate Pow:   1.79 x 10ResultsPreliminary estimateApproximate solubility in n-octa-5
Log10Pow:   -4.75

         Definitive test

The absorbances obtained for the standard, stock and sample solutions are shown in the following two tables:

Organic Phase

Solution

Absorbance*

Standard 0.226 mg/l

1.720 x 10-3

Standard 0.452 mg/l

3.790 x 10-3

Standard 0.510 mg/l

4.790 x 10-3

Standard 0.678 mg/l

7.350 x 10-3

Standard 0.904 mg/l

9.770 x 10-3

Standard 1.13 mg/l

1.403 x 10-2

Sample 1

-0.00176993

Sample 2

-0.00171993

Sample 3

-0.00157973

Sample 4

-0.00190003

Sample 5

-0.00184003

Sample 6

-0.00198003


* corrected for organic blank (water saturated n-octanol:dimethylsulfoxide (1:1))

Aqueous Phase

Solution

Absorbance

Standard 10.2 mg/l

0.390

Standard 10.3 mg/l

0.382

Sample 1

0.400

Sample 2

0.396

Sample 3

0.390

Sample 4

0.390

Sample 5

0.393

Sample 6

0.383

Stock solution A

0.382

Stock solution B

0.391



* corrected for organic blank (water saturated n-octanol:dimethylsulfoxide (1:1))

The total weights (mg) and analysed concentration (mg/l) of the respective phases are shown in the following table:

Sample Number

Volume of Water Saturated

n-octanol (ml)

Volume of Stock Solution (ml)

Total Weight (mg)*

Organic Phase

Aqueous Phase

Analysed Concentration (mg/l)

Weight (mg)†

Analysed Concentration (mg/l)

Weight (mg)†

pH

1

110

11

113

0.438

4.82 x 10-2

1.06 x 104

117

7.2

2

110

11

113

0.438

4.82 x 10-2

1.05 x 104

115

7.3

3

110

22

225

0.438

4.82 x 10-2

1.03 x 104

227

7.2

4

130

26

266

0.438

5.69 x 10-2

1.03 x 104

269

7.4

5

110

44

451

0.438

4.82 x 10-2

1.04 x 104

458

7.4

6

110

44

451

0.438

4.82 x 10-2

1.02 x 104

447

7.2

pH of n-octanol saturated water:           7.5
pH of stock solution:                             7.4
Temperature:                                        23.0 ± 0.5°C

The partition coefficient determined for each sample is shown in the following table:

Sample Number

n-Octanol/Water Volume Ratio

Partition Coefficient

Log10Pow

1

10 : 1

4.13 x 10-5

-4.38

2

4.17 x 10-5

-4.38

3

5 : 1

4.24 x 10-5

-4.37

4

4.24 x 10-5

-4.37

5

5 : 2

4.20 x 10-5

-4.38

6

4.31 x 10-5

-4.37

Overall Pow :4.31 x 10-5                     log10Pow: <-4.37


* from analysis of the stock solution

† from analysis of the respective phase

Validation

The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 0 to 20 mg/l for the aqueous samples.  This was satisfactory with a correlation coefficient of 1.00 being obtained.

Discussion

The limit value for the organic phase samples was obtained from the lowest detectable standard within the experimentally determined linearity of response range.

Substances having a log10Powof greater than 3 are regarded as having the potential to bioaccumulate in the environment.

The test material contained benzene sulphonic acid sodium salt groups and therefore pKa values outside the environmentally relevant pH range for the determination of partition coefficient.  As a result of this, testing was performed at pH 7 using the shake-flask method as recommended for salts.

Conclusion

The partition coefficient of the test material has been determined to be 4.31 x 10-5at 23.0 ± 0.5°C, log10Pow -4.37.

Applicant's summary and conclusion

Conclusions:
The partition coefficient of the test material has been determined to be <4.31 x 10-5 at 23.0 ± 0.5°C, log10 Pow <-4.37.
Executive summary:

The determination for substance C-M5 in project number 0345 -0889 was carried out using the shake-flask method, Method A8 of Commission Directive 92/69/EEC (which constitutes Annex V of Council Directive 67/548/EEC), Method 107 of the OECD Guidelines for Testing of Chemicals, 27 July1995.The partition coefficient of the test material has been determined to be <4.31 x 10-5at 23.0 +/- 0.5 ˚c, log10 Pow <-4.37.