Work Health and Safety (How to Manage and Control Asbestos in the Workplace) Code of Practice 2015

The Code organises asbestos risk management around a small set of recurring legal and technical concepts, repeatedly linking those concepts to specific regulatory duties.

• Hierarchy of controls and the legal standard of "reasonably practicable." The Code requires PCBUs to eliminate exposure so far as is reasonably practicable, and if not achievable, to minimise exposure as far as reasonably practicable (Regulation 420, Chapter 2.1). The practical steps are the standard hierarchy: elimination (preferred), substitution or isolation and engineering controls, administrative controls, and PPE.
• Definitions and exposure metric. The Code fixes technical terms that determine duty scope and operational thresholds: asbestos, ACM, friable versus non‑friable asbestos, in‑situ asbestos, asbestos‑contaminated dust (ACD), naturally occurring asbestos (NOA), competent person, NATA‑accredited laboratory, and respirable asbestos. The exposure standard is a time‑weighted average of 0.1 fibres/ml over an eight‑hour working day measured over a minimum of four hours by the Membrane Filter Method or regulator‑determined method (Chapter 1.3 and Chapter 6.1).
• Identification, assumption and sampling. The Code distinguishes three legal postures for a person with management or control: identify (engage a competent person), assume (treat material as asbestos for legal purposes where identification is not practicable), or take a sample for analysis by an accredited laboratory (Regulations 422-423; Chapters 2.2-2.4). It warns that sampling can itself increase risk if done incorrectly and therefore only competent persons should sample (Chapter 2.4; Appendix A).
• Documentation and information flows. Two documentary artefacts carry central operational weight: the asbestos register (Regulation 425; Chapter 3) and the asbestos management plan (Regulation 429; Chapter 4). The Code sets out required content, who must have access (workers, health and safety representatives, prospective contractors), review cycles (at least every five years for register and plan, Regulations 426 and 430), and transfer obligations on relinquishing management or control (Regulation 428).
• Work categories and regulated exceptions. The statutory prohibition (Regulation 419) is subject to detailed exceptions, captured in the Code as "asbestos‑related work" and "asbestos removal work" for which additional controls and licensing apply (Chapter 1.1 and Chapter 5.4). Asbestos removalist licensing is addressed in the WHS Regulations and the companion Code How to Safely Remove Asbestos; the present Code explains when removal is mandatory (for example, friable asbestos or non‑friable ACM >10 m²) and when alternative controls are acceptable (Chapter 7.1).
• Operational technical controls. The Code sets operational limits that convert risk assessments into concrete controls: no use of high‑pressure water or compressed air on asbestos, restricted use of power tools unless enclosed or provided with extraction, asbestos vacuum cleaner standards (AS/NZS 60335.2.69), wetting and pastes for drilling, negative‑pressure enclosures and clearance monitoring (Regulation 446; Chapters 6.4 and 7).
• Worker protections and duties. The Code imposes worker‑centred obligations: training requirements (Regulation 39 and Regulation 445; Chapter 6.3), access to the asbestos register and management plan (Regulations 427 and 429), health monitoring paid by the PCBU with reports to workers and the regulator where disease is suspected, and retention of medical records for 40 years (Regulations 435-444).

These concepts are repeatedly operationalised with examples, safe work practice templates and cross‑references to standards and the How to Safely Remove Asbestos Code. The Code makes clear that compliance can be achieved either by following its guidance or by adopting an alternative method that provides an equivalent or higher standard (Foreword). The exposure standard, the definitions of friable/non‑friable and the role of competent persons and accredited labs are the technical anchors that determine when a duty is triggered and what controls must be used.

The Code specifies a set of duty holders and identifies their responsibilities by reference to the WHS Act and Regulations. The primary affected groups are:

• Persons conducting a business or undertaking (PCBUs). The PCBU carries broad, primary duties to ensure, so far as is reasonably practicable, that workers and others are not exposed to airborne asbestos. Specific duties include ensuring exposure is eliminated or minimised (Regulation 420), providing health monitoring and paying all associated expenses where required (Regulations 435-444), providing suitable training and instruction (Regulation 39, Regulation 445), ensuring appropriate equipment and decontamination, and controlling the use of equipment that can generate asbestos dust (Regulation 446). The table in Chapter 1.2 summarises these duties.
• Persons with management or control of a workplace. These persons must ensure identification or lawful assumption of asbestos presence, prepare and maintain an asbestos register (Regulation 425), prepare and maintain an asbestos management plan where asbestos is identified or assumed present (Regulation 429), indicate the presence of asbestos by label or sign (Regulation 424), and provide registers and plans to contractors and incoming managers when control transfers (Regulations 427 and 428).
• PCBUs carrying out demolition or refurbishment work. Where a structure or plant was constructed or installed before 31 December 2003, the PCBU conducting demolition/refurbishment must obtain the asbestos register, ensure asbestos likely to be disturbed is identified and removed so far as is reasonably practicable, and if no register exists arrange inspection by a competent person (Regulations 447-457; Chapter 5.3). Emergency demolitions have specific notification and procedural obligations.
• Asbestos removalists and licensed removal workers. The Code points to the licensing and competency requirements in the WHS Regulations and the companion removal Code for removalists. Removalists must be competent and, except in limited circumstances, licensed; removal of friable asbestos or non‑friable >10 m² by licensed removalists is required (Chapter 1.1; Chapter 7.1).
• Workers and health and safety representatives. Workers carrying out work where asbestos may be present must be consulted and trained (Sections 47-48; Chapter 2.1). Workers have rights of access to the asbestos register and asbestos management plan (Regulations 427 and 429), and are entitled to health monitoring when at risk (Regulations 435-444).
• Specialist service providers and laboratories. Competent persons (occupational hygienists, licensed asbestos assessors, asbestos removal supervisors, NATA‑accredited testing labs) are implicated for identification, sampling and exposure monitoring (Regulations 422-423; Chapter 6.1). The Code requires samples be analysed by a NATA‑accredited or regulator‑approved laboratory (Regulation 423).
• Owners and occupants of domestic premises under specific circumstances. The Code notes that some chapters apply to domestic premises where they become a workplace (Scope), and that when a domestic premises becomes a workplace by engagement of a contractor, duties shift to the person conducting the work, who must identify and, if necessary, remove asbestos (Chapter 5.3).
• Businesses involved in disposal, transport and laundering services. Disposal must comply with state or territory EPA requirements and licensed disposal site rules (Chapter 5.5). Laundering of asbestos-contaminated clothing must be done in facilities equipped to handle such clothing; contaminated clothing must not be laundered at home (Chapter 7.7).

Who pays and who decides: the Code consistently places cost and operational decision‑making on the PCBU and the person with management or control of the workplace. The PCBU pays for health monitoring, arranges competent persons and accredited laboratory analyses, funds training, and implements controls. The Code also places procedural duties on regulators (for approval of labs and methods, for receiving emergency notices for demolition, and for occupational hygienist and licensing oversight), which means some decisions require regulator involvement or approval (Regulation 423; demolition emergency requirements in Chapter 5.3).

Behavioural changes expected of these parties include the establishment and maintenance of registers and management plans, training and information flows to workers, altered procurement practices to avoid imported plant or materials that may contain asbestos, changed demolition/refurbishment planning and budgeting for licensed removals where required, and operational changes to tools, cleaning and PPE laundering arrangements.

The Code translates statutory obligations into specific operational duties and rights. Below are the principal duties, the statutory or regulatory basis cited by the Code, and the rights it confers on workers and other parties.

Principal duties placed on PCBUs and persons with management or control:

• Eliminate or minimise exposure. PCBUs must ensure, so far as is reasonably practicable, that exposure of persons at the workplace to airborne asbestos is eliminated; if elimination is not reasonably practicable, exposure must be minimised (Regulation 420; Chapter 2.1). The exposure standard must not be exceeded (Chapter 6.1).
• Identification or assumption. The person with management or control of the workplace must ensure asbestos or ACM is identified by a competent person or, where appropriate, assume presence where materials are inaccessible or likely to contain asbestos (Regulation 422; Chapter 2.2 and 2.3).
• Sampling and laboratory analysis. If sampling is arranged, only a competent person may take samples and analysis must be performed by a NATA‑accredited laboratory, a regulator‑approved laboratory, or a laboratory operated by the regulator (Regulation 423; Chapter 2.4).
• Labelling and signage. Where asbestos is identified or assumed, the person with management or control must ensure its presence and location are clearly indicated, with labels where reasonably practicable and signs in other cases (Regulation 424; Chapter 2.5).
• Asbestos register. Prepare, maintain and make available an asbestos register containing dates, locations, type and condition, with review at least every five years and revision when asbestos is removed, disturbed or newly identified (Regulations 425 and 426; Chapter 3).
• Asbestos management plan. Ensure a written asbestos management plan is prepared and maintained when asbestos is identified or assumed present, and review it at least every five years or when conditions change (Regulation 429 and Regulation 430; Chapter 4).
• Duties for demolition/refurbishment. Prior to demolition/refurbishment of pre‑2004 structures, the person with management or control must review and provide the asbestos register and ensure asbestos likely to be disturbed is identified and removed so far as is reasonably practicable (Regulations 447-457; Chapter 5.3).
• Health monitoring. Provide health monitoring for workers carrying out licensed asbestos removal work, ongoing removal work or asbestos‑related work where there is a risk of exposure, with monitoring under the supervision of a registered medical practitioner, and pay all expenses; retain medical records for 40 years (Regulations 435-444; Chapter 6.2).
• Training. Ensure workers likely to be involved in asbestos removal or asbestos‑related work are trained in identification, safe handling and suitable control measures (Regulation 445; Chapter 6.3). Also ensure information, training and instruction is suitable and adequate for all workers (Regulation 39).
• Control of tools and equipment. Do not use high‑pressure water spray or compressed air on asbestos; other equipment capable of releasing asbestos must be controlled, enclosed or fitted with extraction (Regulation 446; Chapter 6.4).
• Waste handling and disposal. Ensure asbestos waste is contained, labelled in accordance with GHS, and disposed of at licensed facilities as soon as practicable; transport and disposal must comply with state or territory EPA requirements (Chapter 5.5).

Rights and entitlements for workers and other parties:

• Access to information. Workers, health and safety representatives, and persons conducting businesses who will carry out work at the workplace must have ready access to the asbestos register and asbestos management plan (Regulations 427 and 429; Chapters 3.3 and 4.3).
• Right to health monitoring and information. Workers must be informed of health monitoring requirements before commencing work that may expose them to asbestos, and be given copies of medical reports arising from monitoring; reports indicating disease must be provided to the regulator and other PCBUs with a duty to provide monitoring (Chapter 6.2).
• Consultation rights. The WHS Act requires the PCBU to consult, so far as is reasonably practicable, with workers likely to be directly affected by health and safety matters, and where workers are represented by health and safety representatives, consultation must involve them (Sections 47-48; Chapter 2.1).
• Access to safe systems and controls. Workers can expect that the PCBU will implement the hierarchy of controls and appropriate PPE, and that higher‑order controls such as enclosure or removal will be considered before reliance on administrative controls or PPE (Regulation 420; Chapter 2.1).

Other operational rights and duties for third parties:

• Laboratories and competent persons. Only NATA‑accredited or regulator‑approved labs may analyse samples; competent persons must be engaged for identification, sampling and exposure monitoring where required (Regulation 423; Chapters 2.2-2.4 and 6.1).
• Transfer obligations. When management or control is relinquished, the current person with control must provide a copy of the asbestos register to the incoming person, so far as is reasonably practicable (Regulation 428; Chapter 3.4).

The Code clarifies that compliance can be achieved by following the Code or by adopting alternative measures that achieve an equivalent or higher standard of safety, explicitly preserving alternative technical methods where they meet the safety standard (Foreword). The Code also repeatedly ties duties to the "reasonably practicable" test; the Code offers evidence of what is known about controls and procedures that courts and inspectors may rely upon when assessing whether steps were reasonably practicable in particular circumstances.

The Code itself does not create offences or prescribe fines. It functions as an approved code under s 274 of the Work Health and Safety Act 2011 and therefore plays a role in enforcement and litigation by explaining practices that will commonly achieve compliance with the WHS Act and Regulations. The Code states that it is admissible in court proceedings under the Act and Regulations, and that courts may regard it as evidence of what is known about a hazard, risk or control, and may rely on it in determining what is reasonably practicable in the circumstances (Foreword). An inspector may refer to an approved code when issuing an improvement or prohibition notice (Foreword).

Enforcement mechanisms and notifications described in the Code:

• Regulator engagement and notification. The Code requires regulator involvement in certain circumstances, for example regulator approval/operation of laboratories used for sample analysis (Regulation 423), and immediate written notice to the regulator in emergencies preceding demolition where structural unsoundness or imminent collapse affects asbestos exposure risk (Chapter 5.3).
• Inspector notices and evidentiary role. Inspectors may use the Code as an operational reference when issuing improvement or prohibition notices. While the Code does not prescribe penalties, failure to comply with duties in the WHS Act and WHS Regulations that the Code explains may expose duty holders to enforcement action under those primary instruments, including notices, prosecutions and penalties established under the WHS Act and Regulations.
• Licensing and competency enforcement. The Code points to licensing requirements for asbestos removalists in the WHS Regulations and the companion How to Safely Remove Asbestos Code. Licensing is a regulatory mechanism that enables enforcement; the Code explains when Class A or Class B licensed removalists are required (e.g., removal of friable asbestos or non‑friable asbestos >10 m² must be removed by licensed removalists as soon as reasonably practicable, Chapter 7.1).
• Records and inspections. The Code mandates specific records and retention periods that support enforcement, including asbestos registers, asbestos management plans, training records (kept while the worker carries out the work and for five years after cessation, Chapter 6.3), and health monitoring reports retained for at least 40 years (Regulations 435-444; Chapter 6.2). These records enable regulator audits and are relevant to prosecutions and civil liability.
• Monitoring and clearance. The Code endorses air monitoring and clearance monitoring practices to verify controls, and requires competent persons perform exposure monitoring when there is uncertainty about exposure standards (Chapter 6.1). These monitoring obligations and clearance certificates (required for licensed removal work) create enforceable benchmarks for regulator assessment.

Points on penalties and enforcement derived from the Code:

• The Code frames what is likely to be considered "reasonably practicable" in the WHS context by setting out accepted technical controls, sampling procedures, training practices, and documentation. Courts and inspectors may treat the Code as evidentiary guidance when determining compliance and, by extension, when considering penalties under the WHS Act and Regulations.
• The Code clarifies that alternate methods of compliance are acceptable where they provide an equivalent or higher standard; this preserves scope for differing technical approaches but requires the PCBU to document equivalence and effectiveness to regulators and courts (Foreword).
• The operational obligations to notify the regulator about emergencies, to use regulator‑approved labs, and to comply with licensing demonstrate enforcement points where regulators have clear oversight and can take compliance action.

Because the Code is descriptive and advisory rather than prescriptive of penalties, enforcement in practice depends on the underlying WHS Act and Regulations, regulator policies and prosecutorial discretion. The Code reduces uncertainty about the content of compliance by laying out control measures, recordkeeping expectations and monitoring practices that regulators and courts can rely on when assessing whether a duty holder took steps that were reasonably practicable.

The Code repeatedly situates itself within a broader regulatory and standards environment. It is a model code developed by Safe Work Australia under the COAG Inter‑Governmental Agreement and intended for adoption by Commonwealth, state and territory governments (Foreword). The Code therefore interacts with multiple instruments and regimes:

• Work Health and Safety Act 2011 and WHS Regulations. The Code is made under s 274 of the WHS Act and is intended to provide practical guidance on meeting duties under the Act and Regulations, including the asbestos‑specific Regulations cited across Chapters 1-7 (instrument preamble and Foreword). It interprets and operationally explains duties but does not replace statutory obligations.
• Codes and companion COPs. The Code cross‑references the Code of Practice: How to Safely Remove Asbestos for detailed removal, clearance and licensing rules (referred to in multiple places such as Chapters 1.1, 5.5, 7.1 and appendices). It also cross‑references other Safe Work Australia Codes, such as the Code of Practice: How to Manage Work Health and Safety Risks and Consultation, Cooperation and Coordination Code (Chapter 2.1).
• Australian Standards. The Code relies on and references Australian and New Zealand Standards for equipment and PPE, for example AS/NZS 1716 (respiratory protective devices), AS/NZS 1715 (selection, use and maintenance of RPE), AS/NZS 60335.2.69 for asbestos vacuum cleaners, and AS 1319 for safety signs (Chapters 6 and 7).
• Customs and import control. The Code highlights that importation of asbestos and asbestos‑containing materials is generally prohibited under the Customs (Prohibited Imports) Regulations 1956, and advises PCBUs to implement quality assurance systems to ensure imported plant does not contain asbestos where the supplier country permits its use (Chapter 1.1).
• Environmental and waste management laws. For transport and disposal of asbestos waste the Code refers to state and territory environment protection authority (EPA) requirements and notes asbestos waste must be disposed at EPA‑licensed facilities and never via general waste systems (Chapter 5.5). It further cites the Assessment of Site Contamination NEPM as the recommended approach for contaminated site assessment and remediation (Chapter 5.2).
• Public health, building, and local government regulation. The Code acknowledges that other laws may apply, such as public health, building and construction regulation, local government requirements and environmental protection regimes; PCBUs must ensure compliance with those overlapping requirements in addition to WHS duties (Scope and application).
• Medical confidentiality and reporting. Health monitoring must be carried out under the supervision of a registered medical practitioner and reports are confidential, but if test results indicate the worker may have contracted a disease as a result of exposure, the report must be provided to the regulator (Chapter 6.2). Medical record retention for 40 years intersects with privacy and medical records regulation; disclosure rules are conditioned on written worker consent except where professional confidentiality duty requires otherwise.
• Licensing and state variations. Licensing regimes for asbestos removal are set out in the WHS Regulations and implemented by states and territories; the Code explains the licensing threshold and refers to regulator rules. Practical licensing requirements and penalties therefore depend on jurisdictional implementation of the WHS Regulations.

In short, the Code operates as a guide that explains how to meet WHS duties in the asbestos context, and it sits within a web of national standards, customs law, environmental law and jurisdictional licensing schemes. Duty holders must therefore coordinate compliance across WHS duties and other statutory regimes, for example by ensuring disposal arrangements comply with EPA rules, sampling and lab analysis use accredited labs, and licensed removalists meet the licensing criteria prescribed in regulation and the companion removal Code.

The instrument itself carries a limited administrative history in the text provided. Key dates and procedural steps included in the Code are:

• Drafting and consultation. The foreword records that a draft of this Code of Practice was released for public consultation on 7 December 2010, and that it was endorsed by the Workplace Relations Ministers’ Council (now the Ministerial Council) on 10 August 2011 (Foreword).
• Approval. The instrument records approval of the How to Manage and Control Asbestos in the Workplace Code of Practice by the Minister for Employment, Michaelia Cash, with a signature date of 18 March 2016 (instrument header and approval statement, sections 1-3).
• Commencement. Clause 2 states that the instrument commences on the day after it is registered on the Federal Register of Legislative Instruments (Clause 2).
• Origin and legal basis. Clause 3 records that the Code was approved under the Work Health and Safety Act 2011, section 274, and that the approving Minister is satisfied the code was developed by a process described in s 274(2) of the WHS Act.

The Code also notes its status as a Safe Work Australia model code developed under the Council of Australian Governments’ (COAG) inter‑governmental framework, and that it was intended for adoption by Commonwealth, state and territory governments (Foreword). The text does not record subsequent amendments, repeal history or later versions. The Code specifically states that it is an "approved code of practice" under s 274; it does not itself contain an amendment table or later amendment dates in the text provided.

Practical implications of this limited amendment history:

• The Code is a 2015 instrument approved in 2016 following consultation that began in 2010; users should confirm whether the version they hold is current in their jurisdiction and whether state or territory laws have subsequently adopted, amended or supplemented the model code.
• Because the Code is a model produced by Safe Work Australia, jurisdictions may have implemented the content with variations. The Code itself recommends consulting the WHS Regulations, the Code of Practice: How to Safely Remove Asbestos, and jurisdictional requirements such as EPA disposal rules for precise obligations.
• The Code’s cross‑reference to other instruments (Standards, companion COPs, Customs Regulations, NEPM) means changes in those instruments may affect operational compliance; duty holders should monitor updates to the WHS Regulations, relevant Australian Standards and state EPA rules.

The text provided does not contain a timeline of subsequent amendments or case law developments. For up‑to‑date compliance and enforcement consequences, duty holders must check the Federal Register of Legislative Instruments, state/territory adoption schedules and any amendments to the WHS Regulations or companion Codes.

The Code itself contains no litigation history, cases or judicial decisions. It does, however, specify its evidentiary role under the WHS framework: it is admissible in court proceedings under the Work Health and Safety Act and Regulations, and "Courts may regard a code of practice as evidence of what is known about a hazard, risk or control and may rely on the code in determining what is reasonably practicable" (Foreword). That framing has practical litigation implications absent from the Code text:

• Evidentiary role. The Code is expressly positioned as a source of evidence regarding technical controls, industry knowledge and accepted practices. In prosecutions or civil proceedings under the WHS Act and Regulations, a court may treat adherence to the Code as persuasive evidence of compliance, and conversely treat departure from it as evidence that accepted controls were not followed. The Code also expressly permits alternative methods of compliance where they provide an equivalent or higher standard of safety than the Code (Foreword).
• No judicial decisions recorded in the instrument. The Code does not list case authorities or judicial interpretations of its provisions. It therefore does not itself report how courts have applied the Code in particular factual scenarios, nor does it provide precedent examples.
• Practical litigation consequences to expect. While the Code does not supply historic litigation outcomes, the legal mechanics it establishes mean litigators should expect courts to consider whether duty holders followed the Code's guidance when assessing "reasonably practicable" steps. Evidence that a PCBU implemented the Code's register, management plan, sampling and monitoring regimes, training and health monitoring, and used accredited labs, will bear on liability assessments. Conversely, absence of those records or of documented risk assessments may be used by regulators or private litigants to demonstrate failure to meet statutory duties.
• Documents and retention as evidentiary assets. The Code prescribes recordkeeping (asbestos register, asbestos management plan, training records, health monitoring reports for 40 years, sampling and monitoring reports). Those records both create compliance obligations and become central evidence in any proceeding. Practitioners planning litigation or compliance audits should prioritise obtaining these documents.
• Interaction with alternative methods. Because the Code permits alternative technical measures that deliver equivalent or higher safety, litigators should be ready to present technical evidence showing equivalence if a duty holder deviates from the Code.

In summary, while the Code provides no litigation history, it is explicitly designed to be relied upon in court and to guide determinations of what is reasonably practicable for asbestos risk management. Parties should treat adherence to the Code as an important evidentiary and compliance benchmark and should expect its provisions to be engaged by inspectors, regulators and courts in enforcement actions arising from asbestos exposure incidents.

The Code contains numerous operational traps and legal pitfalls for duty holders that are likely to cause unintended non‑compliance if overlooked. Below are concrete "gotchas" drawn directly from the text and the practical examples it gives.

• Assumption vs sampling. If a person with management or control assumes material is asbestos, it is legally treated as asbestos and all management requirements apply; alternatively, if sampling is chosen, only competent persons should sample because sampling can itself release fibres and be more hazardous than leaving the material undisturbed (Regulations 422-423; Chapter 2.3 and 2.4). Mistake: taking informal samples without a competent person or uncertified lab.
• Inaccessible areas treated as asbestos. Areas that are inaccessible during normal daily activities or routine maintenance must be assumed to contain asbestos if likely to do so, and this assumption must be recorded in the asbestos register (Regulation 422; Chapter 2.3). Mistake: failing to document or review presumptions about inaccessible areas, thereby exposing contractors during refurbishment.
• Domestic premises nuance. The Code says some chapters apply to domestic premises when the premises become a workplace, and homeowners are not placed under the same duties as a PCBU; however, once a contractor is engaged the contractor becomes responsible for identifying and removing asbestos likely to be disturbed (Scope; Chapter 5.3). Mistake: homeowner assumes no duties apply to them when a contractor starts work.
• Register transfer on sale or change of control. The person relinquishing management or control must, so far as reasonably practicable, provide a copy of the asbestos register to the incoming manager or owner (Regulation 428; Chapter 3.4). Mistake: failing to transfer the register during sale, which creates downstream liability for the incoming manager and practical compliance gaps.
• Sampling laboratory requirements. Samples must be analysed by a NATA‑accredited laboratory, a regulator‑approved laboratory, or a regulator‑operated lab (Regulation 423; Chapter 2.4). Mistake: relying on unaccredited labs or overseas certificates without regulator approval.
• Banned and controlled equipment. High‑pressure water spray and compressed air cannot be used on asbestos, and power tools are restricted unless enclosed or fitted with extraction (Regulation 446; Chapter 6.4). Mistake: routine use of compressed air or household vacuums which the Code forbids.
• Asbestos removal thresholds. Friable asbestos must be removed by a Class A licensed removalist "as soon as reasonably practicable", and non‑friable ACM larger than 10 m² must be removed by a licensed removalist (Chapter 7.1). Mistake: assuming small quantities escape licensing requirements; the 10 m² threshold is explicit.
• Health monitoring obligations and costs. The PCBU must pay all expenses for health monitoring where required and must provide reports to the worker and to the regulator if the report indicates the worker may have contracted a disease from the work (Regulations 435-444; Chapter 6.2). Mistake: assuming that workers bear monitoring costs or that reporting can be delayed.
• Training records and retention. Training records must be kept while the worker carries out the work and for five years afterwards; health monitoring records must be kept for 40 years (Chapters 6.3 and 6.2). Mistake: failure to maintain these records can undermine defence in enforcement actions.
• Clearance monitoring. Clearance monitoring is required for licensed removal work prior to reoccupation; the Code points to the companion removal Code for details (Chapter 7.8). Mistake: reoccupying areas prematurely without a clearance certificate.
• Waste disposal and jurisdictional variance. Disposal must comply with state/territory EPA and cannot be disposed into general waste. Licensed disposal facilities vary by jurisdiction and the NEPM is recommended for contaminated site remediation (Chapter 5.5 and 5.2). Mistake: transporting asbestos waste to an unlicensed facility or across jurisdictional lines without checking rules.
• NOA management is distinct. Naturally occurring asbestos need not be listed in an asbestos register but must be included in a written asbestos management plan where identified or likely to be present (Chapter 5.1). Mistake: treating NOA the same as product‑borne ACM and omitting a management plan.
• Competent person ambiguity. The WHS Regulations define "competent person" broadly by training, qualifications or experience, and the Code specifies various acceptable competencies (licensed assessors, occupational hygienists, asbestos removal supervisors). Mistake: relying on staff with insufficient demonstrable qualifications.
• Exposure monitoring stoppage. The Code states good practice to stop work and investigate if airborne asbestos in the breathing zone reaches half the exposure standard (i.e. 0.05 fibres/ml), signaling an operational threshold that could trigger stoppage and remediation costs (Chapter 6.1). Mistake: ignoring this trigger and continuing work.
• Alternative compliance burden. The Code permits alternative methods so long as they achieve equivalent or higher safety, but the burden is on the PCBU to demonstrate equivalence if challenged in enforcement or litigation (Foreword). Mistake: adopting ad hoc technical methods without documentation or justification.
• Label impracticability. If labelling ACM is not reasonably practicable, prominent warning signs must be used and the location added to the asbestos register (Regulation 424; Chapter 2.5). Mistake: assuming labelling is optional without recording why it is impracticable.

These "gotchas" are practical traps that translate into compliance and liability risk. The Code includes procedural examples and appendices to mitigate many of these risks, but duty holders must attend to the explicit thresholds, documentation and competent person requirements to avoid inadvertent non‑compliance.

This section translates the Code’s requirements into a compliance checklist and practical steps, with citations to regulatory provisions contained in the Code.

1. Confirm legal obligations and scope

   • Identify whether the workplace is covered by the WHS Act and whether asbestos is likely to be present (Regulation 422; Chapters 1.1 and 2.2).
   • Check whether the workplace was constructed after 31 December 2003; if so and no asbestos is identified or likely, an asbestos register may not be required (Regulation 425; Chapter 3).

2. Identify and document asbestos presence

   • Arrange an inspection by a competent person to identify asbestos or, where appropriate, make reasoned assumptions and record them in the asbestos register (Regulation 422; Chapter 2.2-2.3).
   • If sampling is chosen, ensure a competent person takes samples and that samples are analysed only by a NATA‑accredited laboratory or a regulator‑approved lab (Regulation 423; Appendix A).
   • Include inaccessible areas and assumptions explicitly in the register (Regulation 422; Chapter 2.3).

3. Maintain an asbestos register and management plan

   • Prepare and keep a register at the workplace listing identified or assumed asbestos, condition, location and dates (Regulation 425; Chapter 3.1 and Appendix C/D).
   • Prepare a written asbestos management plan linked to the register, defining control measures, timetables, roles and procedures for incidents and training (Regulation 429; Chapter 4.1).
   • Review and revise the register and plan at least every five years or sooner when asbestos is removed, disturbed or conditions change (Regulations 426 and 430; Chapters 3.2 and 4.2).
   • Ensure the register and plan are readily accessible to workers, health and safety representatives and contractors (Regulations 427 and 429; Chapters 3.3 and 4.3).

4. Adopt the hierarchy of controls

   • Eliminate the asbestos where reasonably practicable. Where elimination is not feasible, prioritise enclosure, encapsulation or sealing, engineering controls and isolation before relying on administrative controls and PPE (Regulation 420; Chapters 2.1 and 7).
   • For friable asbestos and non‑friable asbestos >10 m² arrange licensed removal as soon as reasonably practicable (Chapter 7.1). Engage removalists who meet the licensing and competency requirements specified in the WHS Regulations and the How to Safely Remove Asbestos Code.

5. Control tools and work methods

   • Prohibit high‑pressure water sprays and compressed air, and restrict high‑speed power tools unless enclosed or fitted with effective extraction (Regulation 446; Chapters 6.4 and 7.4).
   • Follow safe work practices and Appendix F examples for drilling, sealing, gutter cleaning, cabling, switchboards and friction materials; use wet methods, pastes or shadow vacuuming as appropriate.
   • Ensure asbestos vacuum cleaners comply with AS/NZS 60335.2.69 and do not use household vacuums (Chapter 7.4).

6. Training and consultation

   • Consult with workers and health and safety representatives regarding asbestos issues and controls (Sections 46-48; Chapter 2.1).
   • Provide targeted training for workers likely to be involved in asbestos removal or asbestos‑related work covering hazard recognition, safe handling, register use, control measures and PPE (Regulation 445; Chapter 6.3).
   • Maintain training records for the period the worker performs the work and five years thereafter (Chapter 6.3).

7. Health monitoring and medical supervision

   • Where required, provide health monitoring before commencing licensed asbestos removal and at least every two years thereafter, or as recommended by a registered medical practitioner; this must be supervised by a registered medical practitioner with relevant competencies (Regulations 435-444; Chapter 6.2).
   • The PCBU must pay all health monitoring costs and retain records for at least 40 years; provide the worker with the report and notify the regulator if the report indicates disease related to the work (Chapter 6.2).

8. Signage, labelling and access

   • Label asbestos where reasonably practicable and otherwise erect signs compliant with AS 1319 at entrances and work areas; include locations on the asbestos register (Regulation 424; Chapter 2.5 and Appendix B).
   • Provide the asbestos register and management plan to contractors before they commence work that may disturb asbestos (Regulation 427; Chapter 3.3). Ensure demolition/refurbishment contractors obtain a copy prior to starting (Regulation 447; Chapter 5.3).

9. Waste handling, transport and disposal

   • Package asbestos waste in heavy‑duty 200 µm plastic bags, seal, label and store in closed containers until disposal (Chapter 5.5).
   • Dispose only at EPA‑licensed facilities and comply with jurisdictional rules for transport and disposal (Chapter 5.5). For contaminated sites engage specialists in accordance with the NEPM (Chapter 5.2).

10. Emergency and demolition procedures

    • For emergency demolitions ensure a procedure to reduce exposure is prepared before demolition, and immediately notify the regulator about the emergency as required by the WHS Regulations (Chapter 5.3).
    • Prior to demolition or refurbishment of pre‑2004 structures, review the asbestos register, provide a copy to demolition contractors and ensure asbestos likely to be disturbed is removed so far as reasonably practicable (Regulations 447-457; Chapter 5.3).

11. Monitoring, verification and clearance

    • Undertake exposure monitoring by competent persons when there is uncertainty about exceeding the exposure standard (Chapter 6.1). Use control and clearance monitoring consistent with the removal Code for licensed removal work (Chapter 6.1 and 7.8).
    • Act on monitoring triggers, for example the Code suggests stopping work and investigating if exposures reach half the exposure standard as a good practice threshold (Chapter 6.1).

12. Documentation and recordkeeping

    • Keep asbestos registers, management plans, sampling and monitoring results, training records, health monitoring reports (40 years) and disposal receipts. Make these documents available to workers, HSRs and contractors (Chapters 3, 4 and 6).

Implementation risks and resource considerations

• Competent persons, licensed removalists and accredited laboratories may be scarce in some areas, creating scheduling delays and higher costs for removals and sampling. Plan procurement and budgets accordingly.
• Health monitoring costs and long record retention create ongoing financial and administrative burdens for PCBUs.
• Demolition and refurbishment planning must allow time for identification and removal; failing to factor this in risks project delays and regulatory non‑compliance.
• Alternative technical measures are permissible but require documented technical justification showing equivalence or superiority to the Code's controls, increasing legal and technical advisory costs.
• Jurisdictional variation in disposal and licensing practices requires local legal and regulatory checks; do not assume a national uniformity in operational details.

By following the Code’s documentation practices and the operational steps above , using competent persons, accredited labs and licensed removalists where required, and keeping comprehensive records , a PCBU will establish a defensible compliance posture. The Code expressly permits other methods that provide equivalent or higher safety; if using an alternative approach, document the technical basis, testing and monitoring that demonstrate equivalence when challenged by inspectors or in litigation.