ENVIRONMENTAL RISK MANAGEMENT AUTHORITY DECISION 16 August 2007 Application code: HSR05111 Application Type To import or manufacture any hazardous substance under Section 28A(2)(b) of the Hazardous Substances and New Organisms Act 1996 (“the Act”) Applicant: Donaghys Industries Ltd Purpose of the Application FoliActive - to manufacture and release this viticulture foliar spray for vine condition and control of common fungal disease such as Powdery Mildew and Botrytis (low hazard) Date application received: 13 April 2007 Consideration Date 16 August 2007 Considered by Rob Forlong (Chief Executive, ERMA New Zealand) 1 Summary of decision 1.1 The application to import or manufacture FoliActive for release is approved with the controls as set out in Appendix 1. This approval has been given in accordance with the relevant provisions of the Act, the relevant HSNO Regulations, and the HSNO (Methodology) Order 1998 (“the Methodology”), based on FoliActive being formulated so that the substance has one or more hazardous properties and each hazardous property has the least degree of hazard for that property. 1.2 The substance has been given the following unique identifier for the ERMA New Zealand Hazardous Substances Register: FoliActive 2 Legislative criteria for the application 2.1 The application was lodged pursuant to section 28. The decision was determined in accordance with section 28A(2)(b), taking into account the requirements of that section and matters specified under Part II of the Act. Unless otherwise stated, references to section numbers in this decision refer to sections of the Act. 2.2 Consideration of the application followed the relevant provisions of the Methodology. Unless otherwise stated, references to clauses in this decision refer to clauses of the Methodology. 3 Application process 3.1 The purpose of this application is to gain approval to import or manufacture FoliActive as viticulture foliar spray for vine condition and control of common fungal disease such as Powdery Mildew and Botrytis. 3.2 3.3 The application was formally received on 13 April 2007. 3.2.1 The application timeframe was extended by 48 working days as the result of a request under section 58 for further time to process the volume of information provided with the application. 3.2.2 The application timeframe was again extended by 30 working days under section 58 to process further information. The Agricultural Compounds & Veterinary Medicines Group (ACVMG) of the New Zealand Food Safety Authority (NZFSA), the Ministry of Health, the Department of Labour Workplace Group and the Department of Conservation were advised of the application (clause 2(2)(e)). 3.3.1 3.4 No responses were received. Evaluation of the application was undertaken by the ERMA New Zealand project team which comprised the following staff members: Margaret Keane Sekove Tinalevu Peter Dawson 3.5 Advisor (Hazardous Substances) Advisor (Hazardous Substances) Principal Scientist (Hazardous Substances). The application was considered by the Chief Executive of ERMA New Zealand as provided for by a delegation from the Environmental Risk Management Authority (the Authority) under section 19(2)(d). 4 Consideration Sequence of the consideration 4.1 Donaghys Industries Ltd seeks approval, under section 28, to import or manufacture FoliActive for release in New Zealand. 4.2 An application can be assessed by rapid assessment procedures, under section 28A(2)(b), if it can be shown that FoliActive has one or more hazardous properties and each hazardous property has the least degree of hazard for that property. 4.3 The approach adopted when considering this application was: to review the information provided; to identify the composition and hazardous properties of the proposed substance, FoliActive; to determine whether FoliActive has one or more hazardous properties and each hazardous property has the least degree of hazard for that property. 4.4 And then: to consider whether there are any effects that mean FoliActive should not be approved under section 28A; and to consider whether the controls that apply under the Act will prevent or manage the adverse effects of FoliActive. Environmental Risk Management Authority Decision: Application HSR05111 Page 2 of 16 Information review 4.5 The project team has reviewed the information supplied by Donaghys Industries Ltd, and considers that the information constitutes an adequate and appropriate basis for assessing the application (clause 8). They also consider that there are no significant uncertainties (ie sufficient to influence decision making) in the scientific and technical information relating to the risks of FoliActive (clauses 29 and 30). Identification and use of FoliActive 4.6 FoliActive will be manufactured in New Zealand, made to order to lessen the risk of overproduction and decrease the likelihood of wastage. The product is to be stored on site until its dispatch via courier to various horticultural merchants and vineyards in New Zealand. 4.7 FoliActive is a water-based product intended for use in vineyards as part of a normal spray calendar for fungal pathogens and as a foliar fertiliser giving vines a low residue boost throughout the growth cycle. The active ingredient is a bacteria naturally occurring in the environment. Hazardous properties of FoliActive 4.8 The project team has determined the hazard profile of FoliActive based on the information provided by the applicant and other available information. The hazard classifications for FoliActive are set out in Table 4.1. Table 4.1: Hazard classifications Hazardous Property Eye irritancy Biocidal use Classification 6.4A 9.1D Meeting the criteria for rapid assessment under section 28A(2)(b) 4.9 Based on the information presented in Table 4.1 the project team considers that the criteria for rapid assessment under section 28A(2)(b) have been met in that FoliActive has been classified as an eye irritant (6.4A) and a biocide (9.1D) and both of these classifications are the least degree of hazard for that property. 4.10 The project team considers that there are no other matters which would prevent this application for FoliActive from being rapidly assessed. 5 Controls and Risk Assessment Default controls 5.1 Based on the hazard classifications determined for FoliActive, a set of associated default controls has been identified by the project team as being applicable to the substance. These default controls, expressed as control codes1, are listed in Table 5.1. 1 Control codes are those assigned by ERMA NZ to enable easy cross reference with the regulations. A detailed list of these codes is contained in the ERMA New Zealand User Guide to the Controls Regulations. Environmental Risk Management Authority Decision: Application HSR05111 Page 3 of 16 5.2 Section 77 provides for the variation of default controls. These are considered in Paragraph 5.11 below. 5.3 Additional controls under section 77A are available to manage the risks associated with FoliActive, which are not addressed by the default controls. These are considered in Paragraph 5.9 below. 5.4 The following controls are not considered relevant to FoliActive and have therefore not been listed as default controls: 5.4.1 Control T1 relates to limiting exposure to toxic substances through the setting of Tolerable Exposure Limits (TELs). The project team notes that regulation 111 requires an acceptable daily exposure value or RfD value to be set for class 6 substances. However, given that the class 6 hazard classification conferred on FoliActive is 6.4A (eye irritancy), which is not considered to be an ‘appreciable toxic effect’, the project team considers that this control does not apply to FoliActive under clause 11(1)(c)1 and has therefore not been listed as a default control for FoliActive. 5.4.2 Control T2 relates to the requirement to set Workplace Exposure Standards (WESs). The project team notes that the adverse effect of FoliActive on humans is not produced by the inhalation or dermal exposure routes and notes, furthermore, that the toxicological data is not sufficient to enable a WES to be set. The project team therefore considers that this control does not apply to FoliActive under clauses 29(1)(b)1 and (c)1 and therefore has not been listed as a default control for FoliActive. Table 5.1: List of default controls for FoliActive. Toxicity Controls T4 Requirements for equipment used to handle substances T7 Restrictions on the carriage of toxic or corrosive substances on passenger service vehicles Ecotoxicity Controls E1 Limiting exposure to ecotoxic substances through the setting of EELs E2 Restrictions on use of substances in application areas E6 Requirements for equipment used to handle substances Identification Controls I1 Identification requirements, duties of persons in charge, accessibility, comprehensibility, clarity and durability I9 Secondary identifiers for all hazardous substances I11 Secondary identifiers for ecotoxic substances I16 Secondary identifiers for toxic substances I19 Additional information requirements, including situations where substances are in multiple packaging I21 General documentation requirements I28 Specific documentation requirements for toxic substances I29 Signage requirements Packaging Controls P1 General packaging requirements P3 Criteria that allow substances to be packaged to a standard not meeting Packing 1 Hazardous Substances (Classes 6, 8, and 9 Controls) Regulations 2001 Environmental Risk Management Authority Decision: Application HSR05111 Page 4 of 16 Group I, II or III criteria P13 Packaging requirements for toxic substances PS4 Packaging requirements as specified in Schedule 4 Disposal Controls D4 Disposal requirements for toxic and corrosive substances D5 Disposal requirements for ecotoxic substances D6 Disposal requirements for packages D7 Information requirements for manufacturers, importers and suppliers, and persons in charge D8 Documentation requirements for manufacturers, importers and suppliers, and persons in charge Emergency Management Controls EM1 Level 1 information requirements for suppliers and persons in charge EM6 Information requirements for toxic substances EM7 Information requirements for ecotoxic substances EM8 Level 2 information requirements for suppliers and persons in charge EM11 Level 3 emergency management requirements: duties of person in charge, emergency response plans EM12 Level 3 emergency management requirements: secondary containment EM13 Level 3 emergency management requirements: signage Assessment of the adverse effects 5.5 The project team has carried out a qualitative risk assessment to assess the adverse effects to human health and the environment (refer Appendix 2 for qualitative descriptors of risk). Assessment of adverse effects to human health 5.6 With respect to human health hazards, FoliActive is classified as an eye irritant (6.4A). The project team considers the risks to human health arising from the irritancy hazard presented by FoliActive to be negligible. This assessment is based on the following considerations. 5.6.1 The project team considers it is highly improbable, given adherence to HSNO controls (e.g. packaging, identification, emergency management and disposal) and the Health and Safety in Employment Act 1992, that exposure to FoliActive at any stage of its lifecycle will result in adverse effects on people. 5.6.2 The project team considers that if exposure were to occur, the magnitude of any adverse effect will be minimal as the effect would be limited to the exposed individuals and be of a relatively short term and mild in nature. Assessment of adverse environmental effects 5.7 FoliActive is also classified as a biocide (9.1D). The project team notes that the 9.1D biocidal classification assigned to FoliActive was on the basis of its ability to suppress fungal pathogens. The project team also notes that the active ingredient is a naturally occurring bacterium in soil and therefore considers it not necessary to conduct a quantitative environmental exposure assessment to estimate the level of risk resulting from the intended use of FoliActive, as it is unlikely that the use of the product will pose a high acute aquatic risk. Environmental Risk Management Authority Decision: Application HSR05111 Page 5 of 16 5.8 A qualitative risk assessment was not carried out by the project team given that the 9.1D hazard classification was conferred on FoliActive on the basis of its biocidal activity against its intended target pest and not based on any adverse effect to the environment. Additional controls under section 77A 5.9 5.10 Under section 77A, the Authority may impose as controls any obligations and restrictions that the Authority thinks fit. Before imposing a control under this section, the Authority must be satisfied that, against any other specified controls applying to Unite and Tenet: (a) the proposed control is more effective in terms of its effect on the management, use and risks of hazardous substances; or (b) the proposed control is more cost-effective in terms of its effect on the management, use and risks of hazardous substances; or (c) the proposed control is more likely to achieve its purpose. The following additional controls have been proposed for FoliActive by the project team: 5.10.1 The project team notes that, unless specifically allowed for, pesticides should not be applied into or onto water, where water means water in all its physical forms, whether flowing or not, and whether over or under ground, but does not include water in any form while in a pipe, tank or cistern. As the default controls do not prohibit such use, the project team considers that the following control should be applied to FoliActive as being more effective in terms of its effect on the use of the substance: FoliActive shall not be applied directly onto or into water 5.10.2 The project team notes that the default controls do not address the risks associated with stationary container systems. Accordingly, the project team considers that the application of a control addressing these risks will be more effective than the specified (default) controls in terms of their effect on the management, use and risks of the substance. Such controls were applied to pesticides on transfer to the HSNO regime. The project team considers that this control is similarly appropriate for the management of the risks associated with FoliActive and proposes that the following controls should be applied to the substance: The controls relating to stationary container systems, as set out in Schedule 8 of the Hazardous Substances (Dangerous Goods and Scheduled Toxic Substances) Transfer Notice 2004 (Supplement to the New Zealand Gazette, 26 March 2004, No. 35, page 767), as amended, shall apply to this substance, notwithstanding clause 1(1) of that schedule Variation of controls under section 77 5.11 Under section 77, the default controls triggered for the substance may be varied. Under section 77(3), controls may be substituted or added, under section 77(4), controls may be substituted or deleted; and under section 77(5), where a substance triggers more than one hazard classification, controls may be combined. 5.12 The following variations have been proposed for FoliActive by the project team: Environmental Risk Management Authority Decision: Application HSR05111 Page 6 of 16 5.13 5.12.1 Control E1 relates to limiting exposure to ecotoxic substances through the setting of Environmental Exposure Limits (EELs). The project team notes that the active ingredient is a biological agent that naturally occurs in the soil environment, which would render setting an EELsoil unfeasible. Furthermore, this control has been triggered by the 9.1D hazard classification conferred based on FoliActive’s use as a biocide and not based on any adverse effect it would have on the aquatic environment. The project team therefore considers that control E1 can be deleted for FoliActive. 5.12.2 Control E2 relates to restrictions on use within an application area when an EEL has been set. As control E2 is linked to the setting of EELs (control E1) and control E1 can be deleted, the project team considers that control E2 can be deleted for FoliActive. 5.12.3 The Agency considers that the following controls may be combined under section 77(5) for FoliActive as they relate to the same requirements: T4 and E6 (equipment used to handle hazardous substances) D4 and D5 (disposal requirements). The modifications to controls for FoliActive, as above, have been incorporated into the list of controls for FoliActive detailed in Appendix 1. 6 Environmental user charges 6.1 The project team considers that use of controls on FoliActive is an effective means of managing risks associated with this substance. At this time, no consideration has been given to whether or not environmental user charges should be applied to this substance as an alternative or additional means of achieving effective risk management. Accordingly, no report has been made to the Minister for the Environment. 7 Decision 7.1 Pursuant to section 28A, I have considered this application to import or manufacture a hazardous substance for release made under section 28. 7.2 Having considered the composition, hazardous properties and use for FoliActive, I am satisfied that the proposed substances meet the criteria for rapid assessment under section 28A(2)(b) in that it has one or more hazardous properties and each hazardous property has the least degree of hazard for that property. 7.3 Because the risks posed by FoliActive are negligible, I consider that applying the HSNO default controls to FoliActive, with the additions and amendments proposed under paragraphs 5.9 to 5.11 (inclusive), will ensure adequate management of any adverse effects of FoliActive. 7.4 In this consideration, I have also applied the following criteria in the Methodology: clause 9 – equivalent of sections 5, 6 and 8; clause 12 – risk assessment; clause 21 – the decision accords with the requirements of the Act and regulations; clause 24 – the use of recognised risk identification, assessment, evaluation and management techniques; Environmental Risk Management Authority Decision: Application HSR05111 Page 7 of 16 clause 25 – the evaluation of risks; and clause 35 – the costs and benefits of varying the default controls. 7.5 The application for importation and manufacture of the hazardous substance, FoliActive for release is thus approved with controls as detailed in Appendix 1. Rob Forlong Chief Executive, ERMA New Zealand ERMA New Zealand Approval Code: FoliActive Environmental Risk Management Authority Decision: Application HSR05111 Date: 16 August 2007 HSR007829 Page 8 of 16 Appendix 1: Controls applying to FoliActive The controls imposed on FoliActive are as follows. The regulations cited should be referred to for definitions and exemptions. The ERMA New Zealand publication User Guide to Control Regulations provides useful guidance on the controls. Table A1.1: Controls for FoliActive – codes, regulations and variations Control Regulation2 Topic Variations Code1 Hazardous Substances (Classes 6, 8 and 9 Controls) Regulations 2001 -Toxic Property Controls Controls T4 and E6 are combined. T4/E6 7 Requirements for equipment used to handle hazardous substances T7 10 Restrictions on the carriage of hazardous substances on passenger service vehicles Hazardous Substances (Identification) Regulations 2001 I1 6, 7, 32-35, General identification requirements 36 (1)-(7) Regulation 6 – Identification duties of suppliers Regulation 7 – Identification duties of persons in charge Regulations 32 and 33 – Accessibility of information Regulations 34, 35, 36(1)-(7) – Comprehensibility, Clarity and Durability of information I9 18 I11 20 I16 25 I19 29-31 Secondary identifiers for all hazardous substances Secondary identifiers for ecotoxic substances Secondary identifiers for toxic substances Alternative information in certain cases Regulation 29 – Substances in fixed bulk containers or bulk transport containers Regulation 30 – Substances in multiple packaging Regulation 31 – Alternative information when substances are imported I21 37-39, 47-50 Documentation required in places of work Regulation 37 – Documentation duties Note: The numbering system used in this column relates to the coding system used in the ERMA New Zealand Controls Matrix. This links the hazard classification categories to the regulatory controls triggered by each category. It is available from the ERMA New Zealand website www.ermanz.govt.nz/resources and is also contained in the ERMA New Zealand User Guide to the HSNO Control Regulations. 2 These Regulations form the controls applicable to this substance. Refer to the cited Regulations for the formal specification, and for definitions and exemptions. The accompanying explanation is intended for guidance only. 1 Environmental Risk Management Authority Decision: Application HSR05111 Page 9 of 16 of suppliers Regulation 38 – Documentation duties of persons in charge of places of work Regulation 39 – General content requirements for documentation Regulation 47 – Information not included in approval Regulation 48 – Location and presentation requirements for documentation Regulation 49 – Documentation requirements for vehicles Regulation 50 – Documentation to be supplied on request I28 46 Specific documentation requirements for toxic substances I29 51-52 Duties of persons in charge of places with respect to signage. Hazardous Substances (Packaging) Regulations 2001 P1 5, 6, 7 (1), 8 General packaging requirements P3 9 Criteria that allow substances to be packaged to a standard not meeting Packing Group I, II or III criteria P13 19 Packaging requirements for FoliActive PS4 Schedule 4 This schedule describes the minimum packaging requirements that must be complied with for FoliActive when packed in limited quantities. Hazardous Substances (Disposal) Regulations 2001 Controls D4 and D5 are combined. D4 8 Disposal requirements for D5 9 FoliActive D6 10 Disposal requirements for packages D7 11, 12 Disposal information requirements D8 13, 14 Disposal documentation requirements Hazardous Substances (Emergency Management) Regulations 2001 EM1 6, 7, 9-11 Level 1 emergency management information: General requirements EM6 8(e) Information requirements for toxic substances EM7 8(f) Information requirements for ecotoxic substances EM8 12-16, 18-20 Level 2 emergency management documentation requirements EM11 25-34 Level 3 emergency management requirements – emergency response plans EM12 35-41 Level 3 emergency management requirements – secondary containment Environmental Risk Management Authority Decision: Application HSR05111 Page 10 of 16 EM13 42 Level 3 emergency management requirements – signage Hazardous Substances (Tank Wagons and Transportable Containers) Regulations 2004 Regulations 4 to 43 The Hazardous Substances (Tank Wagons and Transportable Containers) where applicable Regulations 2004 prescribe a number of controls relating to tank wagons and transportable containers and must be complied with as relevant. Section 77A Additional Controls The controls relating to stationary container systems, as set out in Schedule 8 of the Hazardous Substances (Dangerous Goods and Scheduled Toxic Substances) Transfer Notice 2004 (Supplement to the New Zealand Gazette, 26 March 2004, No. 35, page 767), as amended, are proposed for these substances, notwithstanding clause 1(1) of that schedule FoliActive shall not be applied directly onto or into water Environmental Risk Management Authority Decision: Application HSR05111 Page 11 of 16 Appendix 2: Scales for qualitative risk assessment Qualitative descriptors are indicative only and they are primarily intended to be used to rank risks and benefits for the purposes of balancing risks and costs against benefits, and so that risks can be prioritised for management. The ‘descriptor’ words should not be seen in any absolute senses – they are simply a means of differentiating levels of significance. Assessing risks, costs and benefits qualitatively This section describes how the Agency staff and the Authority address the qualitative assessment of risks, costs and benefits. Risks and benefits are assessed by estimating the magnitude and nature of the possible effects and the likelihood of their occurrence. For each effect, the combination of these two components determines the level of the risk associated with that effect, which is a two dimensional concept. Because of a lack of data, risks are often presented as singular results. In reality, they are better represented by ‘families’ of data which link probability with different levels of outcome (magnitude). Describing the magnitude of effect The magnitude of effect is described in terms of the element that might be affected. The qualitative descriptors for magnitude of effect are surrogate measures that should be used to gauge the end effect or the ‘what if’ element. Tables A2.1 and A2.2 contain generic descriptors for magnitude of adverse and beneficial effect. These descriptors are examples only, and their generic nature means that it may be difficult to use them in some particular circumstances. They are included here to illustrate how qualitative tables may be used to represent levels of adverse and beneficial effect. The sample qualitative descriptors for effects on the market economy listed in the ERMA New Zealand technical guide to decision making1 include representative numbers. These ‘economic’ descriptors were developed prior to the publication of the technical guide on identification and assessment of effects on the market economy,2 which refines the approach that ERMA New Zealand applies to identifying and assessing economic effects. These numbers do not align well with the qualitative descriptors in the other categories (effects on the environment, effects on human health, and effects on society and communities), as they relate more to an event than an effect. In particular the numbers are unclear about how they take account of time (are they annual, or over the life of the activity) and they do not have a local, regional or national context. ERMA New Zealand has adopted a revised set of qualitative descriptors for the magnitude of effect on the market economy, as shown over the page. 1 2 ERMA New Zealand. 2004. Decision Making: A Technical Guide to Identifying, Assessing and Evaluating Risks, Costs and Benefits, ER-TG-05-01. Wellington: Environmental Risk Management Authority. ERMA New Zealand. 2005. Assessment of Economic Risks, Costs and Benefits: Consideration of Impacts on the Market Economy, ER-TG-06-01. Wellington: Environmental Risk Management Authority. Environmental Risk Management Authority Decision: Application HSR05111 Page 12 of 16 Table A2.1: Magnitude of adverse effect (risks and costs). Descriptor Examples of descriptions: ADVERSE Minimal Mild reversible short term adverse health effects to individuals in highly localised area Highly localised and contained environmental impact, affecting a few (less than ten) individuals members of communities of flora or fauna, no discernible ecosystem impact Local/regional short-term adverse economic effects on small organisations (businesses, individuals), temporary job losses No social disruption Minor Mild reversible short term adverse health effects to identified and isolated groups Localised and contained reversible environmental impact, some local plant or animal com munities temporarily damaged, no discernible ecosystem impact or species damage Regional adverse economic effects on small organisations (businesses, individuals) lasting less than six months, temporary job losses Potential social disruption (community placed on alert) Moderate Minor irreversible health effects to individuals and/or reversible medium term adverse health effects to larger (but surrounding) community (requiring hospitalisation) Measurable long term damage to local plant and animal communities, but no obvious spread beyond defined boundaries, medium term individual ecosystem damage, no species damage Medium term (one to five years) regional adverse economic effects with some national implications, medium term job losses Some social disruption (e.g. people delayed) Major Significant irreversible adverse health effects affecting individuals and requiring hospitalisation and/or reversible adverse health effects reaching beyond the immediate community Long term/irreversible damage to localised ecosystem but no species loss Measurable adverse effect on GDP, some long term (more than five years) job losses Social disruption to surrounding community, including some evacuations Massive Significant irreversible adverse health effects reaching beyond the immediate community and/or deaths Extensive irreversible ecosystem damage, including species loss Significant on-going adverse effect on GDP, long term job losses on a national basis Major social disruption with entire surrounding area evacuated and impacts on wider community Environmental Risk Management Authority Decision: Application HSR05111 Page 13 of 16 Table A2.2: Magnitude of beneficial effect (benefits). Descriptor Examples of descriptions: BENEFICIAL Minimal Mild short term positive health effects to individuals in highly localised area Highly localised and contained environmental impact, affecting a few (less than ten) individuals members of communities of flora or fauna, no discernible ecosystem impact Local/regional short-term beneficial economic effects on small organisations (businesses, individuals), temporary job creation No social effect Minor Mild short term beneficial health effects to identified and isolated groups Localised and contained beneficial environmental impact, no discernible ecosystem impact Regional beneficial economic effects on small organisations (businesses, individuals) lasting less than six months, temporary job creation Minor localised community benefit Moderate Minor health benefits to individuals and/or medium term health impacts on larger (but surrounding) community and health status groups Measurable benefit to localised plant and animal communities expected to pertain to medium term. Medium term (one to five years) regional beneficial economic effects with some national implications, medium term job creation Local community and some individuals beyond immediate community receive social benefit. Major Significant beneficial health effects to localised community and specific groups in wider community Long term benefit to localised ecosystem(s) Measurable beneficial effect on GDP, some long term (more than five years) job creation Substantial social benefit to surrounding community, and individuals in wider community. Massive Significant long term beneficial health effects to the wider community Long term, wide spread benefits to species and/or ecosystems Significant on-going effect beneficial on GDP, long term job creation on a national basis Major social benefit affecting wider community Environmental Risk Management Authority Decision: Application HSR05111 Page 14 of 16 Determining the likelihood of the end effect Likelihood in this context applies to the composite likelihood of the end effect, and not either to the initiating event, or any one of the intermediary events. It includes: the concept of an initiating event (triggering the hazard), and the exposure pathway that links the source (hazard) and the area of impact (public health, environment, economy, or community). Thus, the likelihood is the likelihood of the specified adverse effect1 resulting from that initiating event. It will be a combination of the likelihood of the initiating event and several intermediary likelihoods2. The best way to determine the likelihood is to specify and analyse the complete pathway from source to impact. Likelihood may be expressed as a frequency or a probability. While frequency is often expressed as a number of events within a given time period, it may also be expressed as the number of events per head of (exposed) population. As a probability, the likelihood is dimensionless and refers to the number of events of interest divided by the total number of events (range 0–1). (See Table A2.3.) Table A2.3: Likelihood. Descriptor Description 1 Highly improbable Almost certainly not occurring but cannot be totally ruled out 2 Improbable (remote) Only occurring in very exceptional circumstances. 3 Very unlikely Considered only to occur in very unusual circumstances 4 Unlikely (occasional) Could occur, but is not expected to occur under normal operating conditions. 5 Likely A good chance that it may occur under normal operating conditions. 6 Very likely Expected to occur if all conditions met 7 Extremely likely Almost certain 1 2 The specified effect refers to scenarios established in order to establish the representative risk, and may be as specific as x people suffering adverse health effects, or y% of a bird population being adversely affected. The risks included in the analysis may be those related to a single scenario, or may be defined as a combination of several scenarios. Qualitative event tree analysis may be a useful way of ensuring that all aspects are included. Environmental Risk Management Authority Decision: Application HSR05111 Page 15 of 16 Using magnitude and likelihood to construct the level of risk and benefit Using the magnitude and likelihood tables a matrix representing a level of effect can be constructed (Table A2.4). Table A2.4: Level of risk. Magnitude of effect Likelihood Minimal Minor Moderate Major Massive Highly improbable A A B C D Improbable A B C D E Very unlikely B C D E E Unlikely C D E E F Likely D E E F F Very likely E E F F F Extremely likely E F F F F The Agency considers that, for this substance, the level of risk/benefit can be assigned as follows in Table A2.5. Table A2.5: Assignment of level of risk/benefit. Code Level of risk/benefit A&B Negligible C Low D Medium E High F Extreme Environmental Risk Management Authority Decision: Application HSR05111 Page 16 of 16