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Published

Actions for Managing native vegetation

Managing native vegetation

Environment
Management and administration
Project management
Regulation
Service delivery

The report found the clearing of native vegetation on rural land is not effectively regulated and managed. The processes supporting the regulatory framework are weak and there is no evidence-based assurance that clearing of native vegetation is carried out in accordance with approvals. 

In 2014 an expert panel completed a review of biodiversity legislation in NSW. The panel’s recommendations included repealing the Native Vegetation Act 2003, proposing a new Act with the goal of maintaining a healthy, productive and resilient environment for the greatest wellbeing of the community, and recommending that management of native vegetation in the context of existing agricultural management would be assisted and supervised by Local Land Services (LLS).

Following the panel report, the NSW Government undertook major biodiversity conservation and land management reforms which saw the introduction of the Biodiversity Conservation Act 2016 (NSW) and the Local Land Services Amendment Act 2016 (NSW). The reforms commenced in August 2017. The Native Vegetation Act 2003, the Threatened Species Conservation Act 1995, the Nature Conservation Trust Act 2001, and parts of the National Parks and Wildlife Act 1974 were repealed.

Under the legislative reforms, the Biodiversity Conservation Act 2016 and Local Land Services Amendment Act 2016, which amended the Local Land Services Act 2013, aim to ensure a balanced approach to land management and biodiversity conservation in NSW.

A core objective of the Biodiversity Conservation Act 2016 is to conserve biodiversity at bioregional and state scales. A core objective of the Local Land Service Act 2013 is to ensure the proper management of natural resources in the social, economic and environmental interests of the state, consistently with the principles of ecologically sustainable development.

The integrated package of reforms included:

  • new arrangements that allow land owners to improve productivity while responding to environmental risks
  • new ways to assess and manage the biodiversity impacts of development
  • a new state Environmental Planning Policy for managing impacts on native vegetation in urban areas
  • significant investment in conservation of private land
  • a risk-based system for regulating human and business interactions with native plants and animals
  • streamlined approvals and dedicated resources to help reduce the regulatory burden.

Transition to this land management framework began on 25 August 2017 with the commencement of the Land Management (Native Vegetation) Code.

The overall objectives of the reforms are:

  • to arrest and ultimately reverse the current decline in the state’s biodiversity while facilitating ecologically sustainable development, in particular efficient and sustainable agricultural development
  • enable landholders to improve the efficiency of their agricultural systems and take a more active role in providing incentive and supporting landholders to improve the condition and function of their ecological systems. 

The objective of this audit is to assess whether the clearing of native vegetation in rural areas is effectively regulated and managed by the Office of Environment and Heritage (OEH) and LLS under these legislative frameworks. The audit also examined the progress of the Biodiversity Conservation Trust in implementing the Biodiversity Conservation Investment Strategy as a counterbalance to rural land clearing. 

At the time of this audit OEH was responsible for preparing the Native Vegetation Regulatory map and for compliance enforcement in relation to unlawful land clearing. Post 1 July 2019, under machinery of government changes, OEH will be abolished and its activities relevant to this audit will be moved to the new Department of Planning, Industry and Environment. For the purposes of this audit we will continue to refer to it as OEH. 

Conclusion
The clearing of native vegetation on rural land is not effectively regulated and managed because the processes in place to support the regulatory framework are weak. There is no evidence-based assurance that clearing of native vegetation is being carried out in accordance with approvals. Responses to incidents of unlawful clearing are slow, with few tangible outcomes. Enforcement action is rarely taken against landholders who unlawfully clear native vegetation. 

There are processes in place for approving land clearing but there is limited follow-up to ensure approvals are complied with.
Procedures and systems are in place for assessing applications and issuing approvals for land clearing. Approvals contain conditions for managing clearing and setting aside land for conservation as a counterbalance to permitted clearing. 
There is limited follow-up or capacity to gauge whether landholders are complying with the conditions of approvals and effectively managing areas of their land that have been set aside for conservation (i.e. 'set asides'). 
Certificate assessments are used to grant landholders permission to clear. All assessments we reviewed generally complied with the Land Management (Native Vegetation) Code 2018 (the Code). 
The rules around land clearing may not be responding adequately to environmental risks.
The Code, which contains conditions under which the thinning or clearing of native vegetation can be approved on regulated land, is intended to allow landholders to improve productivity while responding to environmental risks. That said, it may not be achieving this balance. For example, the Code allows some native species to be treated as ‘invasive’ when they may not be invading an area, provides little protection for groundcover and limited management requirements for set asides. There is also limited ability under the Code to reject applications for higher risk clearing proposals.
The release of the Native Vegetation Regulatory (NVR) map has been delayed, limiting landholders' ability to determine if their plans for clearing are lawful.
OEH has applied significant effort in developing a native vegetation regulatory map to guide landholders on which land they can and can’t clear without approval. However, in November 2016 the then Minister for Primary Industries advised Parliament that the two largest land categories of the NVR map will not come into effect until the relevant Ministers are satisfied stakeholders have sufficient confidence in the maps’ accuracy. Not releasing the map has made it harder for landholders to identify the portions of their land that are regulated and ensure they comply with land clearing rules. It has also limited OEH’s ability to consult on and improve the accuracy of the map.
There are significant delays in identifying unlawful clearing and few penalties imposed.
Unexplained land clearing can take over two years to identify and analyse, making it difficult to minimise environmental harm or gather evidence to prosecute unlawful clearing. Despite around 1,000 instances of unexplained clearing identified by OEH and over 500 reports to the environmental hotline each year, with around 300 investigations in progress at any one time, there are only two to three prosecutions, three to five remediation orders and around ten penalty notices issued each year for unlawful clearing. Further, OEH is yet to commence any prosecutions under the current legislation which commenced in August 2017.
Land clearing and private land conservation investment have both increased.
Clearing of native vegetation has increased in recent years. At the same time, the government is also investing in properties with high environmental value with a focus on improving the mix of endangered ecological communities conserved in perpetuity. Processes are in place for identifying and prioritising areas of land for investment but the funding provided to each region is not always consistent with these priorities. 

Local Land Services (LLS) is responsible for processing notifications and issuing certificates to landholders for managing the thinning or clearing of native vegetation on rural land through the ‘Land Management (Native Vegetation) Code 2018’ (the Code). This work includes monitoring and reporting on the implementation of the Code, including the establishment and management of set asides.

OEH is responsible for compliance and enforcement in relation to unlawful land clearing. It is also responsible for producing the NVR map, designed to show landholders where land clearing can occur without approval, where approval is required, and where land clearing is not permitted. Post 1 July 2019, under machinery of government changes, OEH will be abolished and its activities relevant to this audit will be moved to the new Department of Planning, Industry and Environment.

Appendix one - Response from agencies

Appendix two - Authorisations for thinning and clearing, and restoration initiatives under the Native Vegetation Act 2003

Appendix three - About the audit

Appendix four - Performance auditing

 

Parliamentary Reference: Report number #324 - released 27 June 2019

Copyright reserved by the Audit Office of New South Wales. All rights reserved. No part of this publication may be reproduced without prior consent of the Audit Office of New South Wales. The Audit Office does not accept responsibility for loss or damage suffered by any person acting on or refraining from action as a result of any of this material.

Published

Actions for Contracting non-government organisations

Contracting non-government organisations

Community Services
Compliance
Fraud
Management and administration
Procurement
Regulation
Service delivery

This report found the Department of Family and Community Services (FACS) needs to do more to demonstrate it is effectively and efficiently contracting NGOs to deliver community services in the Permanency Support Program (a component of out-of-home-care services) and Specialist Homelessness Services. It notes that FACS is moving to an outcomes-based commissioning model and recommends this be escalated consistent with government policy.

Government agencies, such as the Department of Family and Community Services (FACS), are increasingly contracting non-government organisations (NGOs) to deliver human services in New South Wales. In doing so, agencies are responsible for ensuring these services are achieving expected outcomes. Since the introduction of the Commissioning and Contestability Policy in 2016, all NSW Government agencies are expected to include plans for customer and community outcomes and look for ways to use contestability to raise standards.

Two of the areas receiving the greatest funding from FACS are the Permanency Support Program and Specialist Homelessness Services. In the financial year 2017–18, nearly 500 organisations received $784 million for out-of-home care programs, including the Permanency Support Program. Across New South Wales, specialist homelessness providers assist more than 54,000 people each year and in the financial year 2017–18, 145 organisations received $243 million for providing short term accommodation and homelessness support, including Specialist Homelessness Services.

In the financial year 2017–18, FACS entered into 230 contracts for out-of-home care, of which 49 were for the Permanency Support Program, representing $322 million. FACS also entered into 157 contracts for the provision of Specialist Homelessness Services which totalled $170 million. We reviewed the Permanency Support Program and Specialist Homelessness Services for this audit.

This audit assessed how effectively and efficiently FACS contracts NGOs to deliver community services. The audit could not assess how NGOs used the funds they received from FACS as the Audit Office does not have a mandate that could provide direct assurance that NGOs are using government funds effectively.

Conclusion
FACS cannot demonstrate it is effectively and efficiently contracting NGOs to deliver community services because it does not always use open tenders to test the market when contracting NGOs, and does not collect adequate performance data to ensure safe and quality services are being provided. While there are some valid reasons for using restricted tenders, it means that new service providers are excluded from consideration - limiting contestability. In the service delivery areas we assessed, FACS does not measure client outcomes as it has not yet moved to outcomes-based contracts. 
FACS' procurement approach sometimes restricts the selection of NGOs for the Permanency Support Program and Specialist Homelessness Services
FACS has a procurement policy and plan which it follows when contracting NGOs for the provision of human services. This includes the option to use restricted tenders, which FACS sometimes uses rather than opening the process to the market. The use of restricted tenders is consistent with its procurement plan where there is a limited number of possible providers and the services are highly specialised. However, this approach perpetuates existing arrangements and makes it very difficult for new service providers to enter the market. The recontracting of existing providers means FACS may miss the opportunity to benchmark existing providers against the whole market. 
FACS does not effectively use client data to monitor the performance of NGOs funded under the Permanency Support Program and Specialist Homelessness Services
FACS' contract management staff monitor individual NGO performance including safety, quality of services and compliance with contract requirements. Although FACS does provide training materials on its intranet, FACS does not provide these staff with sufficient training, support or guidance to monitor NGO performance efficiently or effectively. FACS also requires NGOs to self-report their financial performance and contract compliance annually. FACS verifies the accuracy of the financial data but conducts limited validation of client data reported by NGOs to verify its accuracy. Instead, FACS relies on contract management staff to identify errors or inaccurate reporting by NGOs.
FACS' ongoing monitoring of the performance of providers under the Permanency Support Program is particularly limited due to problems with timely data collection at the program level. This reduces FACS' ability to monitor and analyse NGO performance at the program level as it does not have access to ongoing performance data for monitoring service quality.
In the Specialist Homelessness Services program, FACS and NGOs both provide the data required for the National Minimum Data Set on homelessness and provide it to the Australian Institute of Health and Welfare, as they are required to do. However, this data is not used for NGO performance monitoring or management.
FACS does not yet track outcomes for clients of NGOs
FACS began to develop an approach to outcomes-based contracting in 2015. Despite this, none of the contracts we reviewed are using outcomes as a measure of success. Currently, NGOs are required to demonstrate their performance is consistent with the measures stipulated in their contracts as part of an annual check of their contract compliance and financial accounts. NGOs report against activity-based measures (Key Performance Indicators) and not outcomes.
FACS advises that the transition to outcomes-based contracting will be made with the new rounds of funding which will take place in 2020–2021 for Specialist Homelessness Services and 2023 for the Permanency Support Program. Once these contracts are in place, FACS can transition NGOs to outcomes based reporting.
Incomplete data limits FACS' effectiveness in continuous improvement for the Permanency Support Program and Specialist Homelessness Services
FACS has policies and procedures in place to learn from past experiences and use this to inform future contracting decisions. However, FACS has limited client data related to the Permanency Support Program which restricts the amount of continuous improvement it can undertake. In the Specialist Homelessness Support Program data is collected to inform routine contract management discussions with service providers but FACS is not using this data for continuous improvement. 

Appendix one – Response from agency

Appendix two – About the audit

Appendix three – Performance auditing

 

Parliamentary Reference: Report number #323 - released 26 June 2019

Copyright reserved by the Audit Office of New South Wales. All rights reserved. No part of this publication may be reproduced without prior consent of the Audit Office of New South Wales. The Audit Office does not accept responsibility for loss or damage suffered by any person acting on or refraining from action as a result of any of this material.

Published

Actions for Managing Antisocial behaviour in public housing

Managing Antisocial behaviour in public housing

Community Services
Asset valuation
Infrastructure
Regulation
Service delivery
Workforce and capability

The Department of Family and Community Services (FACS) has not adequately supported or resourced its staff to manage antisocial behaviour in public housing according to a report released today by the Deputy Auditor-General for New South Wales, Ian Goodwin. 

In recent decades, policy makers and legislators in Australian states and territories have developed and implemented initiatives to manage antisocial behaviour in public housing environments. All jurisdictions now have some form of legislation or policy to encourage public housing tenants to comply with rules and obligations of ‘good neighbourliness’. In November 2015, the NSW Parliament changed legislation to introduce a new approach to manage antisocial behaviour in public housing. This approach is commonly described as the ‘strikes’ approach. 

When introduced in the NSW Parliament, the ‘strikes’ approach was described as a means to:

  • improve the behaviour of a minority of tenants engaging in antisocial behaviour 
  • create better, safer communities for law abiding tenants, including those who are ageing and vulnerable.

FACS has a number of tasks as a landlord, including a responsibility to collect rent and organise housing maintenance. FACS also has a role to support tenants with complex needs and manage antisocial behaviour. These roles have some inherent tensions. The FACS antisocial behaviour management policy aims are: 

to balance the responsibilities of tenants, the rights of their neighbours in social housing, private residents and the broader community with the need to support tenants to sustain their public housing tenancies.

This audit assessed the efficiency and effectiveness of the ‘strikes’ approach to managing antisocial behaviour in public housing environments.

We examined whether:

  • the approach is being implemented as intended and leading to improved safety and security in social housing environments
  • FACS and its partner agencies have the capability and capacity to implement the approach
  • there are effective mechanisms to monitor, report and progressively improve the approach.
Conclusion

FACS has not adequately supported or resourced its staff to implement the antisocial behaviour policy. FACS antisocial behaviour data is incomplete and unreliable. Accordingly, there is insufficient data to determine the nature and extent of the problem and whether the implementation of the policy is leading to improved safety and security

FACS management of minor and moderate incidents of antisocial behaviour is poor. FACS has not dedicated sufficient training to equip frontline housing staff with the relevant skills to apply the antisocial behaviour management policy. At more than half of the housing offices we visited, staff had not been trained to:

  • conduct effective interviews to determine whether an antisocial behaviour complaint can be substantiated

  • de escalate conflict and manage complex behaviours when required

  • properly manage the safety of staff and tenants

  • establish information sharing arrangements with police

  • collect evidence that meets requirements at the NSW Civil and Administrative Tribunal

  • record and manage antisocial behaviour incidents using the information management system HOMES ASB.

When frontline housing staff are informed about serious and severe illegal antisocial behaviour incidents, they generally refer them to the FACS Legal Division. Staff in the Legal Division are trained and proficient in managing antisocial behaviour in compliance with the policy and therefore, the more serious incidents are managed effectively using HOMES ASB. 


FACS provides housing services to most remote townships via outreach visits from the Dubbo office. In remote townships, the policy is not being fully implemented due to insufficient frontline housing staff. There is very limited knowledge of the policy in these areas and FACS data shows few recorded antisocial behaviour incidents in remote regions. 


The FACS information management system (HOMES ASB) is poorly designed and has significant functional limitations that impede the ability of staff to record and manage antisocial behaviour. Staff at most of the housing offices we visited were unable to accurately record antisocial behaviour matters in HOMES ASB, making the data incorrect and unreliable.

Published

Actions for Regulation of water pollution in drinking water catchments and illegal disposal of solid waste

Regulation of water pollution in drinking water catchments and illegal disposal of solid waste

Environment
Compliance
Internal controls and governance
Management and administration
Regulation
Risk

There are important gaps in how the Environmental Protection Authority (EPA) implements its regulatory framework for water pollution in drinking water catchments and illegal solid waste disposal. This limits the effectiveness of its regulatory responses, according to a report released today by the Auditor-General for New South Wales, Margaret Crawford.

The NSW Environment Protection Authority (the EPA) is the State’s primary environmental regulator. The EPA regulates waste and water pollution under the Protection of the Environment Operations Act 1997 (the Act) through its licensing, monitoring, regulation and enforcement activities. The community should be able to rely on the effectiveness of this regulation to protect the environment and human health. The EPA has regulatory responsibility for more significant and specific activities which can potentially harm the environment.

Activities regulated by the EPA include manufacturing, chemical production, electricity generation, mining, waste management, livestock processing, mineral processing, sewerage treatment, and road construction. For these activities, the operator must have an EPA issued environment protection licence (licence). Licences have conditions attached which may limit the amount and concentrations of substances the activity may produce and discharge into the environment. Conditions also require the licensee to report on its licensed activities.

This audit assessed the effectiveness of the EPA’s regulatory response to water pollution in drinking water catchments and illegal solid waste disposal. The findings and recommendations of this review can be reasonably applied to the EPA’s other regulatory functions, as the areas we examined were indicative of how the EPA regulates all pollution types and incidents.

 
Conclusion
There are important gaps in how the EPA implements its regulatory framework for water pollution in drinking water catchments and illegal solid waste disposal which limit the effectiveness of its regulatory response. The EPA uses a risk-based regulatory framework that has elements consistent with the NSW Government Guidance for regulators to implement outcomes and risk-based regulation. However, the EPA did not demonstrate that it has established reliable practices to accurately and consistently detect the risk of non compliances by licensees, and apply consistent regulatory actions. This may expose the risk of harm to the environment and human health.
The EPA also could not demonstrate that it has effective governance and oversight of its regulatory operations. The EPA operates in a complex regulatory environment where its regional offices have broad discretions for how they operate. The EPA has not balanced this devolved structure with an effective governance approach that includes appropriate internal controls to monitor the consistency or quality of its regulatory activities. It also does not have an effective performance framework that sets relevant performance expectations and outcome-based key performance indicators (KPIs) for its regional offices. 
These deficiencies mean that the EPA cannot be confident that it conducts compliance and enforcement activities consistently across the State and that licensees are complying with their licence conditions or the Act.
The EPA's reporting on environmental and regulatory outcomes is limited and most of the data it uses is self reported by industry. It has not set outcome-based key result areas to assess performance and trends over time. 
The EPA uses a risk-based regulatory framework for water pollution and illegal solid waste disposal but there are important gaps in implementation that reduce its effectiveness.
Elements of the EPA’s risk-based regulatory framework for water pollution and illegal solid waste disposal are consistent with the NSW Government Guidance for regulators to implement outcomes and risk-based regulation. There are important gaps in how the EPA implements its risk-based approach that limit the effectiveness of its regulatory response. The EPA could not demonstrate that it effectively regulates licensees because it has not established reliable practices that accurately and consistently detect licence non compliances or breaches of the Act and enforce regulatory actions.
The EPA lacks effective governance arrangements to support its devolved regional structure. The EPA's performance framework has limited and inconclusive reporting on regional performance to the EPA’s Chief Executive Officer or to the EPA Board. The EPA cannot assure that it is conducting its regulatory responsibilities effectively and efficiently. 
The EPA does not consistently evaluate its regulatory approach to ensure it is effective and efficient. For example, there are no set requirements for how EPA officers conduct mandatory site inspections, which means that there is a risk that officers are not detecting all breaches or non-compliances. The inconsistent approach also means that the EPA cannot rely on the data it collects from these site inspections to understand whether its regulatory response is effective and efficient. In addition, where the EPA identifies instances of non compliance or breaches, it does not apply all available regulatory actions to encourage compliance.
The EPA also does not have a systematic approach to validate self-reported information in licensees’ annual returns, despite the data being used to assess administrative fees payable to the EPA and its regulatory response to non-compliances. 
The EPA does not use performance frameworks to monitor the consistency or quality of work conducted across the State. The EPA has also failed to provide effective guidance for its staff. Many of its policies and procedures are out-dated, inconsistent, hard to access, or not mandated.
Recommendations
By 31 December 2018, to improve governance and oversight, the EPA should:
1. implement a more effective performance framework with regular reports to the Chief Executive Officer and to the EPA Board on outcomes-based key result areas that assess its environmental and regulatory performance and trends over time
By 30 June 2019, to improve consistency in its practices, the EPA should:
2. progressively update and make accessible its policies and procedures for regulatory operations, and mandate procedures where necessary to ensure consistent application
3. implement internal controls to monitor the consistency and quality of its regulatory operations. 
The EPA does not apply a consistent approach to setting licence conditions for discharges to water.
The requirements for setting licence conditions for water pollution are complex and require technical and scientific expertise. In August 2016, the EPA approved guidance developed by its technical experts in the Water Technical Advisory Unit to assist its regional staff. However, the EPA did not mandate the use of the guidance until mid-April 2018. Up until then, the EPA had left discretion to regional offices to decide what guidance their staff use. This meant that practices have differed across the organisation. The EPA is yet to conduct training for staff to ensure they consistently apply the 2016 guidance.
The EPA has not implemented any appropriate internal controls or quality assurance process to monitor the consistency or quality of licence conditions set by its officers across the State. This is not consistent with good regulatory practice.
The triennial 2016 audit of the Sydney drinking water catchment report highlighted that Lake Burragorang has experienced worsening water quality over the past 20 years from increased salinity levels. The salinity levels were nearly twice as high as in other storages in the Sydney drinking water catchment. The report recommended that the source and implication of the increased salinity levels be investigated. The report did not propose which public authority should carry out such an investigation. 
To date, no NSW Government agency has addressed the report's recommendation. There are three public authorities, the EPA, DPE and WaterNSW that are responsible for regulating activities that impact on water quality in the Sydney drinking water catchment, which includes Lake Burragorang. 
Recommendation
By 30 June 2019, to address worsening water quality in Lake Burragorang, the EPA should:
4. (a) review the impact of its licensed activities on water quality in Lake Burragorang, and
  (b) develop strategies relating to its licensed activities (in consultation with other relevant NSW Government agencies) to improve and maintain the lake's water quality.
The EPA’s risk-based approach to monitoring compliance of licensees has limited effectiveness. 
The EPA tailors its compliance monitoring approach based on the performance of licensees. This means that licensees that perform better have a lower administrative fee and fewer mandatory site inspections. 
However, this approach relies on information that is not complete or accurate. Sources of information include licensees’ annual returns, EPA site inspections and compliance audits, and pollution reports from the public. 
Licensees report annually to the EPA on their performance, including compliance against their licence conditions. The Act contains significant financial penalties if licensees provide false and misleading information in their annual returns. However, the EPA does not systematically or consistently validate information self-reported by licensees, or consistently apply regulatory actions if it discovers non-compliance. 
Self-reported compliance data is used in part to assess a licensed premises’ overall environmental risk level, which underpins the calculation of the administrative fee, the EPA’s site inspection frequency, and the licensee’s exposure to regulatory actions. It is also used to assess the load-based licence fee that the licensee pays.
The EPA has set minimum mandatory site inspection frequencies for licensed premises based on its assessed overall risk level. This is a key tool to detect non-compliance or breaches of the Act. However, the EPA has not issued a policy or procedures that define what these mandatory inspections should cover and how they are to be conducted. We found variations in how the EPA officers in the offices we visited conducted these inspections. The inconsistent approach means that the EPA does not have complete and accurate information of licensees’ compliance. The inconsistent approach also means that the EPA is not effectively identifying all non-compliances for it to consider applying appropriate regulatory actions.
The EPA also receives reports of pollution incidents from the public that may indicate non-compliance. However, the EPA has not set expected time frames within which it expects its officers to investigate pollution incidents. The EPA regional offices decide what to investigate and timeframes. The EPA does not measure regional performance regarding timeframes. 
The few compliance audits the EPA conducts annually are effective in identifying licence non-compliances and breaches of the Act. However, the EPA does not have a policy or required procedures for its regulatory officers to consistently apply appropriate regulatory actions in response to compliance audit findings. 
The EPA has not implemented any effective internal controls or quality assurance process to check the consistency or quality of how its regulatory officers monitor compliance across the State. This is not consistent with good regulatory practice.
Recommendations
To improve compliance monitoring, the EPA should implement procedures to:
5. by 30 June 2019, validate self-reported information, eliminate hardcopy submissions and require licensees to report on their breaches of the Act and associated regulations in their annual returns
6. by 31 December 2018, conduct mandatory site inspections under the risk-based licensing scheme to assess compliance with all regulatory requirements and licence conditions.
 
The EPA cannot assure that its regulatory enforcement approach is fully effective.
The EPA’s compliance policy and prosecution guidelines have a large number of available regulatory actions and factors which should be taken into account when selecting an appropriate regulatory response. The extensive legislation determining the EPA’s regulatory activities, and the devolved regional structure the EPA has adopted in delivering its compliance and regulatory functions, increases the risk of inconsistent compliance decisions and regulatory responses. A good regulatory framework needs a consistent approach to enforcement to incentivise compliance. 
The EPA has not balanced this devolved regional structure with appropriate governance arrangements to give it assurance that its regulatory officers apply a consistent approach to enforcement.
The EPA has not issued standard procedures to ensure consistent non-court enforcement action for breaches of the Act or non-compliance with licence conditions. Given our finding that the EPA does not effectively detect breaches and non-compliances, there is a risk that it is not applying appropriate regulatory actions for many breaches and non-compliances.
A recent EPA compliance audit identified significant non-compliances with incident management plan requirements. However, the EPA has not applied regulatory actions for making false statements on annual returns for those licensees that certified their plans complied with such requirements. The EPA also has not applied available regulatory actions for the non-compliances which led to the false or misleading statements.
Recommendation
By 31 December 2018 to improve enforcement, the EPA should:
7. Implement procedures to systematically assess non-compliances with licence conditions and breaches of the Act and to implement appropriate and consistent regulatory actions.
The EPA has implemented the actions listed in the NSW Illegal Dumping Strategy 2014–16. To date, the EPA has also implemented four of the six recommendations made by the ICAC on EPA's oversight of Regional Illegal Dumping Squads.
The EPA did not achieve the NSW Illegal Dumping Strategy 2014–16 target of a 30 per cent reduction in instances of large scale illegal dumping in Sydney, the Illawarra, Hunter and Central Coast from 2011 levels. 
In the reporting period, the incidences of large scale illegal dumping more than doubled. The EPA advised that this increase may be the result of greater public awareness and reporting rather than increased illegal dumping activity. 
By June 2018, the EPA is due to implement one outstanding recommendation made by the ICAC but has not set a time for the other outstanding recommendation.  

Published

Actions for Helping older people access a residential aged care facility

Helping older people access a residential aged care facility

Health
Community Services
Compliance
Internal controls and governance
Management and administration
Risk
Service delivery
Shared services and collaboration
Workforce and capability

Assessment processes for older people needing to go to an Residential Aged Care Facility (RACF) vary depending on the processes of the Aged Care Assessement Teams (ACAT) they see and whether or not they are in hospital. The data collected on ACAT performance was significantly revised during 2004 making comparisons with subsequent years problematic. ACATs have more responsibilities than assessing older people for residential care. It is not clear whether they have sufficient resources for this additional workload.

 

Parliamentary reference - Report number #160 - released 5 December 2006

Published

Actions for Environmental impact assessment of major projects in NSW

Environmental impact assessment of major projects in NSW

Environment
Management and administration
Regulation
Service delivery

The Audit Office is of the opinion that the basis for environmental impact assessment of major projects in NSW is sound. The key concept of 'environmental significance' is well defined. The system is closely specified. The Department of Urban Affairs and Planning (DUAP) leads a whole-of-government approach to environmental impact assessment and its assessments are comprehensive. However, the Audit Office considers that there are opportunities for improvement by more actively managing the participants and the performance of the environmental impact assessment system. DUAP needs to strengthen its internal documentation and must ensure the public have greater involvement.

 

Parliamentary reference - Report number #92 - released 28 November 2001

Published

Actions for Controlling and reducing pollution from industry

Controlling and reducing pollution from industry

Planning
Environment
Compliance
Management and administration
Regulation

The regulatory framework introduced under the Protection of the Environment Operations Act 1997, along with other initiatives progressively being implemented by the Environment Protection Authority (EPA), should enhance the overall effectiveness of environment protection in NSW. The Audit Office is of the opinion that the framework is consistent with best practice and once fully implemented, should contribute to the achievement of further improvements in the environmental performance of industry.

However while the legislative framework supports best practice in regulation and enforcement, there are a number of issues which limit the effectiveness of the reforms. Some of the problems, such as the quality of licences and the effectiveness of compliance activities, have been identified by the EPA and may be addressed through recent initiatives.

 

Parliamentary reference - Report number #82 - released 18 April 2001