I am very happy to announce our first on-the ground biodiversity offset example that is the result of some intense work and exchange. It describes a species offset for the Koala in Queensland (Australia). While we have developed the structure together, Alan Key from Australian consultancy Earthtrade, has provided all the content and illustrations. Many thanks Alan for your time and commitment. This is a valuable resource! Hopefully, others will follow. Please get back with any ideas for examples that could be presented here on the Biodiversity Offsets Blog (for more information see also my previous post). I am happy to support longer or shorter examples. Don’t hesitate to comment on the suggested structure and please do also get in touch if you are missing an important issue that you would like to be included in this (and possible other) example! Your feedback is greatly appreciated! Please leave a reply below!
Summary
Following, the case of an Australian biodiversity offset is presented, which was triggered by the clearing of Koala habitat at the impact or project site, i.e. a species offset for the Koala which is listed as an endangered animal of national significance under the EPBC Act. The developer was conditioned to compensate for the loss of 67.14 ha of habitat critical to the survival of the Koala, by securing and managing a minimum of 161.11 ha of Koala habitat. The details were specified in an Offset Area Management Plan (OAMP). The offset is a legal arrangement between three parties being the Australian Government represented by the Department of Environment (DoE), the Developer and, in this instance, a private landholder on whose property the offset will be secured in perpetuity. A consultancy supports and carries out the planning of the offset. The OAMP is the legal agreement between the Australian Government and the developer. The landholder is bound by a legal contract with the developer with regards the monetary payment amount and schedule, for implementing the agreed management actions within the OAMP, which is bound legally to the property and is therefore binding on current and future owners.
In this case, the landholder recognized the property needed rehabilitating due to the clearing of timber and overgrazing of the property over an extended period resulting in a degraded ecosystem, weed invasion and habitat degradation. A baseline assessment of the canopy, shrub and ground layers of the open Eucalypt forest ecosystem (by using the Bio-condition Methodology as developed by the Queensland Herbarium) found a condition of medium with regards the quality of the forest. The overall goal is therefor to improve the condition to a good condition along with increasing the number of habitat and forage trees for the Koala population. The management regime proposed for the offset area is to enhance the level of protection afforded to existing koala habitat through exclusion of land management practices that are incompatible to achieving a net gain in koala habitat quality. Further, key threatening processes which could interfere with the recovery of koala as described by the Draft EPBC Act referral guidelines for the vulnerable koala are to be actively managed to result in a net gain in koala habitat quality in time.
With a through process, understanding of the technical, legal and financial processes and variables and the determination from the start of the process as to the outcomes required by each of the parties involved, offsets can be negotiated and secured within a reasonable period of time and be legally and financially responsible to the parties involved.
Outline
- Country/location
- Description of the national context (regulation, policy, market)
- Involved parties/responsible
- Motivations/incentives
- Timeframe
- Size
- Brief description of the environmental baseline and the impacts
- Surrogate of the offset
- Goal of the offset
- Brief description of the offset measures
- Impact-Offset-Relation
- Outcome and lessons learned
1. Country/location
South East Queensland, Australia
2. Description of the national context (regulation, policy, market)
a) General description
Both species and ecosystems are a regular requirement for offsetting impacts in Australia. The Australian Government protects both “Threatened Ecological Communities” and “Threatened Species” at the national level. These are ecosystems or species that are threatened at the national scale. The mechanism for this is the Environmental Protection and Biodiversity Conservation Act 1999 (EPBC Act).
Additionally, each state in Australia has their list of “triggers” as to what needs protection at the state level – so again, a list of threatened ecosystems and species. These are protected under a number of different legislative triggers.
b) Case specific description: which legal, procedural or other conditions apply?
In this case, the offset was triggered by the clearing of Koala habitat at the impact or project site. The impact triggered a requirement for an offset for impacts to habitat critical to the Koala which is listed as an endangered animal of national significance under the EPBC Act. The developer was conditioned to provide the following:
- To compensate for the loss of 67.14 ha of habitat critical to the survival of the Koala, the approval holder must secure and manage as Koala habitat, a minimum of 161.11 ha of Koala habitat as shown as “Proposed Offset Area”.
- To compensate for the loss of 67.14 ha of Koala habitat, the approval holder must submit an Offset Area Management Plan (OAMP) to the Minister at least two months prior to commencement.
- The OAMP must include, but not be limited to:
- location of the habitat offset area including maps in electronic Geographic Information System (GIS) format
- details of how the offset site has been or will be legally secured within 2 years of commencement to ensure its long-term protection
- details of how the offset site adequately compensates for residual significant impacts to the Koala in accordance with the EPBC Act Offsets Policy
- a detailed baseline description of the offset site, including surveys undertaken, condition of existing Koala habitat, connectivity with other habitat areas and biodiversity corridors
- management measures to improve Koala habitat quality over time
- specific goals and associated timeframes for habitat management and improvement measures with criteria for assessing the success of habitat management measures and corrective measures to be implemented if criteria are not met
- a monitoring program for the offset site suitable to measure the success of the management measures against stated performance criteria including monitoring locations, parameters and timing
- a description of the potential risks to the successful implementation of the OAMP, and details of measures that will be implemented to mitigate these risks
- an outline of how compliance with the OAMP will be reported
- details of qualifications and experience of persons responsible for undertaking monitoring, review, and implementation of the OAMP
- The approval holder must not commence the action until the OAMP has been approved by the Minister in writing. The approved OAMP must be implemented.
- The most recent approved versions of the plans described in these conditions must remain accessible to the public on the website of the approval holder for the duration of the Approval.
- Within ten days after the commencement of the action, the approval holder must advise the Department in writing of the actual date of commencement.
- The approval holder must maintain accurate records substantiating all activities associated with or relevant to the conditions of approval, including measures taken to implement the plans required by this approval, and make them available upon request to the Department. Such records may be subject to audit by the Department or an independent auditor in accordance with section 458 of the EPBC Act, or used to verify compliance with the conditions of approval. Summaries of audits will be posted on the Department’s website. The results of audits may also be publicized through the general media.
- Any potential or suspected non-compliance with these conditions of approval must be reported to the Department in writing within 48 hours of the approval holder becoming aware of the potential or suspected non-compliance. Within three months of every 12 month anniversary of the commencement of the action, the approval holder must publish a report on their website addressing compliance with each of the conditions of this approval, including implementation of any plans as specified in the conditions. Documentary evidence providing proof of the date of publication must be provided to the Department at the same time as the compliance report is published.
- Upon the direction of the Minister, the approval holder must ensure that an independent audit of compliance with the conditions of approval is conducted and a report submitted to the Minister. The independent auditor and audit criteria must be approved by the Minister prior to the commencement of the audit. The audit report must address the criteria to the satisfaction of the Minister.
3. Involved parties/responsible
Government | NGO | Business | Consultants | Academia | Landowners |
x |
x | x | x |
The offset is a legal arrangement between three parties being the Australian Government represented by the Department of Environment (DoE), the Developer and, in this instance, a private landholder on whose property the offset will be secured. A consultancy supports and carries out the planning of the offset. The offset is also secured on the property by a legally binding instrument administrated by the Queensland (State) Government by the Land Act 1994 and the Land Titles Act 1994.
4. Motivations/incentives
Motivations for landholders vary. Some landholders use the provision of offsets as another service that they can gain an income from much as grazing and cropping returns. Some landholders use offsets as a means of rehabilitating land that has been over cleared or is degraded in some way. Other landholders like to use offsets to protect the land from future development and to rehabilitate and or improve the condition of the ecosystem that is present. All are legitimate approaches to the provision of offsets by landholders.
In this case, the landholder recognized the property needed rehabilitating due to the clearing of timber and overgrazing of the property over an extended period resulting in a degraded ecosystem, weed invasion and habitat degradation. The use of the property for offsets has enabled the landholder to start improving the condition and rehabilitating the ecosystem and habitat with the contract between the landholder and the developer providing the money necessary for this. The land will be secured in perpetuity to prevent the risk of loss in the future.
5. Timeframe
started | planning | implementation | completed |
2014 | July – November 2014 | January 2015 | 2025 |
6. Size
161 ha
7. Brief description of the environmental baseline and the impacts
The open Eucalypt Forest was assessed and had a condition of medium with regards the quality of the forest. The overall goal is to improve the condition to a good condition along with increasing the number of habitat and forage trees for the Koala population. This baseline data collection included the assessment of the canopy, shrub and ground layers of the ecosystem by using the Bio-condition Methodology as developed by the Queensland Herbarium. https://www.qld.gov.au/environment/plants-animals/biodiversity/biocondition/
With reference to the Koala, there were a number of potential threats determined for the site.
- Habitat loss from forestry
- Reduction in habitat and forage tree generation due to fire and grazing
- Predation from wild dogs and other feral animals
- Vehicle strike
Each of these threats was addressed in the management plan (OAMP).
8. Surrogate of the offset
species | Habitat/biotope types | Whole ecosystems and its features |
Koala is the single species targeted for the offset – i.e. the offset is to provide increased habitat and forage trees for the Koala population |
9. Goal of the offset
The management regime proposed for the offset area is to enhance the level of protection afforded to existing koala habitat through exclusion of land management practices that are incompatible to achieving a net gain in koala habitat quality. Further, key threatening processes which could interfere with the recovery of koala as described by the Draft EPBC Act referral guidelines for the vulnerable koala (combined populations of Queensland, New South Wales and the Australian Capital Territory) (DoE, 2013) are to be actively managed to result in a net gain in koala habitat quality in time as articulated by the EPBC Act Environmental Offsets Policy (DoE, 2012) and demonstrated via the Offsets Assessment Guide (DoE, 2012).
10. Brief description of the offset measures
a) Technical-functional
The threats were addressed by the implementation in the management plan of the following key management actions:
- The exclusion of forestry operations within the offset area
- The exclusion of any mechanical or chemical clearing of native vegetation
- Allowing the shrub layer to regenerate via the control of weeds and the use of an ecological fire regime (note that fire is an important part of ecosystem development and function in Australia)
- Fire management plan: including the installation and maintenance of fire control lines, reduced fuel loads via grazing as above and the use of fire at appropriate times for ecological burns. This would usually occur during the cooler months of the year to reduce fuel loads of grass and other dry matter and to encourage the germination of natural tree species
- Weed management plan
- Management of grazing to a limited number of cattle and a limited grazing period only in the circumstances where a reduction in grass was required to minimize the risk of a wild fire
- A pest animal control program, and
- The erection of signage at the entrance to the property with regards the presence of Koala
b) Legal-procedural
The conditions of the development, agreed to between the regulator (DoE) and the developer, require that the agreed Offset Management Plan be implemented. This is the legal agreement between the Australian Government and the developer for what needs to occur for the development to proceed.
The landholder is bound by a legal contract with the developer with regards the monetary payment amount and schedule, for implementing the agreed management actions within the Offset Area Management Plan. This Offset Area Management Plan is bound legally to the property and is therefore binding on current and future owners. Property law in Australia is administered by State Governments. Compliance with regards the implementation of the management plan can therefore be enforced via 3 different legal mechanisms:
- Conditions of development Approval,
- the financial contract between the developer and the landowner,
- and the Offset Management Plan as it is bound to the property.
With regards the financial structure, the money negotiated for managing the offset, in this instance, is held by the landholder in Trust.
Compliance is undertaken by a compliance regime agreed between the 3 parties, and is undertaken by an independent third party to ensure that the Offset Area Management Plan is implemented. This gives confidence to both the regulator and the developer that the agreed management actions are being undertaken and that the offset is progressively achieving its objectives.
11. Impact-Offset-Relation
a) What kinds of impacts/development projects is the offset related to?
The 161ha offset was for the clearing of 67ha of Koala habitat for development. Please see the Referral Guidelines here: http://www.environment.gov.au/biodiversity/threatened/publications/epbc-act-referral-guidelines-vulnerable-koala
b) Loss-Gain calculations: How are impact and offset measured and weighed against each other?
The area of the offset required was calculated using the EPBC Offset Assessment Guide and the “How to use the Offset Assessment Guidelines” which gives guidance to the input figures for the spreadsheet, see more here: http://www.environment.gov.au/epbc/publications/epbc-act-environmental-offsets-policy
12. Outcome and lessons learned
A through process is required and good communication between all the people involved.
A single point of contact for each party involved is essential to ensure that there is a single message being communicated and that there is no delay or confusion in correction to the documentation. This is essential as the documents “cross link” and a change in one document will necessitate the change in a number of other documents. Therefore, document control is paramount along with version control as the documents are reviewed by several parties.
The other critical point is an understood outcome and parameters of each of the parties to be understood and considered during the negotiations for all of the parties. This point is critical as any misunderstanding is exacerbated because of the complexity and as the process is new, the uncertainty of the outcome. This is critical to manage when there are constant changes to management plans as the document is reviewed by the different parties. To illustrate, a change of a management action requested by the regulator, needs to be acceptable to the landholder and of course be practically implementable on the ground, and also to be able to be legally defended and to be measured for compliance purposes.
With a through process, understanding of the technical, legal and financial processes and variables and the determination from the start of the process as to the outcomes required by each of the parties involved, offsets can be negotiated and secured within a reasonable period of time and be legally and financially responsible to the parties involved.
Perhaps I missed it, but I am wondering about the location of the offset site vis-a-vis the Koala habitat lost due to development. Is the offset site contiguous with or at least proximal to the destroyed habitat. Does the location of the offset site take into account the landscape context principle of biodiversity offsetting, ensuring that there is no net loss of Koala habitat at the landscape level.
Good afternoon Divya,
My apologies in the delayed reply.
The offset site is in a different vegetation corridor as the impact site, and is 20km from that site. The Koala population is the same on both sites, ie they Koala are transient throughout a larger regional area. The offset adjoins a corridor which is circa 563.5km² or 56,350 hectares in size and about 60km long. The impact site is adjacent to another area of vegetation thus allowing individuals to move during the clearing of the vegetation on the construction site. A condition of the developments Approval required that an ecologist was on site during clearing and that the clearing was to be undertaken progressively to allow for any Koalas present to move. If any trees that were to be cleared were observed to have Koala in them, they were required to be left standing until the animal had time to move. The offset calculator does take into consideration the landscape context and scale of the impact and offset site to ensure that there is no net loss of habitat.
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