02008R0440 — EN — 08.01.2026 — 011.001


This text is meant purely as a documentation tool and has no legal effect. The Union's institutions do not assume any liability for its contents. The authentic versions of the relevant acts, including their preambles, are those published in the Official Journal of the European Union and available in EUR-Lex. Those official texts are directly accessible through the links embedded in this document

►B

►C1   COMMISSION REGULATION (EC) No 440/2008

of 30 May 2008

laying down test methods pursuant to Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH)

(Text with EEA relevance)  ◄

(OJ L 142 31.5.2008, p. 1)

Amended by:

 

 

Official Journal

  No

page

date

►M1

COMMISSION REGULATION (EC) No 761/2009 of 23 July 2009

  L 220

1

24.8.2009

 M2

COMMISSION REGULATION (EU) No 1152/2010 of 8 December 2010

  L 324

13

9.12.2010

►M3

COMMISSION REGULATION (EU) No 640/2012 of 6 July 2012

  L 193

1

20.7.2012

►M4

COMMISSION REGULATION (EU) No 260/2014 of 24 January 2014

  L 81

1

19.3.2014

►M5

COMMISSION REGULATION (EU) No 900/2014 of 15 July 2014

  L 247

1

21.8.2014

►M6

COMMISSION REGULATION (EU) 2016/266 of 7 December 2015

  L 54

1

1.3.2016

►M7

COMMISSION REGULATION (EU) 2017/735 of 14 February 2017

  L 112

1

28.4.2017

►M8

COMMISSION REGULATION (EU) 2019/1390 of 31 July 2019

  L 247

1

26.9.2019

►M9

COMMISSION REGULATION (EU) 2023/464 of 3 March 2023

  L 68

37

6.3.2023

►M10

COMMISSION REGULATION (EU) 2024/2492 of 23 September 2024

  L 2492

1

24.9.2024

►M11

COMMISSION REGULATION (EU) 2025/2573 of 18 December 2025

  L 2573

1

19.12.2025


Corrected by:

►C1

Corrigendum, OJ L 143, 3.6.2008, p.  55 (440/2008)




▼B

▼C1

COMMISSION REGULATION (EC) No 440/2008

of 30 May 2008

laying down test methods pursuant to Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH)

(Text with EEA relevance)

▼B



Article 1

The test methods to be applied for the purposes of Regulation 1907/2006/EC are set out in the Annex to this Regulation.

Article 2

The Commission shall review, where appropriate, the test methods contained in this Regulation with a view to replacing, reducing or refining testing on vertebrate animals.

Article 3

All references to Annex V to Directive 67/548/EEC shall be construed as references to this Regulation.

Article 4

This Regulation shall enter into force on the day following its publication in the Official Journal of the European Union.

It shall apply from 1 June 2008.




ANNEX

▼M6

Note:

Before using any of the following test methods to test a multi-constituent substance (MCS), a substance of unknown or variable composition, complex reaction product or biological material (UVCB), or a mixture and where its applicability for the testing of MCS, UVCB, or mixtures is not indicated in the respective test method, it should be considered whether the method is adequate for the intended regulatory purpose.

If the test method is used for the testing of a MCS, UVCB or mixture, sufficient information on its composition should be made available, as far as possible, e.g. by the chemical identity of its constituents, their quantitative occurrence, and relevant properties of the constituents.

▼M9




PART 0

INTERNATIONAL TEST METHODS RECOGNISED AS BEING APPROPRIATE FOR GENERATING INFORMATION ON INTRINSIC PROPERTIES OF SUBSTANCES FOR THE PURPOSES OF REGULATION (EC) No 1907/2006

▼M10

TABLE 1: TEST METHODS FOR PHYSICOCHEMICAL PROPERTIES OF THE SUBSTANCE



Basic physicochemical properties

Endpoint

Test method

Corresponding chapter, containing the full description of the test method, in Part A of this Annex (numbers in brackets indicate that the full description of the test method has been deleted from Part A; empty cell: no corresponding test method in Part A of this Annex)

Melting point/freezing point

OECD Test Guideline 102: Melting Point/Melting Range (1995)

A.1.

ASTM D4359-90: Standard Test Method for Determining whether a Material Is a Liquid or a Solid

 

Test for determining fluidity according to section 2.3.4 of Annex A of the Agreement concerning the International Carriage of Dangerous Goods by Road (ADR)

 

Boiling point

OECD Test Guideline 103: Boiling point (1995)

A.2.

Test methods according to Table 2.6.4 of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Flammability

EN 15188:2020 – Determination of the spontaneous ignition behaviour of dust accumulations

 

Lower and upper explosion limit

Test methods according to section 2.2.4.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008 (ISO 10156 and EN 1839)

 

Flash point

Test methods according to table 2.6.3 of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Auto-ignition temperature (liquids, gases)

ISO/IEC 80079-20-1:2017 – Explosive atmospheres – Part 20-1: Material characteristics for gas and vapour classification – Test methods and data

 

Decomposition temperature

Calorimetric test methods according to section 20.3.3.3 of Part II of the UN Manual of Tests and Criteria

 

Test Series H, part II, section 28, of the UN Manual of Tests and Criteria for the self-accelerating decomposition temperature (SADT) (with reference to a specific package)

 

pH

OECD Test Guideline 122: Determination of pH, Acidity and Alkalinity (2013)

 

Kinematic Viscosity

OECD Test Guideline 114: Viscosity of Liquids (2012)

 

Water solubility

OECD Test Guideline 105: Water Solubility (1995)

A.6.

Partition coefficient

n-octanol/water

OECD Test Guideline 107: Partition Coefficient (n-octanol/water): Shake-Flask Method (1995)

(A.8.)

OECD Test Guideline 123: Partition Coefficient (1-Octanol/Water): Slow-Stirring Method (2022)

A.23.

OECD Test Guideline 117: Partition Coefficient (n-octanol/water): HPLC Method (2022)

A.24.

Vapour pressure

OECD Test Guideline 104: Vapour Pressure (2006)

(A.4)

Density/Relative density

OECD Test Guideline 109: Density of Liquids and Solids (2012)

(A.3.)

DIN 66137-2 – Determination of solid state density – Part 2: Gas pycnometry

ISO 12154 – Determination of density by volumetric displacement – Skeleton density by gas pycnometry

Particle characteristics

EU test method A.22. Length Weighted Geometric Mean Diameter of Fibres

A.22.

ISO 21501 – Determination of Particle Size Distribution – Single Particle Light Interaction Methods

 

OECD Test Guideline 124: Determination of the Volume Specific Surface Area of Manufactured Nanomaterials (2022)

 

OECD Test Guideline 125: Particle Size and Particle Size Distribution of Nanomaterials (2023)

 

ISO/TR 14187:2020 – Surface chemical analysis –Characterization of nanostructured materials

▼M11

Dustiness (for nanoforms of a substance)

EN 17199-1:2019 – Workplace exposure – Measurement of dustiness of bulk materials that contain or release respirable NOAA and other respirable particles – Part 1: Requirements and choice of test methods

 

EN 17199-2:2019 Workplace exposure – Measurement of dustiness of bulk materials that contain or release respirable NOAA and other respirable particles – Part 2: Rotating drum method

 

EN 17199-3:2019 Workplace exposure – Measurement of dustiness of bulk materials that contain or release respirable NOAA and other respirable particles – Part 3: Continuous drop method

 

EN 17199-4:2019 Workplace exposure – Measurement of dustiness of bulk materials that contain or release respirable NOAA and other respirable particles – Part 4: Small rotating drum method

 

EN 17199-5:2019 Workplace exposure – Measurement of dustiness of bulk materials that contain or release respirable NOAA and other respirable particles – Part 5: Vortex shaker method

 

EN 15051-1:2013 Workplace exposure – Measurement of the dustiness of bulk materials – Part 1: Requirements and choice of test methods

 

EN 15051-2:2016 Workplace exposure – Measurement of the dustiness of bulk materials – Part 2: Rotating drum method

 

EN 15051-3:2013 Workplace exposure – Measurement of the dustiness of bulk materials – Part 3: Continuous drop method

 

▼M10

Surface tension

OECD Test Guideline 115: Surface Tension of Aqueous Solutions (1995)

A.5.

Dissociation constant

OECD Test Guideline 112: Dissociation Constants in Water. (1981)

A.25.

Hydrophobicity

OECD Test Guideline 126: Determination of the Hydrophobicity Index of Manufactured Nanomaterials Through an Affinity Measurement (2023)

 

Physicochemical hazard properties

Explosives

Test methods for explosives according to section 2.1.2.1. and 2.1.2.3. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

EU Test method A.14 Explosive Properties

A.14

Flammable gases

Test method for the fundamental burning velocity according to section 2.2.4.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Test method for pyrophoric gases according to section 2.2.4.2. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Test method for the chemical instability according to section 2.2.4.4. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Oxidising gases

Test method for oxidising gases according to section 2.4.4. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Flammable liquids

Test method for the sustained combustibility according to section 2.6.4.5. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Test methods for determining the flash point of flammable liquids according to section 2.6.4.4. of Annex I, Part 2 of Regulation (EC) No 1272/2008

Flammable solids

Test method for flammable solids according to section 2.7.2.3. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Self-reactive substances

Test method for self-reactive substances according to section 2.8.4.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Pyrophoric liquids

Test method for pyrophoric liquids according to section 2.9.2.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Pyrophoric solids

Test method for pyrophoric solids according to section 2.10.2.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008,

 

Self-heating substances

Test method for self-heating substances according to section 2.11.2.2 of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Substances which in contact with water emit flammable gases

Test method for substances which in contact with water emit flammable gases according to section 2.12.2.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Oxidising liquids

Test method for oxidising liquids according to section 2.13.2.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Oxidising solids

Test method for oxidising solids according to section 2.14.2.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Organic peroxides

Test methods according to section 2.15.4.1 of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Corrosive to metals

Test method for substances corrosive to metals according to section 2.16.2.1. of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Desensitised explosives

Test methods according to section 2.17.2.1 (b) and (c) and according to section 2.17.2.2 of Annex I, Part 2 of Regulation (EC) No 1272/2008

 

Properties of polymers

OECD Test Guideline 118: Determination of the Number-Average Molecular Weight and the Molecular Weight Distribution of Polymers using Gel Permeation Chromatography (1996)

A.18.

OECD Test Guideline 119: Determination of the Low Molecular Weight Content of a Polymer Using Gel Permeation Chromatography (1996)

A.19.

OECD Test Guideline 120: Solution/Extraction Behaviour of Polymers in Water (2000)

(A.20.)

▼M9

TABLE 2: TEST METHODS FOR TOXICOLOGICAL PROPERTIES



Endpoint

Test method

Corresponding chapter, containing the full description of the test method, in Part B of this Annex (numbers in brackets indicate that a chapter, containing the full description of the test method, has been deleted from Part B; empty cell: no corresponding EU test method in Part B of this Annex)

Skin corrosion/irritation

In vitro:

OECD Test Guideline 430: In vitro Skin Corrosion: Transcutaneous Electrical Resistance Test Method (TER) (2015)

B.40.

OECD Test Guideline 431: In vitro Skin Corrosion: Reconstructed Human Epidermis (RhE) Test Method (2019)

(B.40bis.)

OECD Test Guideline 435: In vitro Membrane Barrier Test Method for Skin Corrosion (2015)

B.65.

OECD Test Guideline 439: In vitro Skin Irritation: Reconstructed Human Epidermis Test Method (2021)

(B.46.)

In vivo:

OECD Test Guideline 404: Acute Dermal Irritation/Corrosion (2015)

B.4.

▼M11

Serious eye damage/eye irritation

In vitro:

OECD Test Guideline 437: Bovine Corneal Opacity and Permeability Test Method for Identifying i) Chemicals Inducing Serious Eye Damage and ii) Chemicals Not Requiring Classification for Eye Irritation or Serious Eye Damage (2023)

(B.47.)

OECD Test Guideline 438: Isolated Chicken Eye Test Method for Identifying i) Chemicals Inducing Serious Eye Damage and ii) Chemicals Not Requiring Classification for Eye Irritation or Serious Eye Damage (2023)

(B.48.)

OECD Test Guideline 460: Fluorescein Leakage Test Method for Identifying Ocular Corrosives and Severe Irritants (2023)

(B.61.)

OECD Test Guideline 491: Short Time Exposure In Vitro Test Method for Identifying i) Chemicals Inducing Serious Eye Damage and ii) Chemicals Not Requiring Classification for Eye Irritation or Serious Eye Damage (2023)

(B.68.)

OECD Test Guideline 492: Reconstructed human Cornea-like Epithelium (RhCE) test method for identifying chemicals not requiring classification and labelling for eye irritation or serious eye damage (2024)

(B.69.)

OECD Test Guideline 492B: Reconstructed Human Cornea-like Epithelium (RHCE) Test Method for Eye Hazard Identification (2024)

 

OECD Test Guideline 494: Vitrigel-Eye Irritancy Test Method for Identifying Chemicals Not Requiring Classification and Labelling for Eye Irritation or Serious Eye Damage (2021)

 

OECD Test Guideline 496: In vitro Macromolecular Test Method for Identifying Chemicals Inducing Serious Eye Damage and Chemicals Not Requiring Classification for Eye Irritation or Serious Eye Damage (2024)

 

OECD Test Guideline 467: Defined Approaches for Serious Eye Damage and Eye Irritation (2024)

 

▼M10

In vivo:

OECD Test Guideline 405: Acute Eye Irritation/Corrosion (2023)

(B.5.)

▼M11

Skin sensitisation

In vitro:

OECD Test Guideline 442C: In Chemico Skin Sensitisation: Assays addressing the Adverse Outcome Pathway key event on covalent binding to proteins (2024)

(B.59.)

OECD Test Guideline 442D: In Vitro Skin Sensitisation: Assays addressing the Adverse Outcome Pathway Key Event on Keratinocyte activation (2024)

(B.60.)

OECD Test Guideline 442E: In Vitro Skin Sensitisation: In Vitro Skin Sensitisation assays addressing the Key Event on activation of dendritic cells on the Adverse Outcome Pathway for Skin Sensitisation (2024)

(B.71.)

OECD Test Guideline 497: Defined Approaches on Skin Sensitisation (2023)

 

▼M9

In vivo:

OECD Test Guideline 429: Skin Sensitisation – Local Lymph Node Assay (2010)

B.42.

OECD Test Guideline 442A: Skin Sensitisation – Local Lymph Node Assay: DA (2010)

B.50.

▼M11

OECD Test Guideline 442B: Skin Sensitisation – Local Lymph Node Assay: BrdU-ELISA or – FCM (2024)

(B.51.)

▼M9

OECD Test Guideline 406: Skin Sensitisation Guinea Pig

Maximisation Test and Buehler Test (2022)

(B.6.)

Mutagenicity

In vitro:

OECD Test Guideline 471: Bacterial Reverse Mutation Test (2020)

(B.13./14.)

OECD Test Guideline 476: In Vitro Mammalian Cell Gene Mutation Test Using the Hprt and xprt Genes (2016)

(B.17.)

OECD Test Guideline 490: In Vitro Mammalian Cell Gene Mutation Tests Using the Thymidine Kinase Gene (2016)

B.67.

OECD Test Guideline 473: In vitro Mammalian Chromosome Aberration Test (2016)

B.10.

►M10  OECD Test Guideline 487. In vitro Mammalian Cell Micronucleus Test (2023) ◄

►M10  (B.49.) ◄

In vivo:

OECD Test Guideline 475: Mammalian Bone Marrow Chromosome Aberration Test (2016)

B.11.

OECD Test Guideline 474: Mammalian Erythrocyte Micronucleus Test (2016)

B.12.

OECD Test Guideline 483: Mammalian Spermatogonial Chromosome Aberration Test (2016)

B.23.

OECD Test Guideline 488: Transgenic Rodent Somatic and Germ Cell Gene Mutation Assays (2022)

(B.58.)

OECD Test Guideline 489: In Vivo Mammalian Alkaline Comet Assay (2016)

B.62.

OECD Test Guideline 470: Mammalian Erythrocyte Pig-a Gene mutation Assay (2022)

 

Acute toxicity

Oral:

OECD Test Guideline 420: Acute Oral Toxicity: Fixed Dose Procedure (2002)

B.1 bis.

OECD Test Guideline 423: Acute Oral Toxicity: Acute Toxic Class Method (2002)

B.1 tris.

OECD Test Guideline 425: Acute Oral Toxicity: Up-and-Down Procedure (2022)

 

Dermal:

OECD Test Guideline 402: Acute Dermal Toxicity – Fixed Dose Procedure (2017)

(B.3.)

Inhalation:

▼M11

OECD Test Guideline 403: Acute Inhalation Toxicity (2024)

(B.2.)

▼M9

OECD Test Guideline 436: Acute Inhalation Toxicity – Acute Toxic Class Method (2009)

B.52.

OECD Test Guideline 433: Acute Inhalation Toxicity: Fixed Concentration Procedure (2018)

 

Repeated dose toxicity

OECD Test Guideline 407: Repeated Dose 28-Day Oral Toxicity Study in Rodents (2008)

B.7.

OECD Test Guideline 412: Subacute Inhalation Toxicity: 28-Day Study (2018)

(B.8.)

OECD Test Guideline 410: Repeated Dose Dermal Toxicity: 21/28-Day Study (1981)

B.9.

OECD Test Guideline 422: Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test (2016)

B.64.

OECD Test Guideline 408: Repeated Dose 90-Day Oral Toxicity Study in Rodents (2018)

(B.26.)

OECD Test Guideline 409: Repeated Dose 90-Day Oral Toxicity Study in Non-Rodents (1998)

B.27.

OECD Test Guideline 413: Subchronic Inhalation Toxicity: 90-Day Study (2018)

(B.29.)

OECD Test Guideline 411: Subchronic Dermal Toxicity: 90-Day Study (1981)

B.28.

OECD Test Guideline 452: Chronic Toxicity Studies (2018)

(B.30.)

OECD Test Guideline 453: Combined Chronic Toxicity/Carcinogenicity Studies (2018)

(B.33.)

Reproductive/developmental toxicity

OECD Test Guideline 443: Extended One-Generation Reproduction Toxicity Study (2018)

(B.56.)

OECD Test Guideline 421: Reproduction/Developmental Toxicity Screening Test (2016)

B.63.

OECD Test Guideline 422: Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test (2016)

B.64.

OECD Test Guideline 414: Prenatal Developmental Toxicity Study (2018)

(B.31.)

Toxicokinetics

OECD Test Guideline 417: Toxicokinetics (2010)

B.36.

OECD Test Guideline 428: Skin Absorption: In Vitro Method (2004)

B.45.

OECD Test Guideline 427: Skin Absorption: In Vivo Method (2004)

B.44.

Carcinogenicity

OECD Test Guideline 451: Carcinogenicity Studies (2018)

(B.32.)

OECD Test Guideline 453: Combined Chronic Toxicity/Carcinogenicity Studies (2018)

(B.33.)

EU test method B.21. In Vitro Mammalian Cell Transformation Test

B.21.

(Developmental) Neurotoxicity

OECD Test Guideline 424: Neurotoxicity Study in Rodents (1997)

B.43.

OECD Test Guideline 426: Developmental Neurotoxicity Study (2007)

B.53.

OECD Test Guideline 418: Delayed Neurotoxicity of Organophosphorus Substances Following Acute Exposure (1995)

B.37.

OECD Test Guideline 419: Delayed Neurotoxicity of Organophosphorus Substances: 28-day Repeated Dose Study (1995)

B.38.

Endocrine disrupting properties

In vitro

OECD Test Guideline 455: Performance-Based Test Guideline for Stably Transfected Transactivation In Vitro Assays to Detect Estrogen Receptor Agonists and Antagonistsals (2021)

(B.66.)

►M10  OECD Test Guideline 456: H295R Steroidogenesis Assay (2023) ◄

►M10  (B.57.) ◄

►M10  OECD Test Guideline 458: Stably Transfected Human Androgen Receptor Transcriptional Activation Assay for Detection of Androgenic Agonist and Antagonist Activity of Chemicals (2023) ◄

 

▼M11

OECD Test Guideline 493: Performance-Based Test Guideline for Human Recombinant Estrogen Receptor (hrER) In Vitro Assays to Detect Chemicals with ER Binding Affinity (2024)

(B.70.)

▼M9

In vivo

OECD Test Guideline 440: Uterotrophic Bioassay in Rodents A short-term screening test for oestrogenic properties (2007)

B.54.

OECD Test Guideline 441: Hershberger Bioassay in Rats, A Short-term Screening Assay for (Anti)Androgenic Properties (2009)

B.55.

Phototoxicity

OECD Test Guideline 432: In Vitro 3T3 NRU Phototoxicity Test (2019)

(B.41.)

OECD Test Guideline 495: Ros (Reactive Oxygen Species) Assay for Photoreactivity (2019)

 

►M10  OECD Test Guideline 498: In Vitro Phototoxicity Reconstructed Human Epidermis Phototoxicity test method (2023) ◄

 

▼M10

Immunotoxicity

OECD Test Guideline 444A: In vitro immunotoxicity IL-2 Luc assay (2023)

 

▼M9

TABLE 3: TEST METHODS FOR ECOTOXICOLOGICAL PROPERTIES



Endpoint

Test method

Corresponding chapter in Part C, containing the full description of the test method, of this Annex (numbers in brackets indicate that a chapter, containing the full description of the test method, has been deleted from Part C; empty cell: no corresponding EU test method in Part C of this Annex)

Aquatic toxicity

OECD Test Guideline 201: Freshwater Alga and Cyanobacteria, Growth Inhibition Test (2011)

C.3.

OECD Test Guideline 209: Activated Sludge, Respiration Inhibition Test (Carbon and Ammonium Oxidation) (2010)

C.11.

OECD Test Guideline 224: Determination of the Inhibition of the Activity of Anaerobic Bacteria (2007)

C.34.

OECD Test Guideline 244: Protozoan Activated Sludge Inhibition Test (2017)

 

OECD Test Guideline 221: Lemna sp. Growth Inhibition Test (2006)

C.26.

OECD Test Guideline 202: Daphnia sp. Acute Immobilisation Test (2004)

C.2.

OECD Test Guideline 211: Daphnia magna Reproduction Test (2012)

C.20.

OECD Test Guideline 203: Fish, Acute Toxicity Test (2019)

(C.1.)

OECD Test Guideline 210: Fish, Early-life Stage Toxicity Test (2013)

C.47.

OECD Test Guideline 215: Fish, Juvenile Growth Test (2000)

C.14.

OECD Test Guideline 236: Fish Embryo Acute Toxicity (FET) Test (2013)

C.49.

OECD Test Guideline 249: Fish Cell Line Acute Toxicity – the RTgill-W1 Cell Line Assay (2021)

 

OECD Test Guideline 242: Potamopyrgus antipodarum Reproduction Test (2016)

 

OECD Test Guideline 243: Lymnaea stagnalis Reproduction Test (2016)

 

Degradation

OECD Test Guideline 111: Hydrolysis as a Function of pH (2004)

C.7.

OECD Test Guideline 301: Ready Biodegradability (1992)

C.4.

OECD Test Guideline 302A: Inherent Biodegradability: Modified SCAS Test (1981)

C.12.

OECD Test Guideline 302B: Inherent Biodegradability: Zahn-Wellens/EMPA Test (1992)

(C.9).

OECD Test Guideline 302C: Inherent Biodegradability: Modified MITI Test (II) (2009)

 

OECD Test Guideline 303: Simulation Test – Aerobic Sewage Treatment — A: Activated Sludge Units; B: Biofilms (2001)

C.10.

OECD Test Guideline 304A: Inherent Biodegradability in Soil (1981)

 

OECD Test Guideline 306: Biodegradability in Seawater (1992)

C.42.

OECD Test Guideline 307: Aerobic and Anaerobic Transformation in Soil (2002)

C.23.

OECD Test Guideline 308: Aerobic and Anaerobic Transformation in Aquatic Sediment Systems (2002)

C.24.

OECD Test Guideline 309: Aerobic Mineralisation in Surface Water – Simulation Biodegradation Test (2004)

C.25.

OECD Test Guideline 310: Ready Biodegradability – CO2 in sealed vessels (Headspace Test) (2014)

C.29.

OECD Test Guideline 311: Anaerobic Biodegradability of Organic Compounds in Digested Sludge: by Measurement of Gas Production (2006)

C.43.

OECD Test Guideline 314: Simulation Tests to Assess the Biodegradability of Chemicals Discharged in Wastewater (2008)

 

►M10  OECD Test Guideline 316: Phototransformation of Chemicals in Water – Direct Photolysis (2023) ◄

 

EU test method C.5. Degradation – Biochemical Oxygen Demand

C.5.

EU test method C.6. Degradation – Chemical Oxygen Demand

C.6.

Fate and behaviour in the environment

OECD Test Guideline 305: Bioaccumulation in Fish: Aqueous and Dietary Exposure (2012)

C.13.

OECD Test Guideline 315: Bioaccumulation in Sediment-Dwelling Benthic Oligochaetes (2008)

C.46.

OECD Test Guideline 317: Bioaccumulation in Terrestrial Oligochaetes (2010)

C.30.

OECD Test Guideline 318: Dispersion Stability of Nanomaterials in Simulated Environmental Media (2017)

 

OECD Test Guideline 121: Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC) (2001)

C.19.

OECD Test Guideline 106: Adsorption – Desorption Using a Batch Equilibrium Method (2000)

C.18.

OECD Test Guideline 312: Leaching in Soil Columns (2004)

C.44.

OECD Test Guideline 313: Estimation of Emissions from Preservative – Treated Wood to the Environment (2007)

C.45.

OECD Test Guideline 319A: Determination of In Vitro Intrinsic Clearance Using Cryopreserved Rainbow Trout Hepatocytes (RT-HEP) (2018)

 

OECD Test Guideline 319B: Determination of In Vitro Intrinsic Clearance Using Rainbow Trout Liver S9 Sub-Cellular Fraction (RT-S9) (2018)

 

OECD Test Guideline 320: Anaerobic Transformation of Chemicals in Liquid Manure (2022)

 

▼M11

OECD Test Guideline 321: Hyalella azteca Bioconcentration Test (HYBIT) (2024)

 

▼M9

Effects on terrestrial organisms

OECD Test Guideline 216: Soil Microorganisms: Nitrogen Transformation Test (2000)

C.21.

OECD Test Guideline 217: Soil Microorganisms: Carbon Transformation Test (2000)

C.22.

OECD Test Guideline 207: Earthworm, Acute Toxicity Tests (1984)

C.8.

OECD Test Guideline 222: Earthworm Reproduction Test (Eisenia fetida/Eisenia andrei) (2016)

(C.33.)

OECD Test Guideline 220: Enchytraeid Reproduction Test (2016)

(C.32.)

OECD Test Guideline 226: Predatory Mite (Hypoaspis (Geolaelaps) aculeifer) Reproduction Test in Soil (2016)

(C.36.)

OECD Test Guideline 232: Collembolan Reproduction Test in Soil (2016)

(C.39.)

OECD Test Guideline 208: Terrestrial Plant Test: Seedling Emergence and Seedling Growth Test (2006)

C.31.

OECD Test Guideline 227: Terrestrial Plant Test: Vegetative Vigour Test (2006)

 

Effects on sediment organisms

►M10  OECD Test Guideline 218: Sediment-Water Chironomid Toxicity Test Using Spiked Sediment (2023) ◄

►M10  (C.27.) ◄

►M10  OECD Test Guideline 219: Sediment-Water Chironomid Toxicity Test Using Spiked Water (2023) ◄

►M10  (C.28.) ◄

OECD Test Guideline 233: Sediment-Water Chironomid Life-Cycle Toxicity Test Using Spiked Water or Spiked Sediment (2010)

C.40.

OECD Test Guideline 235: Chironomus sp., Acute Immobilisation Test (2011)

 

OECD Test Guideline 225: Sediment-Water Lumbriculus Toxicity Test Using Spiked Sediment (2007)

C.35.

OECD Test Guideline 238: Sediment-Free Myriophyllum Spicatum Toxicity Test (2014)

C.50.

OECD Test Guideline 239: Water-Sediment Myriophyllum Spicatum Toxicity Test (2014)

C.51.

Effects on birds

OECD Test Guideline 205: Avian Dietary Toxicity Test (1984)

 

OECD Test Guideline 206: Avian Reproduction Test (1984)

 

OECD Test Guideline 223: Avian Acute Oral Toxicity Test (2016)

 

Effects on insects

OECD Test Guideline 213: Honeybees, Acute Oral Toxicity Test (1998)

C.16.

OECD Test Guideline 214: Honeybees, Acute Contact Toxicity Test (1998)

C.17.

OECD Test Guideline 237: Honey Bee (Apis Mellifera) Larval Toxicity Test, Single Exposure (2013)

 

OECD Test Guideline 245: Honey Bee (Apis Mellifera L.), Chronic Oral Toxicity Test (10-Day Feeding) (2017)

 

OECD Test Guideline 246: Bumblebee, Acute Contact Toxicity Test (2017)

 

OECD Test Guideline 247: Bumblebee, Acute Oral Toxicity Test (2017)

 

OECD Test Guideline 228: Determination of Developmental Toxicity to Dipteran Dung Flies (Scathophaga stercoraria L. (Scathophagidae), Musca autumnalis De Geer (Muscidae)) (2016)

 

Endocrine disrupting properties

OECD Test Guideline 230: 21-Day Fish Assay (2009)

C.37.

OECD Test Guideline 229: Fish Short Term Reproduction Assay (2012)

C.48.

OECD Test Guideline 231: Amphibian Metamorphosis Assay (2009)

C.38.

OECD Test Guideline 234: Fish Sexual Development Test (2011)

C.41.

►M10  OECD Test Guideline 240: Medaka Extended One Generation Reproduction Test (MEOGRT) (2023) ◄

►M10  (C.52.) ◄

OECD Test Guideline 241: The Larval Amphibian Growth and Development Assay (LAGDA) (2015)

C.53.

OECD Test Guideline 248: Xenopus Eleutheroembryonic Thyroid Assay (XETA) (2019)

 

OECD Test Guideline 250: EASZY assay – Detection of Endocrine Active Substances, Acting Through Estrogen Receptors, Using Transgenic tg(cyp19a1b:GFP) Zebrafish embrYos (2021)

 

OECD Test Guideline 251: Rapid Androgen Disruption Activity Reporter (RADAR) Assay (2022)

 

▼M11

OECD Test Guideline 252: Rapid Estrogen Activity In Vivo (REACTIV) assay (2024)

 

OECD Test Guideline 253: Short-term Juvenile Hormone Activity Screening Assay using Daphnia magna (JHASA) (2024)

 

▼B




PART A: METHODS FOR THE DETERMINATION OF PHYSICO-CHEMICAL PROPERTIES

TABLE OF CONTENTS

A.1.

MELTING/FREEZING TEMPERATURE

A.2.

BOILING TEMPERATURE

A.3.

RELATIVE DENSITY

A.4.

VAPOUR PRESSURE

A.5.

SURFACE TENSION

A.6.

WATER SOLUBILITY

A.8.

PARTITION COEFFICIENT

A.9.

FLASH-POINT

A.10.

FLAMMABILITY (SOLIDS)

A.11.

FLAMMABILITY (GASES)

A.12.

FLAMMABILITY (CONTACT WITH WATER)

A.13.

PYROPHORIC PROPERTIES OF SOLIDS AND LIQUIDS

A.14.

EXPLOSIVE PROPERTIES

A.15.

AUTO-IGNITION TEMPERATURE (LIQUIDS AND GASES)

A.16.

RELATIVE SELF-IGNITION TEMPERATURE FOR SOLIDS

A.17.

OXIDISING PROPERTIES (SOLIDS)

A.18.

NUMBER — AVERAGE MOLECULAR WEIGHT AND MOLECULAR WEIGHT DISTRIBUTION OF POLYMERS

A.19.

LOW MOLECULAR WEIGHT CONTENT OF POLYMERS

A.20.

SOLUTION/EXTRACTION BEHAVIOUR OF POLYMERS IN WATER

A.21.

OXIDISING PROPERTIES (LIQUIDS)

A.22.

LENGTH WEIGHTED GEOMETRIC MEAN DIAMETER OF FIBRES

A.23.

PARTITION COEFFICIENT (1-OCTANOL/WATER): SLOW-STIRRING METHOD

A.24.

PARTITION COEFFICIENT (N-OCTANOL/WATER), HIGH PERFORMANCELIQUID CHROMATOGRAPHY (HPLC) METHOD

A.25.

DISSOCIATION CONSTANTS IN WATER (TITRATION METHOD — SPECTROPHOTOMETRIC METHOD — CONDUCTOMETRIC METHOD)

A.1.   MELTING/FREEZING TEMPERATURE

1.   METHOD

The majority of the methods described are based on the OECD Test Guideline (1). The fundamental principles are given in references (2) and (3).

1.1.   INTRODUCTION

The methods and devices described are to be applied for the determination of the melting temperature of substances, without any restriction with respect to their degree of purity.

The selection of the method is dependent on the nature of the substance to be tested. In consequence the limiting factor will be according to, whether or not the substance can be pulverised easily, with difficulty, or not at all.

For some substances, the determination of the freezing or solidification temperature is more appropriate and the standards for these determinations have also been included in this method.

Where, due to the particular properties of the substance, none of the above parameters can be conveniently measured, a pour point may be appropriate.

1.2.   DEFINITIONS AND UNITS

The melting temperature is defined as the temperature at which the phase transition from solid to liquid state occurs at atmospheric pressure and this temperature ideally corresponds to the freezing temperature.

As the phase transition of many substances takes place over a temperature range, it is often described as the melting range.

Conversion of units (K to oC)

t = T - 273,15

t

:

Celsius temperature, degree Celsius (oC)

T

:

thermodynamic temperature, kelvin (K)

1.3.   REFERENCE SUBSTANCES

Reference substances do not need to be employed in all cases when investigating a new substance. They should primarily serve to check the performance of the method from time to time and to allow comparison with results from other methods.

Some calibration substances are listed in the references (4).

1.4.   PRINCIPLE OF THE TEST METHOD

The temperature (temperature range) of the phase transition from the solid to the liquid state or from the liquid to the solid state is determined. In practice while heating/cooling a sample of the test substance at atmospheric pressure the temperatures of the initial melting/freezing and the final stage of melting/freezing are determined. Five types of methods are described, namely capillary method, hot stage methods, freezing temperature determinations, methods of thermal analysis, and determination of the pour point (as developed for petroleum oils).

In certain cases, it may be convenient to measure the freezing temperature in place of the melting temperature.

1.4.1.   Capillary method

1.4.1.1.   Melting temperature devices with liquid bath

A small amount of the finely ground substance is placed in a capillary tube and packed tightly. The tube is heated, together with a thermometer, and the temperature rise is adjusted to less than about 1 K/min during the actual melting. The initial and final melting temperatures are determined.

1.4.1.2.   Melting temperature devices with metal block

As described under 1.4.1.1, except that the capillary tube and the thermometer are situated in a heated metal block, and can be observed through holes in the block.

1.4.1.3.   Photocell detection

The sample in the capillary tube is heated automatically in a metal cylinder. A beam of light is directed through the substance, by way of a hole in the cylinder, to a precisely calibrated photocell. The optical properties of most substances change from opaque to transparent when they are melting. The intensity of light reaching the photocell increases and sends a stop signal to the digital indicator reading out the temperature of a platinum resistance thermometer located in the heating chamber. This method is not suitable for some highly coloured substances.

1.4.2.   Hot stages

1.4.2.1.   Kofler hot bar

The Kofler hot bar uses two pieces of metal of different thermal conductivity, heated electrically, with the bar designed so that the temperature gradient is almost linear along its length. The temperature of the hot bar can range from 283 to 573 K with a special temperature-reading device including a runner with a pointer and tab designed for the specific bar. In order to determine a melting temperature, the substance is laid, in a thin layer, directly on the surface of the hot bar. In a few seconds a sharp dividing line between the fluid and solid phase develops. The temperature at the dividing line is read by adjusting the pointer to rest at the line.

1.4.2.2.   Melt microscope

Several microscope hot stages are in use for the determination of melting temperatures with very small quantities of material. In most of the hot stages the temperature is measured with a sensitive thermocouple but sometimes mercury thermometers are used. A typical microscope hot stage melting temperature apparatus has a heating chamber which contains a metal plate upon which the sample is placed on a slide. The centre of the metal plate contains a hole permitting the entrance of light from the illuminating mirror of the microscope. When in use, the chamber is closed by a glass plate to exclude air from the sample area.

The heating of the sample is regulated by a rheostat. For very precise measurements on optically anisotropic substances, polarised light may be used.

1.4.2.3.   Meniscus method

This method is specifically used for polyamides.

The temperature at which the displacement of a meniscus of silicone oil, enclosed between a hot stage and a cover-glass supported by the polyamide test specimen, is determined visually.

1.4.3.   Method to determine the freezing temperature

The sample is placed in a special test tube and placed in an apparatus for the determination of the freezing temperature. The sample is stirred gently and continuously during cooling and the temperature is measured at suitable intervals. As soon as the temperature remains constant for a few readings this temperature (corrected for thermometer error) is recorded as the freezing temperature.

Supercooling must be avoided by maintaining equilibrium between the solid and the liquid phases.

1.4.4.   Thermal analysis

1.4.4.1   Differential thermal analysis (DTA)

This technique records the difference in temperatures between the substance and a reference material as a function of temperature, while the substance and reference material are subjected to the same controlled temperature programme. When the sample undergoes a transition involving a change of enthalpy, that change is indicated by an endothermic (melting) or exothermic (freezing) departure from the base line of the temperature record.

1.4.4.2   Differential scanning calorimetry (DSC)

This technique records the difference in energy inputs into a substance and a reference material, as a function of temperature, while the substance and reference material are subjected to the same controlled temperature programme. This energy is the energy necessary to establish zero temperature difference between the substance and the reference material. When the sample undergoes a transition involving a change of enthalpy, that change is indicated by an endothermic (melting) or exothermic (freezing) departure from the base line of the heat flow record.

1.4.5.   Pour point

This method was developed for use with petroleum oils and is suitable for use with oily substances with low melting temperatures.

After preliminary heating, the sample is cooled at a specific rate and examined at intervals of 3 K for flow characteristics. The lowest temperature at which movement of the substance is observed is recorded as the pour point.

1.5.   QUALITY CRITERIA

The applicability and accuracy of the different methods used for the determination of the melting temperature/melting range are listed in the following table:

TABLE: APPLICABILITY OF THE METHODS



A.  Capillary methods

Method of measurement

Substances which can be pulverised

Substances which are not readily pulverised

Temperature range

Estimated accuracy (1)

Existing standards

Melting temperature devices with liquid bath

yes

only to a few

273 to 573 K

± 0,3 K

JIS K 0064

Melting temperature with metal block

yes

only to a few

293 to > 573 K

± 0,5 K

ISO 1218 (E)

Photocell detection

yes

several with appliance devices

253 to 573 K

± 0,5 K

 

(1)   

Dependent on type of instrument and on degree of purity of the substance.



B.  Hot stages and freezing methods

Method of measurement

Substances which can be pulverised

Substances which are not readily pulverised

Temperature range

Estimated accuracy (1)

Existing standards

Kofler hot bar

yes

no

283 to > 573 K

± 1K

ANSI/ASTM D 3451-76

Melt microscope

yes

only to a few

273 to > 573 K

± 0,5 K

DIN 53736

Meniscus method

no

specifically for polyamides

293 to > 573 K

± 0,5 K

ISO 1218 (E)

Freezing temperature

yes

yes

223 to 573 K

± 0,5 K

e.g. BS 4695

(1)   

Dependent on type of instrument and on degree of purity of the substance



C.  Thermal analysis

Method of measurement

Substances which can be pulverised

Substances which are not readily pulverised

Temperature range

Estimated accuracy (1)

Existing standards

Differential thermal analysis

yes

yes

173 to 1 273 K

up to 600 K ± 0,5 K up to 1 273 K ± 2,0 K

ASTM E 537-76

Differential scanning calorimetry

yes

yes

173 to 1 273 K

up to 600 K ± 0,5 K up to 1 273 K ± 2,0 K

ASTM E 537-76

(1)   

Dependent on type of instrument and on degree of purity of the substance



D.  Pour point

Method of measurement

Substances which can be pulverised

Substances which are not readily pulverised

Temperature range

Estimated accuracy (1)

Existing standards

Pour point

for petroleum oils and oily substances

for petroleum oils and oily substances

223 to 323 K

± 0,3 K

ASTM D 97-66

(1)   

Dependent on type of instrument and on degree of purity of the substance

1.6.   DESCRIPTION OF THE METHODS

The procedures of nearly all the test methods have been described in international and national standards (see Appendix 1).

1.6.1.   Methods with capillary tube

When subjected to a slow temperature rise, finely pulverised substances usually show the stages of melting shown in figure 1.

Figure 1

image

Text of image

During the determination of the melting temperature, the temperatures are recorded at the beginning of the melting and at the final stage.

1.6.1.1.   Melting temperature devices with liquid bath apparatus

Figure 2 shows a type of standardised melting temperature apparatus made of glass (JIS K 0064); all specifications are in millimeters.

Figure 2

image

Text of image

Bath liquid:

A suitable liquid should be chosen. The choice of the liquid depends upon the melting temperature to be determined, e.g. liquid paraffin for melting temperatures no higher than 473 K, silicone oil for melting temperatures no higher than 573 K.

For melting temperatures above 523 K, a mixture consisting of three parts sulphuric acid and two parts potassium sulphate (in mass ratio) can be used. Suitable precautions should be taken if a mixture such as this is used.

Thermometer:

Only those thermometers should be used which fulfil the requirements of the following or equivalent standards:

ASTM E 1-71, DIN 12770, JIS K 8001.

Procedure:

The dry substance is finely pulverised in a mortar and is put into the capillary tube, fused at one end, so that the filling level is approximately 3 mm after being tightly packed. To obtain a uniform packed sample, the capillary tube should be dropped from a height of approximately 700 mm through a glass tube vertically onto a watch glass.

The filled capillary tube is placed in the bath so that the middle part of the mercury bulb of the thermometer touches the capillary tube at the part where the sample is located. Usually the capillary tube is introduced into the apparatus about 10 K below the melting temperature.

The bath liquid is heated so that the temperature rise is approximately 3 K/min. The liquid should be stirred. At about 10 K below the expected melting temperature the rate of temperature rise is adjusted to a maximum of 1 K/min.

Calculation:

The calculation of the melting temperature is as follows:

T = TD + 0,00016 (TD - TE) n

where:

T

=

corrected melting temperature in K

TD

=

temperature reading of thermometer D in K

TE

=

temperature reading of thermometer E in K

n

=

number of graduations of mercury thread on thermometer D at emergent stem.

1.6.1.2.   Melting temperature devices with metal block

Apparatus:

This consists of:

— 
a cylindrical metal block, the upper part of which is hollow and forms a chamber (see figure 3),
— 
a metal plug, with two or more holes, allowing tubes to be mounted into the metal block,
— 
a heating system, for the metal block, provided for example by an electrical resistance enclosed in the block,
— 
a rheostat for regulation of power input, if electric heating is used,
— 
four windows of heat-resistant glass on the lateral walls of the chamber, diametrically disposed at right-angles to each other. In front of one of these windows is mounted an eye-piece for observing the capillary tube. The other three windows are used for illuminating the inside of the enclosure by means of lamps,
— 
a capillary tube of heat-resistant glass closed at one end (see 1.6.1.1).

Thermometer:

See standards mentioned in 1.6.1.1. Thermoelectrical measuring devices with comparable accuracy are also applicable.

Figure 3

image

Text of image

1.6.1.3.   Photocell detection

Apparatus and procedure:

The apparatus consists of a metal chamber with automated heating system. Three capillary are filled accordingly to 1.6.1.1 and placed in the oven.

Several linear increases of temperature are available for calibrating the apparatus and the suitable temperature rise is electrically adjusted at a pre-selected constant and linear rate. recorders show the actual oven temperature and the temperature of the substance in the capillary tubes.

1.6.2.   Hot stages

1.6.2.1.   Kofler hot bar

See Appendix.

1.6.2.2.   Melt microscope

See Appendix.

1.6.2.3.   Meniscus method (polyamides)

See Appendix.

The heating rate through the melting temperature should be less than 1 K/min.

1.6.3.   Methods for the determination of the freezing temperature

See Appendix.

1.6.4.   Thermal analysis

1.6.4.1.   Differential thermal analysis

See Appendix.

1.6.4.2.   Differential scanning calorimetry

See Appendix.

1.6.5.   Determination of the pour point

See Appendix.

2.   DATA

A thermometer correction is necessary in some cases.

3.   REPORTING

The test report shall, if possible, include the following information:

— 
method used,
— 
precise specification of the substance (identity and impurities) and preliminary purification step, if any,
— 
an estimate of the accuracy.

The mean of at least two measurements which are in the range of the estimated accuracy (see tables) is reported as the melting temperature.

If the difference between the temperature at the beginning and at the final stage of melting is within the limits of the accuracy of the method, the temperature at the final stage of melting is taken as the melting temperature; otherwise the two temperatures are reported.

If the substance decomposes or sublimes before the melting temperature is reached, the temperature at which the effect is observed shall be reported.

All information and remarks relevant for the interpretation of results have to be reported, especially with regard to impurities and physical state of the substance.

4.   REFERENCES

(1) OECD, Paris, 1981, Test Guideline 102, Decision of the Council C(81) 30 final.

(2) IUPAC, B. Le Neindre, B. Vodar, eds. Experimental thermodynamics, Butterworths, London 1975, vol. II, p. 803-834.

(3) R. Weissberger ed.: Technique of organic Chemistry, Physical Methods of Organic Chemistry, 3rd ed., Interscience Publ., New York, 1959, vol. I, Part I, Chapter VII.

(4) IUPAC, Physicochemical measurements: Catalogue of reference materials from national laboratories, Pure and applied chemistry, 1976, vol. 48, p. 505-515.

Appendix

For additional technical details, the following standards may be consulted for example.

1.   Capillary methods

1.1.   Melting temperature devices with liquid bath



ASTM E 324-69

Standard test method for relative initial and final melting points and the melting range of organic chemicals

BS 4634

Method for the determination of melting point and/or melting range

DIN 53181

Bestimmung des Schmelzintervalles von Harzen nach Kapillarverfarehn

JIS K 00-64

Testing methods for melting point of chemical products

1.2.   Melting temperature devices with metal block



DIN 53736

Visuelle Bestimmung der Schmelztemperatur von teilkristallinen Kunststoffen

ISO 1218 (E)

Plastics — polyamides — determination of ‘melting point’

2.   Hot stages

2.1.   Kofler hot bar



ANSI/ASTM D 3451-76

Standard recommended practices for testing polymeric powder coatings

2.2.   Melt microscope



DIN 53736

Visuelle Bestimmung der Schmelztemperatur von teilkristallinen Kunststoffen

2.3.   Meniscus method (polyamides)



ISO 1218 (E)

Plastics — polyamides — determination of ‘melting point’

ANSI/ASTM D 2133-66

Standard specification for acetal resin injection moulding and extrusion materials

NF T 51-050

Résines de polyamides. Détermination du ‘point de fusion’ méthode du ménisque

3.   Methods for the determination of the freezing temperature



BS 4633

Method for the determination of crystallising point

BS 4695

Method for Determination of Melting Point of petroleum wax (Cooling Curve)

DIN 51421

Bestimmung des Gefrierpunktes von Flugkraftstoffen, Ottokraftstoffen und Motorenbenzolen

ISO 2207

Cires de pétrole: détermination de la température de figeage

DIN 53175

Bestimmung des Erstarrungspunktes von Fettsäuren

NF T 60-114

Point de fusion des paraffines

NF T 20-051

Méthode de détermination du point de cristallisation (point de congélation)

ISO 1392

Method for the determination of the freezing point

4.   Thermal analysis

4.1.   Differential thermal analysis



ASTM E 537-76

Standard method for assessing the thermal stability of chemicals by methods of differential thermal analysis

ASTM E 473-85

Standard definitions of terms relating to thermal analysis

ASTM E 472-86

Standard practice for reporting thermoanalytical data

DIN 51005

Thermische Analyse, Begriffe

4.2.   Differential scanning calorimetry



ASTM E 537-76

Standard method for assessing the thermal stability of chemicals by methods of differential thermal analysis

ASTM E 473-85

Standard definitions of terms relating to thermal analysis

ASTM E 472-86

Standard practice for reporting thermoanalytical data

DIN 51005

Thermische Analyse, Begriffe

5.   Determination of the pour point



NBN 52014

Echantillonnage et analyse des produits du pétrole: Point de trouble et point d'écoulement limite — Monsterneming en ontleding van aardolieproducten: Troebelingspunt en vloeipunt

ASTM D 97-66

Standard test method for pour point of petroleum oils

ISO 3016

Petroleum oils — Determination of pour point

A.2.   BOILING TEMPERATURE

1.   METHOD

The majority of the methods described are based on the OECD Test Guideline (1). The fundamental principles are given in references (2) and (3).

1.1.   INTRODUCTION

The methods and devices described here can be applied to liquid and low melting substances, provided that these do not undergo chemical reaction below the boiling temperature (for example: auto-oxidation, rearrangement, degradation, etc.). The methods can be applied to pure and to impure liquid substances.

Emphasis is put on the methods using photocell detection and thermal analysis, because these methods allow the determination of melting as well as boiling temperatures. Moreover, measurements can be performed automatically.

The ‘dynamic method’ has the advantage that it can also be applied to the determination of the vapour pressure and it is not necessary to correct the boiling temperature to the normal pressure (101,325 kPa) because the normal pressure can be adjusted during the measurement by a manostat.

Remarks:

The influence of impurities on the determination of the boiling temperature depends greatly upon the nature of the impurity. When there are volatile impurities in the sample, which could affect the results, the substance may be purified.

1.2.   DEFINITIONS AND UNITS

The normal boiling temperature is defined as the temperature at which the vapour pressure of a liquid is 101,325 kPa.

If the boiling temperature is not measured at normal atmospheric pressure, the temperature dependence of the vapour pressure can be described by the Clausius-Clapeyron equation:

image

where:

p

=

the vapour pressure of the substance in pascals

Δ Hv

=

its heat of vaporisation in J mol-1

R

=

the universal molar gas constant = 8,314  J mol-1 K-1

T

=

thermodynamic temperature in K

The boiling temperature is stated with regard to the ambient pressure during the measurement.

Conversions

Pressure (units: kPa)

100 kPa

=

1 bar = 0,1 MPa

(‘bar’ is still permissible but not recommended)

133 Pa

=

1 mm Hg = 1 Torr

(the units ‘mm Hg’ and ‘Torr’ are not permitted)

1 atm

=

standard atmosphere = 101 325 Pa

(the unit ‘atm’ is not permitted)

Temperature (units: K)

t = T - 273,15

t

:

Celsius temperature, degree Celsius (oC)

T

:

thermodynamic temperature, kelvin (K)

1.3.   REFERENCE SUBSTANCES

Reference substances do not need to be employed in all cases when investigating a new substance. They should primarily serve to check the performance of the method from time to time and to allow comparison with results from other methods.

Some calibration substances can be found in the methods listed in the Appendix.

1.4.   PRINCIPLE OF THE TEST METHOD

Five methods for the determination of the boiling temperature (boiling range) are based on the measurement of the boiling temperature, two others are based on thermal analysis.

1.4.1.   Determination by use of the ebulliometer

Ebulliometers were originally developed for the determination of the molecular weight by boiling temperature elevation, but they are also suited for exact boiling temperature measurements. A very simple apparatus is described in ASTM D 1120-72 (see Appendix). The liquid is heated in this apparatus under equilibrium conditions at atmospheric pressure until it is boiling.

1.4.2.   Dynamic method

This method involves the measurement of the vapour recondensation temperature by means of an appropriate thermometer in the reflux while boiling. The pressure can be varied in this method.

1.4.3.   Distillation method for boiling temperature

This method involves distillation of the liquid and measurement of the vapour recondensation temperature and determination of the amount of distillate.

1.4.4.   Method according to Siwoloboff

A sample is heated in a sample tube, which is immersed in a liquid in a heat-bath. A fused capillary, containing an air bubble in the lower part, is dipped in the sample tube.

1.4.5.   Photocell detection

Following the principle according to Siwoloboff, automatic photo-electrical measurement is made using rising bubbles.

1.4.6.   Differential thermal analysis

This technique records the difference in temperatures between the substance and a reference material as a function of temperature, while the substance and reference material are subjected to the same controlled temperature programme. When the sample undergoes a transition involving a change of enthalpy, that change is indicated by an endothermic departure (boiling) from the base line of the temperature record.

1.4.7.   Differential scanning calorimetry

This technique records the difference in energy inputs into a substance and a reference material as a function of temperature, while the substance and reference material are subjected to the same controlled temperature programme. This energy is the energy necessary to establish zero temperature difference between the substance and the reference material. When the sample undergoes a transition involving a change of enthalpy, that change is indicated by an endothermic departure (boiling) from the base line of the heat flow record.

1.5.   QUALITY CRITERIA

The applicability and accuracy of the different methods used for the determination of the boiling temperature/boiling range are listed in table 1.



Table 1:

Comparison of the methods

Method of measurement

Estimated accuracy

Existing standard

Ebulliometer

± 1,4 K (up to 373 K) (1) (2)

± 2,5 K (up to 600 K) (1) (2)

ASTM D 1120-72 (1)

Dynamic method

± 0,5 K (up to 600 K) (2)

 

Distillation process (boiling range)

± 0,5 K (up to 600 K)

ISO/R 918, DIN 53171, BS 4591/71

According to Siwoloboff

± 2 K (up to 600 K) (2)

 

Photocell detection

± 0,3 K (up to 373 K) (2)

 

Differential thermal calorimetry

± 0,5 K (up to 600 K)

± 2,0 K (up to 1 273 K)

ASTM E 537-76

Differential scanning calorimetry

± 0,5 K (up to 600 K)

± 2,0 K (up to 1 273 K)

ASTM E 537-76

(1)   

This accuracy is only valid for the simple device as for example described in ASTM D 1120-72; it can be improved with more sophisticated ebulliometer devices.

(2)   

Only valid for pure substances. The use in other circumstances should be justified.

1.6.   DESCRIPTION OF THE METHODS

The procedures of some test methods have been described in international and national standards (see Appendix).

1.6.1.   Ebulliometer

See Appendix.

1.6.2.   Dynamic method

See test method A.4 for the determination of the vapour pressure.

The boiling temperature observed with an applied pressure of 101,325 kPa is recorded.

1.6.3.   Distillation process (boiling range)

See Appendix.

1.6.4.   Method according to Siwoloboff

The sample is heated in a melting temperature apparatus in a sample tube, with a diameter of approximately 5 mm (figure 1).

Figure 1 shows a type of standardised melting and boiling temperature apparatus (JIS K 0064) (made of glass, all specifications in millimetres).

Figure 1

image

Text of image

A capillary tube (boiling capillary) which is fused about 1 cm above the lower end is placed in the sample tube. The level to which the test substance is added is such that the fused section of the capillary is below the surface of the liquid. The sample tube containing the boiling capillary is fastened either to the thermometer with a rubber band or is fixed with a support from the side (see figure 2).



Figure 2

Principle according to Siwoloboff

Figure 3

Modified principle

image

image

The bath liquid is chosen according to boiling temperature. At temperatures up to 573 K, silicone oil can be used. Liquid paraffin may only be used up to 473 K. The heating of the bath liquid should be adjusted to a temperature rise of 3 K/min at first. The bath liquid must be stirred. At about 10 K below the expected boiling temperature, the heating is reduced so that the rate of temperature rise is less than 1 K/min. Upon approach of the boiling temperature, bubbles begin to emerge rapidly from the boiling capillary.

The boiling temperature is that temperature when, on momentary cooling, the string of bubbles stops and fluid suddenly starts rising in the capillary. The corresponding thermometer reading is the boiling temperature of the substance.

In the modified principle (figure 3) the boiling temperature is determined in a melting temperature capillary. It is stretched to a fine point about 2 cm in length (a) and a small amount of the sample is sucked up. The open end of the fine capillary is closed by melting, so that a small air bubble is located at the end. While heating in the melting temperature apparatus (b), the air bubble expands. The boiling temperature corresponds to the temperature at which the substance plug reaches the level of the surface of the bath liquid (c).

1.6.5.   Photocell detection

The sample is heated in a capillary tube inside a heated metal block.

A light beam is directed, via suitable holes in the block, through the substance onto a precisely calibrated photocell.

During the increase of the sample temperature, single air bubbles emerge from the boiling capillary. When the boiling temperature is reached the number of bubbles increases greatly. This causes a change in the intensity of light, recorded by a photocell, and gives a stop signal to the indicator reading out the temperature of a platinum resistance thermometer located in the block.

This method is especially useful because it allows determinations below room temperature down to 253,15 K (– 20 oC) without any changes in the apparatus. The instrument merely has to be placed in a cooling bath.

1.6.6.   Thermal analysis

1.6.6.1.   Differential thermal analysis

See Appendix.

1.6.6.2.   Differential scanning calorimetry

See Appendix.

2.   DATA

At small deviations from the normal pressure (max. ± 5 kPa) the boiling temperatures are normalised to Tn by means of the following number-value equation by Sidney Young:

Tn = T + (fT × Δp)

where:

Δp

=

(101,325 - p) [note sign]

P

=

pressure measurement in kPa

fT

=

rate of change of boiling temperature with pressure in K/kPa

T

=

measured boiling temperature in K

Tn

=

boiling temperature corrected to normal pressure in K

The temperature-correction factors, fT, and equations for their approximation are included in the international and national standards mentioned above for many substances.

For example, the DIN 53171 method mentions the following rough corrections for solvents included in paints:



Table 2:

Temperature — corrections factors fT

Temperature T (K)

Correction factor fT (K/kPa)

323,15

0,26

348,15

0,28

373,15

0,31

398,15

0,33

423,15

0,35

448,15

0,37

473,15

0,39

498,15

0,41

523,15

0,4

548,15

0,45

573,15

0,47

3.   REPORTING

The test report shall, if possible, include the following information:

— 
method used,
— 
precise specification of the substance (identity and impurities) and preliminary purification step, if any,
— 
an estimate of the accuracy.

The mean of at least two measurements which are in the range of the estimated accuracy (see table 1) is reported as the boiling temperature.

The measured boiling temperatures and their mean shall be stated and the pressure(s) at which the measurements were made shall be reported in kPa. The pressure should preferably be close to normal atmospheric pressure.

All information and remarks relevant for the interpretation of results have to be reported, especially with regard to impurities and physical state of the substance.

4.   REFERENCES

(1) OECD, Paris, 1981, Test Guideline 103, Decision of the Council C (81) 30 final.

(2) IUPAC, B. Le Neindre, B. Vodar, editions. Experimental thermodynamics, Butterworths, London, 1975, vol. II.

(3) R. Weissberger edition: Technique of organic chemistry, Physical methods of organic chemistry, Third Edition, Interscience Publications, New York, 1959, vol. I, Part I, Chapter VIII.

Appendix

For additional technical details, the following standards may be consulted for example.

1.   Ebulliometer

1.1. Melting temperature devices with liquid bath



ASTM D 1120-72

Standard test method for boiling point of engine anti-freezes

2.   Distillation process (boiling range)



ISO/R 918

Test Method for Distillation (Distillation Yield and Distillation Range)

BS 4349/68

Method for determination of distillation of petroleum products

BS 4591/71

Method for the determination of distillation characteristics

DIN 53171

Losungsmittel für Anstrichstoffe, Bestimmung des Siedeverlaufes

NF T 20-608

Distillation: détermination du rendement et de l'intervalle de distillation

3.   Differential thermal analysis and differential scanning calorimetry



ASTM E 537-76

Standard method for assessing the thermal stability of chemicals by methods of differential thermal analysis

ASTM E 473-85

Standard definitions of terms relating to thermal analysis

ASTM E 472-86

Standard practice for reporting thermoanalytical data

DIN 51005

Thermische Analyse, Begriffe

A.3.   RELATIVE DENSITY

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼M1

A.4.   VAPOUR PRESSURE

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.5.   SURFACE TENSION

1.   METHOD

The methods described are based on the OECD Test Guideline (1). The fundamental principles are given in reference (2).

1.1.   INTRODUCTION

The described methods are to be applied to the measurement of the surface tension of aqueous solutions.

It is useful to have preliminary information on the water solubility, the structure, the hydrolysis properties and the critical concentration for micelles formation of the substance before performing these tests.

The following methods are applicable to most chemical substances, without any restriction in respect to their degree of purity.

The measurement of the surface tension by the ring tensiometer method is restricted to aqueous solutions with a dynamic viscosity of less than approximately 200 mPa s.

1.2.   DEFINITIONS AND UNITS

The free surface enthalpy per unit of surface area is referred to as surface tension.

The surface tension is given as:

N/m (SI unit) or

mN/m (SI sub-unit)

1 N/m = 103 dynes/cm

1 mN/m = 1 dyne/cm in the obsolete cgs system

1.3.   REFERENCE SUBSTANCES

Reference substances do not need to be employed in all cases when investigating a new substance. They should primarily serve to check the performance of the method from time to time and to allow comparison with results from other methods.

Reference substances which cover a wide range of surface tensions are given in references 1 and 3.

1.4.   PRINCIPLE OF THE METHODS

The methods are based on the measurement of the maximum force which is necessary to exert vertically, on a stirrup or a ring in contact with the surface of the liquid being examined placed in a measuring cup, in order to separate it from this surface, or on a plate, with an edge in contact with the surface, in order to draw up the film that has formed.

Substances which are soluble in water at least at a concentration of 1 mg/l are tested in aqueous solution at a single concentration.

1.5.   QUALITY CRITERIA

These methods are capable of greater precision than is likely to be required for environmental assessment.

1.6.   DESCRIPTION OF THE METHODS

A solution of the substance is prepared in distilled water. The concentration of this solution should be 90 % of the saturation solubility of the substance in water; when this concentration exceeds 1 g/l, a concentration of 1 g/l is used for testing. Substances with water solubility lower than 1 mg/l need not be tested.

1.6.1.   Plate method

See ISO 304 and NF T 73-060 (Surface active agents — determination of surface tension by drawing up liquid films).

1.6.2.   Stirrup method

See ISO 304 and NF T 73-060 (Surface active agents — determination of surface tension by drawing up liquid films).

1.6.3.   Ring method

See ISO 304 and NF T 73-060 (Surface active agents — determination of surface tension by drawing up liquid films).

1.6.4.   OECD harmonised ring method

1.6.4.1.   Apparatus

Commercially available tensiometers are adequate for this measurement. They consist of the following elements:

— 
mobile sample table,
— 
force measuring system,
— 
measuring body (ring),
— 
measurement vessel.

1.6.4.1.1.    Mobile sample table

The mobile sample table is used as a support for the temperature-controlled measurement vessel holding the liquid to be tested. Together with the force measuring system, it is mounted on a stand.

1.6.4.1.2.    Force measuring system

The force measuring system (see figure) is located above the sample table. The error of the force measurement shall not exceed ± 10-6 N, corresponding to an error limit of ± 0,1  mg in a mass measurement. In most cases, the measuring scale of commercially available tensiometers is calibrated in mN/m so that the surface tension can be read directly in mN/m with an accuracy of 0,1 mN/m.

1.6.4.1.3.    Measuring body (ring)

The ring is usually made of a platinum-iridium wire of about 0,4  mm thickness and a mean circumference of 60 mm. The wire ring is suspended horizontally from a metal pin and a wire mounting bracket to establish the connection to the force measuring system (see figure).

Figure

Measuring body

(All dimensions expressed in millimetres)

image

Text of image

1.6.4.1.4.    Measurement vessel

The measurement vessel holding the test solution to be measured shall be a temperature-controlled glass vessel. It shall be designed so that during the measurement the temperature of the test solution liquid and the gas phase above its surface remains constant and that the sample cannot evaporate. Cylindrical glass vessels having an inside diameter of not less than 45 mm are acceptable.

1.6.4.2.   Preparation of the apparatus

1.6.4.2.1.    Cleaning

Glass vessels shall be cleaned carefully. If necessary they shall be washed with hot chromo-sulphuric acid and subsequently with syrupy phosphoric acid (83 to 98 % by weight of H3PO4), thoroughly rinsed in tap water and finally washed with double-distilled water until a neutral reaction is obtained and subsequently dried or rinsed with part of the sample liquid to be measured.

The ring shall first be rinsed thoroughly in water to remove any substances which are soluble in water, briefly immersed in chromo-sulphuric acid, washed in double-distilled water until a neutral reaction is obtained and finally heated briefly above a methanol flame.

Note:

Contamination by substances which are not dissolved or destroyed by chromo-sulphuric acid or phosphoric acid, such as silicones, shall be removed by means of a suitable organic solvent.

1.6.4.2.2.    Calibration of the apparatus

The validation of the apparatus consists of verifying the zero point and adjusting it so that the indication of the instrument allows reliable determination in mN/m.

Mounting:

The apparatus shall be levelled, for instance by means of a spirit level on the tensiometer base, by adjusting the levelling screws in the base.

Zero point adjustment:

After mounting the ring on the apparatus and prior to immersion in the liquid, the tensiometer indication shall be adjusted to zero and the ring checked for parallelism to the liquid surface. For this purpose, the liquid surface can be used as a mirror.

Calibrations:

The actual test calibration can be accomplished by means of either of two procedures:

(a) 

Using a mass: procedure using riders of known mass between 0,1 and 1,0  g placed on the ring. The calibration factor, Φa by which all the instrument readings must be multiplied, shall be determined according to equation (1).



image

 

where:

image

(mN/m)

m

=

mass of the rider (g)

g

=

gravity acceleration (981 cm s-2 at sea level)

b

=

mean circumference of the ring (cm)

σa

=

reading of the tensiometer after placing the rider on the ring (mN/m).

(b) 

Using water: procedure using pure water whose surface tension at, for instance, 23 oC is equal to 72,3 mN/m. This procedure is accomplished faster than the weight calibration but there is always the danger that the surface tension of the water is falsified by traces of contamination by surfactants.

The calibration factor, Φb by which all the instrument readings shall be multiplied, shall be determined in accordance with the equation (2):



image

 

where:

σo

=

value cited in the literature for the surface tension of water (mN/m)

σg

=

measured value of the surface tension of the water (mN/m) both at the same temperature.

1.6.4.3.   Preparation of samples

Aqueous solutions shall be prepared of the substances to be tested, using the required concentrations in water, and shall not contain any non-dissolved substances.

The solution must be maintained at a constant temperature (± 0,5 oC). Since the surface tension of a solution in the measurement vessel alters over a period of time, several measurements shall be made at various times and a curve plotted showing surface tension as a function of time. When no further change occurs, a state of equilibrium has been reached.

Dust and gaseous contamination by other substances interfere with the measurement. The work shall therefore be carried out under a protective cover.

1.6.5.   Test conditions

The measurement shall be made at approximately 20 oC and shall be controlled to within ± 0,5 oC.

1.6.6.   Performance of test

The solutions to be measured shall be transferred to the carefully cleaned measurement vessel, taking care to avoid foaming, and subsequently the measurement vessel shall be placed onto the table of the test apparatus. The table-top with measurement vessel shall be raised until the ring is immersed below the surface of the solution to be measured. Subsequently, the table-top shall be lowered gradually and evenly (at a rate of approximately 0,5  cm/min) to detach the ring from the surface until the maximum force has been reached. The liquid layer attached to the ring must not separate from the ring. After completing the measurements, the ring shall be immersed below the surface again and the measurements repeated until a constant surface tension value is reached. The time from transferring the solution to the measurement vessel shall be recorded for each determination. Readings shall be taken at the maximum force required to detach the ring from the liquid surface.

2.   DATA

In order to calculate the surface tension, the value read in mN/m on the apparatus shall be first multiplied by the calibration factor Φa or Φb (depending on the calibration procedure used). This will yield a value which applies only approximately and therefore requires correction.

Harkins and Jordan (4) have empirically determined correction factors for surface-tension values measured by the ring method which are dependent on ring dimensions, the density of the liquid and its surface tension.

Since it is laborious to determine the correction factor for each individual measurement from the Harkins and Jordan tables, in order to calculate the surface tension for aqueous solutions the simplified procedure of reading the corrected surface-tension values directly from the table may be used. (Interpolation shall be used for readings ranging between the tabular values.)



Table:

Correction of the measured surface tension

Only for aqueous solutions, ρ = 1 g/cm3

r

= 9,55  mm (average ring radius)

r

= 0,185  mm (ring wire radius)



Experimental Value (mN/m)

Corrected Value (mN/m)

Weight calibration (see 1.6.4.2.2(a))

Water calibration (see 1.6.4.2.2(b))

20

16,9

18,1

22

18,7

20,1

24

20,6

22,1

26

22,4

24,1

28

24,3

26,1

30

26,2

28,1

32

28,1

30,1

34

29,9

32,1

36

31,8

34,1

38

33,7

36,1

40

35,6

38,2

42

37,6

40,3

44

39,5

42,3

46

41,4

44,4

48

43,4

46,5

50

45,3

48,6

52

47,3

50,7

54

49,3

52,8

56

51,2

54,9

58

53,2

57,0

60

55,2

59,1

62

57,2

61,3

64

59,2

63,4

66

61,2

65,5

68

63,2

67,7

70

65,2

69,9

72

67,2

72,0

74

69,2

76

71,2

78

73,2

This table has been compiled on the basis of the Harkins-Jordan correction. It is similar to that in the DIN Standard (DIN 53914) for water and aqueous solutions (density ρ = 1 g/cm3 and is for a commercially available ring having the dimensions R = 9,55  mm (mean ring radius) and r = 0,185  mm (ring wire radius). The table provides corrected values for surface-tension measurements taken after calibration with weights or calibration with water.

Alternatively, without the preceding calibration, the surface tension call can be calculated according to the following formula:

image

where:

F

=

the force measured on the dynamometer at the breakpoint of the film

R

=

the radius of the ring

f

=

the correction factor (1)

3.   REPORTING

3.1.   TEST REPORT

The test report shall, if possible, include the following information:

— 
method used,
— 
type of water or solution used,
— 
precise specification of the substance (identity and impurities),
— 
measurement results: surface tension (reading) stating both the individual readings and their arithmetic mean as well as the corrected mean (taking into consideration the equipment factor and the correction table),
— 
concentration of the solution,
— 
test temperature,
— 
age of solution used; in particular the time between preparation and measurement of the solution,
— 
description of time dependence of surface tension after transferring the solution to the measurement vessel,
— 
all information and remarks relevant for the interpretation of results have to be reported, especially with regard to impurities and physical state of the substance.

3.2.   INTERPRETATION OF RESULTS

Considering that distilled water has a surface tension of 72,75 mN/m at 20 oC, substances showing a surface tension lower than 60 mN/m under the conditions of this method should be regarded as being surface-active materials.

4.   REFERENCES

(1) OECD, Paris, 1981, Test Guideline 115, Decision of the Council C(81) 30 final.

(2) R. Weissberger ed.: Technique of Organic Chemistry, Physical Methods of Organic Chemistry, 3rd ed., Interscience Publ., New York, 1959, vol. I, Part I, Chapter XIV.

(3) Pure Appl. Chem., 1976, vol. 48, p. 511.

(4) Harkins, W.D., Jordan, H.F., J. Amer. Chem. Soc., 1930, vol. 52, p. 1751.

▼M4

A.6.   WATER SOLUBILITY

INTRODUCTION

1. This Test Method is equivalent to OECD Test Guideline (TG) 105 (1995). This Test Method is a revised version of the original TG 105 which was adopted in 1981. There is no difference of substance between the current version and that from 1981. Mainly the format has been changed. The revision was based on the EU Test Method ‘Water Solubility’ (1).

INITIAL CONSIDERATIONS

2. The water solubility of a substance can be considerably affected by the presence of impurities. This Test Method addresses the determination of the solubility in water of essentially pure substances which are stable in water and not volatile. Before determining water solubility, it is useful to have some preliminary information on the test substance, like structural formula, vapour pressure, dissociation constant and hydrolysis as a function of pH.

3. Two methods, the column elution method and the flask method which cover respectively solubilities below and above 10–2 g/l are described in this Test Method. A simple preliminary test is also described. It allows the determination of approximately the appropriate amount of sample to be used in the final test, as well as the time necessary to achieve saturation.

DEFINITIONS AND UNITS

4. The water solubility of a substance is the saturation mass concentration of the substance in water at a given temperature.

5. Water solubility is expressed in mass of solute per volume of solution. The SI unit is kg/m3 but g/l may also be used.

REFERENCE CHEMICALS

6. Reference chemicals do not need to be employed when investigating a test substance.

DESCRIPTION OF THE METHODS

Test conditions

7. The test is preferably run at 20 ± 0,5 °C. The chosen temperature should be kept constant in all relevant parts of the equipment.

Preliminary test

8. In a stepwise procedure, increasing volumes of water are added at room temperature to approximately 0,1 g of the sample (solid test substances must be pulverized) in a 10 ml glass-stoppered measuring cylinder. After each addition of an amount of water, the mixture is shaken for 10 minutes and is visually checked for any undissolved parts of the sample. If, after addition of 10 ml of water, the sample or parts of it remain undissolved, the experiment is continued in a 100 ml measuring cylinder. The approximate solubility is given in Table 1 below under that volume of water in which complete dissolution of the sample occurs. When the solubility is low, a long time may be required to dissolve a test substance and at least 24 hours should be allowed. If, after 24 hours, the test substance is still not dissolved, more time (up to 96 hours) should be allowed or further dilution should be attempted to ascertain whether the column elution method or flask method should be used.



Table 1

ml of water for 0,1 g soluble

0,1

0,5

1

2

10

100

> 100

approximate solubility in g/l

> 1 000

1 000 to 200

200 to 100

100 to 50

50 to 10

10 to 1

< 1

Column elution method

Principle

9. This method is based on the elution of a test substance with water from a micro-column which is charged with an inert support material, previously coated with an excess of the test substance (2). The water solubility is given by the mass concentration of the eluate when this has reached a plateau as a function of time.

Apparatus

10. The apparatus consists of a microcolumn (Figure 1), maintained at constant temperature. It is connected either to a recirculating pump (Figure 2) or to a levelling vessel (Figure 3). The microcolumn contains an inert support held in place by a small plug of glasswool which also serves to filter out particles. Possible materials which can be employed for the support are glass beads, diatomaceous earth, or other inert materials.

11. The microcolumn shown in Figure 1 is suitable for the set-up with recirculating pump. It has a head space providing for five bed volumes (discarded at the start of the experiment) and the volume of five samples (withdrawn for analysis during the experiment). Alternatively, the size can be reduced if water can be added to the system during the experiment to replace the initial five bed volumes removed with impurities. The column is connected with tubing made of an inert material to the recirculating pump, capable of delivering approximately 25 ml/h. The recirculating pump can be, for example, a peristaltic or membrane pump. Care must be taken that no contamination and/or adsorption occur with the tube material.

12. A schematic arrangement using a levelling vessel is shown in Figure 3. In this arrangement the microcolumn is fitted with a one way stopcock. The connection to the levelling vessel consists of a ground glass joint and tubing made of an inert material. The flow rate from the levelling vessel should be approximately 25 ml/h.

Figure 1

image

Dimensions in mm

A. Connection for ground glass joint

B. Headspace

C. Interior 5

D. Exterior 19

E. Plug of glass wool

F. Stopcock

Figure 2

image

A. Atmospheric equilibration

B. Flowmeter

C. Microcolumn

D. Thermostatically controlled circulating pump

E. Recirculating pump

F. Two-way valve for sampling

Figure 3

image

A. Levelling vessel (e.g. 2,5 litres chemical flask)

B. Column

C. Fraction accumulator

D. Thermostat

E. Teflon tubing

F. Ground glass joint

G. Water line (between thermostat and column, inner diameter approximately 8 mm)

13. Approximately 600 mg of support material is transferred to a 50 ml round-bottom flask. A suitable amount of test substance is dissolved in a volatile solvent of analytical reagent quality and an appropriate amount of this solution is added to the support material. The solvent is completely evaporated, e.g. using a rotary evaporator, as otherwise water saturation of the support will not be achieved during the elution step because of partitioning on the surface. The loaded support material is soaked for two hours in approximately 5 ml of water and the suspension is poured into the microcolumn. Alternatively, dry loaded support material may be poured into the water-filled microcolumn and two hours are allowed for equilibrating.

14. The loading of the support material may cause problems, leading to erroneous results, e.g. when the test substance is deposited as an oil. These problems should be examined and the details reported.

Procedure using a recirculating pump

15. The flow through the column is started. It is recommended that a flow rate of approximately 25 ml/h, corresponding to 10 bed volumes per hour for the column described, be used. At least the first five bed volumes are discarded to remove water soluble impurities. Following this, the pump is allowed to run until equilibrium is established, as defined by five successive samples whose concentrations do not differ by more than ± 30 % in a random fashion. These samples should be separated from each other by time intervals corresponding to the passage of at least ten bed volumes. Depending on the analytical method used, it may be preferable to establish a concentration/time curve to show that equilibrium is reached.

Procedure using a levelling vessel

16. Successive eluate fractions should be collected and analysed by the chosen method. Fractions from the middle eluate range, where the concentrations are constant within ± 30 % in at least five consecutive fractions, are used to determine the solubility.

17. Double distilled water is the preferred eluent. Deionized water with a resistivity above 10 megohms/cm and total organic carbon content below 0,01 % can also be used.

18. Under both procedures, a second run is performed at half the flow rate of the first. If the results of the two runs are in agreement, the test is satisfactory. If the measured solubility is higher with the lower flow rate, then the halving of the flow rate must continue until two successive runs give the same solubility.

19. Under both procedures, the fractions should be checked for the presence of colloidal matter by examination of the Tyndall effect. The presence of particles invalidates the test and the test should be repeated after improvement of the filtering action of the column.

20. The pH of each sample should be measured, preferably by using special indicator strips.

Flask method

Principle

21. The test substance (solids must be pulverized) is dissolved in water at a temperature somewhat above the test temperature. When saturation is achieved, the mixture is cooled and kept at the test temperature. Alternatively, and if it is assured by appropriate sampling that the saturation equilibrium is reached, the measurement can be performed directly at the test temperature. Subsequently, the mass concentration of the test substance in the aqueous solution, which must not contain any undissolved particles, is determined by a suitable analytical method (3).

Apparatus

22. The following materials are needed:

— 
normal laboratory glassware and instrumentation;
— 
a device for the agitation of solutions under controlled constant temperature;
— 
if required for emulsions, a centrifuge (preferably thermostated); and
— 
analytical equipment.

Procedure

23. The quantity of test substance necessary to saturate the desired volume of water is estimated from the preliminary test. About five times that quantity is weighed into each of three glass vessels fitted with glass stoppers (e.g. centrifuge tubes, flasks). A volume of water, chosen in function of the analytical method and solubility range, is added to each vessel. The vessels are tightly stoppered and then agitated at 30 °C. A shaking or stirring device capable of operating at constant temperature should be used, e.g. magnetic stirring in a thermostated water bath. After one day, one of the vessels is equilibrated for 24 hours at the test temperature with occasional shaking. The contents of the vessel are then centrifuged at the test temperature and the concentration of the test substance in the clear aqueous phase is determined by a suitable analytical method. The other two flasks are treated similarly after initial equilibration at 30 °C for two and three days respectively. If the concentrations measured in at least the two last vessels do not differ by more than 15 %, the test is satisfactory. If the results from vessels 1, 2 and 3 show a tendency of increasing values, the whole test should be repeated using longer equilibration times.

24. The test can also be performed without pre-incubation at 30 °C. In order to estimate the rate of establishment of the saturation equilibrium, samples are taken until the stirring time no longer influences the concentrations measured.

25. The pH of each sample should be measured, preferably by using special indicator strips.

Analytical determinations

26. A substance-specific method is preferred since small amounts of soluble impurities can cause large errors in the measured solubility. Examples of such methods are: gas or liquid chromatography, titration, photometry, voltametry.

DATA AND REPORTING

Data

Column elution method

27. For each run, the mean value and standard deviation from at least five consecutive samples taken from the saturation plateau should be calculated. The mean values obtained from two tests with different flows should not differ by more than 30 %.

Flask method

28. The individual results from each of the three flasks, which should not differ by more than 15 %, are averaged.

Test Report

Column elution method

29. The test report must include the following information:

— 
the results of the preliminary test
— 
chemical identity and impurities (preliminary purification step, if any)
— 
the concentrations, flow rates and pH for each sample
— 
the means and standard deviations from at least five samples from the saturation plateau of each run
— 
the average of at least two successive runs
— 
the temperature of the water during the saturation process
— 
the method of analysis
— 
the nature of the support material
— 
loading of the support material
— 
solvent used
— 
evidence of any chemical instability of the substance during the test
— 
all information relevant for the interpretation of the results, in particular with regard to impurities and physical state of the test substance.

Flask method

30. The test report must include the following information:

— 
the results of the preliminary test
— 
chemical identity and impurities (preliminary purification step, if any)
— 
the individual analytical determinations and the average where more than one value was determined for each flask
— 
the pH of each sample
— 
the average of the values for different flasks which were in agreement
— 
the test temperature
— 
the analytical method
— 
evidence of any chemical instability of the substance during the test
— 
all information relevant for the interpretation of the results, in particular with regard to impurities and physical state of the test substance.

LITERATURE:

(1) 

Commission Directive 92/69/EEC of 31 July 1992 adapting to technical progress for the seventeenth time Council Directive 67/548/EEC on the approximation of laws, regulations and administrative provisions relating to the classification, packaging and labelling of dangerous substances (OJ L 383, 29.12.1992, p. 113).

(2) 

NF T 20-045 (AFNOR) (September 1985). Chemical products for industrial use — Determination of water solubility of solids and liquids with low solubility — Column elution method.

(3) 

NF T 20-046 (AFNOR) (September 1985). Chemical products for industrial use — Determination of water solubility of solids and liquids with high solubility — Flask method.

▼B

A.8.   PARTITION COEFFICIENT

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.9.   FLASH-POINT

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.10.   FLAMMABILITY (SOLIDS)

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.11.   FLAMMABILITY (GASES)

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.12.   FLAMMABILITY (CONTACT WITH WATER)

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.13.   PYROPHORIC PROPERTIES OF SOLIDS AND LIQUIDS

▼M11

The full description of this test method has been deleted. The equivalent international test methods, or other applicable test methods for the endpoints in question, appear in Part 0, Table 1.

▼B

A.14.   EXPLOSIVE PROPERTIES

1.   METHOD

1.1.   INTRODUCTION

The method provides a scheme of testing to determine whether a solid or a pasty substance presents a danger of explosion when submitted to the effect of a flame (thermal sensitivity), or to shock or friction (sensitivity to mechanical stimuli), and whether a liquid substance presents a danger of explosion when submitted to the effect of a flame or shock.

The method comprises three parts:

(a) 

a test of thermal sensitivity (1);

(b) 

a test of mechanical sensitivity with respect to shock (1);

(c) 

a test of mechanical sensitivity with respect to friction (1).

The method yields data to assess the likelihood of initiating an explosion by means of certain common stimuli. The method is not intended to ascertain whether a substance is capable of exploding under any conditions.

The method is appropriate for determining whether a substance will present a danger of explosion (thermal and mechanical sensitivity) under the particular conditions specified in the directive. It is based on a number of types of apparatus which are widely used internationally (1) and which usually give meaningful results. It is recognised that the method is not definitive. Alternative apparatus to that specified may be used provided that it is internationally recognised and the results can be adequately correlated with those from the specified apparatus.

The tests need not be performed when available thermodynamic information (e.g. heat of formation, heat of decomposition) and/or absence of certain reactive groups (2) in the structural formula establishes beyond reasonable doubt that the substance is incapable of rapid decomposition with evolution of gases or release of heat (i.e. the material does not present any risk of explosion). A test of mechanical sensitivity with respect to friction is not required for liquids.

1.2.   DEFINITIONS AND UNITS

Explosive:

Substances which may explode under the effect of flame or which are sensitive to shock or friction in the specified apparatus (or are more mechanically sensitive than 1,3 -dinitrobenzene in alternative apparatus).

1.3.   REFERENCE SUBSTANCES

1,3-dinitrobenzene, technical crystalline product sieved to pass 0,5  mm, for the friction and shock methods.

Perhydro-1,3,5-trinitro-1,3,5-triazine (RDX, hexogen, cyclonite — CAS 121-82-4), recrystallised from aqueous cyclohexanone, wet-sieved through a 250 μm and retained on a 150 μm sieve and dried at 103 ± 2 oC (for four hours) for the second series of friction and shock tests.

1.4.   PRINCIPLE OF THE METHOD

Preliminary tests are necessary to establish safe conditions for the performance of the three tests of sensitivity.

1.4.1.   Safety-in-handling tests (3)

For safety reasons, before performing the main tests, very small samples (circa 10 mg) of the substance are subjected to heating without confinement in a gas flame, to shock in any convenient form of apparatus and to friction by the use of a mallet against an anvil or any form of friction machine. The objective is to ascertain if the substance is so sensitive and explosive that the prescribed sensitivity tests, particularly that of thermal sensitivity, should be performed with special precautions so as to avoid injury to the operator.

1.4.2.   Thermal sensitivity

The method involves heating the substance in a steel tube, closed by orifice plates with differing diameters of hole, to determine whether the substance is liable to explode under conditions of intense heat and defined confinement.

1.4.3.   Mechanical sensitivity (shock)

The method involves subjecting the substance to the shock from a specified mass dropped from a specified height.

1.4.4.   Mechanical sensitivity (friction)

The method involves subjecting solid or pasty substances to friction between standard surfaces under specified conditions of load and relative motion.

1.5.   QUALITY CRITERIA

Not stated.

1.6.   DESCRIPTION OF METHOD

1.6.1.   Thermal sensitivity (effect of a flame)

1.6.1.1.   Apparatus

The apparatus consists of a non-reusable steel tube with its re-usable closing device (figure 1), installed in a heating and protective device. Each tube is deep-drawn from sheet steel (see Appendix) and has an internal diameter of 24 mm, a length of 75 mm and wall thickness of 0,5  mm. The tubes are flanged at the open end to enable them to be closed by the orifice plate assembly. This consists of a pressure-resistant orifice plate, with a central hole, secured firmly to a tube using a two-part screw joint (nut and threaded collar). The nut and threaded collar are made from chromium-manganese steel (see Appendix) which is spark-free up to 800 oC. The orifice plates are 6 mm thick, made from heat-resistant steel (see Appendix), and are available with a range of diameters of opening.

1.6.1.2.   Test conditions

Normally the substance is tested as received although in certain cases, e.g. if pressed, cast or otherwise condensed, it may be necessary to test the substance after crushing.

For solids, the mass of material to be used in each test is determined using a two-stage dry run procedure. A tared tube is filled with 9 cm3 of substance and the substance tamped with 80 N force applied to the total cross-section of the tube. For reasons of safety or in cases where the physical form of the sample can be changed by compression other filling procedures may be used; e.g. if the substance is very friction sensitive then tamping is not appropriate. If the material is compressible then more is added and tamped until the tube is filled to 55 mm from the top. The total mass used to fill the tube to the 55 mm level is determined and two further increments, each tamped with 80 N force, are added. Material is then either added with tamping, or taken out, as required, to leave the tube filled to a level 15 mm from the top. A second dry run is performed, starting with a tamped quantity of a third of the total mass found in the first dry run. Two more of these increments are added with 80 N tamping and the level of the substance in the tube adjusted to 15 mm from the top by addition or subtraction of material as required. The amount of solid determined in the second dry run is used for each trial; filling being performed in three equal amounts, each compressed to 9 cm3 by whatever force is necessary. (This may be facilitated by the use of spacing rings).

Liquids and gels are loaded into the tube to a height of 60 mm taking particular care with gels to prevent the formation of voids. The threaded collar is slipped onto the tube from below, the appropriate orifice plate is inserted and the nut tightened after applying some molybdenum disulphide based lubricant. It is essential to check that none of the substance is trapped between the flange and the plate, or in the threads.

Heating is provided by propane taken from an industrial cylinder, fitted with a pressure regulator (60 to 70 mbar), through a meter and evenly distributed (as indicated by visual observation of the flames from the burners) by a manifold to four burners. The burners are located around the test chamber as shown in figure 1. The four burners have a combined consumption of about 3,2 litres of propane per minute. Alternative fuel gases and burners may be used but the heating rate must be as specified in figure 3. For all apparatus, the heating rate must be checked periodically using tubes filled with dibutyl phthalate as indicated in figure 3.

1.6.1.3.   Performance of the tests

Each test is performed until either the tube is fragmented or the tube has been heated for five minutes. A test resulting in the fragmentation of the tube into three or more pieces, which in some cases may be connected to each other by narrow strips of metal as illustrated in figure 2, is evaluated as giving an explosion. A test resulting in fewer fragments or no fragmentation is regarded as not giving an explosion.

A series of three tests with a 6,0  mm diameter orifice plate is first performed and, if no explosions are obtained, a second series of three tests is performed with a 2,0  mm diameter orifice plate. If an explosion occurs during either test series then no further tests are required.

1.6.1.4.   Evaluation

The test result is considered positive if an explosion occurs in either of the above series of tests.

1.6.2.   Mechanical sensitivity (shock)

1.6.2.1.   Apparatus (figure 4)

The essential parts of a typical fall hammer apparatus are a cast steel block with base, anvil, column, guides, drop weights, release device and a sample holder. The steel anvil 100 mm (diameter) × 70 mm (height) is screwed to the top of a steel block 230 mm (length) × 250 mm (width) × 200 mm (height) with a cast base 450 mm (length) × 450 mm (width) × 60 mm (height). A column, made from seamless drawn steel tube, is secured in a holder screwed on to the back of the steel block. Four screws anchor the apparatus to a solid concrete block 60 × 60 × 60 cm such that the guide rails are absolutely vertical and the drop weight falls freely. 5 and 10 kg weights, made from solid steel, are available for use. The striking head of each weight is of hardened steel, HRC 60 to 63, and has a minimum diameter of 25 mm.

The sample under test is enclosed in a shock device consisting of two coaxial solid steel cylinders, one above the other, in a hollow cylindrical steel guide ring. The solid steel cylinders should be of 10 (- 0,003 , - 0,005 ) mm diameter and 10 mm height and have polished surfaces, rounded edges (radius of curvature 0,5  mm) and a hardness of HRC 58 to 65. The hollow cylinder must have an external diameter of 16 mm, a polished bore of 10 (+ 0,005 , + 0,010 ) mm and a height of 13 mm. The shock device is assembled on an intermediate anvil (26 mm diameter and 26 mm height) made of steel and centred by a ring with perforations to allow escape of fumes.

1.6.2.2.   Test conditions

The sample volume should be 40 mm3, or a volume to suit any alternative apparatus. Solid substances should be tested in the dry state and prepared as follows:

(a) 

powdered substances are sieved (sieve size 0,5  mm); all that has passed through the sieve is used for testing;

(b) 

pressed, cast or otherwise condensed substances are broken into small pieces and sieved; the sieve fraction from 0,5 to 1 mm diameter is used for testing and should be representative of the original substance.

Substances normally supplied as pastes should be tested in the dry state where possible or, in any case, following removal of the maximum possible amount of diluent. Liquid substances are tested with a 1 mm gap between the upper and lower steel cylinders.

1.6.2.3.   Performance of the tests

A series of six tests are performed dropping the 10 kg mass from 0,40  m (40 J). If an explosion is obtained during the six tests at 40 J, a further series of six tests, dropping a 5 kg mass from 0,15  m (7,5  J), must be performed. In other apparatus, the sample is compared with the chosen reference substance using an established procedure (e.g. up-and-down technique etc.).

1.6.2.4.   Evaluation

The test result is considered positive if an explosion (bursting into flame and/or a report is equivalent to explosion) occurs at least once in any of the tests with the specified shock apparatus or the sample is more sensitive than 1,3-dinitrobenzene or RDX in an alternative shock test.

1.6.3.   Mechanical sensitivity (friction)

1.6.3.1.   Apparatus (figure 5)

The friction apparatus consists of a cast steel base plate on which is mounted the friction device. This consists of a fixed porcelain peg and moving porcelain plate. The porcelain plate is held in a carriage which runs in two guides. The carriage is connected to an electric motor via a connecting rod, an eccentric cam and suitable gearing such that the porcelain plate is moved, once only, back and forth beneath the porcelain peg for a distance of 10 mm. The porcelain peg may be loaded with, for example, 120 or 360 newtons.

The flat porcelain plates are made from white technical porcelain (roughness 9 to 32 μm) and have the dimensions 25 mm (length) × 25 mm (width) × 5 mm (height). The cylindrical porcelain peg is also made of white technical porcelain and is 15 mm long, has a diameter of 10 mm and roughened spherical end surfaces with a radius of curvature of 10 mm.

1.6.3.2.   Test conditions

The sample volume should be 10 mm3 or a volume to suit any alternative apparatus.

Solid substances are tested in the dry state and prepared as follows:

(a) 

powdered substances are sieved (sieve size 0,5  mm); all that has passed through the sieve is used for testing;

(b) 

pressed, cast or otherwise condensed substances are broken into small pieces and sieved; the sieve fraction < 0,5  mm diameter is used for testing.

Substances normally supplied as pastes should be tested in the dry state where possible. If the substance cannot be prepared in the dry state, the paste (following removal of the maximum possible amount of diluent) is tested as a 0,5  mm thick, 2 mm wide, 10 mm long film, prepared with a former.

1.6.3.3.   Performance of the tests

The porcelain peg is brought onto the sample under test and the load applied. When carrying out the test, the sponge marks of the porcelain plate must lie transversely to the direction of the movement. Care must be taken that the peg rests on the sample, that sufficient test material lies under the peg and also that the plate moves correctly under the peg. For pasty substances, a 0,5  mm thick gauge with a 2 × 10 mm slot is used to apply the substance to the plate. The porcelain plate has to move 10 mm forwards and backwards under the porcelain peg in a time of 0,44 seconds. Each part of the surface of the plate and peg must only be used once; the two ends of each peg will serve for two trials and the two surfaces of a plate will each serve for three trials.

A series of six tests are performed with a 360 N loading. If a positive event is obtained during these six tests, a further series of six tests must be performed with a 120 N loading. In other apparatus, the sample is compared with the chosen reference substance using an established procedure (e.g. up-and-down technique, etc.).

1.6.3.4.   Evaluation

The test result is considered positive if an explosion (crepitation and/or a report or bursting into flame are equivalent to explosion) occurs at least once in any of the tests with the specified friction apparatus or satisfies the equivalent criteria in an alternative friction test.

2.   DATA

In principle, a substance is considered to present a danger of explosion in the sense of the directive if a positive result is obtained in the thermal, shock or friction sensitivity test.

3.   REPORTING

3.1.   TEST REPORT

The test report shall, if possible, include the following information:

— 
identity, composition, purity, moisture content, etc. of the substance tested,
— 
the physical form of the sample and whether or not it has been crushed, broken and/or sieved,
— 
observations during the thermal sensitivity tests (e.g. sample mass, number of fragments, etc.),
— 
observations during the mechanical sensitivity tests (e.g. formation of considerable amounts of smoke or complete decomposition without a report, flames, sparks, report, crepitation, etc.),
— 
results of each type of test,
— 
if alternative apparatus has been used, scientific justification as well as evidence of correlation between results obtained with specified apparatus and those obtained with equivalent apparatus must be given,
— 
any useful comments such as reference to tests with similar products which might be relevant to a proper interpretation of the results,
— 
all additional remarks relevant for the interpretation of the results.

3.2.   INTERPRETATION AND EVALUATION OF RESULTS

The test report should mention any results which are considered false, anomalous or unrepresentative. If any of the results should be discounted, an explanation and the results of any alternative or supplementary testing should be given. Unless an anomalous result can be explained, it must be accepted at face value and used to classify the substance accordingly.

4.   REFERENCES

(1) Recommendations on the Transport of Dangerous Goods: Tests and criteria, 1990, United Nations, New York.

(2) Bretherick, L., Handbook of Reactive Chemical Hazards, 4th edition, Butterworths, London, ISBN 0-750-60103-5, 1990.

(3) Koenen, H., Ide, K.H. and Swart, K.H., Explosivstoffe, 1961, vol. 3, 6-13 and 30-42.

(4) NF T 20-038 (September 85) Chemical products for industrial use — Determination of explosion risk.

Appendix

Example of material specification for thermal sensitivity test (see DIN 1623)

(1) Tube: Material specification No 1.0336.505 g

(2) Orifice plate: Material specification No 1.4873

(3) Threaded collar and nut: Material specification No 1.3817

Figure 1

Thermal sensitivity test apparatus

(all dimensions in millimetres)

image

Text of image

Figure 2

Thermal sensitivity test

(example of fragmentation)

image

Text of image

Figure 3

Heating rate calibration for thermal sensitivity test

image

Text of image

Temperature/time curve obtained on heating dibutyl phtalate (27 cm3) in a closed (1,5  mm orifice plate) tube using a propane flow rate of 3,2 litre/minute. The temperature is measured with a 1 mm diameter stainless steel sheathed chromel/alumel thermocouple, placed centrally 43 mm below the rim of the tube. The heating rate between 135 oC and 285 oC should be between 185 and 215 K/minute.

Figure 4

Shock test apparatus

(all dimensions in millimetres)

image

Text of image

Figure 4

Continued

image

Text of image

Figure 5

Friction sensitivity apparatus

image

Text of image

A.15.   AUTO-IGNITION TEMPERATURE (LIQUIDS AND GASES)

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.16.   RELATIVE SELF-IGNITION TEMPERATURE FOR SOLIDS

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.17.   OXIDISING PROPERTIES (SOLIDS)

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.18.   NUMBER-AVERAGE MOLECULAR WEIGHT AND MOLECULAR WEIGHT DISTRIBUTION OF POLYMERS

1.   METHOD

This Gel Permeation Chromatographic method is a replicate of the OECD TG 118 (1996). The fundamental principles and further technical information are given in reference (1).

1.1.   INTRODUCTION

Since the properties of polymers are so varied, it is impossible to describe one single method setting out precisely the conditions for separation and evaluation which cover all eventualities and specificities occurring in the separation of polymers. In particular, complex polymer systems are often not amenable to gel permeation chromatography (GPC). When GPC is not practicable, the molecular weight may be determined by means of other methods (see Appendix). In such cases, full details and justification should be given for the method used.

The method described is based on DIN Standard 55672 (1). Detailed information about how to carry out the experiments and how to evaluate the data can be found in this DIN Standard. In case modifications of the experimental conditions are necessary, these changes must be justified. Other standards may be used, if fully referenced. The method described uses polystyrene samples of known polydispersity for calibration and it may have to be modified to be suitable for certain polymers, e.g. water soluble and long-chain branched polymers.

1.2.   DEFINITIONS AND UNITS

The number-average molecular weight Mn and the weight average molecular weight Mw are determined using the following equations:



image

image

where,

Hi is the level of the detector signal from the baseline for the retention volume Vi,

Mi is the molecular weight of the polymer fraction at the retention volume Vi, and

n is the number of data points.

The breadth of the molecular weight distribution, which is a measure of the dispersity of the system, is given by the ratio Mw/Mn.

1.3.   REFERENCE SUBSTANCES

Since GPC is a relative method, calibration must be undertaken. Narrowly distributed, linearly constructed polystyrene standards with known average molecular weights Mn and Mw and a known molecular weight distribution are normally used for this. The calibration curve can only be used in the determination of the molecular weight of the unknown sample if the conditions for the separation of the sample and the standards have been selected in an identical manner.

A determined relationship between the molecular weight and elution volume is only valid under the specific conditions of the particular experiment. The conditions include, above all, the temperature, the solvent (or solvent mixture), the chromatography conditions and the separation column or system of columns.

The molecular weights of the sample determined in this way are relative values and are described as ‘polystyrene equivalent molecular weights’. This means that dependent on the structural and chemical differences between the sample and the standards, the molecular weights can deviate from the absolute values to a greater or a lesser degree. If other standards are used, e.g. polyethylene glycol, polyethylene oxide, polymethyl methacrylate, polyacrylic acid, the reason should be stated.

1.4.   PRINCIPLE OF THE TEST METHOD

Both the molecular weight distribution of the sample and the average molecular weights (Mn, Mw) can be determined using GPC. GPC is a special type of liquid chromatography in which the sample is separated according to the hydrodynamic volumes of the individual constituents (2).

Separation is effected as the sample passes through a column which is filled with a porous material, typically an organic gel. Small molecules can penetrate the pores whereas large molecules are excluded. The path of the large molecules is thereby shorter and these are eluted first. The medium-sized molecules penetrate some of the pores and are eluted later. The smallest molecules, with a mean hydrodynamic radius smaller than the pores of the gel, can penetrate all of the pores. These are eluted last.

In an ideal situation, the separation is governed entirely by the size of the molecular species, but in practice it is difficult to avoid at least some absorption effects interfering. Uneven column packing and dead volumes can worsen the situation (2).

Detection is effected by, e.g. refractive index or UV-absorption, and yields a simple distribution curve. However, to attribute actual molecular weight values to the curve, it is necessary to calibrate the column by passing down polymers of known molecular weight and, ideally, of broadly similar structure e.g. various polystyrene standards. Typically a Gaussian curve results, sometimes distorted by a small tail to the low molecular weight side, the vertical axis indicating the quantity, by weight, of the various molecular weight species eluted, and the horizontal axis the log molecular weight.

1.5.   QUALITY CRITERIA

The repeatability (Relative Standard Deviation: RSD) of the elution volume should be better than 0,3  %. The required repeatability of the analysis has to be ensured by correction via an internal standard if a chromatogram is evaluated time-dependently and does not correspond to the above mentioned criterion (1). The polydispersities are dependent on the molecular weights of the standards. In the case of polystyrene standards typical values are:



Mp < 2 000

Mw/Mn < 1,20

2 000 ≤ Mp ≤ 106

Mw/Mn < 1,05

Mp > 106

Mw/Mn < 1,20

(Mp is the molecular weight of the standard at the peak maximum)

1.6.   DESCRIPTION OF THE TEST METHOD

1.6.1.   Preparation of the standard polystyrene solutions

The polystyrene standards are dissolved by careful mixing in the chosen eluent. The recommendations of the manufacturer must be taken into account in the preparation of the solutions.

The concentrations of the standards chosen are dependent on various factors, e.g. injection volume, viscosity of the solution and sensitivity of the analytical detector. The maximum injection volume must be adapted to the length of the column, in order to avoid overloading. Typical injection volumes for analytical separations using GPC with a column of 30 cm × 7,8  mm are normally between 40 and 100 μl. Higher volumes are possible, but they should not exceed 250 μl. The optimal ratio between the injection volume and the concentration must be determined prior to the actual calibration of the column.

1.6.2.   Preparation of the sample solution

In principle, the same requirements apply to the preparation of the sample solutions. The sample is dissolved in a suitable solvent, e.g. tetrahydrofuran (THF), by shaking carefully. Under no circumstances should it be dissolved using an ultrasonic bath. When necessary, the sample solution is purified via a membrane filter with a pore size of between 0,2 and 2 μm.

The presence of undissolved particles must be recorded in the final report as these may be due to high molecular weight species. An appropriate method should be used to determine the percentage by weight of the undissolved particles. The solutions should be used within 24 hours.

1.6.3.   Apparatus

— 
solvent reservoir,
— 
degasser (where appropriate),
— 
pump,
— 
pulse dampener (where appropriate),
— 
injection system,
— 
chromatography columns,
— 
detector,
— 
flowmeter (where appropriate),
— 
data recorder-processor,
— 
waste vessel.

It must be ensured that the GPC system is inert with regard to the utilised solvents (e.g. by the use of steel capillaries for THF solvent).

1.6.4.   Injection and solvent delivery system

A defined volume of the sample solution is loaded onto the column either using an auto-sampler or manually in a sharply defined zone. Withdrawing or depressing the plunger of the syringe too quickly, if done manually, can cause changes in the observed molecular weight distribution. The solvent-delivery system should, as far as possible, be pulsation-free ideally incorporating a pulse dampener. The flow rate is of the order of 1 ml/min.

1.6.5.   Column

Depending on the sample, the polymer is characterised using either a simple column or several columns connected in sequence. A number of porous column materials with defined properties (e.g. pore size, exclusion limits) are commercially available. Selection of the separation gel or the length of the column is dependent on both the properties of the sample (hydrodynamic volumes, molecular weight distribution) and the specific conditions for separation such as solvent, temperature and flow rate (1)(2)(3).

1.6.6.   Theoretical plates

The column or the combination of columns used for separation must be characterised by the number of theoretical plates. This involves, in the case of THF as elution solvent, loading a solution of ethyl benzene or other suitable non-polar solute onto a column of known length. The number of theoretical plates is given by the following equation:



image

or

image

where,

N

=

the number of theoretical plates

Ve

=

the elution volume at the peak maximum

W

=

the baseline peak width

W1/2

=

the peak width at half height

1.6.7.   Separation efficiency

In addition to the number of theoretical plates, which is a quantity determining the bandwidth, a part is also played by the separation efficiency, this being determined by the steepness of the calibration curve. The separation efficiency of a column is obtained from the following relationship:

image

where,

Ve, Mx

=

the elution volume for polystyrene with the molecular weight Mx

Ve,(10.Mx)

=

the elution volume for polystyrene with a ten times greater molecular weight

The resolution of the system is commonly defined as follows:

image

where,

Ve1, Ve2

=

the elution volumes of the two polystyrene standards at the peak maximum

W1, W2

=

the peak widths at the base-line

M1, M2

=

the molecular weights at the peak maximum (should differ by a factor of 10)

The R-value for the column system should be greater than 1.7 (4).

1.6.8.   Solvents

All solvents must be of high purity (for THF purity of 99,5  % is used). The solvent reservoir (if necessary in an inert gas atmosphere) must be sufficiently large for the calibration of the column and several sample analyses. The solvent must be degassed before it is transported to the column via the pump.

1.6.9.   Temperature control

The temperature of the critical internal components (injection loop, columns, detector and tubing) should be constant and consistent with the choice of solvent.

1.6.10.   Detector

The purpose of the detector is to record quantitatively the concentration of sample eluted from the column. In order to avoid unnecessary broadening of peaks the cuvette volume of the detector cell must be kept as small as possible. It should not be larger than 10 μl except for light scattering and viscosity detectors. Differential refractometry is usually used for detection. However, if required by the specific properties of the sample or the elution solvent, other types of detectors can be used, e.g. UV/VIS, IR, viscosity detectors, etc.

2.   DATA AND REPORTING

2.1.   DATA

The DIN Standard (1) should be referred to for the detailed evaluation criteria as well as for the requirements relating to the collecting and processing of data.

For each sample, two independent experiments must be carried out. They have to be analysed individually.

Mn, Mw, Mw/Mn and Mp must be provided for every measurement. It is necessary to indicate explicitly that the measured values are relative values equivalent to the molecular weights of the standard used.

After determination of the retention volumes or the retention times (possibly corrected using an internal standard), log Mp values (Mp being the peak maxima of the calibration standard) are plotted against one of those quantities. At least two calibration points are necessary per molecular weight decade, and at least five measurement points are required for the total curve, which should cover the estimated molecular weight of the sample. The low molecular weight end-point of the calibration curve is defined by n-hexyl benzene or another suitable non-polar solute. The number average and the weight-average molecular weights are generally determined by means of electronic data processing, based on the formulas of section 1.2. In case manual digitisation is used, ASTM D 3536-91 can be consulted (3).

The distribution curve must be provided in the form of a table or as figure (differential frequency or sum percentages against log M). In the graphic representation, one molecular weight decade should be normally about 4 cm in width and the peak maximum should be about 8 cm in height. In the case of integral distribution curves the difference in the ordinate between 0 and 100 % should be about 10 cm.

2.2.   TEST REPORT

The test report must include the following information:

2.2.1.   Test substance:

— 
available information about test substance (identity, additives, impurities),
— 
description of the treatment of the sample, observations, problems.

2.2.2.   Instrumentation:

— 
reservoir of eluent, inert gas, degassing of the eluent, composition of the eluent, impurities,
— 
pump, pulse dampener, injection system,
— 
separation columns (manufacturer, all information about the characteristics of the columns, such as pore size, kind of separation material, etc., number, length and order of the columns used),
— 
number of the theoretical plates of the column (or combination), separation efficiency (resolution of the system),
— 
information on symmetry of the peaks,
— 
column temperature, kind of temperature control,
— 
detector (measurement principle, type, cuvette volume),
— 
flowmeter if used (manufacturer, measurement principle),
— 
system to record and process data (hardware and software).

2.2.3.   Calibration of the system:

— 
detailed description of the method used to construct the calibration curve,
— 
information about quality criteria for this method (e.g. correlation coefficient, error sum of squares, etc.),
— 
information about all extrapolations, assumptions and approximations made during the experimental procedure and the evaluation and processing of data,
— 
all measurements used for constructing the calibration curve have to be documented in a table which includes the following information for each calibration point:
— 
name of the sample,
— 
manufacturer of the sample,
— 
characteristic values of the standards Mp, Mn, Mw, Mw/Mn, as provided by the manufacturer or derived by subsequent measurements, together with details about the method of determination,
— 
injection volume and injection concentration,
— 
Mp value used for calibration,
— 
elution volume or corrected retention time measured at the peak maxima,
— 
Mp calculated at the peak maximum,
— 
percentage error of the calculated Mp and the calibration value.

2.2.4.   Evaluation:

— 
evaluation on a time basis: methods used to ensure the required reproducibility (method of correction, internal standard, etc.),
— 
information about whether the evaluation was effected on the basis of the elution volume or the retention time,
— 
information about the limits of the evaluation if a peak is not completely analysed,
— 
description of smoothing methods, if used,
— 
preparation and pre-treatment procedures of the sample,
— 
the presence of undissolved particles, if any,
— 
injection volume (μl) and injection concentration (mg/ml),
— 
observations indicating effects which lead to deviations from the ideal GPC profile,
— 
detailed description of all modifications in the testing procedures,
— 
details of the error ranges,
— 
any other information and observations relevant for the interpretation of the results.

3.   REFERENCES

(1) DIN 55672(1995) Gelpermeationschromatographie (GPC) mit Tetrahydrofuran (THF) als Elutionsmittel, Teil 1.

(2) Yau, W.W., Kirkland, J.J., and Bly, D.D. eds., (1979) Modern Size Exclusion Liquid Chromatography, J. Wiley and Sons.

(3) ASTM D 3536-91, (1991). Standard Test Method for Molecular Weight Averages and Molecular Weight Distribution by Liquid Exclusion Chromatography (Gel Permeation Chromatography-GPC) American Society for Testing and Materials, Philadelphia, Pennsylvania.

(4) ASTM D 5296-92, (1992) Standard Test Method for Molecular Weight Averages and Molecular Weight Distribution of Polystyrene by High Performance Size-Exclusion Chromatography. American Society for Testing and Materials, Philadelphia, Pennsylvania.

Appendix

Examples of other methods for determination of number average molecular weight (Mn) for polymers

Gel permeation chromatography (GPC) is the preferred method for determination of Mn, especially when a set of standards are available, whose structure are comparable with the polymer structure. However, where there are practical difficulties in using GPC or there is already an expectation that the substance will fail a regulatory Mn criterion (and which needs confirming), alternative methods are available, such as:

1.   Use of colligative properties

1.1. Ebullioscopy/Cryoscopy

involves measurement of boiling point elevation (ebullioscopy) or freezing point depression (cryoscopy) of a solvent, when the polymer is added. The method relies on the fact that the effect of the dissolved polymer on the boiling/freezing point of the liquid is dependent on the molecular weight of the polymer (1) (2).

Applicability, Mn < 20 000 .

1.2. Lowering of vapour pressure

involves the measurement of the vapour pressure of a chosen reference liquid before and after the addition of known quantities of polymer (1) (2).

Applicability, Mn < 20 000 (theoretically; in practice however of limited value).

1.3 Membrane osmometry

relies on the principle of osmosis, i.e. the natural tendency of solvent molecules to pass through a semi-permeable membrane from a dilute to a concentrated solution to achieve equilibrium. In the test, the dilute solution is at zero concentration, whereas the concentrated solution contains the polymer. The effect of drawing solvent through the membrane causes a pressure differential that is dependent on the concentration and the molecular weight of the polymer (1) (3) (4).

Applicability, Mn between 20 000 - 200 000 .

1.4 Vapour phase osmometry

involves comparison of the rate of evaporation of a pure solvent aerosol to at least three aerosols containing the polymer at different concentrations (1)(2)(4).

Applicability, Mn < 20 000 .

2.   End-group analysis

To use this method, knowledge of both the overall structure of the polymer and the nature of the chain terminating end groups is needed (which must be distinguishable from the main skeleton by, e.g. NMR or titration/derivatisation). The determination of the molecular concentration of the end groups present on the polymer can lead to a value for the molecular weight (7) (8) (9).

Applicability, Mn up to 50 000 (with decreasing reliability).

3.   References

(1) Billmeyer, F.W. Jr., (1984) Textbook of Polymer Science, 3rd Edn., John Wiley, New York.

(2) Glover, C.A., (1975) Absolute Colligative Property Methods. Chapter 4. In: Polymer Molecular Weights, Part I P.E. Slade, Jr. ed., Marcel Dekker, New York.

(3) ASTM D 3750-79, (1979) Standard Practice for Determination of Number-Average Molecular Weight of Polymers by Membrane Osmometry. American Society for Testing and Materials, Philadelphia, Pennsylvania.

(4) Coll, H. (1989) Membrane Osmometry. In: Determination of Molecular Weight, A.R. Cooper ed., J. Wiley and Sons, pp. 25-52.

(5) ASTM 3592-77, (1977) Standard Recommended Practice for Determination of Molecular Weight by Vapour Pressure, American Society for Testing and Materials, Philadelphia, Pennsylvania.

(6) Morris, C.E.M., (1989) Vapour Pressure Osmometry. In: Determinationn of Molecular Weight, A.R. Cooper ed., John Wiley and Sons.

(7) Schröder, E., Müller, G., and Arndt, K-F., (1989) Polymer Characterisation, Carl Hanser Verlag, Munich.

(8) Garmon, R.G., (1975) End-Group Determinations, Chapter 3 In: Polymer Molecular Weights, Part I, P.E. Slade, Jr. ed., Marcel Dekker, New York.

(9) Amiya, S., et al. (1990) Pure and Applied Chemistry, 62, 2139-2146.

A.19.   LOW MOLECULAR WEIGHT CONTENT OF POLYMERS

1.   METHOD

This Gel Permeation Chromatographic method is a replicate of the OECD TG 119 (1996). The fundamental principles and further technical information are given in the references.

1.1.   INTRODUCTION

Since the properties of polymers are so varied, it is impossible to describe one single method setting out precisely the conditions for separation and evaluation which cover all eventualities and specificities occurring in the separation of polymers. In particular, complex polymer systems are often not amenable to gel permeation chromatography (GPC). When GPC is not practicable, the molecular weight may be determined by means of other methods (see Appendix). In such cases, full details and justification should be given for the method used.

The method described is based on DIN Standard 55672 (1). Detailed information about how to carry out the experiments and how to evaluate the data can be found in this DIN Standard. In case modifications of the experimental conditions are necessary, these changes must be justified. Other standards may be used, if fully referenced. The method described uses polystyrene samples of known polydispersity for calibration and it may have to be modified to be suitable for certain polymers, e.g. water soluble and long-chain branched polymers.

1.2.   DEFINITIONS AND UNITS

Low molecular weight is arbitrarily defined as a molecular weight below 1 000 dalton.

The number-average molecular weight Mn and the weight average molecular weight Mw are determined using the following equations:



image

image

where,

Hi

=

the level of the detector signal from the baseline for the retention volume Vi,

Mi

=

the molecular weight of the polymer fraction at the retention volume Vi, and n is the number of data points

The breadth of the molecular weight distribution, which is a measure of the dispersity of the system, is given by the ratio Mw/Mn.

1.3.   REFERENCE SUBSTANCES

Since GPC is a relative method, calibration must be undertaken. Narrowly distributed, linearly constructed polystyrene standards with known average molecular weights Mn and Mw and a known molecular weight distribution are normally used for this. The calibration curve can only be used in the determination of the molecular weight of the unknown sample if the conditions for the separation of the sample and the standards have been selected in an identical manner.

A determined relationship between the molecular weight and elution volume is only valid under the specific conditions of the particular experiment. The conditions include, above all, the temperature, the solvent (or solvent mixture), the chromatography conditions and the separation column or system of columns.

The molecular weights of the sample determined in this way are relative values and are described as ‘polystyrene equivalent molecular weights’. This means that dependent on the structural and chemical differences between the sample and the standards, the molecular weights can deviate from the absolute values to a greater or a lesser degree. If other standards are used, e.g. polyethylene glycol, polyethylene oxide, polymethyl methacrylate, polyacrylic acid, the reason should be stated.

1.4.   PRINCIPLE OF THE TEST METHOD

Both the molecular weight distribution of the sample and the average molecular weights (Mn, Mw) can be determined using GPC. GPC is a special type of liquid chromatography in which the sample is separated according to the hydrodynamic volumes of the individual constituents (2).

Separation is effected as the sample passes through a column which is filled with a porous material, typically an organic gel. Small molecules can penetrate the pores whereas large molecules are excluded. The path of the large molecules is thereby shorter and these are eluted first. The medium-sized molecules penetrate some of the pores and are eluted later. The smallest molecules, with a mean hydrodynamic radius smaller than the pores of the gel, can penetrate all of the pores. These are eluted last.

In an ideal situation, the separation is governed entirely by the size of the molecular species, but in practice it is difficult to avoid at least some absorption effects interfering. Uneven column packing and dead volumes can worsen the situation (2).

Detection is effected by e.g. refractive index or UV-absorption and yields a simple distribution curve. However, to attribute actual molecular weight values to the curve, it is necessary to calibrate the column by passing down polymers of known molecular weight and, ideally, of broadly similar structure, e.g. various polystyrene standards. Typically a Gaussian curve results, sometimes distorted by a small tail to the low molecular weight side, the vertical axis indicating the quantity, by weight, of the various molecular weight species eluted, and the horizontal axis the log molecular weight.

The low molecular weight content is derived from this curve. The calculation can only be accurate if the low molecular weight species respond equivalently on a per mass basis to the polymer as a whole.

1.5.   QUALITY CRITERIA

The repeatability (Relative Standard Deviation: RSD) of the elution volume should be better than 0,3  %. The required repeatability of the analysis has to be ensured by correction via an internal standard if a chromatogram is evaluated time-dependently and does not correspond to the above mentioned criterion (1). The polydispersities are dependent on the molecular weights of the standards. In the case of polystyrene standards typical values are:



Mp < 2 000

Mw/Mn < 1,20

2 000 < Mp < 106

Mw/Mn < 1,05

Mp > 106

Mw/Mn < 1,20

(Mp is the molecular weight of the standard at the peak maximum)

1.6.   DESCRIPTION OF THE TEST METHOD

1.6.1.   Preparation of the standard polystyrene solutions

The polystyrene standards are dissolved by careful mixing in the chosen eluent. The recommendations of the manufacturer must be taken into account in the preparation of the solutions.

The concentrations of the standards chosen are dependent on various factors, e.g. injection volume, viscosity of the solution and sensitivity of the analytical detector. The maximum injection volume must be adapted to the length of the column, in order to avoid overloading. Typical injection volumes for analytical separations using GPC with a column of 30 cm × 7,8  mm are normally between 40 and 100 μl. Higher volumes are possible, but they should not exceed 250 μl. The optimal ratio between the injection volume and the concentration must be determined prior to the actual calibration of the column.

1.6.2.   Preparation of the sample solution

In principle, the same requirements apply to the preparation of the sample solutions. The sample is dissolved in a suitable solvent, e.g. tetrahydrofuran (THF), by shaking carefully. Under no circumstances should it be dissolved using an ultrasonic bath. When necessary, the sample solution is purified via a membrane filter with a pore size of between 0,2 and 2 μm.

The presence of undissolved particles must be recorded in the final report as these may be due to high molecular weight species. An appropriate method should be used to determine the percentage by weight of the undissolved particles. The solutions should be used within 24 hours.

1.6.3.   Correction for content of impurities and additives

Correction of the content of species of M < 1 000 for the contribution from non-polymer specific components present (e.g. impurities and/or additives) is usually necessary, unless the measured content is already < 1 %. This is achieved by direct analysis of the polymer solution or the GPC eluate.

In cases where the eluate, after passage through the column, is too dilute for a further analysis it must be concentrated. It may be necessary to evaporate the eluate to dryness and dissolve it again. Concentration of the eluate must be effected under conditions which ensure that no changes occur in the eluate. The treatment of the eluate after the GPC step is dependent on the analytical method used for the quantitative determination.

1.6.4.   Apparatus

GPC apparatus comprises the following components:

— 
solvent reservoir,
— 
degasser (where appropriate),
— 
pump,
— 
pulse dampener (where appropriate),
— 
injection system,
— 
chromatography columns,
— 
detector,
— 
flowmeter (where appropriate),
— 
data recorder-processor,
— 
waste vessel.

It must be ensured that the GPC system is inert with regard to the utilised solvents (e.g. by the use of steel capillaries for THF solvent).

1.6.5.   Injection and solvent delivery system

A defined volume of the sample solution is loaded onto the column either using an auto-sampler or manually in a sharply defined zone. Withdrawing or depressing the plunger of the syringe too quickly, if done manually, can cause changes in the observed molecular weight distribution. The solvent-delivery system should, as far as possible, be pulsation-free ideally incorporating a pulse dampener. The flow rate is of the order of 1 ml/min.

1.6.6.   Column

Depending on the sample, the polymer is characterised using either a simple column or several columns connected in sequence. A number of porous column materials with defined properties (e.g. pore size, exclusion limits) are commercially available. Selection of the separation gel or the length of the column is dependent on both the properties of the sample (hydrodynamic volumes, molecular weight distribution) and the specific conditions for separation such as solvent, temperature and flow rate (1) (2) (3).

1.6.7.   Theoretical plates

The column or the combination of columns used for separation must be characterised by the number of theoretical plates. This involves, in the case of THF as elution solvent, loading a solution of ethyl benzene or other suitable non-polar solute onto a column of known length. The number of theoretical plates is given by the following equation:



image

or

image

where,

N

=

the number of theoretical plates

Ve

=

the elution volume at the peak maximum

W

=

the baseline peak width

W1/2

=

the peak width at half height

1.6.8.   Separation efficiency

In addition to the number of theoretical plates, which is a quantity determining the bandwidth, a part is also played by the separation efficiency, this being determined by the steepness of the calibration curve. The separation efficiency of a column is obtained from the following relationship:

image

where,

Ve, Mx

=

the elution volume for polystyrene with the molecular weight Mx

Ve,(10.Mx)

=

the elution volume for polystyrene with a ten times greater molecular weight

The resolution of the system is commonly defined as follows:

image

where,

Ve1, Ve2

=

the elution volumes of the two polystyrene standards at the peak maximum

W1, W2

=

the peak widths at the base-1ine

M1, M2

=

the molecular weights at the peak maximum (should differ by a factor of 10).

The R-value for the column system should be greater than 1,7 (4).

1.6.9.   Solvents

All solvents must be of high purity (for THF purity of 99,5  % is used). The solvent reservoir (if necessary in an inert gas atmosphere) must be sufficiently large for the calibration of the column and several sample analyses. The solvent must be degassed before it is transported to the column via the pump.

1.6.10.   Temperature control

The temperature of the critical internal components (injection loop, columns, detector and tubing) should be constant and consistent with the choice of solvent.

1.6.11.   Detector

The purpose of the detector is to record quantitatively the concentration of sample eluted from the column. In order to avoid unnecessary broadening of peaks the cuvette volume of the detector cell must be kept as small as possible. It should not be larger than 10 μl except for light scattering and viscosity detectors. Differential refractometry is usually used for detection. However, if required by the specific properties of the sample or the elution solvent, other types of detectors can be used, e.g. UV/VIS, IR, viscosity detectors, etc.

2.   DATA AND REPORTING

2.1.   DATA

The DIN Standard (1) should be referred to for the detailed evaluation criteria as well as for the requirements relating to the collecting and processing of data.

For each sample, two independent experiments must be carried out. They have to be analysed individually. In all cases it is essential to determine also data from blanks, treated under the same conditions as the sample.

It is necessary to indicate explicitly that the measured values are relative values equivalent to the molecular weights of the standard used.

After determination of the retention volumes or the retention times (possibly corrected using an internal standard), log Mp values (Mp being the peak maxima of the calibration standard) are plotted against one of those quantities. At least two calibration points are necessary per molecular weight decade, and at least five measurement points are required for the total curve, which should cover the estimated molecular weight of the sample. The low molecular weight end-point of the calibration curve is defined by n-hexyl benzene or another suitable non-polar solute. The portion of the curve corresponding to molecular weights below 1 000 is determined and corrected as necessary for impurities and additives. The elution curves are generally evaluated by means of electronic data processing. In case manual digitisation is used, ASTM D 3536-91 can be consulted (3).

If any insoluble polymer is retained on the column, its molecular weight is likely to be higher than that of the soluble fraction, and if not considered would result in an overestimation of the low molecular weight content. Guidance for correcting the low molecular weight content for insoluble polymer is provided in the Appendix.

The distribution curve must be provided in the form of a table or as figure (differential frequency or sum percentages against log M). In the graphic representation, one molecular weight decade should be normally about 4 cm in width and the peak maximum should be about 8 cm in height. In the case of integral distribution curves the difference in the ordinate between 0 and 100 % should be about 10 cm.

2.2.   TEST REPORT

The test report must include the following information:

2.2.1.   Test substance:

— 
available information about test substance (identity, additives, impurities),
— 
description of the treatment of the sample, observations, problems.

2.2.2.   Instrumentation:

— 
reservoir of eluent, inert gas, degassing of the eluent, composition of the eluent, impurities,
— 
pump, pulse dampener, injection system,
— 
separation columns (manufacturer, all information about the characteristics of the columns, such as pore size, kind of separation material, etc., number, length and order of the columns used),
— 
number of the theoretical plates of the column (or combination), separation efficiency (resolution of the system),
— 
information on symmetry of the peaks,
— 
column temperature, kind of temperature control,
— 
detector (measurement principle, type, cuvette volume),
— 
flowmeter if used (manufacturer, measurement principle),
— 
system to record and process data (hardware and software).

2.2.3.   Calibration of the system:

— 
detailed description of the method used to construct the calibration curve,
— 
information about quality criteria for this method (e.g. correlation coefficient, error sum of squares, etc.),
— 
information about all extrapolations, assumptions and approximations made during the experimental procedure and the evaluation and processing of data,
— 
all measurements used for constructing the calibration curve have to be documented in a table which includes the following information for each calibration point:
— 
name of the sample,
— 
manufacturer of the sample,
— 
characteristic values of the standards Mp, Mn, Mw, Mw/Mn, as provided by the manufacturer or derived by subsequent measurements, together with details about the method of determination,
— 
injection volume and injection concentration,
— 
Mp value used for calibration,
— 
elution volume or corrected retention time measured at the peak maxima,
— 
Mp calculated at the peak maximum,
— 
percentage error of the calculated Mp and the calibration value.

2.2.4.   Information on the low molecular weight polymer content:

— 
description of the methods used in the analysis and the way in which the experiments were conducted,
— 
information about the percentage of the low molecular weight species content (w/w) related to the total sample,
— 
information about impurities, additives and other non-polymer species in percentage by weight related to the total sample.

2.2.5.   Evaluation:

— 
evaluation on a time basis: all methods to ensure the required reproducibility (method of correction, internal standard etc.),
— 
information about whether the evaluation was effected on the basis of the elution volume or the retention time,
— 
information about the limits of the evaluation if a peak is not completely analysed,
— 
description of smoothing methods, if used,
— 
preparation and pre-treatment procedures of the sample,
— 
the presence of undissolved particles, if any,
— 
injection volume (μl) and injection concentration (mg/ml),
— 
observations indicating effects which lead to deviations from the ideal GPC profile,
— 
detailed description of all modifications in the testing procedures,
— 
details of the error ranges,
— 
any other information and observations relevant for the interpretation of the results.

3.   REFERENCES

(1) DIN 55672 (1995) Gelpermeationschromatographie (GPC) mit Tetrahydrofuran (THF) als Elutionsmittel, Teil 1.

(2) Yau, W.W., Kirkland, J.J., and Bly, D.D. eds. (1979) Modern Size Exclusion Liquid Chromatography, J. Wiley and Sons.

(3) ASTM D 3536-91, (1991) Standard Test method for Molecular Weight Averages and Molecular Weight Distribution by Liquid Exclusion Chromatography (Gel Permeation Chromatography-GPC). American Society for Testing and Materials, Philadelphia, Pennsylvania.

(4) ASTM D 5296-92, (1992) Standard Test method for Molecular Weight Averages and Molecular Weight Distribution of Polystyrene by High Performance Size-Exclusion Chromatography. American Society for Testing and Materials, Philadelphia, Pennsylvania.

Appendix

Guidance for correcting low molecular content for the presence of insoluble polymer

When insoluble polymer is present in a sample, it results in mass loss during the GPC analysis. The insoluble polymer is irreversibly retained on the column or sample filter while the soluble portion of the sample passes through the column. In the case where the refractive index increment (dn/dc) of the polymer can be estimated or measured, one can estimate the sample mass lost on the column. In that case, one makes a correction using an external calibration with standard materials of known concentration and dn/dc to calibrate the response of the refractometer. In the example hereafter a poly(methyl methacrylate) (pMMA) standard is used.

In the external calibration for analysis of acrylic polymers, a pMMA standard of known concentration in tetrahydrofuran, is analysed by GPC and the resulting data are used to find the refractometer constant according to the equation:

K = R/(C × V × dn/dc)

where:

K

=

the refractometer constant (in microvolt second/ml),

R

=

the response of the pMMA standard (in microvolt/second),

C

=

the concentration of the pMMA standard (in mg/ml),

V

=

the injection volume (in ml), and

dn/dc

=

the refractive index increment for pMMA in tetrahydrofuran (in ml/mg).

The following data are typical for a pMMA standard:

R

=

2 937 891

C

=

1,07  mg/ml

V

=

0,1  ml

dn/dc

=

9 × 10-5 ml/mg

The resulting K value, 3,05  × 1011 is then used to calculate the theoretical detector response if 100 % of the polymer injected had eluted through the detector.

A.20.   SOLUTION/EXTRACTION BEHAVIOUR OF POLYMERS IN WATER

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼B

A.21.   OXIDISING PROPERTIES (LIQUIDS)

▼M9

The full description of this test method has been deleted. The equivalent international test method, or other applicable test methods for the endpoint in question, appear in Table 1 of Part 0.

▼M1

A.22.   LENGTH WEIGHTED GEOMETRIC MEAN DIAMETER OF FIBRES

1.   METHOD

1.1.   INTRODUCTION

This method describes a procedure to measure the Length Weighted Geometric Mean Diameter (LWGMD) of bulk Man Made Mineral Fibres (MMMF). As the LWGMD of the population will have a 95 % probability of being between the 95 % confidence levels (LWGMD ± two standard errors) of the sample, the value reported (the test value) will be the lower 95 % confidence limit of the sample (i.e. LWGMD — 2 standard errors). The method is based on an update (June 1994) of a draft HSE industry procedure agreed at a meeting between ECFIA and HSE at Chester on 26/9/93 and developed for and from a second inter-laboratory trial (1, 2). This measurement method can be used to characterise the fibre diameter of bulk substances or products containing MMMFs including refractory ceramic fibres (RCF), man-made vitreous fibres (MMVF), crystalline and polycrystalline fibres.

Length weighting is a means of compensating for the effect on the diameter distribution caused by the breakage of long fibres when sampling or handling the material. Geometric statistics (geometric mean) are used to measure the size distribution of MMMF diameters because these diameters usually have size distributions that approximate to log normal.

Measuring length as well as diameter is both tedious and time consuming but, if only those fibres that touch an infinitely thin line on a SEM field of view are measured, then the probability of selecting a given fibre is proportional to its length. As this takes care of the length in the length weighting calculations, the only measurement required is the diameter and the LWGMD-2SE can be calculated as described.

1.2.   DEFINITIONS

Particle: An object with a length to width ratio of less than 3:1.

Fibre: An object with a length to with ratio (aspect ratio) of at least 3:1.

1.3.   SCOPE AND LIMITATIONS

The method is designed to look at diameter distributions which have median diameters from 0,5 μm to 6 μm. Larger diameters can be measured by using lower SEM magnifications but the method will be increasingly limited for finer fibre distributions and a TEM (transmission electron microscope) measurement is recommended if the median diameter is below 0,5 μm.

1.4.   PRINCIPLE OF THE TEST METHOD

A number of representative core samples are taken from the fibre blanket or from loose bulk fibre. The bulk fibres are reduced in length using a crushing procedure and a representative sub-sample dispersed in water. Aliquots are extracted and filtered through a 0,2 μm pore size, polycarbonate filter and prepared for examination using scanning electron microscope (SEM) techniques. The fibre diameters are measured at a screen magnification of × 10 000 or greater ( 1 ) using a line intercept method to give an unbiased estimate of the median diameter. The lower 95 % confidence interval (based on a one sided test) is calculated to give an estimate of the lowest value of the geometric mean fibre diameter of the material.

1.5.   DESCRIPTION OF THE TEST METHOD

1.5.1.   Safety/precautions

Personal exposure to airborne fibres should be minimised and a fume cupboard or glove box should be used for handling the dry fibres. Periodic personal exposure monitoring should be carried out to determine the effectiveness of the control methods. When handling MMMF’s disposable gloves should be worn to reduce skin irritation and to prevent cross-contamination.

1.5.2.   Apparatus/equipment

— 
Press and dyes (capable of producing 10 MPa).
— 
0,2 μm pore size polycarbonate capillary pore filters (25 mm diameter).
— 
5 μm pore size cellulose ester membrane filter for use as a backing filter.
— 
Glass filtration apparatus (or disposable filtration systems) to take 25 mm diameter filters (e.g. Millipore glass microanalysis kit, type No XX10 025 00).
— 
Freshly distilled water that has been filtered through a 0,2 μm pore size filter to remove micro-organisms.
— 
Sputter coater with a gold or gold/palladium target.
— 
Scanning electron microscope capable of resolving down to 10 nm and operating at × 10 000 magnification.
— 
Miscellaneous: spatulas, type 24 scalpel blade, tweezers, SEM tubes, carbon glue or carbon adhesive tape, silver dag.
— 
Ultrasonic probe or bench top ultrasonic bath.
— 
Core sampler or cork borer, for taking core samples from MMMF blanket.

1.5.3.   Test Procedure

1.5.3.1.   Sampling

For blankets and bats a 25 mm core sampler or cork borer is used to take samples of the cross-section. These should be equally spaced across the width of a small length of the blanket or taken from random areas if long lengths of the blanket are available. The same equipment can be used to extract random samples from loose fibre. Six samples should be taken when possible, to reflect spatial variations in the bulk material.

The six core samples should be crushed in a 50 mm diameter dye at 10 MPa. The material is mixed with spatula and re-pressed at 10 MPa. The material is then removed from the dye and stored in a sealed glass bottle.

1.5.3.2.   Sample Preparation

If necessary, organic binder can be removed by placing the fibre inside a furnace at 450 °C for about one hour.

Cone and quarter to subdivide the sample (this should be done inside a dust cupboard).

Using a spatula, add a small amount (< 0,5 g) of sample to 100 ml of freshly distilled water that has been filtered through a 0,2 μm membrane filter (alternative sources of ultra pure water may be used if they are shown to be satisfactory). Disperse thoroughly by the use of an ultrasonic probe operated at 100 W power and tuned so that cavitation occurs. (If a probe is not available use the following method: repeatedly shake and invert for 30 seconds; ultrasonic in a bench top ultrasonic bath for five minutes; then repeatedly shake and invert for a further 30 seconds.)

Immediately after dispersion of the fibre, remove a number of aliquots (e.g. three aliquots of 3, 6 and 10 ml) using a wide-mouthed pipette (2-5 ml capacity).

Vacuum filter each aliquot through a 0,2 μm polycarbonate filter supported by a 5 μm pore MEC backing filter, using a 25 mm glass filter funnel with a cylindrical reservoir. Approximately 5 ml of filtered distilled water should be placed into the funnel and the aliquot slowly pipetted into the water holding the pipette tip below the meniscus. The pipette and the reservoir must be flushed thoroughly after pipetting, as thin fibres have a tendency to be located more on the surface.

Carefully remove the filter and separate it from the backing filter before placing it in a container to dry.

Cut a quarter or half filter section of the filtered deposit with a type 24 scalpel blade using a rocking action. Carefully attach the cut section to a SEM stub using a sticky carbon tab or carbon glue. Silver dag should be applied in at least three positions to improve the electrical contact at the edges of the filter and the stub. When the glue/silver dag is dry, sputter coat approximately 50 nm of gold or gold/palladium onto the surface of the deposit.

1.5.3.3.   SEM calibration and operation

1.5.3.3.1.   Calibration

The SEM calibration should be checked at least once a week (ideally once a day) using a certified calibration grid. The calibration should be checked against a certified standard and if the measured value (SEM) is not within ± 2  % of the certified value, then the SEM calibration must be adjusted and re-checked.

The SEM should be capable of resolving at least a minimum visible diameter of 0,2 μm, using a real sample matrix, at a magnification of × 2 000 .

1.5.3.3.2.   Operation

The SEM should be operated at 10 000 magnification ( 2 ) using conditions that give good resolution with an acceptable image at slow scan rates of, for example, 5 seconds per frame. Although the operational requirements of different SEMs may vary, generally to obtain the best visibility and resolution, with relatively low atomic weight materials, accelerating voltages of 5-10 keV should be used with a small spot size setting and short working distance. As a linear traverse is being conducted, then a 0° tilt should be used to minimise re-focussing or, if the SEM has a eucentric stage, the eucentric working distance should be used. Lower magnification may be used if the material does not contain small (diameter) fibres and the fibre diameters are large (> 5 μm).

1.5.3.4.   Sizing

1.5.3.4.1.   Low magnification examination to assess the sample

Initially the sample should be examined at low magnification to look for evidence of clumping of large fibres and to assess the fibre density. In the event of excessive clumping it is recommended that a new sample is prepared.

For statistical accuracy it is necessary to measure a minimum number of fibres and high fibre density may seem desirable as examining empty fields is time consuming and does not contribute to the analysis. However, if the filter is overloaded, it becomes difficult to measure all the measurable fibres and, because small fibres may be obscured by larger ones, they may be missed.

Bias towards over estimating the LWGMD may result from fibre densities in excess of 150 fibres per millimetre of linear traverse. On the other hand, low fibre concentrations will increase the time of analysis and it is often cost effective to prepare a sample with a fibre density closer to the optimum than to persist with counts on low concentration filters. The optimum fibre density should give an average of about one or two countable fibre per fields of view at 5 000 magnification. Nevertheless the optimum density will depend on the size (diameter) of the fibres, so it is necessary that the operator uses some expert judgement in order to decide whether the fibre density is close to optimal or not.

1.5.3.4.2.   Length weighting of the fibre diameters

Only those fibres that touch (or cross) an (infinitely) thin line drawn on the screen of the SEM are counted. For this reason a horizontal (or vertical) line is drawn across the centre of the screen.

Alternatively a single point is placed at the centre of the screen and a continuous scan in one direction across the filter is initiated. Each fibre of aspect ratio grater than 3:1 touching or crossing this point has its diameter measured and recorded.

1.5.3.4.3.   Fibre sizing

It is recommended that a minimum of 300 fibres are measured. Each fibre is measured only once at the point of intersection with the line or point drawn on the image (or close to the point of intersection if the fibre edges are obscured). If fibres with non-uniform cross sections are encountered, a measurement representing the average diameter of the fibre should be used. Care should be taken in defining the edge and measuring the shortest distance between the fibre edges. Sizing may be done on line, or off-line on stored images or photographs. Semi-automated image measurement systems that download data directly into a spreadsheet are recommended, as they save time, eliminate transcription errors and calculations can be automated.

The ends of long fibres should be checked at low magnification to ensure that they do not curl back into the measurement field of view and are only measured once.

2.   DATA

2.1.   TREATMENT OF RESULTS

Fibre diameters do not usually have a normal distribution. However, by performing a log transformation it is possible to obtain a distribution that approximates to normal.

Calculate the arithmetic mean (mean lnD) and the standard deviation (SDlnD) of the log to base e values (lnD) of the n fibre diameters (D).



image

(1)

image

(2)

The standard deviation is divided by the square root of the number of measurements (n) to obtain the standard error (SElnD).



image

(3)

Subtract two times the standard error from the mean and calculate the exponential of this value (mean minus two standard errors) to give the geometric mean minus two geometric standard errors.



image

(4)

3.   REPORTING

TEST REPORT

The test report should include at least the following information:

— 
The value of LWGMD-2SE.
— 
Any deviations and particularly those which may have an effect on the precision or accuracy of the results with appropriate justifications.

4.   REFERENCES

1. 

B. Tylee SOP MF 240. Health and Safety Executive, February 1999.

2. 

G. Burdett and G. Revell. Development of a standard method to measure the length-weigthed geometric mean fibre diameter: Results of the Second inter-laboratory exchange. IR/L/MF/94/07. Project R42.75 HPD. Health and Safety Executive, Research and Laboratory Services Division, 1994.

▼M4

A.23.   PARTITION COEFFICIENT (1-OCTANOL/WATER): SLOW-STIRRING METHOD

INTRODUCTION

1. This Test Method is equivalent to OECD Test Guideline (TG) 123 (2006). 1-octanol/water partition coefficient (POW) values up to a log POW of 8,2 have been accurately determined by the slow-stirring method (1). Therefore it is a suitable experimental approach for the direct determination of POW of highly hydrophobic substances.

2. Other methods for the determination of the 1-octanol/water partition coefficient (POW) are the ‘shake-flask’ method (2), and the determination of the POW from reversed phase HPLC-retention behaviour (3). The ‘shake-flask’ method is prone to artifacts due to transfer of octanol micro-droplets into the aqueous phase. With increasing values of POW the presence of these droplets in the aqueous phase leads to an increasing overestimation of the concentration of the test substance in the water. Therefore, its use is limited to substances with log POW < 4. The second method relies on solid data of directly determined POW values to calibrate the relationship between HPLC-retention behaviour and measured values of POW. A draft OECD guideline was available for determining 1-octanol/water partition coefficients of ionisable substances (4) but shall no longer be used.

3. This Test Method has been developed in The Netherlands. The precision of the methods described here has been validated and optimized in a ring-test validation study in which 15 laboratories participated (5).

INITIAL CONSIDERATIONS

Significance and use

4. For inert organic substances highly significant relationships have been found between 1-octanol/water partition coefficients (POW) and their bioaccumulation in fish. Moreover, POW has been demonstrated to be correlated to fish toxicity as well as to sorption of chemicals to solids such as soils and sediments. An extensive overview of the relationships has been given in reference (6).

5. A wide variety of relationships between the 1-octanol/water partition coefficient and other substance properties of relevance to environmental toxicology and chemistry have been established. As a consequence, the 1-octanol/water partition coefficient has evolved as a key parameter in the assessment of the environmental risk of chemicals as well as in the prediction of fate of chemicals in the environment.

Scope

6. The slow-stirring experiment is thought to reduce the formation of micro-droplets from 1-octanol droplets in the water phase. As a consequence, overestimation of the aqueous concentration due to test substance molecules associated to such droplets does not occur. Therefore, the slow-stirring method is particularly suitable for the determination of POW for substances with expected log POW values of 5 and higher, for which the shake-flask method (2) is prone to yield erroneous results.

DEFINITION AND UNITS

7. The partition coefficient of a substance between water and a lipophilic solvent (1-octanol) characterizes the equilibrium distribution of the chemical between the two phases. The partition coefficient between water and 1-octanol (POW) is defined as the ratio of the equilibrium concentrations of the test substance in 1-octanol saturated with water (CO) and water saturated with 1-octanol (CW).

image

As a ratio of concentrations it is dimensionless. Most frequently it is given as the logarithm to the base 10 (log POW). POW is temperature dependent and reported data should include the temperature of the measurement.

PRINCIPLE OF THE METHOD

8. In order to determine the partitioning coefficient, water, 1-octanol, and the test substance are equilibrated with each other at constant temperature. Then the concentrations of the test substance in the two phases are determined.

9. The experimental difficulties associated with the formation of micro-droplets during the shake-flask experiment can be reduced in the slow-stirring experiment proposed here. In the slow-stirring experiment, water, 1-octanol and the test substance are equilibrated in a thermostated stirred reactor. Exchange between the phases is accelerated by stirring. The stirring introduces limited turbulence which enhances the exchange between 1-octanol and water without micro-droplets being formed (1).

APPLICABILITY OF THE TEST

10. Since the presence of substances other than the test substance might influence the activity coefficient of the test substance, the test substance should be tested as a pure substance. The highest purity commercially available should be employed for the 1-octanol/water partition experiment.

11. The present method applies to pure substances that do not dissociate or associate and that do not display significant interfacial activity. It can be applied to determine the 1-octanol/water partition ratio of such substances and of mixtures. When the method is used for mixtures, the 1-octanol/water partition ratios determined are conditional and depend on the chemical composition of the mixture tested and on the electrolyte composition employed as aqueous phase. Provided additional steps are taken, the method is also applicable to dissociating or associating compounds (paragraph 12).

12. Due to the multiple equilibria in water and 1-octanol involved in the 1-octanol/water partitioning of dissociating substances such as organic acids and phenols, organic bases, and organometallic substances, the 1-octanol/water partition ratio is a conditional constant strongly dependent on electrolyte composition (7)(8). Determination of the 1-octanol/water partition ratio therefore requires that pH and electrolyte composition be controlled in the experiment and reported. Expert judgement has to be employed in the evaluation of these partition ratios. Using the value of dissociation constant(s), suitable pH-values need to be selected, such that a partitioning ratio is determined for each ionization state. Non-complexing buffers must be used when testing organometallic compounds (8). Taking the existing knowledge on the aqueous chemistry (complexation constants, dissociation constants) into account, the experimental conditions should be chosen in such a manner that the speciation of the test substance in the aqueous phase can be estimated. The ionic strength should be identical in all experiments by employing a background electrolyte.

13. Difficulties in the test may arise in conducting the test for substances with low water solubility or high POW, due to the fact that the concentrations in the water become very low such that their accurate determination is difficult. This Test Method provides guidance on how to deal with this problem.

INFORMATION ON THE TEST SUBSTANCE

14. Chemical reagents should be of analytical grade or of higher purity. The use of non-labelled test substances with known chemical composition and preferably at least 99 % purity, or of radiolabelled test substances with known chemical composition and radiochemical purity, is recommended. In the case of short half-life tracers, decay corrections should be applied. In the case of radiolabelled test substances, a chemical specific analytical method should be employed to ensure that the measured radioactivity is directly related to the test substance.

15. An estimate of log POW may be obtained by using commercially available software for estimation of log POW, or by using the ratio of the solubilities in both solvents.

16. Before carrying out a slow-stirring experiment for determination of POW, the following information on the test substance should be available:

(a) 

structural formula

(b) 

suitable analytical methods for determination of the concentration of the substance in water and 1-octanol

(c) 

dissociation constant(s) of ionisable substances (OECD Guideline 112 (9))

(d) 

aqueous solubility (10)

(e) 

abiotic hydrolysis (11)

(f) 

ready biodegradability (12)

(g) 

vapour pressure (13).

DESCRIPTION OF THE METHOD

Equipment and apparatus

17. Standard laboratory equipment is required, in particular, the following:

— 
magnetic stirrers and Teflon coated magnetic stir bars are employed to stir the water phase;
— 
analytical instrumentation, suitable for determination of the concentration of the test substance at the expected concentrations;
— 
stirring-vessel with a tap at the bottom. Dependent on the estimate of log POW and the Limit of Detection (LOD) of the test compound, the use of a reaction vessel of the same geometry larger than one litre has to be considered, so that a sufficient volume of water can be obtained for chemical extraction and analysis. This will result in higher concentrations in the water extract and thus a more reliable analytical determination. A table giving estimates of the minimum volume needed, the LOD of the compound, its estimated log POW and its water solubility is given in Appendix 1. The table is based on the relationship between log POW and the ratio between the solubilities in octanol and water, as presented by Pinsuwan et al. (14):

image

where

image

(in molarity);
and the relationship given by Lyman (15) for predicting water solubility. Water solubilities calculated with the equation given in Appendix 1 must be seen as a first estimate. It should be noted that the user is free to generate an estimate of water solubility by means of any relationship that is considered to better represent the relationship between hydrophobicity and solubility. For solid compounds, inclusion of melting point in the prediction of solubility is for instance recommended. In case a modified equation is used, it should be ascertained that the equation for calculation of solubility in octanol is still valid. A schematic drawing of a glass-jacketed stirring-vessel with a volume of ca. one litre is given in Appendix 2. The proportions of the vessel shown in Appendix 2 have proven favourable and should be maintained when apparatus of a different size is used;
— 
a means for keeping the temperature constant during the slow-stirring experiment is essential.

18. Vessels should be made from inert material such that adsorption to vessel surfaces is negligible.

Preparation of the test solutions

19. The POW determination should be carried out with the highest purity 1-octanol that is commercially available (at least + 99 %). Purification of 1-octanol by extraction with acid, base and water and subsequent drying is recommended. In addition, distillation can be used to purify 1-octanol. Purified 1-octanol is to be used to prepare standard solutions of the test substances. Water to be used in the POW determination should be glass or quartz distilled, or obtained from a purification system, or HPLC-grade water may be used. Filtration through a 0,22 μm filter is required for distilled water, and blanks should be included to check that no impurities are in the concentrated extracts that may interfere with the test substance. If a glass fibre filter is used, it should be cleaned by baking for at least three hours at 400 °C.

20. Both solvents are mutually saturated prior to the experiment by equilibrating them in a sufficiently large vessel. This is accomplished by slow-stirring the two-phase system for two days.

21. An appropriate concentration of test substance is selected and dissolved in 1-octanol (saturated with water). The 1-octanol/water partition coefficient needs to be determined in dilute solutions in 1-octanol and water. Therefore the concentration of the test substance should not exceed 70 % of its solubility with a maximum concentration of 0,1 M in either phase (1). The 1-octanol solutions used for the experiment must be devoid of suspended solid test substance.

22. The appropriate amount of test substance is dissolved in 1-octanol (saturated with water). If the estimate of log POW exceeds five, care has to be taken that the 1-octanol solutions used for the experiment are devoid of suspended solid test substance. To that end, the following procedure for chemicals with an estimated value of log POW > 5 is followed:

— 
the test substance is dissolved in 1-octanol (saturated with water);
— 
the solution is given sufficient time for the suspended solid substance to settle out. During the settling period, the concentration of the test substance is monitored;
— 
after the measured concentrations in the 1-octanol-solution have attained stable values, the stock solution is diluted with an appropriate volume of 1-octanol;
— 
the concentration of the diluted stock solution is measured. If the measured concentration is consistent with the dilution, the diluted stock solution can be employed in the slow-stirring experiment.

Extraction and analysis of samples

23. A validated analytical method should be used for the assay of test substance. The investigators have to provide evidence that the concentrations in the water saturated 1-octanol as well as in the 1-octanol saturated water phase during the experiment are above the method limit of quantification of the analytical procedures employed. Analytical recoveries of the test substance from the water phase and from the 1-octanol phase need to be established prior to the experiment in those cases for which extraction methods are necessary. The analytical signal needs to be corrected for blanks and care should be taken that no carry-over of analyte from one sample to another can occur.

24. Extraction of the water phase with an organic solvent and preconcentration of extract are likely to be required prior to analysis, due to rather low concentrations of hydrophobic test substances in the water phase. For the same reason it is necessary to reduce eventual blank concentrations. To that end, it is necessary to employ high purity solvents, preferably solvents for residue analysis. Moreover, working with carefully pre-cleaned (e.g. solvent washing or baking at elevated temperature) glassware can help to avoid cross-contamination.

25. An estimate of log POW may be obtained from an estimation program or by expert judgment. If the value is higher than six then blank corrections and analyte carry-over need to be monitored closely. Similarly, if the estimate of log POW exceeds six, the use of a surrogate standard for recovery correction is mandatory, so that high preconcentration factors can be reached. A number of software programs for the estimation of log POW are commercially available ( 3 ), e.g. Clog P (16), KOWWIN (17), ProLogP (18) and ACD log P (19). Descriptions of the estimation approaches can be found in references (20-22).

26. The limits of quantification (LOQ) for determination of the test substance in 1-octanol and water are established using accepted methods. As a rule of thumb, the method limit of quantification can be determined as the concentration in water or 1-octanol that produces a signal to noise ratio of ten. A suitable extraction and pre-concentration method should be selected and analytical recoveries should also be specified. A suitable pre-concentration factor is selected in order to obtain a signal of the required size upon analytical determination.

27. On the basis of the parameters of the analytical method and the expected concentrations, an approximate sample size required for an accurate determination of the compound concentration is determined. The use of water samples that are too small to obtain a sufficient analytical signal should be avoided. Also, the use of excessively large water samples should be avoided, since otherwise there might be too little water left for the minimum number of analyses required (n = 5). In Appendix 1, the minimum sample volume is indicated as a function of the vessel volume, the LOD of the test substance and the solubility of the test substance.

28. Quantification of the test substances occurs by comparison with calibration curves of the respective compound. The concentrations in the samples analysed must be bracketed by concentrations of standards.

29. For test substances with a log POW estimate higher than six a surrogate standard has to be spiked to the water sample prior to extraction in order to register losses occurring during extraction and pre-concentration of the water samples. For accurate recovery correction, the surrogates must have properties that are very close to, or identical with, those of the test substance. Preferably, (stable) isotopically-labelled analogues of the substances of interest (for example, perdeuterated or 13C-labelled) are used for this purpose. If the use of labelled stable isotopes, i.e. 13C or 2H, is not possible it should be demonstrated from reliable data in the LITERATURE that the physical-chemical properties of the surrogate are very close to those of the test substance. During liquid-liquid extraction of the water phase emulsions can form. They can be reduced by addition of salt and allowing the emulsion to settle overnight. Methods used for extracting and pre-concentrating the samples need to be reported.

30. Samples withdrawn from the 1-octanol phase may, if necessary, be diluted with a suitable solvent prior to analysis. Moreover, the use of surrogate standards for recovery correction is recommended for substances for which the recovery experiments demonstrated a high degree of variation in the recovery experiments (relative standard deviation > 10 %).

31. The details of the analytical method need to be reported. This includes the method of extraction, pre-concentration and dilution factors, instrument parameters, calibration routine, calibration range, analytical recovery of the test substance from water, addition of surrogate standards for recovery correction, blank values, detection limits and limits of quantification.

Performance of the Test

Optimal 1-octanol/water volume ratios

32. When choosing the water and 1-octanol volumes, the LOQ in 1-octanol and water, the pre-concentration factors applied to the water samples, the volumes sampled in 1-octanol and water, and the expected concentrations should be considered. For experimental reasons, the volume of 1-octanol in the slow-stirring system should be chosen such that the 1-octanol layer is sufficiently thick (> 0,5 cm) in order to allow for sampling of the 1-octanol phase without disturbing it.

33. Typical phase ratios used for the determinations of compounds with log POW of 4,5 and higher are 20 to 50 ml of 1-octanol and 950 to 980 ml of water in a one litre vessel.

Test conditions

34. During the test the reaction vessel is thermostated to reduce temperature variation to below 1 °C. The assay should be performed at 25 °C.

35. The experimental system should be protected from daylight by either performing the experiment in a dark room or by covering the reaction vessel with aluminium foil.

36. The experiment should be performed in a dust-free (as far as possible) environment.

37. The 1-octanol-water system is stirred until equilibrium is attained. In a pilot experiment the length of the equilibration period is assessed by performing a slow-stirring experiment and sampling water and 1-octanol periodically. The sampling time points should be interspersed by a minimum period of five hours.

38. Each POW determination has to be performed employing at least three independent slow-stirring experiments.

Determination of the equilibration time

39. It is assumed that the equilibrium is achieved when a regression of the 1-octanol/water concentration ratio against time over a time span of four time points yields a slope that is not significantly different from zero at a p-level of 0,05. The minimum equilibration time is one day before sampling can be started. As a rule of thumb, sampling of substances with a log POW estimate of less than five can take place during days two and three. The equilibration might have to be extended for more hydrophobic compounds. For a compound with log POW of 8,23 (decachlorobiphenyl) 144 hours were sufficient for equilibration. Equilibrium is assessed by means of repeated sampling of a single vessel.

Starting the experiment

40. At the start of the experiment the reaction vessel is filled with 1-octanol-saturated water. Sufficient time should be allowed to reach the thermostated temperature.

41. The desired amount of test substance (dissolved in the required volume of 1-octanol saturated with water) is carefully added to the reaction vessel. This is a crucial step in the experiment, since turbulent mixing of the two phases has to be avoided. To that end, the 1-octanol phase can be pipetted slowly against the wall of the experimental vessel, close to the water surface. It will subsequently flow along the glass wall and form a film above the water phase. The decantation of 1-octanol directly into the flask should always be avoided; drops of 1-octanol should not be allowed to fall directly into the water.

42. After starting the stirring, the stirring rate should be increased slowly. If the stirring motors cannot be appropriately adjusted the use of a transformer should be considered. The stirring rate should be adjusted so that a vortex at the interface between water and 1-octanol of 0,5 to maximally 2,5 cm depth is created. The stirring rate should be reduced if the vortex depth of 2,5 cm is exceeded; otherwise micro-droplets may be formed from 1-octanol droplets in the water phase, leading to an overestimation of the concentration of the test substance in the water. The maximum stirring rate of 2,5 cm is recommended on the basis of the findings in the ring-test validation study (5). It is a compromise between achieving a rapid rate of equilibration, while limiting the formation of 1-octanol micro-droplets.

Sampling and Sample Treatment

43. The stirrer should be turned off prior to sampling and the liquids should be allowed to stop moving. After sampling is completed, the stirrer is started again slowly, as described above, and then the stirring rate is increased gradually.

44. The water phase is sampled from a stopcock at the bottom of the reaction vessel. Always discard the dead volume of water contained in the taps (approximately 5 ml in the vessel shown in the Appendix 2). The water in the taps is not stirred and therefore not in equilibrium with the bulk. Note the volume of the water samples, and make sure that the amount of test substance present in the discarded water is taken into account when setting up a mass balance. Evaporative losses should be minimized by allowing the water to flow quiescently into the separatory funnel, such that there is no disturbance of the water/1-octanol layer.

45. 1-Octanol samples are obtained by withdrawing a small aliquot (ca. 100 μl) from the 1-octanol layer with a 100 microlitre all glass-metal syringe. Care should be taken not to disturb the boundary. The volume of the sampled liquid is recorded. A small aliquot is sufficient, since the 1-octanol sample will be diluted.

46. Unnecessary sample transfer steps should be avoided. To that end the sample volume should be determined gravimetrically. In case of water samples this can be achieved by collecting the water sample in a separatory funnel that contains already the required volume of solvent.

DATA AND REPORTING

47. According to the present Test Method, POW is determined by performing three slow-stirring experiments (three experimental units) with the compound under investigation employing identical conditions. The regression used to demonstrate attainment of equilibrium should be based on the results of at least four determinations of CO/CW at consecutive time points. This allows for calculating variance as a measure of the uncertainty of the average value obtained by each experimental unit.

48. The POW can be characterized by the variance in the data obtained for each experimental unit. This information is employed to calculate the POW as the weighted average of the results of the individual experimental units. To do so, the inverse of the variance of the results of the experimental units is employed as weight. As a result, data with a large variation (expressed as the variance) and thus with lower reliability have less influence on the result than data with a low variance.

49. Analogously, the weighted standard deviation is calculated. It characterizes the repeatability of the POW measurement. A low value of the weighted standard deviation indicates that the POW determination was very repeatable within one laboratory. The formal statistical treatment of the data is outlined below.

Treatment of the results

Demonstration of attainment of equilibrium

50. The logarithm of the ratio of the concentration of the test substance in 1-octanol and water (log (CO/Cw)) is calculated for each sampling time. Achievement of chemical equilibrium is demonstrated by plotting this ratio against time. A plateau in this plot that is based on at least four consecutive time points indicates that equilibrium has been attained, and that the compound is truly dissolved in 1-octanol. If not, the test needs to be continued until four successive time points yield a slope that is not significantly different from 0 at a p-level of 0,05, indicating that log Co/Cw is independent of time.

Log POW-calculation

51. The value of log POW of the experimental unit is calculated as the weighted average value of log Co/Cw for the part of the curve of log Co/Cw vs. time, for which equilibrium has been demonstrated. The weighted average is calculated by weighting the data with the inverse of the variance so that the influence of the data on the final result is inversely proportional to the uncertainty in the data.

Average log POW

52. The average value of log POW of different experimental units is calculated as the average of the results of the individual experimental units weighted with their respective variances.

The calculation is performed as follows:

image

where:

log POW,i

=

the log POW value of the individual experimental unit i;

log POW,Av

=

the weighted average value of the individual log POW determinations;

wi

=

the statistical weight assigned to the log POW value of the experimental unit i.

The reciprocal of the variance of log POW,i is employed as wi (
image )

53. The error of the average of log POW is estimated as the repeatability of log Co/Cw determined during the equilibrium phase in the individual experimental units. It is expressed as the weighted standard deviation of log POW,Avlog Pow,Av) which in turn is a measure of the error associated with log POW,Av. The weighted standard deviation can be computed from the weighted variance (varlog Pow,Av) as follows:

image

image

The symbol n stands for the number of experimental units.

Test Report

54. The test report should include the following information:

Test substance:
— 
common name, chemical name, CAS number, structural formula (indicating position of label when radiolabelled substance is used) and relevant physical-chemical properties (see paragraph 17)
— 
purity (impurities) of test substance
— 
label purity of labelled chemicals and molar activity (where appropriate)
— 
the preliminary estimate of log Pow, as well as the method used to derive the value.
Test conditions:
— 
dates of the performance of the studies
— 
temperature during the experiment
— 
volumes of 1-octanol and water at the beginning of the test
— 
volumes of withdrawn 1-octanol and water samples
— 
volumes of 1-octanol and water remaining in the test vessels
— 
description of the test vessels and stirring conditions (geometry of the stirring bar and of the test vessel, vortex height in mm, and when available: stirring rate) used
— 
analytical methods used to determine the test substance and the method limit of quantification
— 
sampling times
— 
the aqueous phase pH and the buffers used, when pH is adjusted for ionizable molecules
— 
number of replicates.
Results:
— 
repeatability and sensitivity of the analytical methods used
— 
determined concentrations of the test substance in 1-octanol and water as a function of time
— 
demonstration of mass balance
— 
temperature and standard deviation or the range of temperature during the experiment
— 
the regression of concentration ratio against time
— 
the average value log Pow,Av and its standard error
— 
discussion and interpretation of the results
— 
examples of raw data figures of representative analysis (all raw data have to be stored in accordance with GLP standards), including recoveries of surrogates, and the number of levels used in the calibration (along with the criteria for the correlation coefficient of the calibration curve), and results of quality assurance/quality control (QA/QC)
— 
when available: validation report of the assay procedure (to be indicated among references).

LITERATURE:

(1) 

De Bruijn JHM, Busser F, Seinen W, Hermens J. (1989). Determination of octanol/water partition coefficients with the ‘slow-stirring’ method. Environ. Toxicol. Chem. 8: 499-512.

(2) 

Chapter A.8 of this Annex, Partition Coefficient.

(3) 

Chapter A.8 of this Annex, Partition Coefficient.

(4) 

OECD (2000). OECD Draft Guideline for the Testing of Chemicals: 122 Partition Coefficient (n-Octanol/Water): pH-Metric Method for Ionisable Substances. Paris.

(5) 

Tolls J (2002). Partition Coefficient 1-Octanol/Water (Pow) Slow-Stirring Method for Highly Hydrophobic Chemicals, Validation Report. RIVM contract-Nrs 602730 M/602700/01.

(6) 

Boethling RS, Mackay D (eds.) (2000). Handbook of property estimation methods for chemicals. Lewis Publishers Boca Raton, FL, USA.

(7) 

Schwarzenbach RP, Gschwend PM, Imboden DM (1993). Environmental Organic Chemistry. Wiley, New York, NY.

(8) 

Arnold CG, Widenhaupt A, David MM, Müller SR, Haderlein SB, Schwarzenbach RP (1997). Aqueous speciation and 1-octanol-water partitioning of tributyl- and triphenyltin: effect of pH and ion composition. Environ. Sci. Technol. 31: 2596-2602.

(9) 

OECD (1981) OECD Guidelines for the Testing of Chemicals: 112 Dissociation Constants in Water. Paris.

(10) 

Chapter A.6 of this Annex, Water Solubility.

(11) 

Chapter C.7 of this Annex, Degradation – Abiotic Degradation Hydrolysis as a Function of pH.

(12) 

Chapter C.4 — Part II – VII (Method A to F) of this Annex, Determination of ‘Ready’ Biodegradability.

(13) 

Chapter A.4 of this Annex, Vapour Pressure.

(14) 

Pinsuwan S, Li A and Yalkowsky S.H. (1995). Correlation of octanol/water solubility ratios and partition coefficients, J. Chem. Eng. Data. 40: 623-626.

(15) 

Lyman WJ (1990). Solubility in water. In: Handbook of Chemical Property Estimation Methods: Environmental Behavior of Organic Compounds, Lyman WJ, Reehl WF, Rosenblatt DH, Eds. American Chemical Society, Washington, DC, 2-1 to 2-52.

(16) 

Leo A, Weininger D (1989). Medchem Software Manual. Daylight Chemical Information Systems, Irvine, CA.

(17) 

Meylan W (1993). SRC-LOGKOW for Windows. SRC, Syracuse, N.Y.

(18) 

Compudrug L (1992). ProLogP. Compudrug, Ltd, Budapest.

(19) 

ACD. ACD logP; Advanced Chemistry Development: Toronto, Ontario M5H 3V9, Canada, 2001.

(20) 

Lyman WJ (1990). Octanol/water partition coefficient. In Lyman WJ, Reehl WF, Rosenblatt DH, eds, Handbook of chemical property estimation, American Chemical Society, Washington, D.C.

(21) 

Rekker RF, de Kort HM (1979). The hydrophobic fragmental constant: An extension to a 1 000 data point set. Eur. J. Med. Chem. Chim. Ther. 14: 479-488.

(22) 

Jübermann O (1958). Houben-Weyl, ed, Methoden der Organischen Chemie: 386-390.

Appendix 1

Spreadsheet for computation of minimum volumes of water required for detection of test substances of different log POW values in aqueous phase

Assumptions:

— 
Maximum volume of individual aliquots = 10 % of total volume; 5 aliquots = 50 % of total volume.
— 

image

. In case of lower concentrations, larger volumes would be required.
— 
Volume used for LOD determination = 100 ml.
— 
log Pow vs. log Sw and log Pow vs. SR (Soct/Sw) are reasonable representations of relationships for test substances.

Estimation of Sw



log Pow

Equation

log Sw

Sw (mg/l)

4

image

0,496

3,133E+00

4,5

image

0,035

1,084E+00

5

image

–0,426

3,750E-01

5,5

image

–0,887

1,297E-01

6

image

–1,348

4,487E-02

6,5

image

––1,809

1,552E-02

7

image

–2,270

5,370E-03

7,5

image

–2,731

1,858E-03

8

image

–3,192

6,427E-04

Estimation of Soct



log Pow

Equation

Soct (mg/l)

4

image

3,763E+04

4,5

image

4,816E+04

5

image

6,165E+04

5,5

image

7,890E+04

6

image

1,010E+05

6,5

image

1,293E+05

7

image

1,654E+05

7,5

image

2,117E+05

8

image

2,710E+05



Total Mass test substance

(mg)

Massoct/Masswater

MassH2O

(mg)

ConcH2O

(mg/l)

Massoct

(mg)

Concoct

(mg/l)

1 319

526

2,5017

2,6333

1 317

26 333

1 686

1 664

1,0127

1,0660

1 685

33 709

2 158

5 263

0,4099

0,4315

2 157

43 149

2 762

16 644

0,1659

0,1747

2 762

55 230

3 535

52 632

0,0672

0,0707

3 535

70 691

4 524

1664 36

0,0272

0,0286

4 524

90 480

5 790

5263 16

0,0110

0,0116

5 790

115 807

7 411

1 664 357

0,0045

0,0047

7 411

148 223

9 486

5 263 158

0,0018

0,0019

9 486

189 713

Computation of volumes



Minimum volume required for H2O phase at each LOD concentration

log Kow

LOD (micrograms/l)→

0,001

0,01

0,10

1,00

10

4

 

0,04

0,38

3,80

38

380

4,5

 

0,09

0,94

9,38

94

938

5

 

0,23

2,32

23,18

232

2 318

5,5

 

0,57

5,73

57,26

573

5 726

6

 

1,41

14,15

141

1 415

14 146

6,5

 

3,50

34,95

350

3 495

34 950

7

 

8,64

86,35

864

8 635

86 351

7,5

 

21,33

213

2 133

21 335

213 346

8

 

52,71

527

5 271

52 711

527 111

Volume used for LOD (l)

0,1

 

 

 

 

 

Key to Computations

Represents < 10 % of total volume of aqueous phase, 1 litre equilibration vessel.

Represents < 10 % of total volume of aqueous phase, 2 litre equilibration vessel.

Represents < 10 % of total volume of aqueous phase, 5 litre equilibration vessel.

Represents < 10 % of total volume of aqueous phase, 10 litre equilibration vessel.

Exceeds 10 % of even the 10 liter equilibration vessel.



Overview of volumes required, as a function of water solubility and Log Pow

Minimum volume required for H2O phase at each LOD concentration (ml)

log Pow

Sw (mg/l)

LOD (micrograms/l)→

0,001

0,01

0,10

1,00

10

4

10

 

0,01

0,12

1,19

11,90

118,99

 

5

 

0,02

0,24

2,38

23,80

237,97

 

3

 

0,04

0,40

3,97

39,66

396,62

 

1

 

0,12

1,19

11,90

118,99

1 189,86

4,5

5

 

0,02

0,20

2,03

20,34

203,37

 

2

 

0,05

0,51

5,08

50,84

508,42

 

1

 

0,10

1,02

10,17

101,68

1 016,83

 

0,5

 

0,20

2,03

20,34

203,37

2 033,67

5

1

 

0,09

0,87

8,69

86,90

869,01

 

0,5

 

0,17

1,74

17,38

173,80

1 738,02

 

0,375

 

0,23

2,32

23,18

231,75

2 317,53

 

0,2

 

0,43

4,35

43,45

434,51

4 345,05

5,5

0,4

 

0,19

1,86

18,57

185,68

1 856,79

 

0,2

 

0,37

3,71

37,14

371,36

3 713,59

 

0,1

 

0,74

7,43

74,27

742,72

7 427,17

 

0,05

 

1,49

14,85

148,54

1 485,43

14 854,35

6

0,1

 

0,63

6,35

63,48

634,80

6 347,95

 

0,05

 

1,27

12,70

126,96

1 269,59

12 695,91

 

0,025

 

2,54

25,39

253,92

2 539,18

25 391,82

 

0,0125

 

5,08

50,78

507,84

5 078,36

50 783,64

6,5

0,025

 

2,17

21,70

217,02

2 170,25

21 702,46

 

0,0125

 

4,34

43,40

434,05

4 340,49

43 404,93

 

0,006

 

9,04

90,43

904,27

9 042,69

90 426,93

 

0,003

 

18,09

180,85

1 808,54

18 085,39

180 853,86

7

0,006

 

7,73

77,29

772,89

7 728,85

77 288,50

 

0,003

 

15,46

154,58

1 545,77

15 457,70

154 577,01

 

0,0015

 

23,19

231,87

2 318,66

23 186,55

231 865,51

 

0,001

 

46,37

463,73

4 637,31

46 373,10

463 731,03

7,5

0,002

 

19,82

198,18

1 981,77

19 817,73

198 177,33

 

0,001

 

39,64

396,35

3 963,55

39 635,47

396 354,66

 

0,0005

 

79,27

792,71

7 927,09

79 270,93

792 709,32

 

0,00025

 

158,54

1 585,42

15 854,19

158 541,86

1 585 418,63

8

0,001

 

33,88

338,77

3 387,68

33 876,77

338 767,72

 

0,0005

 

67,75

677,54

6 775,35

67 753,54

677 535,44

 

0,00025

 

135,51

1 355,07

13 550,71

135 507,09

1 355 070,89

 

0,000125

 

271,01

2 710,14

27 101,42

271 014,18

2 710 141,77

Volume used for LOD (l)

0,1

 

 

 

 

 

Appendix 2

An example of glass-jacketed test vessel for the slow-stirring experiment for determination of POW

image

▼M6

A.24.   PARTITION COEFFICIENT (N-OCTANOL/WATER), HIGH PERFORMANCELIQUID CHROMATOGRAPHY (HPLC) METHOD

INTRODUCTION

This test method is equivalent to OECD test guideline (TG) 117 (2004)

1. 

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 the case of n-octanol and water,

image

The partition coefficient being the quotient of two concentrations, is dimensionless and is usually given in the form of its logarithm to base ten.

2. 

Pow is a key parameter in studies of the environmental fate of chemical substances. A highly-significant relationship between the Pow of non-ionised form of substances and their bioaccumulation in fish has been shown. It has also been shown that Pow is a useful parameter in the prediction of adsorption on soil and sediments and for establishing quantitative structure-activity relationships for a wide range of biological effects.

3. 

The original proposal for this test method was based on an article by C.V. Eadsforth and P. Moser (1). The development of the test method and an OECD inter-laboratory comparison test were coordinated by the Umweltbundesamt of the Federal Republic of Germany during 1986 (2).

INITIAL CONSIDERATIONS

4. log Pow values in the range – 2 to 4 (occasionally up to 5 and more) ( 4 ) can be experimentally determined by the Shake-Flask method (Chapter A.8 of this Annex, OECD Test Guideline 107). The HPLC method covers log Pow in the range of 0 to 6 (1)(2)(3)(4)(5). This method may require an estimation of Pow to assign suitable reference substances and support any conclusions drawn from the data generated by the test. Calculation methods are briefly discussed in the Appendix to this test method. The HPLC operation mode is isocratic.

5. The Pow values depend on the environmental conditions such as temperature, pH, ionic strength etc, and these should be defined in the experiment for the correct interpretation of Pow data. For ionisable substances, another method (e.g. draft OECD guideline on pH metric method for ionised substances (6)) may become available and could be used as an alternative method. Although this draft OECD guideline may appropriate be suitable to determine Pow for those ionisable substances, in some cases it is more appropriate to use the HPLC method at an environmentally relevant pH (see paragraph 9).

PRINCIPLE OF THE METHOD

6. Reverse phase HPLC is performed on analytical columns packed with a commercially available solid phase containing long hydrocarbon chains (e.g. C8, C18) chemically bound onto silica.

7. A chemical injected on such a column partitions between the mobile solvent phase and the hydrocarbon stationary phase as it is transported along the column by the mobile phase. The substances are retained in proportion to their hydrocarbon-water partition coefficient, with hydrophilic substances eluted first and lipophilic substances last. The retention time is described by the capacity factor k given by the expression:

image

where tR is the retention time of the test substance, and t0 is the dead-time, i.e. the average time a solvent molecule needs to pass the column. Quantitative analytical methods are not required and only the determination of retention times is necessary.

8. The octanol/water partition coefficient of a test substance can be computed by experimentally determining its capacity factor k and then inputting k into the following equation:

image

where

a, b

=

linear regression coefficients.

The equation above can be obtained by linearly regressing the log of octanol/water partition coefficients of reference substances against the log of capacity factors of the reference substances.

9. Reverse phase HPLC method enables partition coefficients to be estimated in the log Pow range between 0 and 6, but can be expanded to cover the log Pow range between 6 and 10 in exceptional cases. This may require that the mobile phase is modified (3). The method is not applicable to strong acids and bases, metal complexes, substances which react with the eluent, or surface-active agents. Measurements can be performed on ionisable substances in their non-ionised form (free acid or free base) only by using an appropriate buffer with a pH below the pKa for a free acid or above the pKa for a free base. Alternatively, the pH-metric method for the testing of ionisable substances (6) may become available and could be used as an alternative method (6). If the log Pow value is determined for the use in environmental hazard classification or in environmental risk assessment, the test should be performed in the pH range relevant for the natural environment, i.e. in the pH range of 5,0 - 9.

10. In some cases impurities can make the interpretation of the results difficult due to uncertainty in peak assignments. For mixtures which result in an unresolved band, upper and lower limits of log Pow, and the area % of each log Pow peak should be reported. For mixtures which are a group of homologues, the weighted average log Pow should also be stated (7), calculated based on the single Pow values and the corresponding area % values (8). All peaks that contribute an area of 5 % or more to the total peak area should be taken into consideration in the calculation (9):

image

The weighed average log Pow is valid only for substances or mixtures (e.g. tall oils) consisting of homologues (e.g. series of alkanes). Mixtures can be measured with meaningful results, provided that the analytical detector used has the same sensitivity towards all the substances in the mixture and that they can be adequately resolved.

INFORMATION ON THE TEST SUBSTANCE

11. The dissociation constant, structural formula, and solubility in the mobile phase should be known before the method is used. In addition, information on hydrolysis would be helpful.

QUALITY CRITERIA

12. In order to increase the confidence in the measurement, duplicate determinations must be made.

— 
Repeatability: The value of log Pow derived from repeated measurements made under identical conditions and using the same set of reference substances should fall within a range of ± 0,1 log units.
— 
Reproducibility: If the measurements are repeated with a different set of reference substances, results may differ. Typically, the correlation coefficient R for the relationship between log k and log Pow for a set of test substances is around 0,9, corresponding to an octanol/water partition coefficient of log Pow ± 0,5 log units.

13. The inter-laboratory comparison test has shown that with the HPLC method log Pow values can be obtained to within ± 0,5 units of the Shake-Flask values (2). Other comparisons can be found in the literature (4)(5)(10)(11)(12). Correlation graphs based on structurally related reference substances give the most accurate results (13).

REFERENCE SUBSTANCES

14. In order to correlate the measured capacity factor k of a substance with its Pow, a calibration graph using at least 6 points has to be established (see paragraph 24). It is up to the user to select the appropriate reference substances. The reference substances should normally have log Pow values which encompass the log Pow of the test substance, i.e. at least one reference substance should have a Pow above that of the test substance, and another a Pow below that of the test substance. Extrapolation should only be used in exceptional cases. It is preferable that these reference substances should be structurally related to the test substance. log Pow values of the reference substances used for the calibration should be based on reliable experimental data. However, for substances with high log Pow (normally more than 4), calculated values may be used unless reliable experimental data are available. If extrapolated values are used a limit value should be quoted.

15. Extensive lists of log Pow values for many groups of chemicals are available (14)(15). If data on the partition coefficients of structurally related substances are not available, a more general calibration, established with other reference substances, may be used. Recommended reference substances and their Pow values are listed in Table 1. For ionisable substances the values given apply to the non-ionised form. The values were checked for plausibility and quality during the inter-laboratory comparison test.



Table 1

Recommended reference substances

 

CAS Number

Reference substance

log Pow

pKa

1

78-93-3

2-Butanone

(Methylethylketone)

0,3

 

2

1122-54-9

4-Acetylpyridine

0,5

 

3

62-53-3

Aniline

0,9

 

4

103-84-4

Acetanilide

1,0

 

5

100-51-6

Benzyl alcohol

1,1

 

6

150-76-5

4-Methoxyphenol

1,3

pKa = 10,26

7

122-59-8

Phenoxyacetic acid

1,4

pKa = 3,12

8

108-95-2

Phenol

1,5

pKa = 9,92

9

51-28-5

2,4-Dinitrophenol

1,5

pKa = 3,96

10

100-47-0

Benzonitrile

1,6

 

11

140-29-4

Phenylacetonitrile

1,6

 

12

589-18-4

4-Methylbenzyl alcohol

1,6

 

13

98-86-2

Acetophenone

1,7

 

14

88-75-5

2-Nitrophenol

1,8

pKa = 7,17

15

121-92-6

3-Nitrobenzoic acid

1,8

pKa = 3,47

16

106-47-8

4-Chloroaniline

1,8

pKa = 4,15

17

98-95-3

Nitrobenzene

1,9

 

18

104-54-1

Cinnamyl alcohol

(Cinnamic alcohol)

1,9

 

19

65-85-0

Benzoic acid

1,9

pKa = 4,19

20

106-44-5

p-Cresol

1,9

pKa = 10,17

21

140-10-3

(trans)

Cinnamic acid

2,1

pKa = 3,89 (cis)

4,44 (trans)

22

100-66-3

Anisole

2,1

 

23

93-58-3

Methyl benzoate

2,1

 

24

71-43-2

Benzene

2,1

 

25

99-04-7

3-Methylbenzoic acid

2,4

pKa = 4,27

26

106-48-9

4-Chlorophenol

2,4

pKa = 9,1

27

79-01-6

Trichloroethylene

2,4

 

28

1912-24-9

Atrazine

2,6

 

29

93-89-0

Ethyl benzoate

2,6

 

30

1194-65-6

2,6-Dichlorobenzonitrile

2,6

 

31

535-80-8

3-Chlorobenzoic acid

2,7

pKa = 3,82

32

108-88-3

Toluene

2,7

 

33

90-15-3

1-Naphthol

2,7

pKa = 9,34

34

608-27-5

2,3-Dichloroaniline

2,8

 

35

108-90-7

Chlorobenzene

2,8

 

36

1746-13-0

Allyl phenyl ether

2,9

 

37

108-86-1

Bromobenzene

3,0

 

38

100-41-4

Ethylbenzene

3,2

 

39

119-61-9

Benzophenone

3,2

 

40

92-69-3

4-Phenylphenol

3,2

pKa = 9,54

41

89-83-8

Thymol

3,3

 

42

106-46-7

1,4-Dichlorobenzene

3,4

 

43

122-39-4

Diphenylamine

3,4

pKa = 0,79

44

91-20-3

Naphthalene

3,6

 

45

93-99-2

Phenyl benzoate

3,6

 

46

98-82-8

Isopropylbenzene

3,7

 

47

88-06-2

2,4,6-Trichlorophenol

3,7

pKa = 6

48

92-52-4

Biphenyl

4,0

 

49

120-51-4

Benzyl benzoate

4,0

 

50

88-85-7

2,4-Dinitro-6-sec-butylphenol

4,1

 

51

120-82-1

1,2,4-Trichlorobenzene

4,2

 

52

143-07-7

Dodecanoic acid

4,2

pKa = 5,3

53

101-84-8

Diphenyl ether

4,2

 

54

85-01-8

Phenanthrene

4,5

 

55

104-51-8

n-Butylbenzene

4,6

 

56

103-29-7

Dibenzyl

4,8

 

57

3558-69-8

2,6-Diphenylpyridine

4,9

 

58

206-44-0

Fluoranthene

5,1

 

59

603-34-9

Triphenylamine

5,7

 

60

50-29-3

DDT

6,5

 

DESCRIPTION OF THE METHOD

Preliminary estimate of the partition coefficient

16. If it is necessary, the partition coefficient of the test substance may be estimated preferably by using a calculation method (see Appendix, or where appropriate, by using the ratio of the solubility of the test substance in the pure solvents.

Apparatus

17. A liquid-phase chromatograph fitted with a low-pulse pump and a suitable detection system is required. A UV detector, using a wavelength of 210 nm, or an RI detector is applicable to the wide variety of chemical groups. The presence of polar groups in the stationary phase may seriously impair the performance of the HPLC column. Therefore, stationary phases should have a minimal percentage of polar groups (16). Commercial microparticulate reverse-phase packing or ready-packed columns can be used. A guard column may be positioned between the injection system and the analytical column.

Mobile phase

18. HPLC-grade methanol and distilled or de-ionised water are used to prepare the eluting solvent, which is degassed before use. Isocratic elution should be employed. Methanol/water ratios with minimum water content of 25 % should be used. Typically a 3:1 (v/v) methanol-water mixture is satisfactory for eluting substances with a log P of 6 within an hour, at a flow rate of 1 ml/min. For substances with a log P above 6 it may be necessary to shorten the elution time (and those of the reference substances) by decreasing the polarity of the mobile phase or the column length.

19. The test substance and the reference substances must be soluble in the mobile phase in sufficient concentration to allow their detection. Additives may be used with the methanol-water mixture in exceptional cases only, since they will change the properties of the column. In these cases it must be confirmed that the retention time of the test and reference substances are not influenced. If methanol-water is not appropriate, other organic solvent-water mixtures can be used, e.g. ethanol-water, acetonitrile-water or isopropyl alcohol (2-propanol)-water.

20. The pH of the eluent is critical for ionisable substances. It should be within the operating pH range of the column, usually between 2 and 8. Buffering is recommended. Care must be taken to avoid salt precipitation and column deterioration which occur with some organic phase/buffer mixtures. HPLC measurements with silica-based stationary phases above pH 8 are not normally advisable since the use of an alkaline mobile phase may cause rapid deterioration in the performance of the column.

Solutes

21. The test and reference substances must be sufficiently pure in order to assign the peaks in the chromatograms to the respective substances. Substances to be used for test or calibration purposes are dissolved in the mobile phase if possible. If a solvent other than the mobile phase is used to dissolve the test and reference substances, the mobile phase should be used for the final dilution prior to injection.

Test conditions

22. The temperature during the measurement should not vary by more than ± 1 °C.

Determination of dead time to

23. The dead time t0 can be measured by using unretained organic substances (e.g. thiourea or formamide). A more precise dead time can be derived from the retention times measured or a set of approximately seven members of a homologous series (e.g. n-alkyl methyl ketones) (17). The retention times tR (nC + 1) are plotted against tR (nC), where nC is the number of carbon atoms. A straight line, tR (nC + 1) = A tR (nC) + (1 – A)t0, is obtained, where A, representing k(nC + 1)/k(nC), is constant. The dead time t0 is obtained from the intercept (1 – A)t0 and the slope A.

Regression Equation

24. The next step is to plot a correlation log k versus log P for appropriate reference substances with log P values near the value expected for the test substance. In practice, from 6 to 10 reference substances are injected simultaneously. The retention times are determined, preferably on a recording integrator linked to the detection system. The corresponding logarithms of the capacity factors, log k, are plotted as a function of log P. The regression equation is performed at regular intervals, at least once daily, so that account can be taken of possible changes in column performance.

DETERMINATION OF THE POW OF THE TEST SUBSTANCE

25. The test substance is injected in the smallest detectable quantities. The retention time is determined in duplicate. The partition coefficient of the test substance is obtained by interpolation of the calculated capacity factor on the calibration graph. For very low and very high partition coefficients extrapolation is necessary. Especially in these cases attention must be given to the confidence limits of the regression line. If the retention time of sample is outside the range of retention times obtained for the standards, a limit value should be quoted.

DATA AND REPORTING

Test report

26. The following must be included in the report:

— 
if determined the preliminary estimate of the partition coefficient, the estimated values and the method used; and if a calculation method was used, its full description including identification of the data base and detailed information on the choice of fragments;
— 
test and reference substances: purity, structural formula and CAS number,
— 
description of equipment and operating conditions: analytical column, guard column,
— 
mobile phase, means of detection, temperature range, pH;
— 
elution profiles (chromatograms);
— 
deadtime and how it was measured;
— 
retention data and literature log Pow values for reference substances used in calibration;
— 
details on fitted regression line (log k versus log Pow) and the correlation coefficient of the line including confidence intervals;
— 
average retention data and interpolated log Pow value for the test substance;
— 
in case of a mixture: elution profile chromatogram with indicated cut-offs;
— 
log Pow values relative to area % of the log Pow peak;
— 
calculation using a regression line;
— 
calculated weighted average log Pow values, when appropriate.

LITERATURE

(1) C.V. Eadsforth and P. Moser. (1983). Assessment of Reverse Phase Chromatographic Methods for Determining Partition Coefficients. Chemosphere. 12, 1459.

(2) W. Klein, W. Kördel, M. Weiss and H.J. Poremski. (1988). Updating of the OECD Test Guideline 107 Partition Coefficient n-Octanol-Water, OECD Laboratory Intercomparison Test on the HPLC Method. Chemosphere. 17, 361.

(3) C.V. Eadsforth. (1986). Application of Reverse H.P.L.C. for the Determination of Partition Coefficient. Pesticide Science. 17, 311.

(4) H. Ellgehausen, C. D'Hondt and R. Fuerer (1981). Reversed-phase chromatography as a general method for determining octan-1-ol/water partition coefficients. Pesticide. Science. 12, 219.

(5) B. McDuffie (1981). Estimation of Octanol Water Partition Coefficients for Organic Pollutants Using Reverse Phase High Pressure Liquid Chromatography. Chemosphere. 10, 73.

(6) OECD (2000). Guideline for Testing of Chemicals — Partition Coefficient (n-octanol/water): pH-metric Method for Ionisable Substances. Draft Guideline, November 2000.

(7) OSPAR (1995). ‘Harmonised Offshore Chemicals Notification Format (HOCFN) 1995’, Oslo and Paris Conventions for the Prevention of Marine Pollution Programmes and Measures Committee (PRAM), Annex 10, Oviedo, 20–24 February 1995.

(8) M. Thatcher, M. Robinson, L. R. Henriquez and C. C. Karman. (1999). An User Guide for the Evaluation of Chemicals Used and Discharged Offshore, A CIN Revised CHARM III Report 1999. Version 1.0, 3. August.

(9) E. A. Vik, S. Bakke and K. Bansal. (1998). Partitioning of Chemicals. Important Factors in Exposure Assessment of Offshore Discharges. Environmental Modelling & Software Vol. 13, pp. 529-537.

(10) L.O. Renberg, S.G. Sundstroem and K. Sundh-Nygård. (1980). Partition coefficients of organic chemicals derived from reversed-phase thin-layer chromatography. Evaluation of methods and application on phosphate esters, polychlorinated paraffins and some PCB-substitutes. Chemosphere. 9, 683.

(11) W.E. Hammers, G.J.Meurs and C.L. De-Ligny. (1982). Correlations between liquid chromatographic capacity ratio data on Lichrosorb RP-18 and partition coefficients in the octanol-water system. J. Chromatography 247, 1.

(12) J.E. Haky and A.M. Young. (1984). Evaluation of a simple HPLC correlation method for the estimation of the octanol-water partition coefficients of organic compounds. J. Liq. Chromatography. 7, 675.

(13) S. Fujisawa and E. Masuhara. (1981). Determination of Partition Coefficients of Acrylates Methacrylates and Vinyl Monomers Using High Performance Liquid Chromatography. Journal of Biomedical Materials Research. 15, 787.

(14) C. Hansch and A. J. Leo. (1979). Substituent Constants for Correlation Analysis in Chemistry and Biology. John Willey, New York.

(15) C. Hansch, chairman; A.J. Leo, dir. (1982). Log P and Parameter Database: A tool for the quantitative prediction of bioactivity — Available from Pomona College Medical Chemistry Project, Pomona College, Claremont, California 91711.

(16) R. F. Rekker, H. M. de Kort. (1979). The hydrophobic fragmental constant: An extension to a 1 000 data point set. Eur. J. Med. Chem. — Chim. Ther. 14, 479.

(17) G.E. Berendsen, P.J. Schoenmakers, L. de Galan, G. Vigh, Z. Varga-Puchony, and J. Inczédy. (1980). On determination of hold-up time in reversed-phase liquid chromatography. J. Liq. Chromato. 3, 1669.

Appendix

POW calculation methods

INTRODUCTION

1. This appendix provides a short introduction to the calculation of Pow. For further information the reader is referred to textbooks (1)(2).

2. Calculated values of Pow are used for:

— 
deciding which experimental method to use: Shake Flask method for log Pow between – 2 and 4 and HPLC method for log Pow between 0 and 6;
— 
selecting conditions to be used in HPLC (reference substances, methanol/water ratio);
— 
checking the plausibility of values obtained through experimental methods;
— 
providing an estimate when experimental methods cannot be applied.

Principle of calculation methods

3. The calculation methods suggested here are based on the theoretical fragmentation of the molecule into suitable substructures for which reliable log Pow increments are known. The log Pow is obtained by summing the fragment values and the correction terms for intramolecular interactions. Lists of fragment constants and correction terms are available (1)(2)(3)(4)(5)(6). Some are regularly updated (3).

Reliability of calculated values

4. In general, the reliability of calculation methods decreases as the complexity of the substance under study increases. In the case of simple molecules of low molecular weight and with one or two functional groups, a deviation of 0,1 to 0,3 log Pow units between the results of the different fragmentation methods and the measured values can be expected. The margin of error will depend on the reliability of the fragment constants used, the ability to recognise intramolecular interactions (e.g. hydrogen bonds) and the correct use of correction terms. In the case of ionising substances the charge and degree of ionisation must be taken into consideration (10).

Fujita-Hansch π-method

5. The hydrophobic substituent constant, π, originally introduced by Fujita et al. (7) is defined as:

πX = log Pow (PhX) – log Pow (PhH)

where PhX is an aromatic derivative and PhH the parent substance.



e.g.

πCl

= log Pow (C6H5Cl) – log Pow (C6H6)

= 2,84 – 2,13

= 0,71

The π-method is primarily of interest for aromatic substances. π-values for a large number of substituents are available (4)(5).

Rekker method

6. Using the Rekker method (8) the log Pow value is calculated as:

image

where ai is the number of times a given fragment occurs in the molecule and fi is the log Pow increment of the fragment. The interaction terms can be expressed as an integral multiple of one single constant Cm (so-called ‘magic constant’). The fragment constants fi and Cm have been determined from a list of 1 054 experimental Pow values of 825 substances using multiple regression analysis (6)(8). The determination of the interaction terms is carried out according to set rules (6)(8)(9).

Hansch-Leo method

7. Using the Hansch and Leo method (4), the log Pow value is calculated as:

image

where fi is a fragment constant, Fj a correction term (factor), ai and bj the corresponding frequency of occurence. Lists of atomic and group fragmental values and of correction terms Fj were derived by trial and error from experimental Pow values. The correction terms have been divided into several different classes (1)(4). Sofware packages have been developed to take into account all the rules and correction terms (3).

COMBINED METHOD

8. The calculation of log Pow of complex molecules can be considerably improved, if the molecule is dissected into larger substructures for which reliable log Pow values are available, either from tables (3)(4) or by existing measurements. Such fragments (e.g. heterocycles, anthraquinone, azobenzene) can then be combined with the Hansch- π values or with Rekker or Leo fragment constants.

Remarks:

(i) 

The calculation methods are only applicable to partly or fully ionised substances when the necessary correction factors are taken into account.

(ii) 

If the existence of intramolecular hydrogen bonds can be assumed, the corresponding correction terms (approx. + 0,6 to + 1,0 log Pow units) must be added (1). Indications on the presence of such bonds can be obtained from stereo models or spectroscopic data.

(iii) 

If several tautomeric forms are possible, the most likely form should be used as the basis of the calculation.

(iv) 

The revisions of lists of fragment constants should be followed carefully.

LITERATURE ON CALCULATION METHODS

(1) W.J. Lyman, W.F. Reehl and D.H. Rosenblatt (ed.). Handbook of Chemical Property Estimation Methods, McGraw-Hill, New York (1982).

(2) W.J. Dunn, J.H. Block and R.S. Pearlman (ed.). Partition Coefficient, Determination and Estimation, Pergamon Press, Elmsford (New York) and Oxford (1986).

(3) Pomona College, Medicinal Chemistry Project, Claremont, California 91711, USA, Log P Database and Med. Chem. Software (Program CLOGP-3).

(4) C. Hansch and A.J. Leo. Substituent Constants for Correlation Analysis in Chemistry and Biology, John Wiley, New York (1979).

(5) Leo, C. Hansch and D. Elkins. (1971) Partition coefficients and their uses. Chemical. Reviews. 71, 525.

(6) R. F. Rekker, H. M. de Kort. (1979). The hydrophobic fragmental constant: An extension to a 1 000 data point set. Eur. J. Med. Chem. — Chim. Ther. 14, 479.

(7) Toshio Fujita, Junkichi Iwasa & Corwin Hansch (1964). A New Substituent Constant, π, Derived from Partition Coefficients. J. Amer. Chem. Soc. 86, 5175.

(8) R.F. Rekker. The Hydrophobic Fragmental Constant, Pharmacochemistry Library, Vol. 1, Elsevier, New York (1977).

(9) C.V. Eadsforth and P. Moser. (1983). Assessment of Reverse Phase Chromatographic Methods for Determining Partition Coefficients. Chemosphere. 12, 1459.

(10) R.A. Scherrer. ACS — Symposium Series 255, p. 225, American Chemical Society, Washington, D.C. (1984).

▼M7

A.25.   DISSOCIATION CONSTANTS IN WATER (TITRATION METHOD — SPECTROPHOTOMETRIC METHOD — CONDUCTOMETRIC METHOD)

INTRODUCTION

This test method is equivalent to OECD test guideline 112 (1981)

Prerequisites

— 
Suitable analytical method
— 
Water solubility

Guidance information

— 
Structural formula
— 
Electrical conductivity for conductometric method

Qualifying statements

— 
All test methods may be carried out on pure or commercial grade substances. The possible effects of impurities on results should be considered.
— 
The titration method is not suitable for low solubility substances (see Test solutions, below).
— 
The spectrophotometric method is only applicable to substances having appreciably different UV/VIS-absorption spectra for the dissociated and undissociated forms. This method may also be suitable for low solubility substances and for non-acid/base dissociations, e.g. complex formation.
— 
In cases where the Onsager equation holds, the conductometric method may be used, even at moderately low concentrations and even in cases for non-acid/base equilibria.

Standard documents

This test method is based on methods given in the references listed in the section ‘Literature’ and on the Preliminary Draft Guidance for Premanufacture Notification EPA, August 18, 1978.

METHOD — INTRODUCTION, PURPOSE, SCOPE, RELEVANCE, APPLICATION AND LIMITS OF TEST

The dissociation of a substance in water is of importance in assessing its impact upon the environment. It governs the form of the substance which in turn determines its behaviour and transport. It may affect the adsorption of the chemical on soils and sediments and absorption into biological cells.

Definitions and units

Dissociation is the reversible splitting into two or more chemical species which may be ionic. The process is indicated generally by

RXR ++ X

and the concentration equilibrium constant governing the reaction is

image

For example, in the particular case where R is hydrogen (the substance is an acid), the constant is

image

or

image

Reference substances

The following reference substances need not be employed in all cases when investigating a new substance. They are provided primarily so that calibration of the method may be performed from time to time and to offer the chance to compare the results when another method is applied.



 

pKa (1)

Temp. in °C

p-Nitrophenol

7,15

25 (1)

Benzoic acid

4,12

20

p-Chloroaniline

3,93

20

(1)   

No value for 20 °C is available, but it can be assumed that the variability of measurement results is higher than the temperature dependence to be expected.

It would be useful to have a substance with several pKs as indicated in Principle of the method, below. Such a substance could be:



Citric acid

pKa (8)

Temp. in °C

 

(1) 3,14

20

 

(2) 4,77

20

 

(3) 6,39

20

Principle of the test method

The chemical process described is generally only slightly temperature dependent in the environmentally relevant temperature range. The determination of the dissociation constant requires a measure of the concentrations of the dissociated and undissociated forms of the chemical substance. From the knowledge of the stoichiometry of the dissociation reaction indicated in Definitions and units, above, the appropriate constant can be determined. In the particular case described in this test method the substance is behaving as an acid or a base, and the determination is most conveniently done by determining the relative concentrations of the ionised and unionised forms of the substance and the pH of the solution. The relationship between these terms is given in the equation for pKa in Definitions and units, above. Some substances exhibit more than one dissociation constant and similar equations can be developed. Some of the methods described herein are also suitable for non-acid/base dissociation.

Quality criteria

Repeatability

The dissociation constant should be replicated (a minimum of three determinations) to within ± 0,1 log units.

DESCRIPTION OF THE TEST PROCEDURES

There are two basic approaches to the determination of pKa. One involves titrating a known amount of substance with standard acid or base, as appropriate; the other involves determining the relative concentration of the ionised and unionised forms and its pH dependence.

Preparations

Methods based on those principles may be classified as titration, spectrophotometric and conductometric procedures.

Test solutions

For the titration method and conductometric method the chemical substance should be dissolved in distilled water. For spectrophotometric and other methods buffer solutions are used. The concentration of the test substance should not exceed the lesser of 0,01 M or half the saturation concentration, and the purest available form of the substance should be employed in making up the solutions. If the substance is only sparingly soluble, it may be dissolved in a small amount of a water-miscible solvent prior to adding to the concentrations indicated above.

Solutions should be checked for the presence of emulsions using a Tyndall beam, especially if a co-solvent has been used to enhance solubility. Where buffer solutions are used, the buffer concentration should not exceed 0,05 M.

Test conditions

Temperature

The temperature should be controlled to at least ± 1 °C. The determination should preferably be carried out at 20 °C.

If a significant temperature dependence is suspected, the determination should be carried out at least at two other temperatures. The temperature intervals should be 10 °C in this case and the temperature control ± 0,1 °C.

Analyses

The method will be determined by the nature of the substance being tested. It must be sufficiently sensitive to allow the determination of the different species at each test solution concentration.

Performance of the test

Titration method

The test solution is determined by titration with the standard base or acid solution as appropriate, measuring the pH after each addition of titrant. At least 10 incremental additions should be made before the equivalence point. If equilibrium is reached sufficiently rapidly, a recording potentiometer may be used. For this method both the total quantity of substance and its concentration need to be accurately known. Precautions must be taken to exclude carbon dioxide. Details of procedure, precautions, and calculation are given in standard tests, e.g. references (1), (2), (3), (4).

Spectrophotometric method

A wavelength is found where the ionised and unionised forms of the substance have appreciably different extinction coefficients. The UV/VIS absorption spectrum is obtained from solutions of constant concentration under a pH condition where the substance is essentially unionised and fully ionised and at several intermediate pHs. This may be done, either by adding increments of concentrated acid (base) to a relatively large volume of a solution of the substance in a multicomponent buffer, initially at high (low) pH (ref. 5), or by adding equal volumes of a stock solution of the substance in e.g. water, methanol, to constant volumes of various buffer solutions covering the desired pH range. From the pH and absorbance values at the chosen wavelength, a sufficient number of values for the pKa is calculated using data from at least 5 pHs where the substance is at least 10 per cent and less than 90 per cent ionised. Further experimental details and method of calculation are given in reference (1).

Conductometric method

Using a cell of small, known cell constant, the conductivity of an approximately 0,1 M solution of the substance in conductivity water is measured. The conductivities of a number of accurately-made dilutions of this solution are also measured. The concentration is halved each time, and the series should cover at least an order of magnitude in concentration. The limiting conductivity at infinite dilution is found by carrying out a similar experiment with the Na salt and extrapolating. The degree of dissociation may then be calculated from the conductivity of each solution using the Onsager equation, and hence using the Ostwald Dilution Law the dissociation constant may be calculated as K = α2C/(1 – α) where C is the concentration in moles per litre and α is the fraction dissociated. Precautions must be taken to exclude CO2. Further experimental details and method of calculation are given in standard texts and references (1), (6) and (7).

DATA AND REPORTING

Treatment of results

Titration method

The pKa is calculated for 10 measured points on the titration curve. The mean and standard deviation of such pKa values are calculated. A plot of pH versus volume of standard base or acid should be included along with a tabular presentation.

Spectrophotometric methods

The absorbance and pH are tabulated from each spectrum. At least five values for the pKa are calculated from the intermediate spectra data points, and the mean and standard deviation of these results are also calculated.

Conductometric method

The equivalent conductivity Λ is calculated for each acid concentration and for each concentration of a mixture of one equivalent of acid, plus 0,98 equivalent of carbonate-free sodium hydroxide. The acid is in excess to prevent an excess of OH due to hydrolysis. 1/Λ is plotted against C and Λo of the salt can be found by extrapolation to zero concentration.

Λo of the acid can be calculated using literature values for H+ and Na+. The pKa can be calculated from α = Λio and Ka = α2C/(1 – α) for each concentration. Better values for Ka can be obtained by making corrections for mobility and activity. The mean and standard deviations of the pKa values should be calculated.

Test report

All raw data and calculated pKa values should be submitted together with the method of calculation (preferably in a tabulated format, such as suggested in ref. 1) as should the statistical parameters described above. For titration methods, details of the standardisation of titrants should be given.

For the spectrophotometric method, all spectra should be submitted. For the conductometric method, details of the cell constant determination should be reported. Information on technique used, analytical methods and the nature of any buffers used should be given.

The test temperature(s) should be reported.

LITERATURE:

(1) 

Albert, A. & Sergeant, E.P.: Ionization Constants of Acids and Bases, Wiley, Inc., New York, 1962.

(2) 

Nelson, N.H. & Faust, S.D.: Acidic dissociation constants of selected aquatic herbicides, Env. Sci. Tech. 3, II, pp. 1186-1188 (1969).

(3) 

ASTM D 1293 — Annual ASTM Standards, Philadelphia, 1974.

(4) 

Standard Method 242. APHA/AWWA/WPCF, Standard Methods for the Examination of Water and Waste Water, 14th Edition, American Public Health Association, Washington, D.C., 1976.

(5) 

Clark, J. & Cunliffe, A.E.: Rapid spectrophotometric measurement of ionisation constants in aqueous solution. Chem. Ind. (London) 281, (March 1973).

(6) 

ASTM D 1125 — Annual ASTM Standards, Philadelphia, 1974.

(7) 

Standard Method 205 — APHA/AWWA/NPCF (see above (4)).

(8) 

Handbook of Chemistry and Physics, 60th ed. CRC-Press, Boca Raton, Florida, 33431 (1980).

▼B




PART B: METHODS FOR THE DETERMINATION OF TOXICITY AND OTHER HEALTH EFFECTS

TABLE OF CONTENTS

GENERAL INTRODUCTION

B.1 bis.

ACUTE ORAL TOXICITY — FIXED DOSE PROCEDURE

B.1 tris.

ACUTE ORAL TOXICITY — ACUTE TOXIC CLASS METHOD

B.2.

ACUTE INHALATION TOXICITY

B.3.

ACUTE TOXICITY (DERMAL)

B.4.

ACUTE DERMAL IRRITATION/CORROSION

B.5.

ACUTE EYE IRRITATION/CORROSION

B.6.

SKIN SENSITISATION

B.7.

REPEATED DOSE 28-DAY ORAL TOXICITY STUDY IN RODENTS

B.8.

SUBACUTE INHALATION TOXICITY: 28-DAY STUDY

B.9.

REPEATED DOSE (28 DAYS) TOXICITY (DERMAL)

B.10.

IN VITRO MAMMALIAN CHROMOSOMAL ABERRATION TEST

B.11.

MAMMALIAN BONE MARROW CHROMOSOMAL ABERRATION TEST

B.12.

MAMMALIAN ERYTHROCYTE MICRONUCLEUS TEST

B.13/14.

MUTAGENICITY: REVERSE MUTATION TEST USING BACTERIA

B.17.

IN VITRO MAMMALIAN CELL GENE MUTATION TESTS USING THE HPRT AND XPRT GENES

B.21.

IN VITRO MAMMALIAN CELL TRANSFORMATION TESTS

B.22.

RODENT DOMINANT LETHAL TEST

B.23.

MAMMALIAN SPERMATOGONIAL CHROMOSOMAL ABERRATION TEST

B.25.

MOUSE HERITABLE TRANSLOCATION

B.26.

SUB-CHRONIC ORAL TOXICITY TEST REPEATED DOSE 90 — DAY ORAL TOXICITY STUDY IN RODENTS

B.27.

SUB-CHRONIC ORAL TOXICITY TEST REPEATED DOSE 90 — DAY ORAL TOXICITY STUDY IN NON-RODENTS

B.28.

SUB-CHRONIC DERMAL TOXICITY STUDY 90-DAY REPEATED DERMAL DOSE STUDY USING RODENT SPECIES

B.29.

SUBCHRONIC INHALATION TOXICITY: 90-DAY STUDY

B.30.

CHRONIC TOXICITY STUDIES

B.31.

PRENATAL DEVELOPMENTAL TOXICITY STUDY

B.32.

CARCINOGENICITY STUDIES

B.33.

COMBINED CHRONIC TOXICITY/CARCINOGENICITY STUDIES

B.34.

ONE-GENERATION REPRODUCTION TOXICITY TEST

B.35.

TWO-GENERATION REPRODUCTION TOXICITY STUDY

B.36.

TOXICOKINETICS

B.37.

DELAYED NEUROTOXICITY OF ORGANOPHOSPHORUS SUBSTANCES FOLLOWING ACUTE EXPOSURE

B.38.

DELAYED NEUROTOXICITY OF ORGANOPHOSPHORUS SUBSTANCES 28 DAY REPEATED DOSE STUDY

B.39.

UNSCHEDULED DNA SYNTHESIS (UDS) TEST WITH MAMMALIAN LIVER CELLS IN VIVO

B.40.

IN VITRO SKIN CORROSION: TRANSCUTANEOUS ELECTRICAL RESISTANCE TEST METHOD (TER)

B.40 BIS.

IN VITRO SKIN CORROSION: RECONSTRUCTED HUMAN EPIDERMIS (RhE) TEST METHOD

B.41.

IN VITRO 3T3 NRU PHOTOTOXICITY TEST

B.42.

SKIN SENSITISATION: LOCAL LYMPH NODE ASSAY

B.43.

NEUROTOXICITY STUDY IN RODENTS

B.44.

SKIN ABSORPTION: IN VIVO METHOD

B.45.

SKIN ABSORPTION: IN VITRO METHOD

B.46.

IN VITRO SKIN IRRITATION: RECONSTRUCTED HUMAN EPIDERMIS TEST METHOD

B.47.

BOVINE CORNEAL OPACITY AND PERMEABILITY TEST METHOD FOR IDENTIFYING (I) CHEMICALS INDUCING SERIOUS EYE DAMAGE AND (II) CHEMICALS NOT REQUIRING CLASSIFICATION FOR EYE IRRITATION OR SERIOUS EYE DAMAGE

B.48.

ISOLATED CHICKEN EYE TEST METHOD FOR IDENTIFYING I) CHEMICALS INDUCING SERIOUS EYE DAMAGE AND II) CHEMICALS NOT REQUIRING CLASSIFICATION FOR EYE IRRITATION OR SERIOUS EYE DAMAGE

B.49.

IN VITRO MAMMALIAN CELL MICRONUCLEUS TEST

B.50.

SKIN SENSITISATION: LOCAL LYMPH NODE ASSAY: DA

B.51.

SKIN SENSITISATION: LOCAL LYMPH NODE ASSAY: BrdU-ELISA

B.52.

ACUTE INHALATION TOXICITY — ACUTE TOXIC CLASS METHOD

B.53.

DEVELOPMENTAL NEUROTOXICITY STUDY

B.54.

UTEROTROPHIC BIOASSAY IN RODENTS: A SHORT-TERM SCREENING TEST FOR OESTROGENIC PROPERTIES

B.55.

HERSHBERGER BIOASSAY IN RATS: A SHORT-TERM SCREENING ASSAY FOR (ANTI)ANDROGENIC PROPERTIES

B.56.

EXTENDED ONE-GENERATION REPRODUCTIVE TOXICITY STUDY

B.57.

H295R STEROIDOGENESIS ASSAY

B.58.

TRANSGENIC RODENT SOMATIC AND GERM CELL GENE MUTATION ASSAYS

B.59.

IN CHEMICO SKIN SENSITISATION: DIRECT PEPTIDE REACTIVITY ASSAY (DPRA)

B.60.

IN VITRO SKIN SENSITISATION: ARE-NRF2 LUCIFERASE TEST METHOD

B.61.

FLUORESCEIN LEAKAGE TEST METHOD FOR IDENTIFYING OCULAR CORROSIVES AND SEVERE IRRITANTS

B.62.

IN VIVO MAMMALIAN ALKALINE COMET ASSAY

B.63.

REPRODUCTION/DEVELOPMENTAL TOXICITY SCREENING TEST

B.64.

COMBINED REPEATED DOSE TOXICITY STUDY WITH THE REPRODUCTION/DEVELOPMENTAL TOXICITY SCREENING TEST

B.65.

IN VITRO MEMBRANE BARRIER TEST METHOD FOR SKIN CORROSION

B.66.

STABLY TRANSFECTED TRANSACTIVATION IN VITRO ASSAYS TO DETECT ESTROGEN RECEPTOR AGONISTS AND ANTAGONISTS

B.67.

IN VITRO MAMMALIAN CELL GENE MUTATION TESTS USING THE THYMIDINE KINASE GENE

B.68.

SHORT TIME EXPOSURE IN VITRO TEST METHOD FOR IDENTIFYING i) CHEMICALS INDUCING SERIOUS EYE DAMAGE AND ii) CHEMICALS NOT REQUIRING CLASSIFICATION FOR EYE IRRITATION OR SERIOUS EYE DAMAGE

B.69.

RECONSTRUCTED HUMAN CORNEA-LIKE EPITHELIUM (RhCE) TEST METHOD FOR IDENTIFYING CHEMICALS NOT REQUIRING CLASSIFICATION AND LABELLING FOR EYE IRRITATION OR SERIOUS EYE DAMAGE

B.70.

HUMAN RECOMBINANT ESTROGEN RECEPTOR (hrER) IN VITRO ASSAYS TO DETECT CHEMICALS WITH ER BINDING AFFINITY

B.71.

IN VITRO SKIN SENSITISATION ASSAYS ADDRESSING THE KEY EVENT ON ACTIVATION OF DENDRITIC CELLS ON THE ADVERSE OUTCOME PATHWAY (AOP) FOR SKIN SENSITISATION

GENERAL INTRODUCTION

A.   CHARACTERISATION OF THE TEST SUBSTANCE

The composition of the test substance, including major impurities, and its relevant physico-chemical properties including stability, should be known prior to the initiation of any toxicity study.

The physico-chemical properties of the test substance provide important information for the selection of the route of administration, the design of each particular study and the handling and storage of the test substance.

The development of an analytical method for qualitative and quantitative determination of the test substance (including major impurities when possible) in the dosing medium and the biological material should precede the initiation of the study.

All information relating to the identification, the physico-chemical properties, the purity, and behaviour of the test substance should be included in the test report.

B.   ANIMAL CARE

Stringent control of environmental conditions and proper animal care techniques are essential in toxicity testing.

(i)   Housing conditions

The environmental conditions in the experimental animal rooms or enclosures should be appropriate to the test species. For rats, mice and guinea pigs, suitable conditions are a room temperature of 22 oC ± 3 oC with a relative humidity of 30 to 70 %; for rabbits the temperature should be 20 ± 3 oC with a relative humidity of 30 to 70 %.

Some experimental techniques are particularly sensitive to temperature effects and, in these cases, details of appropriate conditions are included in the description of the test method. In all investigations of toxic effects, the temperature and humidity should be monitored, recorded, and included in the final report of the study.

Lighting should be artificial, the sequence being 12 hours light, 12 hours dark. Details of the lighting pattern should be recorded and included in the final report of the study.

Unless otherwise specified in the method, animals may be housed individually, or be caged in small groups of the same sex; for group caging, no more than five animals should be housed per cage.

In reports of animal experiments, it is important to indicate the type of caging used and the number of animals housed in each cage both during exposure to the chemical and any subsequent observation period.

(ii)   Feeding conditions

Diets should meet all the nutritional requirements of the species under test. Where test substances are administered to animals in their diet the nutritional value may be reduced by interaction between the substance and a dietary constituent. The possibility of such a reaction should be considered when interpreting the results of tests. Conventional laboratory diets may be used with an unlimited supply of drinking water. The choice of the diet may be influenced by the need to ensure a suitable admixture of a test substance when administered by this method.

Dietary contaminants which are known to influence the toxicity should not be present in interfering concentrations.

C.   ALTERNATIVE TESTING

The European Union is committed to promoting the development and validation of alternative techniques which can provide the same level of information as current animal tests, but which use fewer animals, cause less suffering or avoid the use of animals completely.

Such methods, as they become available, must be considered wherever possible for hazard characterisation and consequent classification and labelling for intrinsic hazards and chemical safety assessment.

D.   EVALUATION AND INTERPRETATION

When tests are evaluated and interpreted, limitations in the extent to which the results of animal and in vitro studies can be extrapolated directly to man must be considered and therefore, evidence of adverse effects in humans, where available, may be used for confirmation of testing results.

E.   LITERATURE REFERENCES

Most of these methods are developed within the framework of the OECD programme for Testing Guidelines, and should be performed in conformity with the principles of Good Laboratory Practice, in order to ensure as wide as possible ‘mutual acceptance of data’.

Additional information may be found in the references listed in the OECD guidelines and the relevant literature published elsewhere.

B.1 bis.   ACUTE ORAL TOXICITY — FIXED DOSE PROCEDURE

1.   METHOD

This test method is equivalent to OECD TG 420 (2001)

1.1.   INTRODUCTION

Traditional methods for assessing acute toxicity use death of animals as an endpoint. In 1984, a new approach to acute toxicity testing was suggested by the British Toxicology Society based on the administration at a series of fixed dose levels (1). The approach avoided using death of animals as an endpoint, and relied instead on the observation of clear signs of toxicity at one of a series of fixed dose levels. Following UK (2) and international (3) in vivo validation studies the procedure was adopted as a testing method in 1992. Subsequently, the statistical properties of the Fixed Dose Procedure have been evaluated using mathematical models in a series of studies (4)(5)(6). Together, the in vivo and modelling studies have demonstrated that the procedure is reproducible, uses fewer animals and causes less suffering than the traditional methods and is able to rank substances in a similar manner to the other acute toxicity testing methods.

Guidance on the selection of the most appropriate test method for a given purpose can be found in the Guidance Document on Acute Oral Toxicity Testing (7). This guidance document also contains additional information on the conduct and interpretation of Testing Method B.1bis.

It is a principle of the method that in the main study only moderately toxic doses are used, and that administration of doses that are expected to be lethal should be avoided. Also, doses that are known to cause marked pain and distress, due to corrosive or severely irritant actions, need not be administered. Moribund animals, or animals obviously in pain or showing signs of severe and enduring distress shall be humanely killed, and are considered in the interpretation of the test results in the same way as animals that died on test. Criteria for making the decision to kill moribund or severely suffering animals, and guidance on the recognition of predictable or impending death, are the subject of a separate Guidance Document (8).

The method provides information on the hazardous properties and allows the substance to be ranked and classified according to the Globally Harmonised System (GHS) for the classification of chemicals which cause acute toxicity (9).

The testing laboratory should consider all available information on the test substance prior to conducting the study. Such information will include the identity and chemical structure of the substance; its physico-chemical properties; the results of any other in vitro or in vivo toxicity tests on the substance; toxicological data on structurally related substances; and the anticipated use(s) of the substance. This information is necessary to satisfy all concerned that the test is relevant for the protection of human health, and will help in the selection of an appropriate starting dose.

1.2.   DEFINITIONS

Acute oral toxicity: refers to those adverse effects occurring following oral administration of a single dose of a substance or multiple doses given within 24 hours.

Delayed death: means that an animal does not die or appear moribund within 48 hours but dies later during the 14-day observation period.

Dose: is the amount of test substance administered. Dose is expressed as weight of test substance per unit weight of test animal (e.g. mg/kg).

Evident toxicity: is a general term describing clear signs of toxicity following the administration of test substance (see (3) for examples) such that at the next highest fixed dose either severe pain and enduring signs of severe distress, moribund status (criteria are presented in the Humane Endpoints Guidance Document (8)), or probable mortality in most animals can be expected.

GHS: Globally Harmonised Classification System for Chemical Substances and Mixtures. A joint activity of OECD (human health and the environment), UN Committee of Experts on Transport of Dangerous Goods (physical-chemical properties) and ILO (hazard communication) and coordinated by the Interorganisation Programme for the Sound Management of Chemicals (IOMC).

Impending death: when moribund state or death is expected prior to the next planned time of observation. Signs indicative of this state in rodents could include convulsions, lateral position, recumbence and tremor. (See the Humane Endpoint Guidance Document (8) for more details).

LD 50 (median lethal dose): is a statistically derived single dose of a substance that can be expected to cause death in 50 % of animals when administered by the oral route. The LD 50 value is expressed in terms of weight of test substance per unit weight of test animal (mg/kg).

Limit dose: refers to a dose at an upper limitation on testing (2 000 or 5 000 mg/kg).

Moribund status: being in a state of dying or inability to survive, even if treated. (See the Humane Endpoint Guidance Document (8) for more details).

Predictable death: presence of clinical signs indicative of death at a known time in the future before the planned end of the experiment, for example: inability to reach water or food. (See the Humane Endpoint Guidance Document (8) for more details).

1.3.   PRINCIPLE OF THE TEST METHOD

Groups of animals of a single sex are dosed in a stepwise procedure using the fixed doses of 5, 50, 300 and 2 000 mg/kg (exceptionally an additional fixed dose of 5 000 mg/kg may be considered, see Section 1.6.2). The initial dose level is selected on the basis of a sighting study as the dose expected to produce some signs of toxicity without causing severe toxic effects or mortality. Clinical signs and conditions associated with pain, suffering, and impending death, are described in detail in a separate OECD Guidance Document (8). Further groups of animals may be dosed at higher or lower fixed doses, depending on the presence or absence of signs of toxicity or mortality. This procedure continues until the dose causing evident toxicity or no more than one death is identified, or when no effects are seen at the highest dose or when deaths occur at the lowest dose.

1.4.   DESCRIPTION OF THE TEST METHOD

1.4.1.   Selection of animal species

The preferred rodent species is the rat, although other rodent species may be used. Normally females are used (7). This is because literature surveys of conventional LD50 tests show that usually there is little difference in sensitivity between the sexes, but in those cases where differences are observed, females are generally slightly more sensitive (10). However, if knowledge of the toxicological or toxicokinetic properties of structurally related chemicals indicates that males are likely to be more sensitive then this sex should be used. When the test is conducted in males, adequate justification should be provided.

Healthy young adult animals of commonly used laboratory strains should be employed. Females should be nulliparous and non-pregnant. Each animal, at the commencement of its dosing, should be between eight and 12 weeks old and its weight should fall in an interval within ± 20 % of the mean weight of any previously dosed animals.

1.4.2.   Housing and feeding conditions

The temperature of the experimental animal room should be 22 oC (± 3 oC). Although the relative humidity should be at least 30 % and preferably not exceed 70 % other than during room cleaning the aim should be 50-60 %. Lighting should be artificial, the sequence being 12 hours light, 12 hours dark. For feeding, conventional laboratory diets may be used with an unlimited supply of drinking water. Animals may be group-caged by dose, but the number of animals per cage must not interfere with clear observations of each animal.

1.4.3.   Preparation of animals

The animals are randomly selected, marked to permit individual identification, and kept in their cages for at least five days prior to the start of dosing to allow for acclimatisation to the laboratory conditions.

1.4.4.   Preparation of doses

In general test substances should be administered in a constant volume over the range of doses to be tested by varying the concentration of the dosing preparation. Where a liquid end product or mixture is to be tested however, the use of the undiluted test substance, i.e. at a constant concentration, may be more relevant to the subsequent risk assessment of that substance, and is a requirement of some regulatory authorities. In either case, the maximum dose volume for administration must not be exceeded. The maximum volume of liquid that can be administered at one time depends on the size of the test animal. In rodents, the volume should not normally exceed 1ml /100 g of body weight: however in the case of aqueous solutions 2 ml/100 g body weight can be considered. With respect to the formulation of the dosing preparation, the use of an aqueous solution/suspension/emulsion is recommended wherever possible, followed in order of preference by a solution/suspension/emulsion in oil (e.g. corn oil) and then possibly solution in other vehicles. For vehicles other than water the toxicological characteristics of the vehicle should be known. Doses must be prepared shortly prior to administration unless the stability of the preparation over the period during which it will be used is known and shown to be acceptable.

1.5.   PROCEDURE

1.5.1.   Administration of doses

The test substance is administered in a single dose by gavage using a stomach tube or a suitable intubation canula. In the unusual circumstance that a single dose is not possible, the dose may be given in smaller fractions over a period not exceeding 24 hours.

Animals should be fasted prior to dosing (e.g. with the rat, food but not water should be withheld over-night; with the mouse, food but not water should be withheld for three to four hours). Following the period of fasting, the animals should be weighed and the test substance administered. After the substance has been administered, food may be withheld for a further three to four hours in rats or one to two hours in mice. Where a dose is administered in fractions over a period of time, it may be necessary to provide the animals with food and water depending on the length of the period.

1.5.2.   Sighting study

The purpose of the sighting study is to allow selection of the appropriate starting dose for the main study. The test substance is administered to single animals in a sequential manner following the flowcharts in Appendix 1. The sighting study is completed when a decision on the starting dose for the main study can be made (or if a death is seen at the lowest fixed dose).

The starting dose for the sighting study is selected from the fixed dose levels of 5, 50, 300 and 2 000 mg/kg as a dose expected to produce evident toxicity based, when possible, on evidence from in vivo and in vitro data from the same chemical and from structurally related chemicals. In the absence of such information, the starting dose will be 300 mg/kg.

A period of at least 24 hours will be allowed between the dosing of each animal. All animals should be observed for at least 14 days.

Exceptionally, and only when justified by specific regulatory needs, the use of an additional upper fixed dose level of 5 000 mg/kg may be considered (see Appendix 3). For reasons of animal welfare concern, testing of animals in GHS Category 5 ranges (2 000 -5 000 mg/kg is discouraged and should only be considered when there is a strong likelihood that the results of such a test have a direct relevance for protecting human or animal health or the environment.

In cases where an animal tested at the lowest fixed dose level (5 mg/kg) in the sighting study dies, the normal procedure is to terminate the study and assign the substance to GHS Category 1 (as shown in Appendix 1). However, if further confirmation of the classification is required, an optional supplementary procedure may be conducted, as follows. A second animal is dosed at 5 mg/kg. If this second animal dies, then GHS Category 1 will be confirmed and the study will be immediately terminated. If the second animal survives, then a maximum of three additional animals will be dosed at 5 mg/kg. Because there will be a high risk of mortality, these animals should be dosed in a sequential manner to protect animal welfare. The time interval between dosing each animal should be sufficient to establish that the previous animal is likely to survive. If a second death occurs, the dosing sequence will be immediately terminated and no further animals will be dosed. Because the occurrence of a second death (irrespective of the number of animals tested at the time of termination) falls into outcome A (two or more deaths), the classification rule of Appendix 2 at the 5 mg/kg fixed dose is followed (Category 1 if there are two or more deaths or Category 2 if there is no more than one death). In addition, Appendix 4 gives guidance on the classification in the EU system until the new GHS is implemented.

1.5.3.   Main study

1.5.3.1.   Numbers of animals and dose levels

The action to be taken following testing at the starting dose level is indicated by the flowcharts in Appendix 2. One of three actions will be required; either stop testing and assign the appropriate hazard classification class, test at a higher fixed dose or test at a lower fixed dose. However, to protect animals, a dose level that caused death in the sighting study will not be revisited in the main study (see Appendix 2). Experience has shown that the most likely outcome at the starting dose level will be that the substance can be classified and no further testing will be necessary.

A total of five animals of one sex will normally be used for each dose level investigated. The five animals will be made up of one animal from the sighting study dosed at the selected dose level together with an additional four animals (except, unusually, if a dose level used on the main study was not included in the sighting study).

The time interval between dosing at each level is determined by the onset, duration, and severity of toxic signs. Treatment of animals at the next dose should be delayed until one is confident of survival of the previously dosed animals. A period of three or four days between dosing at each dose level is recommended, if needed, to allow for the observation of delayed toxicity. The time interval may be adjusted as appropriate, e.g. in case of inconclusive response.

When the use of an upper fixed dose of 5 000 mg/kg is considered, the procedure outlined in Appendix 3 should be followed (see also section 1.6.2).

1.5.3.2.   Limit test

The limit test is primarily used in situations where the experimenter has information indicating that the test material is likely to be nontoxic, i.e., having toxicity only above regulatory limit doses. Information about the toxicity of the test material can be gained from knowledge about similar tested compounds or similar tested mixtures or products, taking into consideration the identity and percentage of components known to be of toxicological significance. In those situations where there is little or no information about its toxicity, or in which the test material is expected to be toxic, the main test should be performed.

Using the normal procedure, a sighting study starting dose of 2 000 mg/kg (or exceptionally 5 000 mg/kg) followed by dosing of a further four animals at this level serves as a limit test for this guideline.

1.6.   OBSERVATIONS

Animals are observed individually after dosing at least once during the first 30 minutes, periodically during the first 24 hours, with special attention given during the first four hours, and daily thereafter, for a total of 14 days, except where they need to be removed from the study and humanely killed for animal welfare reasons or are found dead. However, the duration of observation should not be fixed rigidly. It should be determined by the toxic reactions, time of onset and length of recovery period, and may thus be extended when considered necessary. The times at which signs of toxicity appear and disappear are important, especially if there is a tendency for toxic signs to be delayed (11). All observations are systematically recorded, with individual records being maintained for each animal.

Additional observations will be necessary if the animals continue to display signs of toxicity. Observations should include changes in skin and fur, eyes and mucous membranes, and also respiratory, circulatory, autonomic and central nervous systems, and somatomotor activity and behaviour pattern. Attention should be directed to observations of tremors, convulsions, salivation, diarrhoea, lethargy, sleep and coma. The principles and criteria summarised in the Humane Endpoints Guidance Document should be taken into consideration (8). Animals found in a moribund condition and animals showing severe pain or enduring signs of severe distress should be humanely killed. When animals are killed for humane reasons or found dead, the time of death should be recorded as precisely as possible.

1.6.1.   Body weight

Individual weights of animals should be determined shortly before the test substance is administered and at least weekly thereafter. Weight changes should be calculated and recorded. At the end of the test surviving animals are weighed and then humanely killed.

1.6.2.   Pathology

All test animals (including those that die during the test or are removed from the study for animal welfare reasons) should be subjected to gross necropsy. All gross pathological changes should be recorded for each animal. Microscopic examination of organs showing evidence of gross pathology in animals surviving 24 or more hours after the initial dosing may also be considered because it may yield useful information.

2.   DATA

Individual animal data should be provided. Additionally, all data should be summarised in tabular form, showing for each test group the number of animals used, the number of animals displaying signs of toxicity, the number of animals found dead during the test or killed for humane reasons, time of death of individual animals, a description and the time course of toxic effects and reversibility, and necropsy findings.

3.   REPORTING

3.1.   TEST REPORT

The test report must include the following information, as appropriate:

Test substance:
— 
physical nature, purity, and, where relevant, physico-chemical properties (including isomerisation),
— 
identification data, including CAS number.
Vehicle (if appropriate):
— 
justification for choice of vehicle, if other than water.
Test animals:
— 
species/strain used,
— 
microbiological status of the animals, when known,
— 
number, age and sex of animals (including, where appropriate, a rationale for use of males instead of females),
— 
source, housing conditions, diet, etc.
Test conditions:
— 
details of test substance formulation, including details of the physical form of the material administered,
— 
details of the administration of the test substance including dosing volumes and time of dosing,
— 
details of food and water quality (including diet type/source, water source),
— 
the rationale for the selection of the starting dose.
Results:
— 
tabulation of response data and dose level for each animal (i.e. animals showing signs of toxicity including mortality, nature, severity and duration of effects),
— 
tabulation of body weight and body weight changes,
— 
individual weights of animals at the day of dosing, in weekly intervals thereafter, and at time of death or sacrifice,
— 
date and time of death if prior to scheduled sacrifice,
— 
time course of onset of signs of toxicity and whether these were reversible for each animal,
— 
necropsy findings and histopathological findings for each animal, if available.
Discussion and interpretation of results.
Conclusions.

4.   REFERENCES

(1) British Toxicology Society Working Party on Toxicity (1984) Special report: a new approach to the classification of substances and preparations on the basis of their acute toxicity. Human Toxicol., 3, p. 85-92.

(2) Van den Heuvel, M.J., Dayan, A.D. and Shillaker, R.O (1987) Evaluation of the BTS approach to the testing of substances and preparations for their acute toxicity. Human Toxicol.‚ 6, p. 279-291.

(3) Van den Heuvel, M.J., Clark, D.G., Fielder, R.J., Koundakjian, P.P., Oliver, G.J.A., Pelling, D., Tomlinson, N.J. and Walker, A.P (1990) The international validation of a fixed-dose procedure as an alternative to the classical LD50 test. Fd. Chem. Toxicol. 28, p. 469-482.

(4) Whitehead, A. and Curnow, R.N (1992) Statistical evaluation of the fixed-dose procedure. Fd. Chem. Toxicol., 30, p. 313-324.

(5) Stallard, N. and Whitehead, A (1995) Reducing numbers in the fixed-dose procedure. Human Exptl. Toxicol. 14, p. 315-323.

(6) Stallard, N., Whitehead, A and Ridgeway, P. (2002) Statistical evaluation of the revised fixed dose procedure. Hum. Exp. Toxicol., 21, p. 183-196.

(7) OECD (2001) Guidance Document on Acute Oral Toxicity Testing. Environmental Health and Safety Monograph Series on Testing and Assessment No 24. Paris

(8) OECD (2000) Guidance Document on the Recognition, Assessment and Use of Clinical Signs as Humane Endpoints for Experimental Animals Used in Safety Evaluation. Environmental Health and Safety Monograph Series on Testing and Assesment No 19.

(9) OECD (1998) Harmonised Integrated Hazard Classification for Human Health and Environmental Effects of Chemical Substances as endorsed by the 28th Joint Meeting of the Chemicals Committee and the Working Party on Chemicals in November 1998, Part 2, p. 11 [http://webnet1.oecd.org/oecd/pages/home/displaygeneral/0,3380, EN-documents-521-14-no-24-no-0,FF.html].

(10) Lipnick, R.L., Cotruvo, J.A., Hill, R.N., Bruce, R.D., Stitzel, K.A., Walker, A.P., Chu, I., Goddard, M., Segal, L., Springer, J.A. and Myers, R.C (1995) Comparison of the Up-and-Down, Conventional LD50, and Fixed-Dose Acute Toxicity Procedures. Fd. Chem. Toxicol. 33, p. 223-231.

(11) Chan P.K and A. W Hayes (1994) Chapter 16 Acute Toxicity and Eye Irritation. In: Principles and Methods of Toxicology. 3rd Edition. A.W. Hayes, Editor. Raven Press Ltd. New York, USA.

Appendix 1

FLOW CHART FOR THE SIGHTING STUDY

image

Text of image