Subscribe to RSS

DOI: 10.1055/a-2625-5344
Supporting Safe-by-Design of Multicomponent Nanomaterials by Linking Functionality-Related Properties with Potential Safety Issues
Supported by: EU H2020 SUNSHINE 952924
Funding Information This work is part of the SUNSHINE project and has received funding from the European Union’s Horizon 2020 research and innovation program under grant agreement 952924.
- Abstract
- Introduction
- Outline and Application of a Material Property-Guided Approach
- Estimations of the Impact on Aspects of Risk for 21 Material Properties
- Case Studies
- Discussion
- Conclusions
- References
Abstract
Advanced materials, including multicomponent nanomaterials (MCNMs), are rationally designed to show specific new or enhanced functionalities. They are considered key in solving current societal challenges, such as the energy transition, yet they represent a challenge themselves to safe innovation and risk assessment. One challenge is the lack of available toxicological information at early innovation stages. Instead, information on functionality and related material properties is generally available at these early innovation stages, but such information is typically not used in safety assessments. Safe-by-Design (SbD) aims to improve the safety of materials and products by integrating safety considerations with functionality as early as possible in the innovation process. To exploit the information on functionality for SbD purposes, a conceptual approach is presented that uses functionality-related material properties to flag potential impacts on risks and guide SbD. This approach relies on insights into relations between material properties and their potential impact on release, fate/toxicokinetics, and toxicity. These relations have been illustrated for 21 new or enhanced material properties that are incorporated in the design of MCNMs. For example, a set of “mechanical properties” was identified as likely to have an impact on release and fate/toxicokinetics of MCNMs, while “reactive properties” were expected to be able to affect their toxicity. The applicability of this approach was briefly explored through several case studies. The presented approach is designed to “flag” potential aspects of risk that require further consideration. These identified aspects can then support the application of SbD for MCNMs, including grouping of similar MCNMs to enable sharing of safety information. The approach is relevant at early stages in the innovation process, where toxicological information is still mostly absent.
#
Keywords
Material properties - Safe-and-sustainable-by-design - Safe innovation - Risk - Physicochemical properties - Advanced materialsAdvanced materials are increasingly being developed. It is critical that these new materials are not only functional but also safe. Safe-by-Design principles have been developed to support safer innovation of chemicals and materials. Applying such principles and tools is essential for operationalizing the Sustainable Development Goals set by the United Nations. We propose that, at very early innovation stages, before safety information is available, physicochemical and functionality information can be used to flag the potential for safety issues. Here we demonstrate the use of such information for multicomponent nanomaterials.
Introduction
Over the last two decades, manufactured nanomaterials (NMs) have been a key driver of material innovation. These versatile and diverse materials can be tailored to exhibit specific desirable functionalities, with applications ranging from medical and pharmaceutical fields to electronics, paints and coatings, food, and consumer products.[1] [2] [3] [4] [5] Quick progress in nanotechnology has resulted in the development of even more complex and advanced materials. For example, multicomponent nanomaterials (MCNMs) have been generated in a wide variety of forms, ranging from simple core–shell structures to complexes of two or more different nanomaterials.[6] [7] These structures may be included within a matrix to generate an MCNM-enabled product. Some of the most widely used components are (combinations of) carbonaceous (e.g., fullerenes, carbon nanotubes, graphene) or inorganic (metal or metal oxide) NMs with or without organic coatings (e.g., polymers, macromolecules, and enzymes).[6] MCNMs are typically designed to create or improve the functionalities of a material. The functionality may result from the interaction between NMs and/or the structuring of materials within the MCNM. As a result, the properties of these MCNMs may differ (in part) from the intrinsic properties of the individual components.
Although there are still considerable knowledge gaps for many single-component NMs, information on NM safety is increasingly available, for example, within the data repository eNanoMapper.[8] However, due to their novel functional feasibilities and multicomponent nature, MCNMs present an additional challenge in ensuring safety for human and environmental health compared to single-component NMs.[9] For instance, the release, fate, and toxicokinetics of active substances encapsulated in nanocarriers are different from those of the active substance.[10] [11] Moreover, when MCNMs (partly) degrade, dissociate, or transform in a cell, tissue, or organ, concurrent exposure to the individual component(s) may result in mixture effects.[12] The safety assessment is further complicated by the lack of fundamental toxicological research on MCNMs. New possibilities may result in new hazards. For example, much material innovation research is being done to obtain MCNMs with electromagnetic properties.[13] Yet, it is not clear if and how such properties have an impact on hazard and whether existing test methods are sufficiently equipped to measure potential adverse effects. Taken together, the implications for safety of combining different substances into an MCNM with new or improved functionality are not well understood.
Over recent years, several test guidelines and test standards specific to NMs have been developed, such as those available within the Organization for Economic Co-operation and Development (OECD). Also, modifications to legislation have been introduced to accommodate NMs. For example, in the EU, REACH (Registration, Evaluation, Authorization, and Restriction of Chemicals) annexes currently have NM-specific clarifications and provisions.[14] However, most of these adaptations have been made with “simpler” NMs in mind, and it remains unclear to what extent these adaptations are sufficient to address specific issues of MCNMs.[15] Uncertainty regarding the critical safety issues of these complex materials and the validity of existing regulatory test methods could affect the regulatory acceptance of MCNMs. This uncertainty regarding regulatory acceptance may, in turn, result in uncertainty for innovators who develop MCNMs, which could act as a barrier for innovation.[16] [17]
Some of these uncertainties may be reduced when safety is specifically considered as early as possible in the innovation process. This can be seen as a complementary and preventative strategy before legal safety obligations (e.g., as those laid out in REACH in the EU) at the near-market stage. To that end, the concept of “Safe-and-Sustainable-by-Design” (SSbD), which considers both safety and sustainability from an early innovation stage on, has been developed over the last several years (e.g., within the European Commission (EC),[18] [19] [20] European projects,[21] [22] OECD,[23] European Environment Agency (EEA),[24] Cefic,[25] [26] [27] and ChemSec[28]). SSbD is a central component of the EC Chemicals Strategy for Sustainability[18] and a framework has been proposed by the EC’s Joint Research Centre (EC-JRC)[19] [20] and discussed with stakeholders to support the design and development of safe and sustainable chemicals and materials. SSbD goes beyond Safe-by-Design (SbD), as sustainability considerations are also included. SSbD encourages scientists, innovators, and industry to integrate safety and sustainability with the desired functionality of the chemical/material and economic aspects, in an iterative way during the innovation process.[1] [29] [30] [31] [32] [33] [34] [35] SSbD efforts are most beneficial when applied at early Research and Development (R&D) stages because the possibility to make changes to a product decreases with the maturation of an innovation.[36] [37]
Specific tools for SSbD/SbD for NMs are becoming more and more available due to current developments.[36] [37] [38] A SSbD tool can be more or less specific to elements in SSbD, such as only covering safety aspects (SbD), or to specific innovation stages. It can be assumed that multiple tools are needed to gather the information to support decision-making moments during innovation. An example includes an approach for applying SSbD early in the innovation process tailored toward small and medium enterprises (SME).[31] Thus far, most of these approaches and tools rely on toxicological information of the material or final product for the assessment of the safety. However, toxicological information for a specific material is often unavailable, especially at the initial design stages. The toxicity of a material is driven by its physicochemical properties and route of exposure/environmental compartment, toxicokinetics, and dose reaching target organ(s) or species. However, due to the novelty of advanced and nanomaterials and the ongoing process of developing test guidelines and guidance documents for these materials, limited data and even fewer in silico predictive models, such as QSARs and other machine-learning (nano) models, are available.[39] [40] [41] Furthermore, innovators of materials in many cases do not design materials for their specific physicochemical properties per se, but rather for the function that can be achieved by altering material properties (such as specific mechanical or optical properties), which in turn are determined by their physicochemical properties. It can be presumed that typically innovators have some, but limited, information on physicochemical properties (like elemental composition and general information on size and morphology) at initial innovation stages, while also the type of material properties that underlie the intended functionality is known. A tool that uses the functionality as a starting point for SbD will thus be a valuable complementary approach that is particularly relevant at early design stages.
Here, we argue that in the absence of specific toxicological information, indications for potential safety issues of an MCNM (or any advanced material) can be inferred by examining the material properties that enable a certain functionality. Such indications could then be used by innovators to better consider safety in their innovation and for targeting specific safety testing. For example, it has been reported that the elasticity of (nano)materials can affect the uptake into cells.[41] Therefore, when an MCNM is designed to achieve a certain (high or low) elasticity, one could expect that these design choices may impact their fate and toxicokinetics and thereby the risk of the materials. Furthermore, we foresee that such information may also inform the development of grouping and read-across arguments of MCNMs. For example, if the impact on release, fate/toxicokinetics, or hazard is potentially high, this should be considered in grouping hypotheses and assessed via Integrated Approaches to Testing and Assessment (IATAs).[43] [44] [45] [46] Risk assessors can benefit from a better general understanding of the functionality in relation to toxicity. Such insights based on functionality are typically not used in risk assessment, but we argue that they can help regulators to evaluate possible hazards associated with new or enhanced functionalities of specific materials, and to consider whether current regulations are adequate for such materials.
In this article, we describe a novel conceptual approach that uses material properties to guide the identification of possible risks at early innovation stages to support safer development of MCNMs. Although the focus of this approach is on MCNMs, the principle of the approach may also be applicable to other advanced materials or “simple” NMs like spherical single-component NMs. The approach should be regarded as conceptual, aiming to demonstrate that functionality and related material properties may be used as a starting point in the safer design of materials. Further work at later innovation stages would be required for a more informed approach to SbD and, of course, to meet chemical regulatory requirements. In the current study, we focus on how information on functionality can be used in the early innovation stages of SbD, that is, without considerations on sustainability. The approach can be used along with other tools and approaches that support SbD or SSbD.
#
Outline and Application of a Material Property-Guided Approach
In the following sections, first, the general outline of the approach is explained. In the section that follows, the potential impact of 21 material properties on key aspects of risk is qualitatively assessed. This list can be expanded to include additional properties in the future. Lastly, the approach is briefly applied in several case studies to further demonstrate the use of the approach for SbD of MCNMs.
Functionality links to the material properties and physicochemical properties of a material. In the context of this study, functionality relates to the intended use of the materials, such as insulation, CO2 storage, and imaging. To achieve a certain functionality, specific material properties can be modified (see [Table 2] for the material properties considered). For example, the material property “heat conductivity” can be modified to improve thermal insulation of a material. Material properties are, in turn, determined by physicochemical properties, like the elemental composition. The term physicochemical properties is currently used for those physicochemical properties that are used in the risk assessment of nanomaterials. These include, but are not limited to, elemental composition, shape, size distribution, crystallinity, specific surface area, and surface chemistry.[47] [48]
The approach and its content were developed through literature searches and group discussion between the authors and within the EU Horizon project SUNSHINE (www.h2020sunshine.eu). The expertise covered by the authors includes human health and environmental risk assessment, materials science, chemistry, physics, biology, European chemical legislation, and SSbD.
Outline of the Approach
The material property-guided approach consists of three main phases: “existing information,” “impact assessment,” and “use,” as depicted in a schematic overview in [Fig. 1]. Details of the different phases are explained in the following sections. Briefly, the “existing information” part collects information on the functionality and the material and physicochemical properties that are already available for the MCNM (or its enabled product) that is being developed at a very early innovation stage. The aim of the “impact assessment” is to link specific material properties to potential impacts on three “aspects of risk." These key aspects are “release,” “fate/toxicokinetics,” and “toxicity”; see [Table 1] for definitions of these terms as used in this article. Each of these “aspects of risk” is an element that may influence the risk. In this article, we refer to the links between material properties and aspects of risk as (potential) “material property–risk relations.” Note that the approach does not predict the risks of an MCNM. Rather, it assesses whether an impact should be considered on one of the key aspects of risk. Also note that such an impact can be both positive and negative, meaning that the risk can increase or decrease. Once the relations between material properties and aspects of risk are understood, then this information can be fed into the decision-making process that underlies the safer development (or use) of an MCNM. For example, this approach can be used for several purposes, that is, as input for SbD of the MCNM via risk mitigation or targeted testing, or as input for the grouping and read-across of MCNMs. The obtained insights can also provide additional understanding relevant to the risk assessment.


Aspects of risk |
Description |
Justification of use in this approach |
---|---|---|
Release |
“Release” relates to the environmental compartment into which the MCNM (or its components) are released, as well as the form and extent of release |
The most relevant environmental compartments and human routes of exposure determine the context for potential risks. The extent of release provides information on the exposure level |
Fate/toxicokinetics |
The “fate” in the environment relates to mass flows in environmental compartments. “Toxicokinetic behavior” focuses on uptake, distribution, accumulation in the human body, and potential target organs |
In the present context, the focus is on how the material property related to new or enhanced functionality affects bioavailability, accumulation, and distribution in the environmental compartments and the environmental species to consider. Fate and toxicokinetics determine the actual or internal exposure and thereby the toxicity |
Toxicity |
“Toxicity” relates to the endpoints of toxicity of interest (e.g., oxidative stress, genotoxicity) |
A specific endpoint for human or environmental toxicity may arise, increase or decrease as related to a material property |
#
Existing Information
In this phase, the existing information related to functionality, material properties, and physicochemical properties is collected ([Fig. 1]). MCNMs or MCNM-enabled products are designed to exhibit specific functionalities. To achieve certain functionality, material properties such as electrical conductivity, light absorption, or tensile strength of the material are considered. These material properties that underlie the intended functionality are therefore typically known at very early stages of innovation. In addition, some physicochemical information, like elemental composition and general information on size and morphology, is often also known.
Note that many material properties are interrelated, meaning that modifications of certain intended material properties may also have an inadvertent effect on other material properties. For example, changing the porous structure to achieve better insulation properties may also affect the availability of reactive sites and thereby the reactivity of the materials.
Thus, the existing information phase of the approach requires the user to identify and describe the intended functionality, the underlying material, and the physicochemical properties that are known. Also, any inadvertently altered material properties (if known) should be described in this phase.
#
Impact Assessment
First, as depicted in [Fig. 1], it should be considered whether the material property applies to the MCNM itself, the MCNM-enabled product, or both. This is relevant to consider because it could impact the associated risks. For example, embedding an MCNM into a product can affect the release of (components of) MCNMs to the environment and thereby potentially impact risk. Note that not all material properties apply to both the MCNM itself and the MNCM-enabled product. For example, MCNMs may be added to a medium to alter the viscosity of the final product. However, MCNMs themselves do not inherently exhibit viscosity, as it is a macroscopic property of a fluid. Thus, the material property viscosity is only relevant for MCNM-enabled products and not MCNMs themselves.
Next, the potential implications of a material property on aspects of risk for the MCNM and/or MCNM-enabled product should be assessed. This impact is assessed for three key aspects of risk: “release,” “fate/kinetics,” and “toxicity” (see [Table 1] for details on the meaning of these terms in context). There are several approaches by which these material property–risk relations can be evaluated. For example, these relations may be estimated based on literature searches and/or expert judgment. In some cases, predictive models, when available, can be used to assess property–risk relations.[49] [50] For example, Banerjee and co-workers used predictive models to demonstrate that electronic properties contribute to cytotoxic properties of MCNMs.[50] However, in most cases, the impacts are qualitatively considered. Consequently, the overall impact of a material on risk is also qualitative and not quantitative.
In this paper, a set of 21 “material property–risk relations” was explored to allow for direct application. These relations were determined through literature research and expert assessment. For our work on the considered properties, three levels of impact were used: “large,” “medium,” and “small.” Arrangement into these three levels was for pragmatic reasons to establish a principle, that is, no formal criteria were applied.
#
Use of Impact Information
Applying this approach results in the identification or flagging of aspects of risk for specific material properties (related to new/enhanced functionalities) that could potentially impact risk. The resulting estimations of the impact assessment can be used to guide SbD in the following ways ([Fig. 1]).
For entirely novel materials with a specific functionality and material properties, identified flags (i.e., aspects of risks for which large potential impacts are identified) could either be prioritized in safety tests during innovation, or used in selection or considerations of alternatives, as relevant in SbD. In particular, the proposed approach can be used in the very early stages of technological innovation, that is, before the strategic decision to start the development of a new MCNM/MCNM-enabled product (Technology Readiness Levels (TRL) 1–3).[51] Therefore, the approach provides input to support decision-making on continuation, termination, or changes to the innovation process using the limited information available. The approach can also provide input during the early development stages (TRL4), without incurring too much cost. This can facilitate the development of safer materials/products, thereby supporting effective SbD MCNM innovation.
The information on potential impact could also help in grouping and read-across, which could be used to steer SbD based on existing information of similar materials. Strategies built to support the process of grouping and read-across, as developed within GRACIOUS,[48] use grouping hypotheses and IATAs to gather the information needed to substantiate grouping and read-across.[32] [33] [34] Information from material properties can offer insights and can be used to formulate grouping hypotheses and data collection via application of tailored IATAs. For example, if an MCNM exhibits enhanced elasticity due to the combination of components, its potential for uptake by animals or plants can be increased as compared to its single components. This would mean that a similarity assessment of an MCNM and its single components should include uptake as a criterion to accept or reject the grouping hypothesis. When knowing the potential impact of the introduction of, or change in, material properties on a certain risk aspect, it becomes easier to judge whether a grouping hypothesis is relevant to pursue.[46] Further, the overall risk assessment can benefit from an additional perspective to consider the available information.
#
#
Estimations of the Impact on Aspects of Risk for 21 Material Properties
To demonstrate the feasibility of the approach detailed above, and to aid in the practical application of the approach, an extensive but nonexhaustive overview is provided of the potential impact of in total of 21 material properties on aspects of risk.
Selection and Definition of the Material Properties
Material properties that are potentially exploited to enhance functionalities of MCNMs were identified through a literature review and expert assessments. This resulted in the identification of a total of 21 material properties, which are described in [Table 2] and Table S1 of the Supplementary Information. Many of the identified properties were also independently identified by Tavernaro et al.,[1] whose research in part examines the relation between NM functionality and material properties at a more conceptual level. The identified new or enhanced properties are currently organized into one of seven types: “electromagnetic,” “heat and thermodynamics,” “optical,” “surfaces,” “liquid media,” “mechanical”, and “reactive."
The 21 identified properties set the scope for this work on material property–risk relations. It is acknowledged that there are more properties that may be relevant to MCNMs that are not considered in this paper. The potential impact of such additional properties may be assessed by innovators, researchers, and/or risk assessors through the use of the approach described here.
#
Applicability of Material Properties to MCNM and/or MCNM-Enabled Product
As explained in the above section, the properties related to new or enhanced functionality might apply to the MCNMs themselves and/or in MCNM-enabled products. By our judgment and based on literature studies, for 11 of the 21 identified material properties, the property related to new or enhanced functionality applies to MCNM themselves and in the MCNM-enabled product. Five properties were judged to only apply to MCNM, while five different properties apply to MCNM-enabled products. Supplementary Information Table S1 provides an overview of whether a property applies to the MCNM and/or the MCNM-enabled product, including a rationale.
#
Qualitative Assessment Material Properties–Risk Relations
For each of the 21 properties, qualitative estimations of the impact on the release, fate/toxicokinetics, and toxicity of an MCNM were made, based on examples from literature, where available, or based on expert assessment ([Table 2]). Note that the impact of the introduction of, or change in, material property can either have a decreasing or increasing effect on risk, which is not specified in this work. When a large impact on, for example, release is possible for a given changed property, this does not necessarily mean an increased risk is associated with these MCNMs, but rather that this potential impact should be taken into consideration for further safety assessment or grouping and read-across. In fact, if further studies demonstrate that a given change in certain property results in lower release of the MCNM (or components thereof), a reduced risk may be expected. Thus, the approach presented here aims to flag potential safety issues so that they can be assessed. It does not aim to make a statement on the actual impact of risk itself. Further information and support for the assessment of the 21 properties can be found in Supplementary Information Tables S2.1–S2.7.
Material property |
Applicable to |
Release |
Fate/ toxicokinetics |
Toxicity |
---|---|---|---|---|
aFor applications with increased thermal conductivity as their primary goal, such as medical applications, the impact is considered to be large. Typically, an external energy source is required for materials to display thermal conductivity. bFor certain medical applications where increased heat capacitance is a primary goal, the impact on toxicity can be large. cIn the absence of light. In the presence of light, impacts on toxicity may be large (e.g., through generation of creating reactive oxygen species). dHigh aspect ratio materials like fibers may induce frustrated phagocytosis due to their stiffness. eIn the case of application as a medical implant, that is, MCNM-enabled product applied in the body. |
||||
Electromagnetic |
||||
Electrical conductivity |
MCNM-enabled product |
Medium[52] |
Large[53] |
|
Electrical capacitance |
MCNM-enabled product |
Medium[52] |
Small |
Large |
Magnetism |
MCNM |
Small |
||
Heat and thermodynamics |
||||
Thermal conductivity |
MCNM |
Small |
Small |
|
MCNM-enabled product |
Small |
Small |
||
Heat capacitance |
MCNM-enabled product |
Small |
Small |
Small or Largeb [64] |
Optical |
||||
Light absorption (includes photoconductivity, photothermal effects, and plasmonic effects) |
MCNM |
Small |
Small |
|
MCNM-enabled product |
Small |
Small |
Smallc or Large[65] |
|
Luminescence |
MCNM |
Small |
Small |
Smallc or Large[67] |
MCNM-enabled product |
Small |
Small |
Smallc or Large[67] |
|
Surfaces |
||||
Pore characteristics |
MCNM |
Small |
Small |
Large |
MCNM-enabled product |
Medium |
Medium |
||
Wettability and surface tension |
MCNM |
Small |
Small |
|
MCNM-enabled product |
Large |
Medium |
Small |
|
Relative permeability |
MCNM |
Small |
Small |
Medium |
MCNM-enabled product |
Medium |
Small |
Small |
|
Adhesion/cohesion |
MCNM |
Large[73] |
Large[74] |
Medium[74] |
MCNM-enabled product |
Large |
Large |
Small |
|
Liquid media |
||||
Dissolution rate |
MCNM |
Large |
||
MCNM-enabled product |
Large[78] |
Large[79] |
Large |
|
Dispersibility |
MCNM-enabled product |
Large[80] |
||
Viscosity |
MCNM-enabled product |
Medium |
Medium[87] |
Small |
Mechanical |
||||
Tensile strength |
MCNM |
Small |
Large |
Small or Larged [88] |
MCNM-enabled product |
Large |
Large |
Small or Largee [89] |
|
Ductility |
MCNM |
Small |
Large |
Small or Larged [88] |
MCNM-enabled product |
Large |
Large |
Small or Largee [89] |
|
Elasticity |
MCNM |
Small |
Small or Larged [88] |
|
MCNM-enabled product |
Large |
Large |
Small or Largee [89] |
|
Reactive |
||||
Oxygen vacancies |
MCNM |
Small |
Small |
|
Reactive sites |
MCNM |
Small |
Small |
|
Redox reactivity |
MCNM |
Small |
Small |
Large[99] |
Metal oxide acid-base reactivity |
MCNM |
Small |
Small |
Based on [Table 2], some general observations can be made for the estimated potential impact on aspects of risk for the property classes focused on. First, for MCNMs and MCNM-enabled products that have intended new or enhanced functionalities related to “heat and thermodynamics” and “optical” properties, in general, we expect no or a small impact on related risk aspects. One possible exception where the impact may be large for optical properties is for either intentional dermal applications or inadvertent release of MCNMs to the environment or contacting skin. In such cases, the optical properties may result in photoreactivity, resulting in toxicity. Another exception for properties related to heat and thermodynamics may occur where there is an external energy source that can trigger heating of the MCNM or the MCNM-enabled product, as, for example, may be the case for certain medical applications, which may damage biological molecules and/or kill cells.
Impacts on risk aspects for properties dealing with “liquid media” are considered to be medium or large for release and fate/toxicokinetics, whereas the impact on toxicity can be small or large. The impact of dissolution rate on toxicity is considered to be potentially large, as toxicity can differ between materials and the corresponding solutes (molecules, ions). Overall, this suggests that researchers, innovators, and risk assessors should pay attention to the impacts on risk aspects for MCNMs and MCNM-enabled products that have intended new or enhanced functionalities related to dissolution rate, dispersibility, or viscosity.
Impact on risk aspects for “electromagnetic” properties and properties related to “surfaces” may be considerable. However, by our judgment, which risk aspect is impacted seems to be property-dependent. Large impacts on risk for electromagnetic properties are mostly expected on fate/toxicokinetics and toxicity, whereas for surfaces, the potential impact is even more property-specific. For example, both electrochemical activity (conductivity and conductance) and pore characteristics may have an impact on toxicity by affecting the reactivity of a material through the potential to produce reactive oxygen species. When the properties related to magnetism or adhesion/cohesion are altered, this may impact the agglomeration behavior of the material, which is likely to have an impact on fate/toxicokinetics.
Our assessment also shows that MCNMs having new or enhanced functionalities related to “mechanical” properties may have a large impact on fate/toxicokinetics. For MCNM-enabled products (but not MCNMs themselves), mechanical properties may also have a large impact on the release of (components of) MCNMs. Here we hypothesize that mechanical properties mostly affect the extent or form of release from a MCNM-enabled product, due to, e.g., abrasion, weathering, use, or end-of-life. Further, when materials are sufficiently elastic, the uptake kinetics into an organism of a material might be altered, which in turn might increase or decrease the potential risk of a material. When mechanical properties are introduced or changed through a combination of single components (be it as MCNMs themselves or in an MCNM-enabled product), the risk assessment of these materials should specifically address potential issues related to fate/toxicokinetics.
When MCNMs are designed to have altered “reactive” properties, this can, by our judgment, affect toxicity. A common mechanism by which these properties may affect toxicity is through altering the production of reactive oxygen species. When reactive properties are introduced or changed through a combination of single components (be it as MCNMs themselves or in an MCNM-enabled product), the risk assessment of these materials should specifically address potential issues related to toxicity.
#
#
Case Studies
To further demonstrate its feasibility for early innovation, the material property-guided approach was applied in several case studies of MCNMs that are in use or are being developed within the EU Horizon 2020 project SUNSHINE [22]. These case study MCNMs include two materials with a mesoporous silica core (i.e., SiO2-APTES, SiO2@ZnO), and a core–shell SiC@TiO2. For each case study, the relevant intended application, functionality, physicochemical, and material properties were identified. Following the approach ([Fig. 1]), the material property–risk relations were applied, and the potential implications from a functionality point of view were considered. These considerations can be used in early stages of innovations, and complemented with other considerations, such as those related to toxicological information from components of the MCNM. Results of these case studies are reported in [Table 3].
MCNM, physicochemical information, and application |
Information on material properties related to new or enhanced functionality |
Potential impact on aspects of risk related to material propertyb |
Potential implications for innovation and research (SbD) |
---|---|---|---|
aSee [Tables 2] and S2.1–S2.7 for further details. bAPTES: 3-aminopropyltriethoxysilane. cAs a general consideration of using SiO2@ZnO, note that the ZnO coating may result in Zn-ion release that may be hazardous to the environment. dAs a general consideration of using SiC and/or TiO2, note that SiC, TiO2, and SiC-TiO2 can be very persistent. This may result in accumulation, provided that there is release from the MCNM-enabled product. |
|||
SiO2-APTESb: Spherical 20 nm mesoporous SiO2 with covalently bound APTESa NPs |
Liquid media (dispersibility): The amine groups of the APTES provide polarity, which
improves the dispersibility in ionic media, such as Portland cement pastes |
Release: large |
Consider the form of release during manufacturing, abrasion/weathering and at end-of-life, and their consequent fate/toxicokinetics in view of potential risk |
Mechanical properties (tensile strength and ductility of MCNM-enabled product): The
SiO2-APTES promotes a change in the microstructure of cement pastes by delaying the initial
hydration reactions, but promoting the pozzolanic reaction later. The changed porous
structure improves the mechanical performance of the resulting concrete[101]
|
|||
SiO2@ZnO (core–shell) |
Optical (photocatalytic reactive properties): Chemical reaction (oxidation of NO
x
) is facilitated in the presence of light (photocatalytic effects are considered under
“light absorption”). The use of the additive results in better selectivity toward
the formation of nitrates instead of NO2
−
|
Release: small |
Consider if dermal exposure to SiO2@ZnO is possible, e.g., during manufacturing, use or end-of-life, and if so, consider potential phototoxicity/ROS formation |
SiC@TiO2 (core–shell) |
Surfaces (adhesion/cohesion; wettability and surface tension): a mixture of two different
nanoscale dimensions of SiC@TiO2 MCNMs in ceramic matrix is used to develop rough fractal surfaces (at the nanoscale),
thereby increasing hydrophobicity and providing antistick properties |
Release: large |
Consider the form of release during manufacturing, during use and at end-of-life, and their subsequent fate/toxicokinetics in view of potential risk |
Liquid media (dispersibility): TiO2 shell is used to improve compatibility with the ceramic sol-gel matrix. This allows
the use of the SiC properties in the product, such as chemical and heat resistance,
thermal conductivity, and mechanical resistance |
#
Discussion
Next to many promising benefits from material innovations, the development of increasingly complex (nano)materials, including MCNMs and other advanced materials, poses a challenge to safe innovation and risk assessment. One of the key challenges in identifying SbD considerations for the early stages of the innovation is the lack of low-cost and easily accessible information regarding the safety of advanced materials. Here, it is argued that when specific toxicological information is yet unavailable, potential safety issues of MCNMs (and other advanced materials) can be identified by examining the material properties linked to the new or enhanced functionality of the material. This study, therefore, provides an outline of a novel material property-guided approach to support SbD. The approach presented complements existing SbD and SSbD tools and methods. It may assist innovators, researchers, and risk assessors in identifying flags based on limited existing information related to functionality that can trigger further evaluation or decision-making at these very early innovation stages. Other tools can be used to identify other aspects relevant for decision-making in innovation, for example, related to sustainability. Ultimately, the current approach aims to support the development of MCNMs and other advanced materials according to SSbD principles.
As detailed in the above sections, the basis of the approach is to assess “material property–risk relations.” In this study, 21 of these relations were qualitatively estimated on the basis of literature studies and expert assessment. However, the conducted literature studies were not exhaustive and should therefore be considered as preliminary findings, demonstrating the concept of taking functionality and material properties into account in SbD of materials. We encourage innovators, scientists, and risk assessors to become familiar with the approach and suggest modifications and refinements, e.g., by further investigating specific “material property–risk relations” of the properties relevant to the functionality of their materials. The better these relations are known, the more effective the tool can be to steer toward safer materials in early innovation stages.
Over the last decades, much of the nanotoxicology research has been focused on how nanomaterials behave in environmental media and the human body, and how nanomaterials react with cells, organs, and individuals, subsequently causing toxicity. As a result, for some material properties that are key to both functionality and risk, there is currently a considerable knowledge base. For example, information is available on how properties like dissolution, dispersibility, and reactivity affect the release, fate/toxicokinetics, and toxicity of nanomaterials.[75] [76] [81] [82] [83] [84] [85] [92] [93] [94] [95] [96] [97] [98] [99] [100] [101] [102] Other properties, such as heat and thermodynamics, and some optical properties, have received much less toxicological examination. Consequently, there is less certainty on the potential impact of these properties on release, fate/toxicokinetics, and toxicity. The uncertainty in the relations between material properties and risk, therefore, varies. Assessing the level of uncertainty for different material properties–risk relations was beyond the scope of this study and requires additional investigation. However, it is encouraged to consider the uncertainty of any identified “material property–risk relations,” for example, by analyzing the existing information on this relation.
Furthermore, some of the properties mentioned are interrelated, meaning that a change in one property also affects another property. An example is that the pore characteristics of a material also directly affect the mechanical strength of the material (see Tables S2.4 and S2.6 in Supplementary Information). Such interrelations are not always obvious. This underlines the continued need for safety testing of MCNMs that should be part of further stages of innovation, which our approach cannot substitute.
The current list of material properties related to new or improved functionality of MCNMs is not exhaustive. Instead, the list focused on properties commonly used in MCNM applications or those expected to influence aspects of risks. Innovators, researchers or risk assessors could take this list as a starting point, and are invited to assess the potential impact on risk for additional relevant material properties. For example, many carrier materials can be considered MCNMs. These materials are specifically designed to facilitate the precise delivery of active ingredients like medicines or pesticides. The carriers can therefore significantly influence fate and toxicokinetics.[10] [11] The current approach does not (yet) consider carrier functionality but presents an opportunity for its inclusion in assessments.
While this approach focused on safety, it is recognized that a full SSbD approach should address (environmental) sustainability as well. Modified or new properties can affect sustainability at different stages of the life cycle of an MCNM or MCNM-enabled product, for example, regarding impact categories related to pollution [20]. Hence, although out of the scope of the present work, the impact of material properties related to new or enhanced functionalities on sustainability aspects may be considered for an MCNM, or any other advanced material, in the context of SSbD. Sustainability and further safety considerations in the innovation process may (also) be addressed by other existing or to be developed tools.
#
Conclusions
In this work, we have outlined a material property-guided approach to estimate impacts on aspects of risks linked to new or enhanced functionality in MCNMs. These relations may be used in SbD of new materials in very early innovation stages where toxicological information is (mostly) absent. By identifying potential flags, potential risks can be mitigated and further evaluation can be triggered in a targeted manner. They may also support grouping and read-across of MCNMs as well as overarching considerations in risk assessment. Our preliminary findings, for example, indicate that mechanical properties may have an impact on fate/toxicokinetics, while reactive properties are expected to affect toxicity. It is important to note that the estimated impact can be both positive and negative, meaning that the risk can increase or decrease. For both directions of the impact, this information may help regulators, scientists, and innovators in the assessment of the safety of their materials, and thereby, our approach may facilitate SbD, especially at early innovation stages. Through the approach, several potential implications for innovation and research were identified for several case study MCNMs, which, when sufficiently addressed, may contribute to safer use of MCNMs in society. These potential implications could be used along with information from other tools, approaches that can support SbD. Further research should consolidate the reported relations (including uncertainties) via additional information from literature or experimental and/or modeling studies.
#
#
Contributors’ Statement
P.v.K., N.K., V.S., and A.O.: conceptualized the paper and formulated research goals and aims. D.H., L.S.-H., V.S., and A.O. were involved in funding acquisition. Research, i.e., identification of properties, literature studies, impact assessments, was performed by E.B., A.B., V.C., P.v.K., T.F., N.K., A.G., H.R., V.S., and A.O. The methodology was developed by E.S., J.H.W., P.v.K., N.K., E.B., A.B., and A.O. Writing and editing were performed by all authors, with original drafts by E.S., J.H.W., and A.O.
Conflict of Interest
The authors declare that they have no conflict of interest.
Acknowledgment
Jacqueline van Engelen and Walter Brand (both RIVM) are acknowledged for reviewing and assisting in formatting the manuscript.
-
References
- 1 Tavernaro I, Dekkers S, Soeteman-Hernández LG, Herbeck-Engel P, Noorlander C, Kraegeloh A. NanoImpact 2021; 24: 100354
- 2 D'mello SR, Cruz CN, Chen M, Kapoor M, Lee S, Tyner KM. Na Nanotechnol 2017; 12: 523-529
- 3 Peters RJB, Bouwmeester H, Gottardo S. et al. Trends Food Sci Technol 2016; 54: 155-164
- 4 Piccinno F, Gottschalk F, Seeger S, Nowack B. J Nanopart Res 2012; 14: 1109
- 5 Dang Y, Zhang Y, Fan L, Chen H, Roco MC. Trends in worldwide nanotechnology patent applications: 1991 to 2008. J Nanopart Res 2010; 12: 687-706
- 6 Banin U, Ben-Shahar Y, Vinokurov K. Chem Mater 2013; 26: 97-110
- 7 Giese B, Drapalik M, Zajicek L, Jepsen D, Reihlen A, Zimmermann T. Advanced Materials: Overview of the Field and Screening Criteria for Relevance Assessment. Dessau-Roßlau, Germany: German Environment Agency (UBA); 2020
- 8 eNanoMapper, http://enanomapper.net/ 2022
- 9 Saleh NB, Aich N, Plazas-Tuttle J, Lead JR, Lowry GV. Research strategy to determine when novel nanohybrids pose unique environmental risks. Environ Sci: Nano 2015; 2: 11-18
- 10 Ahrens B, Berkner S, Blum C. et al. Advanced Materials. Cornerstones for a Safe and Sustainable Life Cycle. Dessau-Roßlau, Germany: German Environment Agency (UBA); 2023
- 11 Gressler S, Hipfinger C, Pavlicek A. et al. Nanocarrier – Part I: Overview and Categorization of Nanocarriers. Dessau-Roßlau, Germany: German Environment Agency (UBA); 2024
- 12 Zhang F, Wang Z, Peijnenburg WJGM, Vijver MG. Environ Sci Technol 2022; 56: 15238-15250
- 13 Zeng H, Sun S. Adv Funct Mater 2008; 18: 391-400
- 14
Heunisch E,
Cassee F,
Bleeker E,
Kuhlbusch T,
Gonzales M.
Development or revisions of OECD test guideline (TG) and guidance documents (GD) applicable
for nanomaterials, Nanoharmony, Nanomet, A status report. July 2022
- 15 Bleeker EAJ, Swart E, Braakhuis H. et al. Regul Toxicol Pharmacol 2023; 139: 105360
- 16 Soeteman-Hernandez LG, Apostolova MD, Bekker C. et al. Mater Today Commun 2019; 20: 100548
- 17 Martínez-Azúa BC, Sama-Berrocal C. J Open Innov: Technol, Market, Complex 2022; 8: 134
- 18
European Commission.
Chemicals strategy. The EU’s chemicals strategy for sustainability towards a toxic-free
environment, https://environment.ec.europa.eu/strategy/chemicals-strategy_en 2020
- 19 Abbate E, Garmendia Aguirre I, Bracalente G. et al. Safe and Sustainable by Design Chemicals and Materials – Methodological Guidance. Luxembourg: Publications Office of the European Union; 2024. https://publications.jrc.ec.europa.eu/repository/handle/JRC138035
- 20 Caldeira C, Farcal R, Garmendia Aguirre I. et al. Safe and sustainable by design chemicals and materials. Framework for the definition of criteria and evaluation procedure for chemicals and materials, JRC Technical Report, JRC128591. Luxembourg: Publications Office of the European Union; 2022
- 21 NanoReg2. https://www.rivm.nl/en/international-projects/nanoregii (accessed 16/07/2024)
- 22 SUNSHINE. https://www.h2020sunshine.eu/ (accessed 16/07/2024).
- 23
OECD.
Sustainability and safe and sustainable by design: working descriptions for the safer
innovation approach, Series on the Safety of Manufactured Nanomaterials No. 105, ENV/CBC/MONO(2022)30;
2022
- 24
EEA.
Designing safe and sustainable products requires a new approach for chemicals; 2021
https://www.eea.europa.eu/publications/designing-safe-and-sustainable-products-1/delivering-products-that-are-safe
- 25
Cefic.
Safe and Sustainable-by-Design: Boosting innovation and growth within the European
chemical industry; 2021 https://cefic.org/app/uploads/2021/09/Safe-and-Sustainable-by-Design-Report-Boosting-innovation-and-growth-within-the-European-chemical-industry.pdf
- 26
Cefic.
Safe and Sustainable-by-Design: a transformative power; 2022 https://cefic.org/app/uploads/2022/04/Safe-and-Sustainable-by-Design-Guidance-A-transformative-power.pdf
- 27
Cefic.
Safe and Sustainableby-Design: A guidance to unleash the transformative power of innovation;
2024 https://cefic.org/app/uploads/2024/03/Safe-and-Sustainable-by-Design-a-guidance-to-unleash-the-transformative-power-of-innovation.pdf
- 28
ChemSec.
Our view on Safe and Sustainable by Design criteria; 2021 https://chemsec.org/reports/our-view-on-safe-and-sustainable-by-design-criteria/
- 29 Morose G. J Clean Prod 2010; 18: 285-289
- 30 Soeteman-Hernández LG, Blanco CF, Koese M, Sips AJAM, Noorlander CW, Peijnenburg WJGM. iScience 2023; 26: 106060
- 31 Pizzol L, Livieri A, Salieri B. et al. Clean Environ Syst 2023; 10: 100132
- 32 Caldeira C, Farcal R, Moretti C. et al. Safe and sustainable by design chemicals and materials. Review of safety and sustainability dimensions, aspects, methods, indicators, and tools, JRC Technical Report. Luxembourg: Publications Office of the European Union; 2022
- 33 Jacobs JF, van de Poel IR, Osseweijer P. Fiedeler U, Coenen C, Davies SR. Ferrari. eds Towards Safety and Sustainability by Design Nano-Sized TiO2 in Sunscreens, in Understanding Nanotechnology: Philosophy, Policy and Publics. Heidelberg, Germany: Akademische Verlagsgesellschaft AKA; 2010: 187-198
- 34 Nath D, Banerjee P. Environ Toxicol Pharmacol 2013; 36: 997-1014
- 35 Hristozov D, Zabeo A, Soeteman-Hernández LG, Pizzol L, Stoycheva S. RSC Sustainability 2023; 1: 838-846
- 36
European Commission.
Commission Recommendation of 8.12.2022 establishing a European assessment framework
for ‘safe and sustainable by design’ chemicals and materials; 2022
- 37
OECD.
Moving towards a Safe(r) Innovation Approach (SIA) for more sustainable nanomaterials
and nano-enabled products, Series on the Safety of Manufactured Nanomaterials No.
96, ENV/JM/MONO/(2020)36/REV1; 2020
- 38 Wohlleben W, Persson M, Suarez-Merino B. et al. Environ Sci: Nano 2024; 11: 2948-2967
- 39 Basei G, Hristozov D, Lamon L. et al. NanoImpact 2019; 13: 76-99
- 40 Balraadjsing S, Peijnenburg WJGM, Vijver MG. Chemosphere 2022; 307: 135930
- 41 Zhou Y, Wang Y, Peijnenburg W, Vijver MG, Balraadjsing S, Fan W. Environ Sci Technol 2023; 57: 17786-17795
- 42 Li L, Luo Y, Li R. et al. Effective uptake of submicrometre plastics by crop plants via a crack-entry mode. Nat Sustainability 2020; 3: 929-937
- 43 Braakhuis HM, Murphy F, Ma-Hock L. et al. Appl In Vitro Toxicol 2021; 7: 112-128
- 44 Di Cristo L, Janer G, Dekkers S. et al. Nanotoxicology 2022; 16: 310-332
- 45 Di Cristo L, Oomen AG, Dekkers S. et al. Nanomaterials 2021; 11: 2623
- 46 Murphy FA, Johnston HJ, Dekkers S. et al. ALTEX 2023; 40: 125-140
- 47
European Commission.
Commission Regulation (EU) 2018/1881 of 3 December 2018 amending Regulation (EC) No
1907/2006 of the European Parliament and of the Council on the Registration, Evaluation,
Authorisation and Restriction of Chemicals (REACH) as regards Annexes I, III, VI,
VII, VIII, IX, X, XI, and XII to address nanoforms of substances; 2018
- 48 Stone V, Gottardo S, Bleeker EAJ. et al. Nano Today 2020; 35: 100941
- 49 Stoliński F, Rybińska-Fryca A, Gromelski M, Mikolajczyk A, Puzyn T. Nanotoxicology 2022; 16: 276-289
- 50 Banerjee A, Kar S, Pore S, Roy K. Nanotoxicology 2023; 17: 78-93
- 51 European Commission – About technology readiness levels. https://euraxess.ec.europa.eu/career-development/researchers/manual-scientific-entrepreneurship/major-steps/trl (accessed 16/07/2024)
- 52 Goff JM, Sinnott SB, Dabo I. J Chem Phys 2020; 152: 064102
- 53 Sukhanova A, Bozrova S, Sokolov P, Berestovoy M, Karaulov A, Nabiev I. Nanoscale Res Lett 2018; 13: 44
- 54 Burello E, Worth AP. Nanotoxicology 2011; 5: 228-235
- 55 Yin S, Liu J, Kang Y, Lin Y, Li D, Shao L. Br J Pharmacol 2019; 176: 3754-3774
- 56 Zhang H, Ji Z, Xia T. et al. ACS Nano 2012; 6: 4349-4368
- 57 Gutiérrez L, de la Cueva L, Moros M. et al. Nanotechnology 2019; 30: 112001
- 58 Lim EWC, Feng R. J Chem Phys 2012; 136: 124109
- 59 Huss A, Spoerri A, Egger M, Kromhout H, Vermeulen R, Cohort SN. Amyotroph Lateral Scler Frontotemp Degener 2015; 16: 80-85
- 60 Koeman T, Slottje P, Schouten LJ. et al. Occup Environ Med 2017; 74: 578-585
- 61 Jose J, Kumar R, Harilal S. et al. Environ Sci Pollut Res Int 2020; 27: 19214-19225
- 62 Mohapatra J, Xing M, Liu JP. Materials 2019; 12: 3208
- 63 Nobrega G, de Souza RR, Gonçalves IM, Moita AS, Ribeiro JE, Lima RA. Appl Sci 2022; 12: 1115
- 64 Bischof JC, Diller KR. Ann Rev Biomed Eng 2018; 20: 301-327
- 65 Hartmann NIB, Skjolding LM, Hansen SF, Baun A, Kjølholt J, Gottschalk F. Environmental Fate and Behaviour of Nanomaterials. New Knowledge on Important Transfomation Processes. Copenhagen, Denmark: Danish Environmental Protection Agency; 2014
- 66 Yu H, Peng Y, Yang Y, Li Z-Y. npj Comput Mater 2019; 5: 45
- 67 Ramírez-García G, Martínez-Alfaro M, d'Orlyé F. et al. Int J Pharm 2017; 532: 696-703
- 68 Ferreira-Gonçalves T, Constantin C, Neagu M, Pinto Reis C, Sabri F, Simón-Vázquez R. Biomed Pharm 2021; 144: 112356
- 69 Kumeria T, McInnes SJP, Maher S, Santos A. Expert Opin Drug Delivery 2017; 14: 1407-1422
- 70 Singh N, Son S, An J. et al. Chem Soc Rev 2021; 50: 12883-12896
- 71 Liu Y, Zhu S, Gu Z, Chen C, Zhao Y. Particuology 2022; 69: 31-48
- 72 Yagublu V, Karimova A, Hajibabazadeh J. et al. J Funct Biomater 2022; 13: 196
- 73 Krans NA, van der Feltz EC, Xie J, Dugulan IA, Zečević J, de Jong KP. Chem Cat Chem 2018; 10: 3388-3391
- 74 Kobos L, Shannahan J. Wiley Interdiscip Rev Nanomed Nanobiotechnol 2020; 12: 1608
- 75 EFSA Scientific Committee. More S, Bampidis V, Benford D. et al. EFSA J 2021; 19: 6768
- 76 Misra SK, Dybowska A, Berhanu D, Luoma SN, Valsami-Jones E. Sci Total Environ 2012; 438: 225-232
- 77 Peijnenburg WJGM, Ruggiero E, Boyles M. et al. Materials 2020; 13: 2235
- 78 Bhakta HC, Lin JM, Grover WH. Sci Rep 2020; 10: 19734
- 79 Amorim MJB, Lin S, Schlich K. et al. Environ Sci Technol 2018; 52: 1514-1524
- 80 Kennedy AJ, Coleman JG, Diamond SA. et al. Nanotoxicology 2017; 11: 546-557
- 81 Halamoda-Kenzaoui B, Ceridono M, Urbán P. et al. J Nanobiotechnol 2017; 15: 48
- 82 Wick P, Manser P, Limbach LK. et al. Toxicol Lett 2007; 168: 121-131
- 83 Li X, Wang B, Zhou S. et al. J Nanbiotechnol 2020; 18: 45
- 84 Yuan X, Zhang X, Sun L, Wei Y, Wei X. Part Fibre Toxicol 2019; 16: 18
- 85 Murugadoss S, Brassinne F, Sebaihi N. et al. Part Fibre Toxicol 2020; 17: 10
- 86 Murugadoss S, Mülhopt S, Diabaté S. et al. Nanomaterials 2021; 11: 3226
- 87 EFSA Panel on Food Additives and Nutrient Sources added to Food (ANS). scientific opinion on the use of high viscosity white mineral oils as a food additive. EFSA J 2009; 7: 1387
- 88 Murphy F, Dekkers S, Braakhuis H. et al. NanoImpact 2021; 22: 100314
- 89 Abaricia JO, Farzad N, Heath TJ, Simmons J, Morandini L, Olivares-Navarrete R. Acta Biomater 2021; 133: 58-73
- 90 Anselmo AC, Zhang M, Kumar S. et al. ACS Nano 2015; 9: 3169-3177
- 91 Cifuentes-Rius A, Boase NRB, Font I. et al. ACS Appl Mater Interfaces 2017; 9: 11461-11471
- 92 Boostani H, Modirrousta S. Procedia Eng 2016; 145: 1541-1548
- 93 Feng G, Hu M, Wu B. et al. Nanomaterials 2022; 12: 742
- 94 Nundy S, Ghosh A, Tahir A, Mallick TK. ACS Appl Mater Interfaces 2021; 13: 25540-25552
- 95 Pastrana HF, Cartagena-Rivera AX, Raman A, Ávila A. J Nanobiotechnol 2019; 17: 32
- 96 Pešić M, Podolski-Renić A, Stojković S. et al. Chem-Biol Interact 2015; 232: 85-93
- 97 Bahl A, Hellack B, Wiemann M. et al. NanoImpact 2020; 19: 100234
- 98 Warheit DB, Reed KL, Sayes CM. Inhalation Toxicol 2009; 21: 61-67
- 99 Sims CM, Hanna SK, Heller DA. et al. Nanoscale 2017; 9: 15226-15251
- 100 Pavan C, Delle Piane M, Gullo M. et al. Part Fibre Toxicol 2019; 16: 32
- 101 Kaymaz SV, Nobar HM, Sarıgül H, Soylukan C, Akyüz L, Yüce M. Adv Colloid Interface Sci 2023; 322: 103035
- 102 Vasconcellos JS, Bomfim Fraga YS, da Silva Rêgo JH, Confessori Sartoratto PP, Rojas MF. Dev Built Environ 2023; 14: 100157
- 103 Svendsen C, Walker LA, Matzke M. et al. Nat Nanotechnol 2020; 15: 731-742
Correspondence
Publication History
Received: 20 January 2025
Accepted after revision: 31 March 2025
Accepted Manuscript online:
02 June 2025
Article published online:
30 June 2025
© 2025. The Author(s). This is an open access article published by Thieme under the terms of the Creative Commons Attribution License, permitting unrestricted use, distribution, and reproduction so long as the original work is properly cited. (https://creativecommons.org/licenses/by/4.0/).
Georg Thieme Verlag KG
Oswald-Hesse-Straße 50, 70469 Stuttgart, Germany
Elmer Swart, Jan-Harm Westerdiep, Elena Badetti, Andrea Brunelli, Virginia Cazzagon, Teresa Fernandes, Anniek M. C Gielen, Danail Hristozov, Petra C. E. van Kesteren, Nynke A. Krans, Samia Ouhajji, Willie J. G. M. Peijnenburg, Hubert Rauscher, Lya G. Soeteman-Hernández, Vicki Stone, Georgia Tsiliki, Agnes G. Oomen. Supporting Safe-by-Design of Multicomponent Nanomaterials by Linking Functionality-Related Properties with Potential Safety Issues. Sustainability & Circularity NOW 2025; 02: a26255344.
DOI: 10.1055/a-2625-5344
-
References
- 1 Tavernaro I, Dekkers S, Soeteman-Hernández LG, Herbeck-Engel P, Noorlander C, Kraegeloh A. NanoImpact 2021; 24: 100354
- 2 D'mello SR, Cruz CN, Chen M, Kapoor M, Lee S, Tyner KM. Na Nanotechnol 2017; 12: 523-529
- 3 Peters RJB, Bouwmeester H, Gottardo S. et al. Trends Food Sci Technol 2016; 54: 155-164
- 4 Piccinno F, Gottschalk F, Seeger S, Nowack B. J Nanopart Res 2012; 14: 1109
- 5 Dang Y, Zhang Y, Fan L, Chen H, Roco MC. Trends in worldwide nanotechnology patent applications: 1991 to 2008. J Nanopart Res 2010; 12: 687-706
- 6 Banin U, Ben-Shahar Y, Vinokurov K. Chem Mater 2013; 26: 97-110
- 7 Giese B, Drapalik M, Zajicek L, Jepsen D, Reihlen A, Zimmermann T. Advanced Materials: Overview of the Field and Screening Criteria for Relevance Assessment. Dessau-Roßlau, Germany: German Environment Agency (UBA); 2020
- 8 eNanoMapper, http://enanomapper.net/ 2022
- 9 Saleh NB, Aich N, Plazas-Tuttle J, Lead JR, Lowry GV. Research strategy to determine when novel nanohybrids pose unique environmental risks. Environ Sci: Nano 2015; 2: 11-18
- 10 Ahrens B, Berkner S, Blum C. et al. Advanced Materials. Cornerstones for a Safe and Sustainable Life Cycle. Dessau-Roßlau, Germany: German Environment Agency (UBA); 2023
- 11 Gressler S, Hipfinger C, Pavlicek A. et al. Nanocarrier – Part I: Overview and Categorization of Nanocarriers. Dessau-Roßlau, Germany: German Environment Agency (UBA); 2024
- 12 Zhang F, Wang Z, Peijnenburg WJGM, Vijver MG. Environ Sci Technol 2022; 56: 15238-15250
- 13 Zeng H, Sun S. Adv Funct Mater 2008; 18: 391-400
- 14
Heunisch E,
Cassee F,
Bleeker E,
Kuhlbusch T,
Gonzales M.
Development or revisions of OECD test guideline (TG) and guidance documents (GD) applicable
for nanomaterials, Nanoharmony, Nanomet, A status report. July 2022
- 15 Bleeker EAJ, Swart E, Braakhuis H. et al. Regul Toxicol Pharmacol 2023; 139: 105360
- 16 Soeteman-Hernandez LG, Apostolova MD, Bekker C. et al. Mater Today Commun 2019; 20: 100548
- 17 Martínez-Azúa BC, Sama-Berrocal C. J Open Innov: Technol, Market, Complex 2022; 8: 134
- 18
European Commission.
Chemicals strategy. The EU’s chemicals strategy for sustainability towards a toxic-free
environment, https://environment.ec.europa.eu/strategy/chemicals-strategy_en 2020
- 19 Abbate E, Garmendia Aguirre I, Bracalente G. et al. Safe and Sustainable by Design Chemicals and Materials – Methodological Guidance. Luxembourg: Publications Office of the European Union; 2024. https://publications.jrc.ec.europa.eu/repository/handle/JRC138035
- 20 Caldeira C, Farcal R, Garmendia Aguirre I. et al. Safe and sustainable by design chemicals and materials. Framework for the definition of criteria and evaluation procedure for chemicals and materials, JRC Technical Report, JRC128591. Luxembourg: Publications Office of the European Union; 2022
- 21 NanoReg2. https://www.rivm.nl/en/international-projects/nanoregii (accessed 16/07/2024)
- 22 SUNSHINE. https://www.h2020sunshine.eu/ (accessed 16/07/2024).
- 23
OECD.
Sustainability and safe and sustainable by design: working descriptions for the safer
innovation approach, Series on the Safety of Manufactured Nanomaterials No. 105, ENV/CBC/MONO(2022)30;
2022
- 24
EEA.
Designing safe and sustainable products requires a new approach for chemicals; 2021
https://www.eea.europa.eu/publications/designing-safe-and-sustainable-products-1/delivering-products-that-are-safe
- 25
Cefic.
Safe and Sustainable-by-Design: Boosting innovation and growth within the European
chemical industry; 2021 https://cefic.org/app/uploads/2021/09/Safe-and-Sustainable-by-Design-Report-Boosting-innovation-and-growth-within-the-European-chemical-industry.pdf
- 26
Cefic.
Safe and Sustainable-by-Design: a transformative power; 2022 https://cefic.org/app/uploads/2022/04/Safe-and-Sustainable-by-Design-Guidance-A-transformative-power.pdf
- 27
Cefic.
Safe and Sustainableby-Design: A guidance to unleash the transformative power of innovation;
2024 https://cefic.org/app/uploads/2024/03/Safe-and-Sustainable-by-Design-a-guidance-to-unleash-the-transformative-power-of-innovation.pdf
- 28
ChemSec.
Our view on Safe and Sustainable by Design criteria; 2021 https://chemsec.org/reports/our-view-on-safe-and-sustainable-by-design-criteria/
- 29 Morose G. J Clean Prod 2010; 18: 285-289
- 30 Soeteman-Hernández LG, Blanco CF, Koese M, Sips AJAM, Noorlander CW, Peijnenburg WJGM. iScience 2023; 26: 106060
- 31 Pizzol L, Livieri A, Salieri B. et al. Clean Environ Syst 2023; 10: 100132
- 32 Caldeira C, Farcal R, Moretti C. et al. Safe and sustainable by design chemicals and materials. Review of safety and sustainability dimensions, aspects, methods, indicators, and tools, JRC Technical Report. Luxembourg: Publications Office of the European Union; 2022
- 33 Jacobs JF, van de Poel IR, Osseweijer P. Fiedeler U, Coenen C, Davies SR. Ferrari. eds Towards Safety and Sustainability by Design Nano-Sized TiO2 in Sunscreens, in Understanding Nanotechnology: Philosophy, Policy and Publics. Heidelberg, Germany: Akademische Verlagsgesellschaft AKA; 2010: 187-198
- 34 Nath D, Banerjee P. Environ Toxicol Pharmacol 2013; 36: 997-1014
- 35 Hristozov D, Zabeo A, Soeteman-Hernández LG, Pizzol L, Stoycheva S. RSC Sustainability 2023; 1: 838-846
- 36
European Commission.
Commission Recommendation of 8.12.2022 establishing a European assessment framework
for ‘safe and sustainable by design’ chemicals and materials; 2022
- 37
OECD.
Moving towards a Safe(r) Innovation Approach (SIA) for more sustainable nanomaterials
and nano-enabled products, Series on the Safety of Manufactured Nanomaterials No.
96, ENV/JM/MONO/(2020)36/REV1; 2020
- 38 Wohlleben W, Persson M, Suarez-Merino B. et al. Environ Sci: Nano 2024; 11: 2948-2967
- 39 Basei G, Hristozov D, Lamon L. et al. NanoImpact 2019; 13: 76-99
- 40 Balraadjsing S, Peijnenburg WJGM, Vijver MG. Chemosphere 2022; 307: 135930
- 41 Zhou Y, Wang Y, Peijnenburg W, Vijver MG, Balraadjsing S, Fan W. Environ Sci Technol 2023; 57: 17786-17795
- 42 Li L, Luo Y, Li R. et al. Effective uptake of submicrometre plastics by crop plants via a crack-entry mode. Nat Sustainability 2020; 3: 929-937
- 43 Braakhuis HM, Murphy F, Ma-Hock L. et al. Appl In Vitro Toxicol 2021; 7: 112-128
- 44 Di Cristo L, Janer G, Dekkers S. et al. Nanotoxicology 2022; 16: 310-332
- 45 Di Cristo L, Oomen AG, Dekkers S. et al. Nanomaterials 2021; 11: 2623
- 46 Murphy FA, Johnston HJ, Dekkers S. et al. ALTEX 2023; 40: 125-140
- 47
European Commission.
Commission Regulation (EU) 2018/1881 of 3 December 2018 amending Regulation (EC) No
1907/2006 of the European Parliament and of the Council on the Registration, Evaluation,
Authorisation and Restriction of Chemicals (REACH) as regards Annexes I, III, VI,
VII, VIII, IX, X, XI, and XII to address nanoforms of substances; 2018
- 48 Stone V, Gottardo S, Bleeker EAJ. et al. Nano Today 2020; 35: 100941
- 49 Stoliński F, Rybińska-Fryca A, Gromelski M, Mikolajczyk A, Puzyn T. Nanotoxicology 2022; 16: 276-289
- 50 Banerjee A, Kar S, Pore S, Roy K. Nanotoxicology 2023; 17: 78-93
- 51 European Commission – About technology readiness levels. https://euraxess.ec.europa.eu/career-development/researchers/manual-scientific-entrepreneurship/major-steps/trl (accessed 16/07/2024)
- 52 Goff JM, Sinnott SB, Dabo I. J Chem Phys 2020; 152: 064102
- 53 Sukhanova A, Bozrova S, Sokolov P, Berestovoy M, Karaulov A, Nabiev I. Nanoscale Res Lett 2018; 13: 44
- 54 Burello E, Worth AP. Nanotoxicology 2011; 5: 228-235
- 55 Yin S, Liu J, Kang Y, Lin Y, Li D, Shao L. Br J Pharmacol 2019; 176: 3754-3774
- 56 Zhang H, Ji Z, Xia T. et al. ACS Nano 2012; 6: 4349-4368
- 57 Gutiérrez L, de la Cueva L, Moros M. et al. Nanotechnology 2019; 30: 112001
- 58 Lim EWC, Feng R. J Chem Phys 2012; 136: 124109
- 59 Huss A, Spoerri A, Egger M, Kromhout H, Vermeulen R, Cohort SN. Amyotroph Lateral Scler Frontotemp Degener 2015; 16: 80-85
- 60 Koeman T, Slottje P, Schouten LJ. et al. Occup Environ Med 2017; 74: 578-585
- 61 Jose J, Kumar R, Harilal S. et al. Environ Sci Pollut Res Int 2020; 27: 19214-19225
- 62 Mohapatra J, Xing M, Liu JP. Materials 2019; 12: 3208
- 63 Nobrega G, de Souza RR, Gonçalves IM, Moita AS, Ribeiro JE, Lima RA. Appl Sci 2022; 12: 1115
- 64 Bischof JC, Diller KR. Ann Rev Biomed Eng 2018; 20: 301-327
- 65 Hartmann NIB, Skjolding LM, Hansen SF, Baun A, Kjølholt J, Gottschalk F. Environmental Fate and Behaviour of Nanomaterials. New Knowledge on Important Transfomation Processes. Copenhagen, Denmark: Danish Environmental Protection Agency; 2014
- 66 Yu H, Peng Y, Yang Y, Li Z-Y. npj Comput Mater 2019; 5: 45
- 67 Ramírez-García G, Martínez-Alfaro M, d'Orlyé F. et al. Int J Pharm 2017; 532: 696-703
- 68 Ferreira-Gonçalves T, Constantin C, Neagu M, Pinto Reis C, Sabri F, Simón-Vázquez R. Biomed Pharm 2021; 144: 112356
- 69 Kumeria T, McInnes SJP, Maher S, Santos A. Expert Opin Drug Delivery 2017; 14: 1407-1422
- 70 Singh N, Son S, An J. et al. Chem Soc Rev 2021; 50: 12883-12896
- 71 Liu Y, Zhu S, Gu Z, Chen C, Zhao Y. Particuology 2022; 69: 31-48
- 72 Yagublu V, Karimova A, Hajibabazadeh J. et al. J Funct Biomater 2022; 13: 196
- 73 Krans NA, van der Feltz EC, Xie J, Dugulan IA, Zečević J, de Jong KP. Chem Cat Chem 2018; 10: 3388-3391
- 74 Kobos L, Shannahan J. Wiley Interdiscip Rev Nanomed Nanobiotechnol 2020; 12: 1608
- 75 EFSA Scientific Committee. More S, Bampidis V, Benford D. et al. EFSA J 2021; 19: 6768
- 76 Misra SK, Dybowska A, Berhanu D, Luoma SN, Valsami-Jones E. Sci Total Environ 2012; 438: 225-232
- 77 Peijnenburg WJGM, Ruggiero E, Boyles M. et al. Materials 2020; 13: 2235
- 78 Bhakta HC, Lin JM, Grover WH. Sci Rep 2020; 10: 19734
- 79 Amorim MJB, Lin S, Schlich K. et al. Environ Sci Technol 2018; 52: 1514-1524
- 80 Kennedy AJ, Coleman JG, Diamond SA. et al. Nanotoxicology 2017; 11: 546-557
- 81 Halamoda-Kenzaoui B, Ceridono M, Urbán P. et al. J Nanobiotechnol 2017; 15: 48
- 82 Wick P, Manser P, Limbach LK. et al. Toxicol Lett 2007; 168: 121-131
- 83 Li X, Wang B, Zhou S. et al. J Nanbiotechnol 2020; 18: 45
- 84 Yuan X, Zhang X, Sun L, Wei Y, Wei X. Part Fibre Toxicol 2019; 16: 18
- 85 Murugadoss S, Brassinne F, Sebaihi N. et al. Part Fibre Toxicol 2020; 17: 10
- 86 Murugadoss S, Mülhopt S, Diabaté S. et al. Nanomaterials 2021; 11: 3226
- 87 EFSA Panel on Food Additives and Nutrient Sources added to Food (ANS). scientific opinion on the use of high viscosity white mineral oils as a food additive. EFSA J 2009; 7: 1387
- 88 Murphy F, Dekkers S, Braakhuis H. et al. NanoImpact 2021; 22: 100314
- 89 Abaricia JO, Farzad N, Heath TJ, Simmons J, Morandini L, Olivares-Navarrete R. Acta Biomater 2021; 133: 58-73
- 90 Anselmo AC, Zhang M, Kumar S. et al. ACS Nano 2015; 9: 3169-3177
- 91 Cifuentes-Rius A, Boase NRB, Font I. et al. ACS Appl Mater Interfaces 2017; 9: 11461-11471
- 92 Boostani H, Modirrousta S. Procedia Eng 2016; 145: 1541-1548
- 93 Feng G, Hu M, Wu B. et al. Nanomaterials 2022; 12: 742
- 94 Nundy S, Ghosh A, Tahir A, Mallick TK. ACS Appl Mater Interfaces 2021; 13: 25540-25552
- 95 Pastrana HF, Cartagena-Rivera AX, Raman A, Ávila A. J Nanobiotechnol 2019; 17: 32
- 96 Pešić M, Podolski-Renić A, Stojković S. et al. Chem-Biol Interact 2015; 232: 85-93
- 97 Bahl A, Hellack B, Wiemann M. et al. NanoImpact 2020; 19: 100234
- 98 Warheit DB, Reed KL, Sayes CM. Inhalation Toxicol 2009; 21: 61-67
- 99 Sims CM, Hanna SK, Heller DA. et al. Nanoscale 2017; 9: 15226-15251
- 100 Pavan C, Delle Piane M, Gullo M. et al. Part Fibre Toxicol 2019; 16: 32
- 101 Kaymaz SV, Nobar HM, Sarıgül H, Soylukan C, Akyüz L, Yüce M. Adv Colloid Interface Sci 2023; 322: 103035
- 102 Vasconcellos JS, Bomfim Fraga YS, da Silva Rêgo JH, Confessori Sartoratto PP, Rojas MF. Dev Built Environ 2023; 14: 100157
- 103 Svendsen C, Walker LA, Matzke M. et al. Nat Nanotechnol 2020; 15: 731-742

