Abstract A major challenge for the global nanotechnology sector is the development of safe and functional engineered nanomaterials (ENMs) and nano-enabled products (NEPs). In order to minimise the risks to human and environmental health during the engineering of NEPs the goal of the Safe-by-Design for Nano (SbD4Nano) project is to create a novel e-infrastructure for the definition, performance testing and implementation of Safe-by-Design (SbD) approaches in the nanotechnology supply chains. The project aims to demonstrate how selecting appropriate surface modification of nanomaterials can reduce the hazard and risk to workers, consumers and the environment whilst maintaining its functionality. The presentation will give an introduction to the project and outline the results generated thus far. This project has received funding from the European Union's Horizon 2020 research and innovation program under grant agreement No. 862195
Abstract Multicomponent nanomaterials (MCNM), sometimes called nanohybrids, are advanced materials receiving increased interest in their novel or enhanced properties. Research into MCNM is in its infancy meaning that little is known about their hazard, risk or whether there is regulatory preparedness for their increased use. SUNSHINE is an industry-oriented project, where leading research and technology organisations will cooperate with SMEs and large industries to develop and implement simple, robust, and cost-effective Safe and Sustainable by Design (SSbD) strategies for materials and products incorporating advanced multi-component nanomaterials. This presentation will introduce the key elements in the project including investigations into whether existing characterisation and toxicology testing protocols are applicable and whether existing regulatory frameworks are fit for purpose for these complex structures. It will also introduce how MCNM are being used as a case study for the use of the Safe and Sustainable by Design framework. SUNSHINE project has received funding from the European Union's Horizon 2020 research and innovation programme under grant agreement No 952924.
Building on Stimson's (2000) analysis, this paper examines the shift from a focus on health towards one of crime within UK drug policy. The increased use of coerced or compulsory treatment of drug users is discussed with reference to harm reduction theory and the question of whose harm is prioritised in shaping drug services. We also identify mechanisms by which the efficacy of treatment approaches based on coercion may be lessened or reduce the efficacy of other existing services. Failure to consider these may be an important omission in any appraisal of the impact of policies that increasingly prioritise crime prevention and coercion over heath and voluntarism.
<i>Aims:</i> To describe and assess trends in the use of hallucinogens and other adjunct drugs over a 5-year period. <i>Design:</i> Repeated-measures cross-sectional survey. <i>Setting and Participants:</i> Annual magazine-based survey targeting people who use drugs in dance contexts. <i>Measurements:</i> Lifetime use prevalence (ever used); age of first use; current use prevalence (any use within the last month), and extent of use within the last month (number of days used) for LSD, psilocybin, ketamine, GHB and nitrates. <i>Findings:</i> Prevalence increases for psilocybin, ketamine, GHB and nitrates use have been detected, with a sharp recent rise in current psilocybin use in 2002–2003 contrasting with more gradual and comprehensive evidence of increased ketamine use throughout the period 1999–2003. The declining prevalence of LSD use in general population surveys is replicated in this sentinel population study. <i>Conclusions:</i> The rise in prevalence of hallucinogen and other adjunct drugs identified among dance drug users may be mirrored by wider prevalence increases among young people with a consequent need to study these trends carefully and to develop effective interventions, where required.
The ability of the UK criminal justice system to divert drug-dependent offenders into treatment has been enhanced during recent years. Despite the rapid expansion of such coercive measures, research findings to date are equivocal about their impact. This article draws on qualitative data from in-depth interviews with professionals and those mandated to treatment by the courts to assess the uses and limitations of two defining features of court-ordered drug treatment in Britain and elsewhere — drug testing and court review hearings — as a means of promoting and monitoring compliance with the conditions of these disposals.
<i>Aim:</i> This study evaluates quasi-compulsory drug treatment (QCT) arrangements for substance-dependent offenders receiving treatment instead of imprisonment in comparison to voluntary treatment within five European countries. <i>Methods:</i> Participants were interviewed with the European Addiction Severity Index, the ASI-crime module, questions on perception of pressure and self-efficacy, and the Readiness-to-Change Questionnaire at treatment entry and after 6, 12, and 18 months. <i>Results:</i> Reductions in substance use and crime as well as improvements in health and social integration were observed in QCT and voluntary treatment groups. After controlling for various factors, subjects in the QCT and the comparison group showed similar reductions in substance use and crime over time. Study retention was comparable in both groups. <i>Conclusion:</i> QCT is as effective as voluntary treatment provided in the same services in reducing substance use and crime.
<i>Background:</i> Policies and practices related to the quasi-compulsory treatment (QCT) of substance-dependent offenders are currently implemented in many countries, despite the absence of reliable knowledge about significant predictors of treatment retention. This study aimed to identify such predictors in QCT and voluntary treatment. <i>Methods:</i> Participants were treated in one of 65 institutions in 5 European countries. They were interviewed at intake on substance use, crimes committed, perceived pressure for treatment, self-efficacy, stage of change, employment, and health-related variables. Binary logistic regression models were computed to identify predictors of treatment retention at an 18-month follow-up. Moderator analyses were computed to investigate whether these predictors vary by treatment condition (QCT vs. voluntary). <i>Results:</i> A higher number of working days in the previous month was positively associated with treatment retention, while use of heroin, crack, and multiple drugs, psychiatric problems in the previous month, and lifetime depression were negatively associated with treatment retention. Higher perceived medical pressure resulted in higher treatment retention rates only for participants in QCT. <i>Conclusion:</i>Predictors of substance abuse treatment retention are quite similar across both QCT and voluntary treatments. Perceived medical pressure is of higher relevance than the often-believed legal pressure for treatment retention in QCT.
This paper reports on intake data from Quasi-Compulsory Treatment in Europe, a study of quasi-compulsory treatment (QCT) for drug dependent offenders. It explores the link between formal legal coercion, perceived pressure to be in treatment and motivation amongst a sample of 845 people who entered treatment for drug dependence in five European countries, half of them in quasi-compulsory treatment and half 'voluntarily'. Using both quantitative and qualitative data, it suggests that those who enter treatment under QCT do perceive greater pressure to be in treatment, but that this does not necessarily lead to higher or lower motivation than 'volunteers'. Many drug-dependent offenders value QCT as an opportunity to get treatment. Motivation is mutable and can be developed or diminished by the quality of support and services offered to drug-dependent offenders.
An Environmental Risk Assessment (ERA) for nanomaterials (NMs) is outlined in this paper. Contrary to other recent papers on the subject, the main data requirements, models and advancement within each of the four risk assessment domains are described, i.e., in the: (i) materials, (ii) release, fate and exposure, (iii) hazard and (iv) risk characterisation domains. The material, which is obviously the foundation for any risk assessment, should be described according to the legislatively required characterisation data. Characterisation data will also be used at various levels within the ERA, e.g., exposure modelling. The release, fate and exposure data and models cover the input for environmental distribution models in order to identify the potential (PES) and relevant exposure scenarios (RES) and, subsequently, the possible release routes, both with regard to which compartment(s) NMs are distributed in line with the factors determining the fate within environmental compartment. The initial outcome in the risk characterisation will be a generic Predicted Environmental Concentration (PEC), but a refined PEC can be obtained by applying specific exposure models for relevant media. The hazard information covers a variety of representative, relevant and reliable organisms and/or functions, relevant for the RES and enabling a hazard characterisation. The initial outcome will be hazard characterisation in test systems allowing estimating a Predicted No-Effect concentration (PNEC), either based on uncertainty factors or on a NM adapted version of the Species Sensitivity Distributions approach. The risk characterisation will either be based on a deterministic risk ratio approach (i.e., PEC/PNEC) or an overlay of probability distributions, i.e., exposure and hazard distributions, using the nano relevant models.
In: Scott-Fordsmand , J J , Peijnenburg , W J G M , Semenzin , E , Nowack , B , Hunt , N , Hristozov , D , Marcomini , A , Irfan , M-A , Jimenez , A S , Landsiedel , R , Tran , L , Oomen , A G , Bos , P M J & Hund-Rinke , K 2017 , ' Environmental Risk Assessment Strategy for Nanomaterials ' , International Journal of Environmental Research and Public Health , vol. 14 , no. 10 , 1251 . https://doi.org/10.3390/ijerph14101251
An Environmental Risk Assessment (ERA) for nanomaterials (NMs) is outlined in this paper. Contrary to other recent papers on the subject, the main data requirements, models and advancement within each of the four risk assessment domains are described, i.e., in the: (i) materials, (ii) release, fate and exposure, (iii) hazard and (iv) risk characterisation domains. The material, which is obviously the foundation for any risk assessment, should be described according to the legislatively required characterisation data. Characterisation data will also be used at various levels within the ERA, e.g., exposure modelling. The release, fate and exposure data and models cover the input for environmental distribution models in order to identify the potential (PES) and relevant exposure scenarios (RES) and, subsequently, the possible release routes, both with regard to which compartment(s) NMs are distributed in line with the factors determining the fate within environmental compartment. The initial outcome in the risk characterisation will be a generic Predicted Environmental Concentration (PEC), but a refined PEC can be obtained by applying specific exposure models for relevant media. The hazard information covers a variety of representative, relevant and reliable organisms and/or functions, relevant for the RES and enabling a hazard characterisation. The initial outcome will be hazard characterisation in test systems allowing estimating a Predicted No-Effect concentration (PNEC), either based on uncertainty factors or on a NM adapted version of the Species Sensitivity Distributions approach. The risk characterisation will either be based on a deterministic risk ratio approach (i.e., PEC/PNEC) or an overlay of probability distributions, i.e., exposure and hazard distributions, using the nano relevant models.
An Environmental Risk Assessment (ERA) for nanomaterials (NMs) is outlined in this paper. Contrary to other recent papers on the subject, the main data requirements, models and advancement within each of the four risk assessment domains are described, i.e., in the: (i) materials, (ii) release, fate and exposure, (iii) hazard and (iv) risk characterisation domains. The material, which is obviously the foundation for any risk assessment, should be described according to the legislatively required characterisation data. Characterisation data will also be used at various levels within the ERA, e.g., exposure modelling. The release, fate and exposure data and models cover the input for environmental distribution models in order to identify the potential (PES) and relevant exposure scenarios (RES) and, subsequently, the possible release routes, both with regard to which compartment(s) NMs are distributed in line with the factors determining the fate within environmental compartment. The initial outcome in the risk characterisation will be a generic Predicted Environmental Concentration (PEC), but a refined PEC can be obtained by applying specific exposure models for relevant media. The hazard information covers a variety of representative, relevant and reliable organisms and/or functions, relevant for the RES and enabling a hazard characterisation. The initial outcome will be hazard characterisation in test systems allowing estimating a Predicted No-Effect concentration (PNEC), either based on uncertainty factors or on a NM adapted version of the Species Sensitivity Distributions approach. The risk characterisation will either be based on a deterministic risk ratio approach (i.e., PEC/PNEC) or an overlay of probability distributions, i.e., exposure and hazard distributions, using the nano relevant models.
Background: There are several standards which make explicit a consensus view on sound practice in systematic reviews (SRs) for the medical sciences. Until now, no equivalent standard has been published for SRs which focus on human health risks posed by exposure to environmental challenges, chemical or otherwise. Objectives: To develop an expert, cross-sector consensus view on a key set of recommended practices which can function as a standard for the planning and conduct of SRs in the environmental health sciences. Methods: A draft set of practices was derived from two existing standards for SRs in biomedicine and discussed at an international workshop of 33 participants from government, industry, non-government organisations, and academia. The guidance was revised over six follow-up webinars, multiple rounds of email feedback, and bilateral phone calls, until there was group consensus that a comprehensive framework for the planning and conduct of high-quality environmental health SRs had been articulated. Results: The Conduct of Systematic Reviews in Toxicology and Environmental Health Research (COSTER) standard is a code of practice consisting of 70 performance elements across eight performance domains, representing the consensus view of a diverse group of experts as to what constitutes "sound and good" practice in the conduct of environmental health SRs. Discussion: COSTER provides a set of practices which, if followed, should facilitate the production of credible, high-value SRs of environmental health evidence. COSTER clarifies sound and good practice in a number of controversial aspects of SR conduct, including the management of conflicts of interest, inclusion of grey literature, and protocol registration and publication. Not all of the practices are yet commonplace but environmental health SRs would benefit from their use.
Background: There are several standards that offer explicit guidance on good practice in systematic reviews (SRs) for the medical sciences; however, no similarly comprehensive set of recommendations has been published for SRs that focus on human health risks posed by exposure to environmental challenges, chemical or otherwise. Objectives: To develop an expert, cross-sector consensus view on a key set of recommended practices for the planning and conduct of SRs in the environmental health sciences. Methods: A draft set of recommendations was derived from two existing standards for SRs in biomedicine and developed in a consensus process, which engaged international participation from government, industry, non-government organisations, and academia. The consensus process consisted of a workshop, follow-up webinars, email discussion and bilateral phone calls. Results: The Conduct of Systematic Reviews in Toxicology and Environmental Health Research (COSTER) recommendations cover 70 SR practices across eight performance domains. Detailed explanations for specific recommendations are made for those identified by the authors as either being novel to SR in general, specific to the environmental health SR context, or potentially controversial to environmental health SR stakeholders. Discussion: COSTER provides a set of recommendations that should facilitate the production of credible, high-value SRs of environmental health evidence, and advance discussion of a number of controversial aspects of conduct of EH SRs. Key recommendations include the management of conflicts of interest, handling of grey literature, and protocol registration and publication. A process for advancing from COSTER's recommendations to developing a formal standard for EH SRs is also indicated.