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Periodical
OECD Guidelines for the Testing of Chemicals, Section 1 : Physical-Chemical properties
ISSN: 20745753 Year: 1981 Publisher: Paris : OECD Publishing.

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Abstract

The OECD Guidelines for the Testing of Chemicals is a collection of about 150 of the most relevant internationally agreed testing methods used by government, industry and independent laboratories to identify and characterise potential hazards of chemicals. They are a set of tools for professionals, used primarily in regulatory safety testing and subsequent chemical and chemical product notification, chemical registration and in chemical evaluation. They can also be used for the selection and ranking of candidate chemicals during the development of new chemicals and products and in toxicology research. This group of tests covers physical-chemical properties.


Periodical
OECD Guidelines for the Testing of Chemicals, Section 2 : Effects on Biotic Systems
ISSN: 20745761 Year: 1984 Publisher: Paris : OECD Publishing.

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Abstract

The OECD Guidelines for the Testing of Chemicals is a collection of about 150 of the most relevant internationally agreed testing methods used by government, industry and independent laboratories to identify and characterise potential hazards of chemicals. They are a set of tools for professionals, used primarily in regulatory safety testing and subsequent chemical and chemical product notification, chemical registration and in chemical evaluation. They can also be used for the selection and ranking of candidate chemicals during the development of new chemicals and products and in toxicology research. This group of tests covers effects on biotic systems.


Periodical
OECD Guidelines for the Testing of Chemicals, Section 5 : Other Test Guidelines
ISSN: 20745796 Year: 2007 Publisher: Paris : OECD Publishing.

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Abstract

The OECD Guidelines for the Testing of Chemicals is a collection of about 150 of the most relevant internationally agreed testing methods used by government, industry and independent laboratories to identify and characterise potential hazards of chemicals. They are a set of tools for professionals, used primarily in regulatory safety testing and subsequent chemical and chemical product notification, chemical registration and in chemical evaluation. They can also be used for the selection and ranking of candidate chemicals during the development of new chemicals and products and in toxicology research. This group of tests covers other test guidelines.


Periodical
OECD Series on Testing and Assessment
ISSN: 20777876 Year: 2019 Publisher: Paris : OECD Publishing.

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Abstract

This Series includes publications related to testing and assessment of chemicals; some of them support the development of OECD Test Guidelines (e.g. validation reports, guidance documents, detailed review papers).


Book
Test No. 478: Rodent Dominant Lethal Test
Author:
ISBN: 9264243119 Year: 2015 Publisher: Paris : OECD Publishing,

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Abstract

The purpose of the Dominant lethal (DL) test is to investigate whether chemical agents produce mutations resulting from chromosomal aberrations in germ cells. In addition, the dominant lethal test is relevant to assessing genotoxicity because, although they may vary among species, factors of in vivo metabolism, pharmacokinetics and DNA-repair processes are active and contribute to the response. Induction of a DL mutation after exposure to a test chemical indicates that the chemical has affected germinal tissue of the test animal. This modified version of the Test Guideline reflects more than thirty years of experience with this test and the potential for integrating or combining this test with other toxicity tests such as developmental, reproductive toxicity, or genotoxicity studies; however due to its limitations and the use of a large number of animals this assay is not intended for use as a primary method, but rather as a supplemental test method which can only be used when there is no alternative for regulatory requirements.


Book
Test No. 312: Leaching in Soil Columns
Author:
ISBN: 9264070567 Year: 2004 Publisher: Paris : OECD Publishing,

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Abstract

The method described in this Test Guideline is based on soil column chromatography in disturbed soil. Two types of experiments are performed to determine (i) the leaching potential of the test substance, and (ii) the leaching potential of transformation products in soils under controlled laboratory conditions. At least duplicate leaching columns are packed with untreated, air-dried and sieved soil (< 2 mm) up to a height of approximately 30 cm. Afterwards they are saturated and equilibrated with an “artificial rain” solution and allowed to drain. Then the surface of each soil column is treated with the test substance (non-volatile in water and soil) and/or with aged residues of the test substance. Artificial rain is applied to the soil columns and the leachate is collected. After the leaching process the soil is removed from the columns and is sectioned into an appropriate number of segments depending on the information required from the study. A reference substance (atrazine or monuron) should be used in the leaching experiments. For each soil segment and leachate fraction, the amounts of test substance, transformation products, non-extractables and, if included, of the reference substance should be given in % of applied initial dose.


Book
Test No. 406: Skin Sensitisation
Authors: ---
ISBN: 9264070664 Year: 2021 Publisher: Paris : OECD Publishing,

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Abstract

This method provides information on health hazard likely to arise from exposure to test substance via intradermical injection and/or epidermical application. In this Test Guideline, the methods preferred over other are: the Guinea Pig Maximisation Test (GPMT) of Magnusson and Kligman which uses adjuvant and the non adjuvant Buehler Test. This Test Guideline is intended primarily for use with guinea pig, but recently mouse models for assessing sensitisation potential have been developed. For the GPMT at least 10 animals in the treatment group and 5 in the control group are used. For the Buehler test, a minimum of 20 animals is used in the treatment group and at least 10 animals in the control group. The test animals are initially exposed to the test substance. Following a rest period, the induction period (10-14 days), during which an immune response may develop, then the animals are exposed to a challenge dose. The GPMT is made during approximately 23-25 days, the Buehler test, during approximately 30-32 days. The concentration of test substance used for each induction exposure should be well-tolerated systemically and should be the highest to cause mild-to moderate skin irritation, for the challenge exposure the highest nonirritant dose should be used. All skin reactions and any unusual findings should be observed and recorded (other procedures may be carried out to clarify doubtful reactions).


Book
Test No. 308: Aerobic and Anaerobic Transformation in Aquatic Sediment Systems
Author:
ISBN: 9264070524 9789264070523 Year: 2002 Publisher: Paris : OECD Publishing,

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This Test Guideline describes a laboratory test method to assess aerobic and anaerobic transformation of organic chemicals in aquatic sediment systems. The method permits the measurement of (i) the transformation rate of the test substance in a water-sediment system and in the sediment (ii) the mineralisation rate of the test substance and/or its transformation products, (iii) the distribution of the test substance and its transformation products between the two phases during a period of incubation in the dark, at constant temperature, and (iv) the identification and quantification of transformation products in water and sediment phases including mass balance. At least two sediments different with respect to organic carbon content and texture are used. Ideally the test substance (one concentration) should be applied as an aqueous solution into the water phase. The duration of the experiment should normally not exceed 100 days, and should continue until the degradation pathway and water/sediment distribution pattern are established or when 90 % of the test substance has been removed by transformation and/or volatilisation. The number of sampling times should be at least six. The study includes: concentration in the water and sediment of the test substance and the transformation products at every sampling time; results from gases/volatiles trapping systems at each sampling time; mineralisation rates; and non-extractable residues in sediment at each sampling point. Half-lives, DT50, DT75 and DT90 values are determined where the data warrant.


Book
Essai n° 455: Ligne directrice axée sur la performance pour les essais in vitro de transactivation par transfection stable visant la détection des substances agonistes et antagonistes des récepteurs des oestrogènes
Author:
ISBN: 9264264639 Year: 2021 Publisher: Paris : OECD Publishing,

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Abstract

Marketing blurb in French   La présente Ligne directrice pour les essais axée sur la performance (LDAP) décrit la méthodologie des essais in vitro de transactivation par transfection stable visant la détection des substances agonistes et antagonistes des récepteurs des œstrogènes (essais de TA ER). Elle comprend des méthodes d’essai structurellement et fonctionnellement similaires pour détecter les substances agonistes et antagonistes des récepteurs des œstrogènes, et devrait faciliter le développement de nouvelles méthodes similaires ou modifiées. La base de la présente LDAP est constituée de deux méthodes d’essai de référence de TA ER. Ces deux méthodes sont les suivantes: essai de TA par transfection stable (essai STTA) faisant appel à la lignée cellulaire hERα-HeLa-9903, dérivée d’une tumeur de col utérin d’origine humaine, et l’essai de TA ER BG1Luc faisant appel à la lignée cellulaire BG-1Luc-4E2, dérivée d’adénocarcinome ovarien d’origine humaine. Les lignées cellulaires utilisées dans ces essais expriment les récepteurs des œstrogènes et ont été transfectées de façon stable avec un gène rapporteur de la luciférase répondant aux ER. Ces essais servent à détecter les substances chimiques qui peuvent activer (activité agoniste) et aussi inhiber (activité antagoniste) la transcription régulée par les ER. Les ER sont activés après liaison du ligand au récepteur Le complexe récepteur-ligand se fixe ensuite à certains éléments de réponse de l’ADN et transactive ainsi le gène rapporteur, induisant une augmentation de l’expression cellulaire d’une enzyme marqueur (par exemple la luciférase dans les sytèmes faisant appel à la luciférase). L’enzyme transforme ensuite son substrat en produit bioluminescent mesurable quantitativement à l’aide d’un luminomètre. Les présentes méthodes sont proposées à des fins de dépistage et de priorisation, mais elles peuvent aussi livrer des informations sur les mécanismes d’action pouvant être utilisées dans le cadre d’une approche fondée sur le poids de la preuve.


Book
Test No. 242: Potamopyrgus antipodarum Reproduction Test
Author:
ISBN: 9264264310 Year: 2016 Publisher: Paris : OECD Publishing,

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Abstract

The Potamopyrgus antopodarumon reproduction test is designed to assess potential effects of prolonged exposure to chemicals on reproduction and survival of parthenogenetic lineages of the freshwater mudsnail Potamopyrgus antipodarum. Adult female P. antipodarum are exposed to a concentration range of the test chemical. The test chemical is dispersed into the reconstituted dilution water, added to test beakers, and adult snails are subsequently introduced into the test beakers. When testing “difficult chemicals” (i.e. volatile, unstable, readily biodegradable and adsorbing chemicals) the test can be conducted under flow-through conditions as an alternative to the semi-static design with fixed renewal periods of the medium (see paragraph 29). P. antipodarum survival over the 28 days exposure period and reproduction at the end of the test after 28 days are examined. Reproduction is evaluated by counting the number of embryo in the brood pouch (without distinction of developmental stages) at the end of 28 days exposure. The toxic effect of the test chemical on embryo numbers is expressed as ECX by fitting an appropriate regression model in order to estimate the concentration that would cause x % reduction in embryo numbers or alternatively as the No Observed Effect Concentration and Lowest Observed Effect Concentration (NOEC/LOEC) value (2).

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