ASTM E1242-23 PDF
Standard Practice for Using Octanol-Water Partition Coefficient to Estimate Median Lethal Concentrations for Fish Due to Narcosis
Standard Practice for Using Octanol-Water Partition Coefficient to Estimate Median Lethal Concentrations for Fish Due to Narcosis
- Статус документа:
- Действующий
- Формат:
- Электронный (PDF)
- Количество страниц:
- 2
- Дата публикации:
- 1 января 2023 г.
- Издание:
- E1242
- ICS:
- 07.080
SIGNIFICANCE AND USE 5.1 This procedure can be used to limit the need for screening tests prior to performing a test for estimating the LC50 of a non-reactive and non-electrolytic chemical to the fathead minnow. By eliminating the screening test, fewer fish need be tested. The time used for preparing and performing the screening test can also be saved. The value obtained in this procedure can be used as the preliminary estimate of the LC50 in a full-scale test. 5.2 Estimates can be used to set testing priority of groups of non-reactive and non-electrolytic chemicals. 5.3 If the estimated value is more than 0.3 times the experimental value, the mechanism of action is probably narcosis. If less, the effect concentration is considered to reflect a different mechanism of action. 5.4 This practice estimates a maximum LC50, that is, non-reactive and non-electrolytic chemicals are at least as toxic as the practice predicts, but may have a lower LC50 if acting by a more specific mechanism. Data on a chemical indicating a lower toxicity than predicted should be considered suspect or an artifact because of limited solubility of the test material. SCOPE 1.1 This practice covers a procedure for estimating the fathead minnow (Pimephales promelas) 96-h LC50 of nonreactive (that is, covalently bonded without unsaturated residues) and nonelectrolytic (that is, require vigorous reagents to facilitate substitution, addition, replacement reactions and are non-ionic, non-dissociating in aqueous solutions) organic chemicals acting solely by narcosis, also referred to as Meyer-Overton toxicity relationship.2 1.2 This procedure is accurate for organic chemicals that are toxic due to narcosis and are non-reactive and non-electrolytic. Examples of appropriate chemicals are: alcohols, ketones, ethers, simple halogenated aliphatics, aromatics, and aliphatic substituted aromatics. It is not appropriate for chemicals whose structures include a potential toxiphore (that structural component of a chemical molecule that has been identified to show mammalian toxicity, for example CN is known to be reponsible for inactivation of enzymes, NO2 for decoupling of oxidative phosphorylation, both leading to mammalian toxicity). Examples of chemicals inappropriate for this practice are: carbamates, organophosphates, phenols, beta-gamma unsaturated alcohols, electrophiles, and quaternary ammonium salts. 1.3 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
Abstract
Overview
ASTM E1242-23: Standard Practice for Using Octanol-Water Partition Coefficient to Estimate Median Lethal Concentrations for Fish Due to Narcosis provides a standardized procedure for estimating the 96-hour median lethal concentration (LC50) of organic chemicals, specifically for the fathead minnow (Pimephales promelas). This practice applies to non-reactive and non-electrolytic organic chemicals that act through narcosis, as described by the Meyer-Overton toxicity relationship.
The method leverages the octanol-water partition coefficient (Kow), a widely used metric in environmental chemistry for assessing the hydrophobicity of chemicals, to estimate toxicity. This approach helps minimize the need for preliminary screening tests, conserving both time and biological resources in aquatic toxicology studies.
Key Topics
-
Scope of Application:
- Relevant for organic chemicals that are non-reactive, non-electrolytic, and whose primary toxicity mechanism is narcosis.
- Examples of applicable chemicals include alcohols, ketones, ethers, simple halogenated aliphatics, aromatics, and aliphatic-substituted aromatics.
- Excludes chemicals with toxiphores-structural components known for specific mammalian toxicity (e.g., cyanides, nitro groups, carbamates, organophosphates).
-
Methodology:
- Utilizes the octanol-water partition coefficient (Kow) to estimate a maximum 96-h LC50 value.
- The estimation acts as a preliminary toxicity value before undertaking full-scale aquatic toxicity tests.
-
Significance and Use:
- Reduces the need for screening tests, thus limiting the number of fish required.
- Saves time in aquatic toxicity assessments.
- Assists in prioritizing the testing of chemical groups and can indicate if a chemical likely acts via the narcosis mechanism.
-
Interpretation of Results:
- If the estimated LC50 significantly exceeds measured LC50 values (by more than 0.3 times), narcosis is likely the main mode of action.
- Lower experimental values than predicted may indicate alternative toxicity pathways or artifacts such as low solubility.
Applications
-
Aquatic Toxicology:
- Efficiently estimate acute toxicity of organic chemicals to fish, particularly fathead minnows, using physicochemical data rather than resource-intensive bioassays.
- Provides a screening tool for environmental risk assessment by regulatory agencies, environmental consultants, and research laboratories.
-
Chemical Prioritization:
- Supports prioritizing substances for further detailed investigation by offering preliminary toxicity assessments.
- Helps identify chemicals that may pose higher ecological risks due to narcosis-based toxicity.
-
Environmental Risk Management:
- Assists in early-stage hazard assessments and environmental impact studies.
- Facilitates compliance with environmental safety regulations and standards in chemical manufacturing and use.
Related Standards
- ASTM E729: Guide for Conducting Acute Toxicity Tests on Test Materials with Fishes, Macroinvertebrates, and Amphibians
- ASTM E943: Terminology Relating to Biological Effects and Environmental Fate (withdrawn 2023)
- ASTM E1023: Guide for Assessing the Hazard of a Material to Aquatic Organisms and Their Uses
- ASTM E1147: Test Method for Partition Coefficient (N-Octanol/Water) Estimation by Liquid Chromatography (withdrawn 2013)
Practical Value
Utilizing the guidelines in ASTM E1242-23 streamlines aquatic toxicity testing for certain organic chemicals, enhancing efficiency in laboratory studies and supporting informed decision-making in environmental assessment and chemical management. Using Kow as a predictive tool simplifies the process of estimating fish toxicity, providing cost-effective and ethical alternatives to traditional bioassays. This standard is essential for professionals in environmental toxicology, regulatory compliance, and risk management seeking reliable and internationally recognized practices.
Технические детали
- Технический комитет
- E50 - Environmental Assessment, Risk Management and Corrective Action
- SKU
- ASTM E1242-23
Похожие стандарты
Другие стандарты ASTM
ASTM-TPT-47
Phase I & Phase II Environmental Site Assessment Processes
Phase I & Phase II Environmental Site Assessment Processes
ASTM-TPT-8
Phase I Environmental Site Assessment Practices For Commercial Real Estate: Phase I Site Assessment & Transac…
ASTM-TPT-1137
ASTM D975 Standard Specification for Diesel Fuel
ASTM D975 Standard Specification for Diesel Fuel
ASTM-TPT-1202
ASTM D8421 Standard Test Method for Determination of Per- and Polyfluoroalkyl Substances (PFAS) in Aqueous Ma…
ASTM D8421 Standard Test Method -- eLearning Course
ASTM-TPT-691
Microaprendizagem para D4057: Amostragem de ponto (PT)
D4057 Microlearning: Spot Sampling Portuguese
ASTM-TPT-1091
Metodo de prueba estandar D4052 de ASTM -- Curso de aprendizaje electrónico (ES)
Modulo eLearning para ASTM D4052 en espanol
ASTM ACEM20180086
Using Neutron Radiography to Quantify the Settlement of Fresh Concrete
Specifications have been implemented for concrete bridge decks in North America that restrict the use of higher slump concrete mixtures primarily because of concerns about differential settlement and…
ASTM ACEM20180041
Experimental Study of Competing Failure of Reinforced Concrete Based on the Weibull Distribution
To predict the failure lifetime of reinforced concrete, a current accelerating corrosion test was performed on concrete by simulating the environment in an area with saline soil. To study the concret…