Biodiversity Offset Strategy For a Gas Pipeline R. Mezzalama, K. Knopff, E. Sizzano, C. Amosso

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Transcription:

Biodiversity Offset Strategy For a Gas Pipeline R. Mezzalama, K. Knopff, E. Sizzano, C. Amosso

The project Gas pipeline from Georgia to Turkey Ca. 1800 km across Turkey (7222 ha footprint) Partly financed by EBRD and World Bank http://www.ebrd.com/work-with-us/projects/esia/azerbaijan-southern-gas-corridor.html

General context ESIA prepared in 2013-2014 to Turkish and IFC standards ESIA fast-tracked: only preliminary CH habitat determination 101 SCCs identified; 54 flora, 7 mammals, 6 birds, 5 reptiles, 1 amphibian, 20 arthropods, 8 fish No offset requirements according to Turkish legislation Compensation largely based on reforestation- afforestation EBRD required the preparation of a Biodiversity Offset Strategy in line with PS6 and PR6 as a first step towards a complete Biodiversity Offset Management Plan

Objectives of the Offset Strategy Identify residual impacts to priority biodiversity features, natural habitats and critical habitats Define accounting methods to calculate losses and gains for natural habitats, priority biodiversity features, and critical habitats. Identify potential offsets and additional conservation actions to achieve No Net Loss or Net Gain Define approaches to stakeholder engagement, monitoring, and adaptive management, including feedback loops that permit recalculation of loss-gain values and facilitate adjustments to the offset strategy to achieve No Net Loss or Net Gain.

Criteria Natural Habitat: No net loss Priority Biodiversity Features (PBF): No net loss (i) threatened habitats; (ii) vulnerable species; (iii) significant biodiversity features identified by a broad set of stakeholders or governments (such as Key Biodiversity Areas or Important Bird Areas); and (iv) ecological structure and functions needed to maintain the viability of priority biodiversity features described in this paragraph. Critical habitat: Net gain

Data availability Habitat map based on EUNIS level III for 500 m around the ROW Ecoregions classification according to Olson 2001 Data on Species of Conservation Concern (from ESIA and BAP): Presence in the ROW Distribution range along the ROW Data on Habitats Location of threatened Habitats according to EU Directive Location of key habitats according to IFC PS6 Data on protected areas Location of national parks Location of listed areas (Ramsar, IPA, IBA, KBA) Main gaps: habitat map for some facilities; habitat degradation, restoration success in 20 years

Loss gain calculation approach Ecosystem based - GIS driven Unit of analysis: patch of a given habitat under the footprint Deriving a «biodiversity value» for each patch Considering all criteria determining PBF CH present in each patch Ranking biodiversity values within each patch Prioritizing CH in case more values are in the same patch Calculating loss-gain within each eco-region (based on Olson 2001) Trying to balance loss-gain within the ecoregion

Loss gain calculation Calculation of the biodiversity value of each patch for each habitat Natural Habitat Species of Conservation concern Habitats and protected areas

V h = The biodiversity value of a group of patches of a given habitat type. a i = The area of the i th habitat patch. d i = The degradation coefficient of the i th habitat patch (coefficient ranging from 0-1). a ij = The area of the i th habitat patch which also contains the j th species of conservation concern. s j = The habitat suitability score assigned to the habitat patch for the j th species of conservation concern (suitability score ranging from 0-1) d ij = The degradation coefficient of the i th habitat patch which also contains the j th species of conservation concern. a ik = The area of the i th habitat patch which overlaps with the k th significant conservation area. p k = The score assigned to the i th habitat patch for the k th significant conservation area (score ranging from 0-1) d ik = The degradation coefficient of the i th habitat patch which overlaps with the k th significant conservation area. R h = The estimated rehabilitation success of each habitat type in 20 yeas (ranging from 0-1),

Definition of some parameters Habitat degradation Habitat suitability for SCCs Conservation areas relative importance

Results

Results Total net loss (in ha) CH: 700,82 PBF/NH: 193,90 Total net loss (in biodiversity value) CH: 2384,76 PBF/NH: 576,24 Most important habitat types Anatolian gypsum steppe: 169,36 Irano Anatolian steppe: 684,28 Calciphilous alpine and subalpine grassland: 243,00 Termophilous deciduous woodland: 250,82 Intensive unmixed crops : 740,46 TOTAL 2087,92 (70%)

Target species Given their importance we considered separately a limited number of species that are Critically Endangered, Local endemic and with low mobility Sj= total suitable habitat for a target species a i = The area of the i th habitat patch d i = The degradation coefficient of the i th habitat patch (coefficient ranging from 0-1). s j = The habitat suitability score assigned to the habitat patch for the j th species of conservation concern (suitability score ranging from 0-1)

Results

Principles: Offset strategy Requirements based on transparent loss-gain assessment Measurable gains based on loss avoidance or actions for gains Offset based on like for like or better principle Offsets secured over the long term and auditable Actions considered Create protected areas in designated areas (KBAs) Strengthen management capacity within existing protected areas Arrest current degradation of biodiversity Improve degraded areas: Rehabilitation Invasive species management Livestock-agriculture-forestry management Reintroduction-management of SCCs

Offset management plan Estimation of the offset potential within the 500 m corridor where habitat data exist confirmed the availability of suitable offsets Next steps will include: Stakeholder engagement with Forestry, Park authorities and NGOs Further studies to confirm degradation and rehabilitation parameters Field studies on selected target species Screening and habitat mapping in selected KBA and protected areas Identification and design of individual offset projects Negotiation with relevant stakeholders Finalization of the plan

Thank you! rmezzalama@golder.com