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  • Feature Paper
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9 October 2018

23 Pages

Risk Management of Hazardous Materials in Manufacturing Processes: Links and Transitional Spaces between Occupational Accidents and Major Accidents

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and
1
Department of Physics, Systems Engineering and Signal Theory, Escuela Politécnica Superior, Universidad de Alicante, Campus de Sant Vicent del Raspeig s/n, 03690 Sant Vicent del Raspeig, Alicante, Spain
2
Manufacturing and Construction Engineering Department, ETS de Ingenieros Industriales, Universidad Nacional de Educación a Distancia, Calle Juan del Rosal, 12, 28040 Madrid, Spain
3
Faculty of Technology, Policy and Management, Safety and Security Science Group (S3G), TU Delft, 2628 BX Delft, The Netherlands
4
Faculty of Applied Economics, Antwerp Research Group on Safety and Security (ARGoSS), University Antwerp, 2000 Antwerp, Belgium

Abstract

Manufacturing processes involving chemical agents are evolving at great speed. In this context, managing chemical risk is especially important towards preventing both occupational accidents and major accidents. Directive 89/391/EEC and Directive 2012/18/EU, respectively, are enforced in the European Union (EU) to this end. These directives may be further complemented by the recent ISO 45001:2018 standard regarding occupational health and safety management systems. These three management systems are closely related. However, scientific literature tackles the researching of these accidents independently. Thus, the main objective of this work is to identify and analyse the links and transitional spaces between the risk management of both types of accident. Among the results obtained, three transitional spaces can be pointed out which result from the intersection of the three systems mentioned. Similarly, the intersection of these spaces gives shape to a specific transitional space defined by the individual directives linked to Directive 89/391/EEC. These results are limited from a regulatory and technical perspective. Thus, the results are a starting point towards developing models that integrate the management systems studied.

1. Introduction

In the past few years, manufacturing processes involving chemical substances have evolved to a great extent, from the new technologies applied to these processes to the new products and materials produced and their regulatory framework. The chemical industry is at the heart of the European Union (EU) manufacturing industry, representing approximately 7% of EU industrial production and a 1.1% share of EU GDP. It supplies two-thirds of its production to other sectors within the manufacturing industry [1].
In regard to the regulatory framework in the EU, two relatively-recent regulations stand out at first glance. Regulation (EC) No 1907/2006 on Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH Regulation), aims to protect human health and the environment by ensuring greater safety in the production and use of chemical substances. The REACH Regulation, which entered into force in 2007, applies to all chemical substances and thus has an impact on many businesses [2]. The classification and labelling of hazardous chemicals is governed by Regulation (EC) No 1272/2008 on classification, labelling and packaging of substances and mixtures (CLP Regulation). The CLP Regulation entered into force in 2009 and it enables identification of dangerous substances by means of classification and labelling, and informing users about their hazards through standard symbols and phrases [3].
In 2018, approximately 145,000 substances were classified according to the CLP Regulation [4]. Also in 2018, more than 21,000 substances were registered in the European Economic Area under the REACH Regulation, of which more than 12,000 are used in manufacturing processes. Figure 1 shows the evolution in the number of chemical substances registered in the European Economic Area under REACH [5] starting in January 2009, when records first exist, until August 2018. To this end, taking into account the uses and exposure to these substances, a distinction is made between their global life cycle and the life cycle applied to manufacturing.
Figure 1. Evolution in the number of chemical substances registered in the European Economic Area under the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH) regulation. January 2009–August 2018 [5].
This context of change generates both opportunities and challenges in many fields of knowledge. Among these fields, risk management is particularly important, both from a systemic point of view and from more specific perspectives. Among these specific perspectives, chemical risk management should be noted in order to prevent both occupational accidents and major accidents in manufacturing environments where hazardous materials are used. For this, two separate and solid legislative frameworks exist in the EU.
In the case of the risk management of occupational accidents, Directive 89/391/EEC on the introduction of measures to encourage improvements in occupational safety and health (OSH) should be pointed out [6]. This directive has been developed through a broad set of specific directives, with Directive 98/24/EC on OSH in the field of chemical agents [7] standing out in the context of hazardous materials.
In the case of the risk management of major accidents and hazards involving dangerous substances, Directive 2012/18/EU is applicable [8]. This directive states that its provisions should be applied without prejudice to the provisions of Union law relating to OSH and the working environment, and, in particular, without prejudice to Council Directive 89/391/EEC [6].
Hence, these risk management frameworks are closely related [9] and, as a result, are open to being studied from an integrative point of view. However, despite the importance of this relationship, scientific literature addresses the study of risk management of occupational accidents and major accidents involving dangerous materials in an independent and practically excluding manner.
In this regard, using the ScienceDirect database [10], the search for the keyword ‘Directive 2012/18/EU’ anywhere in an article, returns 13,584 papers. Similarly, the keyword ‘Directive 89/391/EEC’ returns 473 papers. However, combining both keywords with the AND operator returns three articles, which are: Rasmussen et al. [11], Besserman and Mentzer [12], and Li and Guldenmund [13].
This circumstance defines a closed border between these management systems, making it difficult to develop integrative techniques and methodologies that favour the reduction of risk due to hazardous substances. In addition to the described relationship between directives, the recent opportunity defined by the ISO 45001:2018 standard on OSH management systems [14] should be pointed out.
Thus, the main objective of this study is to identify and analyze the links and transitional spaces between the risk management of occupational accidents and major accidents involving hazardous materials. To achieve this goal, the methodology followed by this study is based on researching and carrying out a comparative analysis of the legal and standardised context described above. To this end, this work is organised as follows: (1) study of the legal context within the framework of the EU; (2) comparative analysis between management systems derived from Directive 89/391/EEC [6] and Directive 2012/18/EU [8]; (3) comparative analysis between management systems derived from the ISO 45001:2018 standard [14] and Directive 2012/18/EU [8]; (4) analysis of transitional spaces between risk management of hazardous materials in manufacturing processes; (5) discussion of results; and (6) conclusions.

3. Comparative Analysis between Management Systems Derived from the Framework Directive and Directive Seveso III

Directive Seveso III indicates that member states shall require the operator to draw up a document in writing setting out the major-accident prevention policy (MAPP) and to ensure that it is properly implemented. The MAPP shall be implemented by appropriate means, structures and by a safety management system, in accordance with Annex III of this directive, and it will be proportionate to the major-accident hazards, and the complexity of the organization or the activities of the establishment. Table 4 shows the structure of the safety management system according to such Annex III. This Annex III is linked, in turn, to Annex II regarding minimum data and information to be considered in the safety report referred to in Article 10 of Directive Seveso III.
Table 4. Correspondence between structures of risk management systems: Directive Seveso III, Framework Directive and ISO 45001:2018 Standard.
The Framework Directive does not explicitly develop a safety management system. However, it contains general principles concerning the prevention of occupational risks, the protection of safety and health, the elimination of risk and accident factors, the informing, consultation, balanced participation in accordance with national laws and/ or practices and training of workers and their representatives, as well as general guidelines for the implementation of the said principles.
In themselves, the aforementioned general principles form the basis for a management system; in this case, a system to manage the safety and health of workers. To develop this, each member state of the European Union must transpose the Framework Directive into their national legal systems.
By way of example, Law 31/1995 on occupational risk prevention transposes the Framework Directive into Spanish law [39]. This Law explicitly states that occupational risk prevention must be integrated into an undertaking’s general management system, across all of the activities and across the hierarchy thereof, by means of implementing and putting into practice an occupational risk prevention plan. This occupational risk prevention plan should include the organisational structure, responsibility, roles, practices, procedures, processes and resources necessary to carry out risk prevention activity in the undertaking. The management and implementation instruments that are essential to the risk prevention plan are: the assessment of occupational risk and the planning of preventive action.
Also, Royal Decree 39/1997, which validates the Regulation on Prevention Services, develops those aspects that make it possible to integrate occupational risk prevention management into the undertaking’s activities and across the hierarchical levels thereof, based on a plan that includes work techniques, organisation and conditions [40]. Thus, as shown in Table 4, correspondence may be established between the structure of the Framework Directive and the management system included in Annex III of Directive Seveso III.
Correspondence may be classified as strong, weak or non-existent. Correspondence is strong when an issue in Annex III has its direct equivalence (major risk management vs. occupational risk management) with one or more articles of the Framework Directive. Correspondence is weak when an issue only has partial equivalence. And, obviously, correspondence is non-existent whet there is no equivalence.
Considering this, there is strong correspondence in regard to the following sections of Annex III: (i) Organization and personnel, (ii) Identification and evaluation of major hazards, (iv) Management of change, and (v) Planning for emergencies.
Correspondence is weak in sections (iii) Operational control and (vi) Monitoring performance. In regard to section (iii), the Framework Directive does not explicitly state: the management and control of risks associated with ageing equipment installed in the establishment and corrosion. In regard to section (vi), the Framework Directive does not explicitly state: the adoption and implementation of procedures for the ongoing assessment of compliance with the objectives set by the operator’s MAPP and safety management system; near misses. There is no (explicit) correspondence in regard to section (vii) regarding Audit and review.
Furthermore, the Framework Directive contains specific guidelines in regard to chemical agents. These guidelines may be understood in terms of the relevance of the risk of such agents on occupational risk overall. Specifically, article 6.2 of the directive states as one of the general principals of preventive activity: replacing the dangerous by the non-dangerous or the less dangerous. Also, article 6.3.a: evaluate the risks to the safety and health of workers, inter alia in the choice of work equipment, the chemical substances or preparations used, and the fitting-out of workplaces. In order to carry out such assessment regarding chemical substances, Directive 98/24/EC [7] and Directive 2004/37/EC [6], on chemical agents and on carcinogens and mutagens at work, respectively, are essential.
Considering that these directives are part of the development of the Framework Directive, they share with it the general principles of risk management. As a result, the minimum provisions for the protection of workers contained in each directive must be managed under the said general management principles. Thus, a correspondence may be observed between the said principles and provisions, from the general to the specific.
Such correspondence makes it possible, in turn, to relate the sections of Annex III of Directive Seveso III with the specific provisions of each directive. This correspondence with the aforementioned directives may be seen in Table 5. The level of detail is lower than that found in Table 4, as in this case, the aim is to offer a global overview of the common thread described, from the general (Table 4) to the specific (Table 5).
Table 5. Correspondence between structures of risk management systems of Directive Seveso III, Directive 98/24/CE on chemical agents and Directive 2004/37/EC on carcinogens or mutagens.
Thus, comparing the results of Table 4 and Table 5 offers the following main learnings: (a) section (i) Organization and personnel of Directive Seveso III corresponds closely with the Framework Directive, while this correspondence is weaker with the individual directives analysed, limited mainly to training requirements; (b) section (ii) to (vi) of Directive Seveso III correspond closely with the individual directives. This correspondence is the result of going from the general in the Framework Directive to the specific on issues regarding chemical agents and carcinogens and mutagens pursuant to Directive 98/24/EC [7] and Directive 2004/37/EC [20], respectively; (c) in regard to section (vii) on Audit and review, which has no correspondence with the Framework Directive, reviewing the risk assessment whenever necessary is explicitly considered, such as when working conditions change, new scientific knowledge is achieved on the effects of chemical agents or limit values, etc.

4. Comparative Analysis between Management Systems Derived from the ISO 45001:2018 Standard and Directive Seveso III

Implementing an OSH management system conforming to the ISO 45001:2018 standard enables an organization to manage its OSH risks and improve its OSH performance [14]. According to this voluntary standard, an OSH management system can assist an organization to fulfil its legal and other requirements. The implementation and maintenance of an OSH management system, its effectiveness and its ability to achieve its intended outcomes are dependent on a number of key factors which can include the integration of the OSH management system into the organization’s business processes and compliance with its legal and other requirements.
As indicated by the ISO 45001:2018 standard, its adoption in a given organization, however, will not in itself guarantee prevention of work-related injury and ill health to workers, provision of safe and healthy workplaces and improvement of OSH performance [14]. So, in the context of this work, that is from the perspective of a risk management system, the adoption or implementation of the ISO 45001:2018 standard [14] may be understood as a tool that may assist an organisation in complying with the Framework Directive and Directive Seveso III.
As with the previous section, which carried out a comparative analysis between management systems derived from the Framework Directive and Directive Seveso III, this section contains a similar analysis, using the same criteria, comparing between management systems derived from the ISO 45001:2018 standard [14] and Directive Seveso III.
Hence, as Table 5 also shows, correspondence may be established between the structure of the ISO 45001:2018 standard [14] and the management system included in Annex III of Directive Seveso III. Consequently, the result obtained makes it possible to establish a similar correspondence between the said standard and the Framework Directive, since Directive Seveso III works as a common denominator.
The results from such analysis establish a strong correspondence with all sections from Annex III except with section (iii) Operational control, where aspects related to management and control of the risks associated with ageing equipment installed in the establishment and corrosion are not explicitly stated by the ISO 45001:2018 standard [14]. This is also true in regard to the Framework Directive, Directive 98/24/CE on chemical agents [7] and Directive 2004/37/EC on carcinogens or mutagens [20].
As a result of this correspondence, the ISO 45001:2018 standard [14] is linked closely, not only to Directive Seveso III but also to the Framework Directive and its individual directives, especially Directive 98/24/EC [7] and Directive 2004/37/EC [20], on chemical agents and carcinogens or mutagens at work, respectively.
On the other hand, the OSH management system approach defined by the ISO 45001:2018 standard [14] is founded on the concept of Plan-Do-Check-Act (PDCA). This standard indicates that it can be applied to a management system and to each of its individual elements, as follows:
  • Plan: determine and assess OSH risks, OSH opportunities and other risks and other opportunities, establish the OSH objectives and processes necessary to deliver results in accordance with the organization’s OSH policy;
  • Do: implement the processes as planned;
  • Check: monitor and measure activities and processes with regard to the OSH policy and OSH objectives, and report the results;
  • Act: take actions to continually improve OSH performance towards achieving the intended outcomes;
The ISO 45001:2018 standard incorporates the PDCA concept into a new framework [14]. This framework can be integrated with the framework defined by Seveso III, considering the results shown in Table 4. The result of such integration is shown in Figure 2.
Figure 2. Integration of the Plan-Do-Check-Act (PDCA) framework defined by the ISO 45001:2018 standard [14] with the management system derived from Directive Seveso III [8].

5. Analysis of Transitional Spaces Between the Risk Management of Hazardous Materials in Manufacturing Processes

An analysis is carried out below of the main transitional spaces that arise from the results obtained in the previous sections. Each of these transitional spaces may be understood as the intersection between the correspondences identified between the different sets analysed: that is, the legal context and management systems derived from Directive Seveso III, the Framework Directive and the ISO 45001:2018 standard [14].

5.1. Legal Context

As a result of the analysis carried out in the legal context section, Figure 3 shows the main correspondence observed between the directives studied; that is, between Directive Seveso III and the individual directives within the meaning of Article 16 (1) of the Framework Directive.
Figure 3. Main links formed between the individual directives (Framework Directive [6]) and Directive Seveso III [8] within the general structure of a manufacturing process.
To show these links summarily, the same thread has been followed that configures the structure of the legal context section. To this end, the basic outline of a general manufacturing process has been considered, involving chemical agents (Directive 98/24/EC [7] and Directive 2004/37/EC [20]). Thus, this manufacturing process may take place in one or more workplaces (Directive 89/654/EEC [15]) where, among other chemical risks, there may be the risk of explosion (Directive 99/92/EC [28]). Such workplaces may be considered as establishments with installations in the scope of implementation of Directive Seveso III, other types of establishments (not falling within Directive Seveso III) or other types of workplaces. In all cases, these workplaces will have installations and work equipment (Directive 2009/104/EC [16]) that will configure the corresponding manufacturing process.
Analysis of directives related to the safety and health of persons other than the individual directives within the meaning of Article 16 (1) of the Framework Directive, are not within the remit of this study. However, it should be pointed out that there may be connections to other regulations, such as the REACH Regulation [2] and CLP Regulation [3], or Directive 2006/42/EC on machinery [41]. These examples may be considered as fundamental regulations in the field of safety and health.
The main transitional spaces between these links, as shown in Figure 3, are describe below, considering in this regard the intersections between Directive Seveso III and the individual directives within the meaning of Article 16 (1) of the Framework Directive:
  • Activity involving chemical agents: Directive 98/24/EC on chemical agents [7] will be applicable to any work activity linked to a manufacturing process that involves the use of any of the dangerous substances collected in Directive Seveso III. Additionally, other individual directives may be applicable depending on the characteristics of the manufacturing process in each specific case, as well as the chemical agents used; for instance, Directive 2004/37/EC on carcinogens or mutagens at work [20], as shown for the substances collected in Table 3.
  • Workplaces: Directive 98/654/EEC on Workplaces [15] is applicable to any work activity linked to a manufacturing process integrated in an establishment, following Directive Seveso III. Additionally, other individual directives may also be applicable depending on the characteristics of the manufacturing process in each specific case, as well as the chemical agents used; for instance, Directive 99/92/EC on explosive atmospheres [28]. This could be the case, for instance, in the case of manufacturing processes that use any of the flammable substances collected in Table 3, such as: ethyleneimine (H225: very flammable liquid and vapours), Ethylene oxide (H220: extremely flammable gas) and propylene oxide (H224: extremely flammable liquid and vapours).
  • Installation: Directive 2009/104/EC on work equipment [16], as well as Directive 89/654/EEC on workplaces [15], will be applicable to any work activity linked to any manufacturing process that involves one or more installations pursuant to Directive Seveso III. In general, a manufacturing process will be configured by elements that fall within the definition of work equipment and workplace, which may completely or partially configure an installation pursuant to Directive Seveso III.

5.2. Management Systems

The four transitional spaces (TS) represented conceptually in Figure 4 are derived from the results obtained in the two comparative analyses carried out between risk management systems (the links shown in Table 4 and Table 5): that is, between Directive Seveso III and the Framework Directive, and between Directive Seveso III and the ISO 45001:2018 standard [14].
Figure 4. Transitional spaces between the following management systems: Directive Seveso III [8], Framework Directive [7] and ISO 45001:2018 standard [14].
Transitional space TS 1 is configured by the correspondence that exists between the structure of the Framework Directive and the management systems derived from Directive Seveso III. Similarly, TS 2 is configured by the correspondence that exists between the structure of the ISO 45001:2018 standard and the management system derived from Directive Seveso III.
Transitional space TS 3 may be considered a ‘natural space’ between the Framework Directive and the ISO 45001:2018 standard [14] since the goal of both systems is to manage safety and health at work. However, studying this transitional space falls outside the aim of this study as such a study would form part of an analysis process regarding the implementation of the ISO 45001:2018 standard [14] by an organisation.
In any case, given that the result of implementing the ISO 45001:2018 standard [14] may be understood as a tool that can help an organisation to meet such legal requirements as complying with the Framework Directive and Directive Seveso III, the three systems may share an intersectional space, giving rise to transitional space TS 4.
Additionally, given that the provisions of Directive 98/24/EC on chemical agents [7] and Directive 2004/37/EC on carcinogens or mutagens at work [20] are in line with the general management guidelines set by the Framework Directive, the correspondence between these directives and Annex III of Directive Seveso III has been studied and the results are collected in Table 5.
The said results may be considered as a specific correspondence transferred from transitional space TS 1 to transitional space TS 4 when the intersection of the three systems takes place. Thus, TS 4 may be considered to include, at least, the provisions of Directive 98/24/EC [7] and Directive 2004/37/EC [20]. In other words, transitional space TS 4 may be considered to be a specific transitional space resulting from the intersection of three general transitional spaces.
Even if this specific transitional space has been studied in regard to the aforementioned directives, it should be pointed out that other directives, from those considered in Table 1, may also be of interest.

6. Discussion

There are signs of a revitalizing interest in foundational issues in risk assessment and management, which is welcome and necessary for meeting the challenges currently faced by the field of risk. These are related to societal problems and complex technological and emerging risks [42] which can exist in manufacturing processes alongside traditional risks [43].
The second European Survey of Enterprises on New and Emerging Risks reveals that dangerous substances (or biological substances) are most prevalent in the European Union in certain sectors such as manufacturing (51.7%) [44]. As a result, new challenges for the management of dangerous substances in the workplace are emerging, for example, in the area of green jobs (bio-energy production, new types of energy storage) and in relation to the use of innovative materials (e.g. nanomaterials) and technologies with currently unknown health risks (such as 3D printing) and substances recognised as endocrine disrupters [45].
In this context, Brocal et al. [46] considered that the relationship between the prevention of occupational accidents and major accidents is especially important. Based on this integrative perspective, Zio [47] points out to the realization that, to manage risk in a systematic and effective way, it is necessary to consider all phases of potential accident scenarios together.
There is a general research focus on dynamic risk assessment and management rather that static or traditional risk assessment [42], which can consider the dynamic evolution of conditions, both internal and external to the system, affecting risk assessment [48]. The effectiveness in the application of a dynamic risk management framework in collecting and considering evidence of emerging risks relies on the continuous development of dynamic techniques for hazard identification and risk assessment, joined with a proper safety culture [49].
However, this study does not distinguish between the risk management of both types of risks; that is, between traditional risk and emerging risk. This is due to the general characteristics of the legal and standardised context in which this study has been carried out, towards meeting the main objective set out.
In any case, this objective may be extended in future research in the direction of emerging risk management. In this regard, the CWA 16649:2013 standard on managing emerging technology-related risks may be considered to be a reference management system [50]. Such a direction may be justified, among others, by considering the data in Figure 1, which shows that the number of chemical substances used in manufacturing processes has increased in the past few years. Furthermore, by considering the hypothesis that, in general, such substances are a source of risk, implementing the TICHNER (Technique to Identify and CHaracterize NERs) technique developed by Brocal et al. [51], it could be stated that the situation described in manufacturing processes could constitute an emerging risk.

6.1. Major Accident and Occupational Accident

In regard to the definitions for ‘accident’ considered in this study, ‘major accident’ is defined by Directive Seveso III, while ‘occupational accident’ is not defined by the directives studied. Therefore, other sources are required. Besserman and Mentzer [12] consider that each country defines their statistics differently including different definitions for lost time incidents, non-fatal injuries, and what constitutes the manufacturing/chemical industry, among others. Furthermore, such authors indicate that there is minimal reporting of true process safety metrics resulting from the loss of containment of a hazardous substance.
In any case, a major accident can also be considered to be an occupational accident if harm to workers exists. Inversely, an occupational accident can also be a major accident when it meets the requirements set out in Directive Seveso III. The causality relationship between both types of accident has not been studied here, although its interest in the sphere of safety is evident. In the 1970s, the effect of human actions and organizational factors on accident occurrence was recognized, but it took until the mid- 1980s before management became aware that they were key to achieving a good level of both occupational and process safety [52]. The incorporation of Bayesian networks into risk assessment may be another interesting focus for both research and industrial purposes, because it allows a systemic approach considering human error and management influences [49].

6.2. Links and Transitional Spaces

The main correspondence between risk management in both types of accidents is the presence in the manufacturing process of one or more of the hazardous substances included in Annex I of Directive Seveso III, for which directives derived from the Framework Directive are also applicable. The said directives may be understood as the deployment of this correspondence into further links that are more specific, giving rise to two types of transitional spaces: functional transitional spaces and regulatory transitional spaces.
Functional transitional spaces (that is, activities involving chemical agents, workplaces and installations) are interconnected as briefly outlined in Figure 3. Such interconnection must be understood as a basic outline that can be extended in different directions in the field of risk management as, for instance: the safety change management studied by Gerbec [53]; management of exposure to nanomaterials studied by Hunt et al. [54]; machine safety, which can be generally defined through Directive 2006/42/EC and the ISO 12100: 2010 and ISO/TR 14121-1: 2012 standards on safety of machinery [55,56]
As regarding regulatory transitional spaces, they are defined by the intersections between the risks management systems studied through the Framework Directive, Directive Seveso III and the ISO 45001:2018 standard.
The links shown in Table 4 between management systems derived from the Framework Directive and Directive Seveso III, have been classified as: four are strong (Annex III sections (i), (ii), (iv) and (v)), two are weak (Annex III sections: ((iii) and (vi)), and one is non-existent (Annex III section (vii)).
This result is coherent under the perspective of the Framework Directive, which compiles a set of general guidelines that are further developed by specific directives, as shown in the results in Table 5. Therefore, the set established by the Framework Directive and individual directives completes and strengthens the seven links above, configuring the transitional space TS 1.
As regards the correspondence between management systems derived from the ISO 45001:2018 standard and Directive Seveso III, shown also in Table 4, 6 of these links have been classified as strong and one as relatively strong (sections Annex III: (iii)), configuring transitional space TS 2.
These results are also coherent with the aim of an OSH management system as defined by the ISO 45001:2018 standard. Moreover, these results make it possible to draw up a coherent correspondence between the structures of the ISO 45001:2018 standard [14] and the Framework Directive, configuring transitional space TS 3.
As regards TS 4, given that it may be considered to be a specific transitional space resulting from the intersection of three general transitional spaces, it is key to defining and channelling the transitions between systems by means of the corresponding individual directives in each case, including at least Directive 98/24/EC on chemical agents [7]. This consideration is still valid when the intersection occurs between two systems, and the linking and transitional role played by the individual directives is equally important.
The risk assessment techniques are a key structuring element between the functional and regulatory transition spaces, as shown in the results of Table 4 and, especially, of Table 5. However, according to Brocal et al. [9] it is necessary to deepen through future research on the analysis of differentiating and applicative criteria between the techniques used in the field of safety occupational and safety linked to major accidents.
These links and transitional spaces may facilitate system integration. In this regard, Li and Guldenmund [13] point out that according to the literature, an integrated management system is more advanced than independent safety systems, as safety is just one of the comprehensive organization management objectives.
In the process of integrating systems, besides the existence of transitional spaces, non-traditional spaces also exist as a result of the specific aspects of each system that have no direct correlation with the other systems. These non-transitional spaces have not been studied here, yet may be equally important in any integration process, since they define the frontiers necessary to avoid unwanted interference with the transitional spaces.

7. Conclusions

The main objective of this study has been met through identifying and analysing the links and transitional spaces between the risk management of occupational accidents and major accidents that involve hazardous substances in manufacturing processes. To this end, the risk management systems derived from Directive Seveso III, the Framework Directive and the ISO 45001:2018 standard [14] have been analysed, obtaining three main results.
The first result of this analysis, the main link identified between the risk management of both types of accidents, is the presence in a manufacturing process of any of the hazardous substances included in Annex I of Directive Seveso III, for which the directives derived from the Framework Directive are also applicable, and the principles and guidelines of the ISO 45001:2018 standard are applicable on a voluntary basis [14].
As a second result, the intersection of Directive Seveso III, the Framework Directive and the ISO 45001:2018 standard, configures three general transitional spaces (TS 1, TS 2 and TS 3).
In turn, and as a third result, the intersection of these three general transitional spaces configures a specific transitional space (TS 4), which is key to defining and channelling the transition between systems by means of the individual directives that may correspond in each case, which will, at least, include the directive on chemical substances. This will enable integration processes between the systems considered.
The above results are limited from a regulatory and technical perspective. In regard to the regulatory perspective, the context is limited to the EU, as well as Directive Seveso III, the Framework Directive and any individual directives that further develop it. Other directives and regulations that are especially relevant in the sphere of safety, as for instance the REACH Regulation [2] and CLP Regulation [3], are open to further analysis to enable their integration into the management systems. From a technical perspective, no distinction has been made between traditional risk management and emerging risk management. Similarly, no distinction has been made between static and dynamic approaches.
The results and limitations stated above may point towards future paths of research, from which models to integrate the risk management of occupational accidents and major accidents may be developed based on real experiences and data.
By way of final conclusion, the identification and analysis of the links and transitional spaces carried out by this study aspire to being a starting point that will inspire other researchers to continue and further develop this study with the end goal of efficiently integrating risk management systems related to accidents derived from dangerous substances in manufacturing processes.

Author Contributions

Conceptualization, F.B., C.G. and M.A.S.; Investigation, F.B., C.G. and M.A.S; Methodology, F.B., C.G.; Supervision, F.B, C.G., M.A.S., G.R. and V.C.; Writing—original draft, F.B., C.G. and M.A.S.; Writing—review and editing, F.B, C.G., M.A.S., G.R. and V.C.

Funding

This research was funded by the Ministry of Economy and Competitiveness of Spain, title: ‘Analysis and Assessment of technological requirements for the design of a New Emerging Risks standardized management SYStem (A2NERSYS)’ with reference DPI2016-79824-R.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. European Commission. Growth–Internal Market, Industry, Entrepreneurship and SMEs; European Commission: Brussels, Belgium, 2018; Available online: https://ec.europa.eu/growth/sectors/chemicals_en (accessed on 24 August 2018).
  2. European Union. Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 Concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), Establishing a European Chemicals Agency, Amending Directive 1999/45/EC and Repealing Council Regulation (EEC) No 793/93 and Commission Regulation (EC) No 1488/94 as well as Council Directive 76/769/EEC and Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC; Official Journal of the European Union: Brussels, Belgium, 2006. [Google Scholar]
  3. European Union. Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on Classification, Labelling and Packaging of Substances and Mixtures, Amending and Repealing Directives 67/548/EEC and 1999/45/EC, and Amending Regulation (EC) No 1907/2006; Official Journal of the European Union: Brussels, Belgium, 2008. [Google Scholar]
  4. European Chemical Agency (ECHA). Classification and Labelling Inventory Database. Available online: https://echa.europa.eu/information-on-chemicals/cl-inventory-database (accessed on 24 August 2018).
  5. European Chemical Agency (ECHA). Registered Substances Database. Available online: https://echa.europa.eu/information-on-chemicals/registered-substances (accessed on 24 August 2018).
  6. European Communities. Directive 89/391/EEC of 12 June 1989 on the Introduction of Measures to Encourage Improvements in the Safety and Health of Workers at Work—‘Framework Directive’ Directive 89/654/EEC—Workplace Requirements of 30 November 1989 Concerning the Minimum Safety and Health Requirements for the Workplace (First Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Communities: Brussels, Belgium, 1989. [Google Scholar]
  7. European Union. Directive 98/24/EC–Risks Related to Chemical Agents at Work of 7 April 1998 on the Protection of the Health and Safety of Workers from the Risks Related to Chemical Agents at Work (Fourteenth Individual Directive within the Meaning of Article 16(1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1998. [Google Scholar]
  8. European Union. Directive 2012/18/EU of the European Parliament and of the Council of 4 July 2012 on the Control of Major-Accident Hazards Involving Dangerous Substances, Amending and Subsequently Repealing Council Directive 96/82/EC Text with EEA Relevance; Official Journal of the European Union: Brussels, Belgium, 2012. [Google Scholar]
  9. Brocal, F.; Sebastián, M.A.; González, C.; Reniers, G.; Paltrinieri, N. Standardized risk assessment techniques: A review in the framework of occupational safety. In Safety and Reliability—Safe Societies in a Changing World, Proceedings of the 28 TH International European Safety and Reliability Conference (ESREL 2018), Trondheim, Norway, 17–21 June 2018; Haugen, S., Barros, A., Gulijk, C.V., Kongsvik, T., Vinnem, J., Eds.; CRC Press: London, UK, 2018. [Google Scholar]
  10. ScienceDirect Databases. Available online: https://www.sciencedirect.com/search/advanced (accessed on 6 August 2018).
  11. Rasmussen, K.; Sokull-Klüttgen, B.; Yu, I.J.; Kanno, J.; Hirose, A.; Gwinn, M.R. Chapter 7–Regulation and Legislation. In Adverse Effects of Engineered Nanomaterials, 2nd ed.; Fadeel, B., Pietroiusti, A., Shvedova, A.A., Eds.; Academic Press: Cambridge, MA, USA, 2017; pp. 159–188. [Google Scholar] [CrossRef] [Scilit]
  12. Besserman, J.; Mentzer, R.A. Review of global process safety regulations: United States, European Union, United Kingdom, China, India. J. Loss Prevent Proc. Ind. 2017, 50, 165–183. [Google Scholar] [CrossRef] [Scilit]
  13. Li, Y.; Guldenmund, F.W. Safety management systems: A broad overview of the literature. Saf. Sci. 2018, 103, 94–123. [Google Scholar] [CrossRef] [Scilit]
  14. ISO 45001–Occupational Health and Safety Management Systems. Requirements with Guidance for Use; International Organization for Standardization (ISO): Geneva, Switzerland, 2018.
  15. European Union. Directive 89/654/EEC of 30 November 1989 Concerning the Minimum Safety and Health Requirements for the Workplace (First Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1989. [Google Scholar]
  16. European Union. Directive 2009/104/EC–Use of Work Equipment of 16 September 2009 Concerning the Minimum Safety and Health Requirements for the Use of Work Equipment by Workers at Work (Second Individual Directive within the Meaning of Article 16(1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 2009. [Google Scholar]
  17. European Union. Directive 89/656/EEC–Use of Personal Protective Equipment of 30 November 1989 on the Minimum Health and Safety Requirements for the Use by Workers of Personal Protective Equipment at the Workplace (Third Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1989. [Google Scholar]
  18. European Union. Directive 90/269/EEC–Manual Handling of Loads of 29 May 1990 on the Minimum Health and Safety Requirements for the Manual Handling of Loads where There Is a Risk Particularly of Back Injury to Workers (Fourth Individual Directive within the meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1990. [Google Scholar]
  19. European Union. Directive 90/270/EEC–Display Screen Equipment of 29 May 1990 on the Minimum Safety and Health Requirements for Work with Display Screen Equipment (Fifth Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1990. [Google Scholar]
  20. European Union. Directive 2004/37/EC–Carcinogens or Mutagens at Work of 29 April 2004 on the Protection of Workers from the Risks Related to Exposure to Carcinogens or Mutagens at Work (Sixth individual Directive within the meaning of Article 16(1) Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 2004. [Google Scholar]
  21. European Union. Directive 2000/54/EC–Biological Agents at Work of the European Parliament and of the Council of 18 September 2000 on the Protection of Workers from Risks Related to Exposure to Biological Agents at Work (Seventh Individual Directive within the Meaning of Article 16(1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 2000. [Google Scholar]
  22. European Union. Directive 92/57/EEC–Temporary or Mobile Construction Sites of 24 June 1992 on the Implementation of Minimum Safety and Health Requirements at Temporary or Mobile Construction Sites (Eighth Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1992. [Google Scholar]
  23. European Union. Directive 92/58/EEC–Safety and/or Health Signs of 24 June 1992 on the Minimum Requirements for the Provision of Safety and/or Health Signs at Work (Ninth Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1992. [Google Scholar]
  24. European Union. Directive 92/85/EEC–Pregnant Workers of 19 October 1992 on the Introduction of Measures to Encourage Improvements in the Safety and Health at Work of Pregnant Workers and Workers who Have Recently Given Birth or Are Breastfeeding (Tenth Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1992. [Google Scholar]
  25. European Union. Directive 92/91/EEC–Mineral-Extracting Industries–Drilling of 3 November 1992 Concerning the Minimum Requirements for Improving the Safety and Health Protection of Workers in the Mineral-Extracting Industries through Drilling (Eleventh Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1992. [Google Scholar]
  26. European Union. Directive 92/104/EEC–Mineral-Extracting Industries of 3 December 1992 on the Minimum Requirements for Improving the Safety and Health Protection of Workers in Surface and Underground Mineral-Extracting Industries (Twelfth Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1992. [Google Scholar]
  27. European Union. Directive 93/103/EC–Work on Board Fishing Vessels of 23 November 1993 Concerning the Minimum Safety and Health Requirements for Work on Board Fishing Vessels (Thirteenth Individual Directive within the Meaning of Article 16 (1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1993. [Google Scholar]
  28. European Union. Directive 99/92/EC–Risks from Explosive Atmospheres of 16 December 1999 on the Minimum Requirements for Improving the Safety and HEALTH protection of Workers Potentially at Risk from Explosive atmospheres (15th individual Directive within the meaning of Article 16(1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 1999. [Google Scholar]
  29. European Union. Directive 2002/44/EC–Vibration of 25 June 2002 on the Minimum Health and Safety Requirements Regarding the Exposure of Workers to the Risks Arising from Physical Agents (Vibration) (Sixteenth Individual Directive within the Meaning of Article 16(1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 2002. [Google Scholar]
  30. European Union. Directive 2003/10/EC–Noise of 6 February 2003 on the Minimum Health and Safety Requirements Regarding the Exposure of Workers to the Risks Arising from Physical Agents (Noise) (Seventeenth Individual Directive within the Meaning of Article 16(1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 2003. [Google Scholar]
  31. European Union. Directive 2004/40/EC of the European Parliament and of the Council of 29 April 2004 on the Minimum Health and Safety Requirements Regarding the Exposure of Workers to the Risks Arising from Physical Agents (Electromagnetic Fields) (18th Individual Directive within the Meaning of Article 16(1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 2004. [Google Scholar]
  32. European Union. Directive 2006/25/EC–Artificial Optical Radiation of 5 April 2006 on the Minimum Health and Safety Requirements Regarding the Exposure of the Workers to Risks Arising from Physical Agents (Artificial Optical Radiation, 19th Individual Directive within the Meaning of Article 16(1) of Directive 89/391/EEC); Official Journal of the European Union: Brussels, Belgium, 2006. [Google Scholar]
  33. European Union. Directive 2013/35/EU–Electromagnetic Fields of 26 June 2013 on the Minimum Health and Safety Requirements Regarding the Exposure of Workers to the Risks Arising from Physical Agents (Electromagnetic Fields) (20th Individual Directive within the Meaning of Article 16(1) of Directive 89/391/EEC) and Repealing Directive 2004/40/EC; Official Journal of the European Union: Brussels, Belgium, 2013. [Google Scholar]
  34. Eurostat. Statistics Explained. Accidents at Work Statistics. Available online: https://ec.europa.eu/eurostat/statistics-explained/index.php/Accidents_at_work_statistics (accessed on 28 June 2018).
  35. Sebastián, M.A.; Brocal, F.M.A. Analysis of Open Resources from INSHT for Application to University Teaching of Industrial Safety Technology. Procedia Eng. 2015, 132, 228–235. [Google Scholar] [CrossRef] [Scilit]
  36. INSHT (National Institute for Safety and Health at Work). INFOCARQUIM (Information about Carcinogens Chemicals) Database. Available online: http://infocarquim.inssbt.es/Forms/About.aspx (accessed on 6 August 2018).
  37. Límites de exposición profesional para agentes químicos en España (Occupational Exposure Limits for Chemical Agents in Spain); INSSBT (National Institute for Safety, Health and Welfare at Work): Madrid, Spain, 2018.
  38. Guía Técnica para la evaluación y prevención de los riesgos relativos a la utilización de equipos de trabajo (Technical Guide for the assessment and prevention of risks related to the use of work equipment) (Royal Decree 1215/1997—BOE nº 188), 2nd ed.; INSHT (National Institute for Safety and Health at Work): Madrid, Spain, 2011.
  39. Spain. Law 31/1995 of 8 November on Prevention of Occupational Risks. (BOE, No. 269, 10.11.1995). Available online: https://www.boe.es/buscar/pdf/1995/BOE-A-1995-24292-consolidado.pdf (accessed on 9 October 2018).
  40. Spain. Royal Decree 39/1997, January 17, adopting Regulations on Prevention Services. (BOE, No. 27, 31.01.1997). Available online: https://www.boe.es/buscar/pdf/1997/BOE-A-1997-1853-consolidado.pdf (accessed on 9 October 2018).
  41. European Union. Directive 2006/42/EC of the European Parliament and of the Council of 17 May 2006 on machinery, and Amending Directive 95/16/EC (recast); Official Journal of the European Union: Brussels, Belgium, 2006. [Google Scholar]
  42. Aven, T. Risk Assessment and Risk management: Review of Recent Advances on Their foundation. Eur. J. Oper. Res. 2016, 253, 1–13. [Google Scholar] [CrossRef] [Scilit]
  43. Brocal, F.; Sebastián, M.A.; González, C. Theoretical framework for the new and emerging occupational risk modeling and its monitoring through technology lifecycle of industrial processes. Saf. Sci. 2017, 99, 178–186. [Google Scholar] [CrossRef] [Scilit]
  44. EU-OSHA (European Agency for Safety and Health at Work) (Jul. 24, 2018). 2014. European Survey of Enterprises on New and Emerging Risks (ESENER-2) [Interactive Survey]. EU-OSHA, Bilbao. Available online: https://osha.europa.eu/en/surveys-and-statistics-osh/esener/2014 (accessed on 6 August 2018).
  45. Helathy Workplaces. Manage Dangerous substances. Campaign Guide; EU-OSHA (European Agency for Safety and Health at Work): Bilbao, Spain, 2018. [Google Scholar]
  46. Brocal, F.; Sebastián, M.A.; González, C. Chapter 2: Advanced manufacturing processes and technologies. In Management of Emerging Public Health Issues and Risks. Multidisciplinary Approaches to the Changing Environment; Benoit, R., Weiss, K., Thireau, V., Eds.; Academic Press (Elsevier): Cambridge, MA, USA, 2018; ISBN 9780128132906. in press. [Google Scholar]
  47. Zio, E. The future of risk assessment. Reliab. Eng. Syst. Safe. 2018, 177, 176–190. [Google Scholar] [CrossRef] [Scilit]
  48. Paltrinieri, N.; Scarponi, G. Addressing dynamic risk in the petroleum industry by means of innovative analysis solutions. Chem. Eng. Trans. 2014, 36, 451–456. [Google Scholar]
  49. Villa, V.; Paltrinieri, N.; Khan, F.; Cozzani, V. Towards dynamic risk analysis: A review of the risk assessment approach and its limitations in the chemical process industry. Saf. Sci. 2016, 89, 77–93. [Google Scholar] [CrossRef] [Scilit]
  50. Managing Emerging Technology-related Risks. CWA 16649:2013; European Committee for Standardization (CEN): Brussels, Belgium, 2013.
  51. Brocal, F.; González, C.; Sebastián, M.A. Technique to identify and characterize new and emerging risks: A new tool for application in manufacturing processes. Saf. Sci. 2018, 109, 144–156. [Google Scholar] [CrossRef] [Scilit]
  52. Jain, P.; Pasman, H.J.; Waldram, S.P.; Rogers, W.J.; Mannan, M.S. Did we learn about risk control since Seveso? Yes, we surely did, but is it enough? An historical brief and problem analysis. J. Loss Prev. Process Ind. 2017, 49, 5–17. [Google Scholar] [CrossRef] [Scilit]
  53. Gerbec, M. Safety change management—A new method for integrated management of organizational and technical changes. Saf. Sci. 2017, 100, 225–234. [Google Scholar] [CrossRef] [Scilit]
  54. Hunt, G.; Lynch, I.; Cassee, F.; Handy, R.D.; Fernandes, T.F.; Berges, M.; Kuhlbusch, T.A.J.; Dusinska, M.; Riediker, M. Towards a Consensus View on Understanding Nanomaterials Hazards and Managing Exposure: Knowledge Gaps and Recommendations. Materials 2013, 6, 1090–1117. [Google Scholar] [CrossRef] [Scilit] [PubMed]
  55. ISO 12100 Preview Safety of Machinery–General Principles for Design–Risk Assessment and Risk Reduction; International Organization for Standardization (ISO): Geneva, Switzerland, 2010.
  56. ISO/TR 14121-2. Preview Safety of Machinery–Risk Assessment–Part 2: Practical Guidance and Examples of Methods; International Organization for Standardization (ISO): Geneva, Switzerland, 2012.

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