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GBZ43193-2023: Nanotechnologies - Considerations for performing toxicokinetic studies with nanomaterials
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Nanotechnologies - Considerations for performing toxicokinetic studies with nanomaterials
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GB/Z 43193-2023
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Basic data | Standard ID | GB/Z 43193-2023 (GB/Z43193-2023) | | Description (Translated English) | Nanotechnologies - Considerations for performing toxicokinetic studies with nanomaterials | | Sector / Industry | National Standard | | Classification of Chinese Standard | C04 | | Classification of International Standard | 07.030 | | Word Count Estimation | 58,527 | | Date of Issue | 2023-09-07 | | Date of Implementation | 2024-04-01 | | Issuing agency(ies) | State Administration for Market Regulation, China National Standardization Administration | GBZ43193-2023: Nanotechnologies - Considerations for performing toxicokinetic studies with nanomaterials
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GB /Z 43193-2023.Research elements of toxicant metabolism kinetics of nanotechnology and nanomaterials
ICS 07.030
CCSC04
National Standardization Guiding Technical Documents of the People's Republic of China
Nanotechnology Nanomaterials Toxicokinetics
research elements
Published on 2023-09-07
2024-04-01 Implementation
State Administration for Market Regulation
Released by the National Standardization Administration Committee
Table of contents
PrefaceⅠ
Introduction II
1 Scope 1
2 Normative reference documents 1
3 Terms and Definitions 1
4 Abbreviations 3
5 The importance of toxicokinetics for risk assessment of nanomaterials3
5.1 Overview 3
5.2 Possible uses of toxicokinetic information3
5.3 Metabolic kinetic issues of key toxicants in nanomaterials 4
6 Factors affecting toxicant metabolism kinetics of nanomaterials 4
6.1 Dissolution rate 4
6.2 Physicochemical properties of nanomaterials that determine toxicant metabolic kinetic behavior 5
7 Challenges of Analytical Methods 8
7.1 Overview 8
7.2 Elemental analysis 8
7.3 Analysis of radioactive or fluorescent labels of elements 9
7.4 Determination of particles 10
7.5 Detection limit 10
8 Questions related to drug administration11
8.1 Overview 11
8.2 Dosage 12
9 Absorption of nanomaterials 12
9.1 Overview12
9.2 Skin 13
9.3 Gastrointestinal tract 13
9.4 Respiratory tract 15
10 distribution18
10.1 Overview 18
10.2 Organ distribution 18
10.3 Transport across the placenta, blood-brain barrier and reproductive organs 19
11 Metabolism/degradation20
12 Excretion 20
13 Conclusion 21
Appendix A (informative) Definitions used in OECDTG417.201025
Appendix B (Informative) Advantages and Challenges of Quantitative Methods for Nanomaterials 28
Reference 33
Foreword
This document complies with the provisions of GB/T 1.1-2020 "Standardization Work Guidelines Part 1.Structure and Drafting Rules of Standardization Documents"
Drafting.
This document is equivalent to ISO /T R22019.2019 "Research Elements of Toxic Metabolism Kinetics of Nanotechnology and Nanomaterials", file type
The ISO technical report was adjusted to my country's standardized guiding technical document.
This document has made the following minimal editorial changes.
---Delete Note 2 of 3.5 in ISO /T R22019.2019;
---Correct "ISO /T S80004-2.2017" in 3.9 in ISO /T R22019.2019 to "ISO /T S80004-2.2015";
---Correct "3.12,3.13" in ISO /T R22019.2019 to "3.10,3.11".
Please note that some content in this document may be subject to patents. The publisher of this document assumes no responsibility for identifying patents.
This document is proposed by the Chinese Academy of Sciences.
This document is under the jurisdiction of the National Nanotechnology Standardization Technical Committee (SAC/TC279).
This document was drafted by. Institute of Basic Medicine, Chinese Academy of Medical Sciences, National Center for Nanoscience.
The main drafters of this document. Wen Tao, Xu Haiyan, Meng Jie, Xu Shilin, Wang Tao, Liu Jian, Gao Jie.
Introduction
Nanomaterials (NMs) are a class of chemicals that, like other chemicals, can produce a range of toxicities. Carry out toxic metabolism activities
Mechanics (also called toxicokinetics) studies are important for evaluating the safety of nanomaterials and identifying the persistence of nanomaterials in different organs (including cells).
It is of great significance to evaluate the similarities and differences between nanomaterials and powder materials of the same chemical composition (such as barrier penetration). exist
In all nanomaterial toxicokinetics studies, proper characterization of the nanomaterial dispersions or aerosols used is critical.
need.
The importance of toxicokinetic information in nanomaterial risk assessment.
Toxicokinetics describes the absorption, distribution, metabolism, and excretion (ADME) of foreign compounds in the body over time.
This situation, which relates exposure dose to in vivo dose, is a key aspect of toxicity assessment. On the one hand, nanomaterials can be used in many ways
(oral, respiratory, skin) is absorbed into the body and enters the blood or lymph circulation. Subsequent distribution in the internal organs will determine its potential target tissues and
toxicity. On the other hand, nanomaterials can directly enter the blood circulation through the intravenous route (e.g., as nanomedicines), leading to widespread differentiation in tissues.
cloth. Toxicokinetics can help to design toxicity studies and identify potential target organs, and can also provide guidance for rational implementation or timely termination.
Antitoxicity studies provide relevant information. In addition, toxicological metabolism information can provide a basic basis for the grouping and cross-comparison of nanomaterials.
Since nanoparticles have specific tissue distribution and accumulation properties, toxicokinetic information is used to perform internal concentration-based analysis.
Risk assessments may be more realistic than those based on exposure dose. Toxicokinetic study results can be used to establish toxicant
Metabolic kinetic models, especially physiologically based pharmacokinetic (PBPK) models, can be used to predict other species, tissues, and exposure routes.
Toxicity experimental data on diameter, time and dose. Since some nanoparticles can accumulate in the body, it is speculated that the impact of long-term exposure on nanoparticles
Materials are particularly important.
Why is it necessary to establish technical standards for toxicant metabolokinetics for nanomaterials?
A large amount of literature, including many national and international guidelines, has used toxicokinetic methods to study the effects of chemical substances in vivo.
The final destination of the inside. TG417 "Guidelines for Toxicokinetic Testing" of the Organization for Economic Co-operation and Development (OECD) (last updated on
2010) provides a detailed description of the evaluation of toxicokinetics of chemicals, but does not include nanomaterials. ISO 10993-16.2017
"Biological Evaluation of Medical Devices Part 16.Toxicokinetic Study Design of Degradation Products and Leachables" provides an overview of medical device extractables
Toxicokinetic studies. In addition, the European Medicines Agency's ICHS3A "Toxicokinetics Guidance Principles. Systemic Exposure in Toxicity Studies"
"Assessment of Exposure" and ICHS3B "Pharmacokinetics. Guiding Principles for Tissue Distribution Studies with Repeated Dosing" on toxicokinetic study design
and implementation provides guidance that can aid the development of new drugs.
Toxicokinetic modeling, particularly the development and application of PBPK models, is also introduced in these guidelines. For example, American food and
The Drug Administration's draft "Industry Guidance for Format and Content of PBPK Assays" provides standard content and
Format; the US Environmental Protection Agency's "Methods for Application of PBPK Models and Supporting Data in Risk Assessment" mainly involves the format used for risk assessment.
Application and evaluation of PBPK model. In.2016, the European Medicines Agency issued the Guidance Document on PBPK Modeling and Simulation Qualifications and Reporting.
"Parts"[1]. The World Health Organization published “Characterization and Application of Physiologically Based Pharmacokinetic Models in Risk Assessment” [2].
As mentioned above, the existing OECDTG417 clearly points out that nanomaterials are different from dissolved ions, molecules and large particles, and their toxic metabolism
The kinetics are also different, so this guideline is not applicable to testing nanomaterials [3]. This point is reflected in the OECD’s preliminary guidance on applicability.
It has also been confirmed in step judgment [4]. In addition, the biodistribution process of nanoparticles is not related to the soluble substances (molecules) involved in the guidance document [5].
or ions), so the PBPK model described in the document is not applicable to nanomaterials either.
Based on this, it is necessary to develop new guidelines or make specific supplements to existing guidelines based on the characteristics of nanomaterials. Toxic to nanomaterials
A review and summary of metabolic kinetic characteristics and current knowledge is necessary to fully understand the necessity of toxicological metabolic testing of nanomaterials.
Base.
How do nanomaterials differ from dissolved ions, molecules, and large particles?
Nanomaterials are a class of substances with unique properties. Due to their granularity and small size, nanomaterials have corresponding bulk or
The different physical and chemical properties of soluble components make nanomaterials likely to have specific toxicity discussed in many reports [6-10].
Toxicokinetic analysis of nanoparticles is of great significance. Typically, smaller sized nanoparticles are
Particles will enter lymph fluid and blood circulation more quickly, and may reach all organs [11]. Furthermore, smaller size particles are
Smaller nanoparticles have wider organ distribution [12], and may also be transported across barriers such as the blood-brain barrier and placenta [13-14].
There are other significant differences between the toxicant metabolic kinetic behavior of soluble molecules or ions and nanomaterials, including the absorption of substances,
Distribution, Metabolism, Excretion (ADME). For dissolved molecules or ionic substances, the toxicant metabolism kinetics consists of 1) passive transport (including simple
diffusion and filtration) and 2) special transport (including active transport, carrier-mediated transport systems, promoted diffusion through cell membranes, enzyme metabolism,
Passive and active excretion) drive. For nanomaterials, toxicokinetics involves aggregation, condensation, protein corona formation, cellular uptake, and
Biodistribution and degradation and excretion of some nanomaterials due to phagocytosis by macrophages [15]. In addition, the surface chemistry and organization of nanoparticles
(also called protein corona) can affect the binding of biomolecules on their surface, which in turn affects the toxicant metabolism kinetics of nanoparticles. nanoparticles
Excretion is usually very limited and may bioaccumulate like other poorly metabolized molecules. Therefore, nanoparticle toxicant metabolism dynamics
Chemical testing and modeling differ significantly from soluble substances. In this regard, especially in repeated exposure and long-term toxicokinetic studies, it is necessary to
Assess the risk of accumulation and persistence of nanomaterials in organs.
Nanotechnology Nanomaterials Toxicokinetics
research elements
1 Scope
This document describes the background and principles for toxicokinetic studies relevant to nanomaterials.
Appendix A contains terms and definitions related to toxicokinetics used in OECD TG 417.2010.
2 Normative reference documents
The contents of the following documents constitute essential provisions of this document through normative references in the text. Among them, the dated quotations
For undated referenced documents, only the version corresponding to that date applies to this document; for undated referenced documents, the latest version (including all amendments) applies to
this document.
ISO /T S80004-1.2015 Nanotechnology terminology Part 1.Core terms (Nanotechnologies-Vocabulary-
Part 1.Coreterms)
Note. GB/T 30544.1-2014 Nanotechnology terminology Part 1.Core terms (ISO /T S80004-1.2010)
ISO /T S80004-2.2015 Nanotechnology terminology Part 2.Nanotechnologies-Vocabulary-
Part 2.Nano-objects)
3 Terms and definitions
The following terms and definitions as defined in ISO /T S80004-1.2015 and ISO /T S80004-2.2015 apply to this document.
The following URLs are database URLs used in standards that ISO and IEC are responsible for.
3.1
agglomerate
The surface area of an accumulation, aggregate or mixture of weakly bound particles is similar to the sum of the surface areas of its individual particles.
Note 1.The forces supporting agglomerates are weak forces, such as van der Waals forces or simple physical entanglements.
Note 2.Agglomerates are also called secondary particles, while source particles are called primary particles.
[Source. ISO 26824.2013,1.2]
3.2
aggregate
New particles formed from particles that are strongly bound or fused together may have an external surface area that is significantly smaller than the sum of the surface areas of the individual particles.
Note 1.The forces supporting aggregates are strong forces, such as covalent bonds or originating from sintering or complex physical entanglements.
Note 2.Aggregates are also called secondary particles, while source particles are called primary particles.
[Source. ISO 26824.2013,1.3, modified]
3.3
nanoscale
In the size range between 1nm and 100nm.
NOTE 1.This size range generally, but not exclusively, exhibits characteristics that cannot be extrapolated from larger sizes. For these properties, the upper and lower scale values are
similar.
Note 2.The purpose of introducing a lower limit (approximately 1 nm) in this definition is to avoid considering individual atoms or clusters of atoms as nano-objects or nano-structural units.
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