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PARTITION COEFFICIENT AND ADSORPTION/DESORPTION
Sponsor
DuPont Specialty Chemicals Jackson Laboratory Chambers Works Deepwater NJ 08023 USA
Research Laboratory Huntingdon Life Sciences Ltd. Eye Suffolk IP23 7PX ENGLAND Draft: 20 August 1999
Final: 7 September 1999
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CONTENTS
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Page
COMPLIANCE WITH GOOD LABORATORY PRACTICE STANDARDS.............................. 3 QUALITY ASSURANCE STATEMENT...................................................................................... 4 RESPONSIBLE PERSONNEL...................................................................................................... 5
6 SUMMARY.................................................................................................................................... INTRODUCTION.......................................................................................................................... 7
TEST SUBSTANCE....................................................................................................................... 8 PHYSICAL PROPERTIES
Partition coefficient.........................................................................................--........................ 9 Adsoqition/desorption................................................................................................................ 11
CpanySann-z.a.D,.sno.oo^TSCACB,
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Huntingdon
Life Sciences
COMPLIANCE WITH GOOD LABORATORY PRACTICE STANDARDS
Partition Coefficient and Adsorption/Desorption
The study described in this report was conducted in compliance with the following Good Laboratory Practice standards and I consider the data generated to be valid.
The UK Good Laboratory Practice Regulations 1997 (Statutory Instrument No 654). EC Commission Directive 1999/1 I/EC of 8 March 1999 (Official Journal No L 77/8). OECD Principles of Good Laboratory Practice (as revised in 1997), ENV/MC/CHEM(98)17.
A. L. Comb, B.Sc., Ph.D. Study Director
Huntingdon Life Sciences Ltd.
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Date
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QUALITY ASSURANCE STATEMENT
Huntingdon
Life Sciences
Partition Coefficient and Adsorption/Desorption
The following inspections and audits have been carried out in relation to this study
Study Phase
.Protocol Audit
Date of Inspection
16 August 1999
Date of Reporting 16 August 1999
Process Based Inspections Partition coefficient
4 August 1999
6 August 1999
Report Audit
6 September 1999
6 September 1999
Protocol Audit: An audit of the protocol for this study was conducted and reported to the Study
Director and Company Management as indicated above.
Process based inspections: At or about the time this study was in progress inspections of routine and
repetitive procedures employed on this type of study were carried out. These were conducted and reported to appropriate Company Management as indicated above.
Report A^idit: This report has been audited by the Quality Assurance Department. This audit was conducted and reported to the Study Director and Company Management as indicated above.
The methods, procedures and observations were found to be accurately described and the reported results to reflect the raw data.
y<-<^
H. Comb, B.Sc. Principal Auditor,
Department of Quality Assurance,
Huntingdon Life Sciences Ltd.
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Date
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RESPONSIBLE PERSONNEL
Huntingdon
Life Sciences
Partition Coefficient and Adsorption/Desorption
The following staff member has reviewed this report. T. C. Cowlyn, EurChem., C.Chem., M.R.S.C. (Scientific Manager, Product Characterisation, Eye)
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SUMMARY
A s t u dUy--w--a s--------^ study was ppeerrffcormed to determine the partition coefficient and adsorption/desorption coefficient of I
Values for the partition coefficient, Pow, were calculated by a computer program (LOGKOW Version 1.63, Syracuse Research Corporation), which estimates the logioPowvalue by reference to compound
ofHHBfi structures for which reliable partition coefficient data is available. The two components
^PlHnvere found to have logioPow values ofJ-Sand 5.8 m their non-ionised state. Values for the partition coefficient in this region indicate thauB^----lhas the potential to bioaccumulate.
Values for the adsorption/desorption coefficient, Koc, were calculated througrLforrelations with the
offJUjJywere estimated partition coefficient values. The two components
found to have
logioKoc values of2J and 3.2 in their non-ionised state. Values for the adsorption coefficient in this
region indicate thaqB----fias medium to low mobility potential in soil.
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INTRODUCTION
j^^B^^----K This study wa^designed to estimate the partition coefficient and adsorption/desorption coefficient of Information on such physico-chemical parameters is important in predicting the
environmentanate of a test substance.
The protocol was approved by the Study Director and Huntingdon Life Sciences Management on 15 August! 999 and by the Sponsor on 18 August 1999.
The experimental phase of the study was undertaken on 17 August 1999.
Location of study
: Huntingdon Life Sciences Ltd. Eye Suffolk IP23 7PX ENGLAND
Primary data from the tests performed at Huntingdon Life Sciences, and a copy of the final report, are stored in the archives of Huntingdon Life Sciences.
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Identity: Chemical name:
Intended use: Appearance: Storage conditions: Lot number: Expiry date: Purity: Date received:
TEST SUBSTANCE
Pale yellow slurry Room temperature 3 2 years from date of receipt 23 June 1998
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PARTITION COEFFICIENT
DEFINITION AND UNITS
The partition coefficient (P) is defined as the ratio of the equilibrium concentrations of a dissolved substance in a two-phase system consisting of two largely immiscible solvents, in this case, n-octanol
and water.
p(w=
C
octanol
C
waler
The partition coefficient is usually given in the form of its logarithm to base ten (logio Pow).
METHOD
Conventional methods iprthedetermmtion of partition coefficient are not^pplicable to surface-
active materials such as^HJHBQValues of logioPow forjH^B|H|^^'ere thus determined
by a calculation methoousing a LOGKOW computer programCVersion^^l, Syracuse Research
Corporation). The program estimates the logioPow value by reference to compound structures for which reliable logioPow data is available.
JHHUHponsists of two principle components, both of which are present in the free acid form
and as the corresponding quartemary ammonium salts. The structures of the components are as
follows:
CF3(CF;)nCH2CH2S03H ,
CF3(CF2)nCH2CH2SO^'N^il+
where, n = 5 or 7
The partition coefficient of a test substance is usually determined on the compound in its non-ionised
form. Consequently the calculations were performed on the free acid components only.
For n = 5, the results were as follows:
Number
2 6 13 1
LogioPow Fragment description
-CH;-
C
-F -SO^-OH
aliphatic carbon aliphatic carbon - no H, not tertiary fluorine, aliphatic attachment sulphonic
equation constant
Coefficient
Value
0.4911 0.9723 -0.0031 -3.1580
Estimated logioPow =
0.9822 5.8338 -0.0403 -3.1580 0.2290
3.8467
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For n = 7, the results were as follows:
Number
LogioPo* Fragment description
Coefficient
Value
2
-CHy
aliphatic carbon
8
C
aliphatic carbon - no H, not tertiary
17
-F
fluorine, aliphatic attachment
1
SO^-OH sulphonic
equation constant
0.4911 0.9723 -0.0031 -3.1580
0.9822 7.7784 -0.0527 -3.1580 0.2290
Estimated logioPow = 5.7789
CONCLUSION
The two non-ionised components o^Pffflffwers estimated to have logio Pow values of 3.8 and
5.8 (equivalept Ppw = 71 OO^and600000 respectively). Values for the partition coefficient in this region
indicate that|mHHI^ias the potential to bioaccumulate.
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ADSORPTION/DESORPTION
DEFINITIONS
The adsorption coefficient, Koc, related to the organic carbon content of the soil is a useful parameter describing the adsorption characteristics ofnon polar substances on a wide variety of different soils. This parameter can be estimated by correlations with the n-octanol/water partition coefficient.
METHOD
Due to the surfactant nature of the test substance, practical determination of the adsorption coefficient was not possible and thus values for logioKoc were estimated based on an empirical relationship* with
the partition coefficient, Pgw, results.
Estimated Koc values foiUHl^IBB^" ^e calculated as follows:
logioKoc = 0.47 logic Pow + 0.50
For the non-ionised components ^iBH^I^Ijthe logioPow values were calculated to be 3.8 and
vas thus estimated to have logio Koc values of 2.3 and 3.2. CONCLUSION
ofJ^fBvere The two non-ionised components
calculated to have logic Koc values of 2.3 and
3.2 (equivalent Koc = 200 and 1700 respectively). Values for the adsorption coefficient in this region
indicate that Zonyl FS-62 has medium to low mobility potential in soil.
^Technical Guidance Document in Support of Commission Directive 93/67/EEC on Risk Assessment of New Notified Substances
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