Archive for the ‘Ecosystem services’ Category

TEEB on TED

Friday, December 30th, 2011

On TED, Pavan Sukhdev – who lead the TEEB initiative – explains why we need to “value nature” in order to manage it sustainably.

He ends his talk on the suggestion to focus efforts on “green” and “blue” carbon as part of climate change mitigation. Green and blue carbon is the carbon stored in terrestrial and marine ecosystems respectively.

Pavan Sukhdev tells us that he strongly supports the REDD+ mechanisms, whereby emitting countries fund projects in forested countries that avoid deforestation and/or forest degradation. There is a lot of potential there for synergies between carbon sequestration goals and the continued provision of other ecosystem services (and biodiversity).

Concerning blue carbon, it is interesting to note how he explains that we, collectively, have made the ethical choice to lose coral reefs through unmitigated climate change. It was probably an implicit choice, but it is quite revealing that Pavan Sukhdev and TEEB recognize that there are critical thresholds of biodiversity and ecosystem service loss. Those thresholds can be ecological (to avoid extinction or complete loss) or social but they certainly define the boundaries of our future life support system. Good debates to be had there…

New books on the shelves

Friday, September 23rd, 2011

Several new books on the topic of market-based instruments for nature conservation were recently published (or will soon be). Expect so see reviews here soon.

The first book is by Royal Gardner, a law specialist, who has worked on wetland mitigation in the USA. Entitled Lawyers, Swamps, and Money: U.S. Wetland Law, Policy, and Politics the book provides an in-depth look into the inner workings of the wetland mitigation “industry” and especially its governance. You can take a look on Amazon.

The second book is by Ece Ozdemioglu of the British consultancy EFTEC. It will provide guidance on ecological equivalency methods that can be applied to biodiversity offsets and payment for ecosystem service schemes. Here is what her personal page on the EFTEC website says:

Her next book (with Josh Lipton and David Chapman, forthcoming in 2011 by Springer) will be on the use of resource equivalency (including economic valuation) methods for assessing environmental damage and liability and selecting the appropriate compensation measures. This will help implement European Directives of Habitats, Wild Birds and Environmental Liability as well as input to new policy instruments like biodiversity offsetting, payments for ecosystem services and habitat banking.

According to Open Trolley, the expected publication date is September 29th, with the title “Equivalency Methods for Environmental Liability in the European Union: Assessing Damage and Compensation Under the Environmental Liability Directive”. Most of the contents probably reflect EFTEC’s work as part of the EU funded REMEDE project which provides lots of interesting insights.

If you haven’t read it yet, you can still have a look at Carroll, Fox and Bayon’s book on conservation and biodiversity banking published by EarthScan.

A first step towards ecosystem service-based certification in forestry

Friday, July 8th, 2011

On July 1st, the Forest Stewardship Council, which certifies timber products worldwide, acknowledged that forest certification should recognise “social issues and the role of ecosystem services” (motion 1.1.)

The FSC does not detail how it might go about including these issues in the certification process but it certainly raises the prospects for expanding the proper assessment and monitoring of ecosystem services in production forests worldwide.

The UK national ecosystem assessment is out!

Wednesday, June 8th, 2011

The UK National Ecosystem Assessment was finalized and is being published on-line.

Started mid 2009, the assessment led by Robert Watson and Steve Albon, it is the first analysis of the UK’s natural environment in terms of the benefits it provides to society and continuing economic prosperity.

The key findings of the assessment were made available on June 2nd (pdf here) while specific technical chapters will be made available through June.

Until then the 87 pages of the synthesis report should keep you busy! Below are some of the main points raised by the assessment:

The authors mention the need to increase food production while at the same time decreasing its negative effects on ecosystem services. In fact, the idea is to harness ecosystem services to actually increase production. This “sustainable intensification” is what the French call “ecological intensification”.

Reversing declines in ecosystem services will require the adoption of more resilient ways of managing ecosystems, and a better balance between production and other ecosystem services – one of the major challenges is to increase food production, but with a smaller environmental footprint through sustainable intensification.

Not surprisingly, the assessment also raises the issue of ecosystem services being undervalued in decision making and the suggested solution is to take into account the monetary and non monetary values of ecosystems in every-day decision making.

Contemporary economic and participatory techniques allow us to take into account the monetary and non-monetary values of a wide range of ecosystem services.

The assessment use six contrasting scenarios to explore alternative futures for ecosystem services in the UK.

The six scenarios used in the UK national ecosystem assessment

Choose yours!

It is also worth noticing that the assessment’s conceptual framework seems to focus on the “goods” that depend (at least in part) on ecosystem services as the linkage between ecosystems and human well-being. A more in-depth look into the figure below shows that in fact, the authors have grouped under the label “goods” all use and non-use, material and non-material benefits from ecosystems that have value for people.

The conceptual framework of the UK national ecosystem assessment

Ecosystem services and offsets in the EU biodiversity strategy

Wednesday, May 25th, 2011

Earlier this month, the European Commission published the European Union’s Biodiversity Strategy to 2020. It has received considerable comment in the press and on-line, in particular regarding the place taken by ecosystem services and the value of nature. BusinessGreen, EurActiv, the Ecosystem Marketplace and others have rejoiced in finding that the strategy explicitly mentions the incorporation of biodiversity and ecosystem services into decision-making through valuation, monitoring and reporting. While this is true, it must be made clear that most of the strategy actually focuses on setting biodiversity targets and developing (incl. funding) the corresponding monitoring and reporting schemes. Valuation issues are only mentioned in the strategy’s introductory section.

The document only makes a passing mention of offsets and PES schemes as mechanisms for involving the private sector in funding biodiversity conservation. As such, it is a bit of a stretch to say that the strategy endorses “species banking” (as did the Ecosystem Marketplace). In fact, it is strange that the key role of offsets in the Habitats directive (article 6.4) did not get mentioned in this context. The strategy does not mention the 2004 environmental liability directive which also includes offsets.

Targets set by the strategy include (1) the full implementation of the Birds (1979) and Habitats (1992) directives (i.e. improving the conservation status of twice the number of habitat types as are currently and 50% more for species), (2) maintaining and enhancing ecosystem services through the development of “green infrastructure” and the restoration of >15% of currently degraded ecosystems (no definition provided), (3) developing a adequate policy response to invasive species and (4) “stepping-up” the EU’s contribution averting global biodiversity loss (whatever that means apart from forking out aid…).

Interesting chapters in the document discuss interactions with existing policies and in particular the Common Agricultural Policy which will have to contribute to the first two targets : improving the conservation status of habitats and species and restoring degraded ecosystems. The forthcoming CAP will have considerable impact on biodiversity and Europe and a lot is certainly at play there. The document states that discussions are in progress for a framework directive aimed at preserving soil resources in the EU. That’s a lot of news to come…

The ideals of ecosystem service research

Thursday, March 3rd, 2011

Ralf Seppelt and his co-authors from the Helmholtz Centre for Environmental Research in Leipzig (Germany) recently published an interesting inquiry into how ecosystem service research is actually conducted (pdf available here). They draw conclusions on how it should be done.

They focused on ecosystem service studies at the regional scale, looking at 153 publications. Most studies focused on single ecosystem services (usually provisioning), using proxy-data (such as land-use or land-cover maps). Interestingly, the authors conclude that less than one third of the studies they reviewed provided a sound basis for their conclusions…

From their review, R. Seppelt and his co-authors suggest four key components for high quality ecosystem service research:

  • Establishing the biophysical basis for ecosystem service delivery
  • Analysing trade-offs between multiple ecosystem services, in a context of environmental change and ecosystem management decisions
  • Analysing off-site effects of ecosystem management decisions on ecosystem services
  • Involving stakeholders in identifying ecosystem services, ground-truthing conclusions and management options
  • They list key criteria on which to assess whether a particular ecosystem service study actually follows their suggested guidelines. Table 1 below is taken from their paper.

    Table 1 from Seppelt et al. (2011) in Journal of Applied Ecology

    The authors mention biophysical realism as a necessary criteria for ecosystem services studies to provide a sound basis for decision making. It could be argued that the same could apply to “socio-political” or “socio-economic” realism. Stakeholder involvement does not necessarily guarantee such realism, especially when stakeholders have very heterogeneous needs and preferences and/or where there are important power asymmetries between stakeholders.

    The science of IPBES in Science…

    Friday, February 18th, 2011

    Science magazine published today a policy article about the challenges facing the recently launched Intergovernmental Platform on Biodiversity and Ecosystem Services (IPBES).

    The authors, all of which are key players in the international earth systems science partnership, present the three key challenges for IPBES to reach its goals:

  • Strengthening the science
  • Strengthening assessments
  • Strengthening policy relevance
  • In discussing these challenges, they insist on the need to broaden their partnerships and in particular to seek more input from the policy community, from less developed nations and the social sciences.

    Greater involvement by social sciences is justified by the need to better incorporate “values” of biodiversity and ecosystem services in order to strengthen policy relevance. The authors argue that this valuation step was missing in the 2005 Millennium Ecosystem Assessment but put forward by the TEEB initiative in 2010. Let us hope that the IPBES will keep a critical outlook on this agenda.

    Has Australian biobanking lost all credibility?

    Friday, February 18th, 2011

    Biobanking was launched in the Australian state of New South Wales (NSW) in 2009* in order to streamline the requirement for developers to avoid, reduce and offset their impacts on biodiversity.

    Biobanking is inspired by similar policy instruments in the USA and elsewhere whereby developers can purchase “credits” sold by “banks” who have created “biodiversity gains” in advance of future impacts. As such, banking schemes solve some of the difficulties of offsetting impacts : taking into account delays between impact losses and offset gains and the uncertainties of actually obtaining these gains.

    On the downside, conservationists often argue that such “banks” give the false impression that all impacts can be offset, thereby giving an incentive to downplay or ignore the requirement to first avoid and reduce impacts.

    A major development operation in the Hunter valley of NSW resorted to biobanking to offset its impacts but it was revealed that errors where made in sizing the required offset actions. This is a serious blow to the credibility of biobanking as an instrument for mitigating development impacts on biodiversity. An article in the Sydney Morning Herald tells us that:

    The 644.4 hectares of clearing requires 37,010 credits, while the 887.0 hectares of biobank site generates 9607 credits. This results in a shortfall of 27,403 credits. The results show that between 2614.5 to 4107 hectares of additional offset is required to satisfy the offset required by the biobanking assessment.

    It will be interesting to see how this particular mishap will play out on the development of biobanking in NSW but also in its spread to other Australian states.

    * The scheme was set up through the Threatened Species Conservation Amendment (Biodiversity Banking) Act of 2006.

    Applying the mitigation hierarchy: where is the avoidance?

    Wednesday, February 16th, 2011

    In her 1996 paper, Barbara Bedford mentioned that wetland mitigation policies are in effect landscape-level policies for managing and distributing wetlands. In a paper* soon to be published in the journal Wetlands Ecology and Management, Shari Clare of the University of Alberta (Canada) and her co-authors make this point further by investigating if and how the mitigation sequence of avoiding, reducing and finally offsetting or compensating is applied in the province of Alberta.

    Through interviews with regulators, developers and actors of the wetland mitigation hierarchy they show that offsetting is systematically used to allow developers to get approval for their project. They argue that the requirement to avoid impacts is not well enforced in part because of:

  • the lack of guidelines on how to assess avoidance measures and alternatives while, in contrast, there are established guidelines for designing and sizing offsets)
  • the lack of a province-wide vision of where development could occur and where avoidance should be sought (i.e. land-use planning does not play its role)
  • the lack of recognized economic value of wetlands (i.e. their “use-value” is not taken into consideration in assessing equivalence)
  • the belief that wetland functions are easy to (re)create or restore (i.e. “techno-arrogance”).
  • To address these issues, the authors suggest watershed-based planning where wetlands are placed within a broader landscape context and alternative land-uses prioritized. This is consistent with the conclusions of Bedford (1996) who argued that project-centred regulation (i.e. command-and-control) is insufficient to reach the goal of no-net-loss of wetland functions. Shari Clare and her co-authors mention systematic conservation planning as one methodology for developing such watershed-level approaches. More generally, having a strategic vision for managing wetland resources at the provincial (or watershed level) is necessary for regulators to be proactive in the permitting process (rather than being reactive to developer requirements) and to effectively take into account cumulative effects (or many small impacts and wetland losses).

    The authors also add that wetland functions need to be better “valued” and suggest that social and economic values be explicitly incorporated into the assessment process. They suggest using the concept of ecosystem services to this end but not necessarily through a monetary valuation exercise. This raises complex assessment and accounting issues but is probably an effective avenue for both the public and developers to acknowledge the purpose of wetland mitigation policies and the option of avoiding impacts.

    Beyond the question of avoidance measures, the paper also gives some interesting (frightening?) insight into the design and sizing of offsets:

    In Alberta, all of the government regulators we interviewed indicated that the most common metric used for comparability or equivalency between impacted and compensatory wetlands is area, with very little consideration given to wetland functions or services.

    Having shown that the mitigation policy suffers from a lack of post-approval monitoring of offsets, the authors also argue for a stronger involvement of civil society in monitoring and control of offset actions: if public authorities are unable to follow-up on their decisions, then the easy solution is to get volunteers to do the work but perhaps that is too easy?

    To conclude, the paper is a very interesting contribution to the argument that, beyond developing adequate methodologies for assessing the equivalence between losses and gains in the context of offsets, the proper implementation of the mitigation hierarchy requires public authorities to be proactive about the goals in terms of wetlands, biodiversity, ecosystems etc. Being proactive means that a strategy must be formulated to managing these “resources” beyond each individual project.

    * Reference of the paper : Clare, S., Krogman, N., Foote, L; & Lemphers, N. (2011): Where is the avoidance in the implementation of wetland law and policy? Wetlands Ecology and Management, in press.

    Oil palm expansion in Indonesia: the case for trade-off analyses of ecosystem services

    Thursday, January 13th, 2011

    In a paper published in the Proceedings of the National Academy of Sciences of the USA (PNAS), Lian Pin Koh and Jaboury Ghazoul present a modelling framework for analysing trade-offs between palm oil production, biodiversity conservation and carbon sequestration.

    Informing policy-makers about these trade-offs is essential in the face of rapidly expanding plantations and the newly established REDD mechanisms (with a possible wildlife premium as discussed here).

    Using a scenario-based approach, the authors assessed the consequences of alternative pathways of oil palm expansion on the area of primary and secondary forests, on forest biodiversity (modelled using species-area models), carbon stocks (in biomass and peat soils) and annual rice production capacity. They show that biodiversity and forest conservation are compatible with the expansion of oil palm production, through appropriate selection of planted areas.

    Our results suggest that the environmental and land-use tradeoffs associated with oil-palm expansion can be largely avoided through the implementation of a properly planned and spatially explicit development strategy

    This rosy conclusion is tempered by the acknowledgement that striking the balance between the goals of biodiversity conservation, carbon sequestration and palm oil production will require the expansion of oil palm plantations to be capped. Are we really willing to make this “sacrifice”?

    The paper by Lian Pin Koh and Jaboury Ghazoul was critiqued by Sean Sloan and Nigel Stork (also in PNAS) for ignoring several spatial processes such as the aggregation of plantations. Lian Pin Koh and Jaboury Ghazoul downplayed the critique and argued for the usefulness of their tool for broad-based analyses of the issues in Indonesia.