Visualisation of habitat measures by means of photo scenarios
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1 Visualisation of habitat measures by means of photo scenarios Berit Köhler NINA Lillehammer EcoManage project In cooperation with: David N. Barton, NINA Bjørnar Dervo, 3D smia Hans-Petter Fjeldstad, Ana Adeva Bustos, Peggy Zinke, SINTEF Svein Haugland, Aleksander Andersen, Agder Energi Foto: Jens Nicolai Thom, NVE
2 EcoManage ( ) Main objective: test, evaluate and adapt new concepts & methods for the improved development & management of energy and water resources. Project lead: Håkon Sundt (SINTEF) NINA part: decision support for habitat Photo: Edelpix restoration and environmental flow measures in regulated rivers method development Case study: Mandalselva (Laudal/Bjelland) Project lead NINA part: David N. Barton
3 EcoManage case study Mandalselva Mandalselva Basin located in Southern Norway Mandalselva is regulated by 6 power plants (Agder Energi).
4 EcoManage case study Mandalselva Mandalselva Basin located in Southern Norway Mandalselva is regulated by 6 power plants (Agder Energi).
5 EcoManage case study Mandalselva Laudal HPP 1977: License 1981: In operation No salmon production Until m 3 s -1 in winter 3 m 3 s -1 in summer 1997:Liming program re-stocking strategy 2001: 11 tons of salmon Salmon production back NVE suggestion: 6 m 3 s -1 in winter spill during smolt migration 8-25 m 3 s -1 summer 5 years trial period ( ) Slide: adopted from Ana A. Bustos
6 EcoManage Method development for MCDA support Bjelland bypass section Off-Setting How much can measures in the minimal release sections Bjelland and Laudal compensate each other? Downstream Bjellad outlet 10 weirs Laudal 2 weirs Bjelland Laudal bypass section MCDA Ranking of habitat restoration and flow regulation measures
7 Multi-criteria decision analysis (MCDA) MCDA: Systematic structuring of decisions in a hierarchy of aims, criteria & alternatives
8 EcoManage: Multi-criteria decision analysis for Mandalselva Main aim Partial Aims Criteria Impacts Power Maximise profit Restoration costs Good ecological potential without disproportionate cost Maximise salmon production Smolt product -ivity Aesth etics Maximise other user interests Fishing experie nce Utility Weighting Weighting Scaling Alternatives 1. Stream flow 2. Weir removals 3. Spawning habitat
9 EcoManage: Photo scenario development for Mandalselva WFD aim Partial aims Criteria Impacts Power Maximise profit Restoration costs Good ecological potential without disproportionate cost Maximise salmon population Smolt product -ivity Aesth etics Maximise other user interests Fishing experie nce Utility Weighting Weighting Scaling Alternatives 1. Stream flow 2. Weir removals 3. Spawning habitat measure stakeholder preferences
10 Photo scenario method Aesthetic preferences as visual evaluation of sites No detour of evaluation through textual description or maps of sites Series of computerized visual simulations of scenarios depicting concrete management alternatives for the status quo situation in a standardized way
11 Example from Swiss study on river restoration representative photo test survey of attitudes towards river restoration computer-aided editing of one basis-photo ecological integrity measured by eco-morphological quality here: classification according to Swiss Module-Step Concept (MSC), and expert validation use in a Switzerland-wide representative survey no restoration lowest rest. effort medium restoration effort considerable rest. effort: MSC-Level: 1 MSC-Level: 2 MSC-Level: 3 MSC-Level: 4 Junker, B. and Buchecker, M. (2008) «Aesthetic preferences versus ecological objectives in river restorations.» Landscape and Urban Planning 85,
12 EcoManage: Photo scenario development for Mandalselva 1. step: baseline photos of all 12 existing weirs (july 2014) Weir 1 4 Weir 2 2b 2c 5
13 EcoManage: Photo scenario development for Mandalselva 1. step: baseline photos in july 2014 of all existing weirs Photos: Berit Köhler Standardized: perspective /distance to weirs / angles / weather/light / no people.
14 EcoManage: Photo scenario development for Mandalselva 2. step: reduction of sites for scenario development sites: 7 highest conflict potential Weir 1 Weir 2 4 management decisions to become relevant 2b 2c 5 Photos: Berit Kohler
15 EcoManage: Photo scenario development for Mandalselva 3. step: decision on scenario simulation criteria (habitat measures) Fossekilen weir weir 3 weir 4 weir 5 Klevland bru weir 6m 3 /s discharge 6m 3 /s discharge 6m 3 /s discharge 6m 3 /s discharge 6m 3 /s discharge 6m 3 /s discharge 6m 3 /s discharge 6m 3 /s discharge 6m 3 /s discharge 6m 3 /s discharge 3m 3 /s discharge 3m 3 /s discharge 3m 3 /s discharge 3m 3 /s discharge 3m 3 /s discharge 15m 3 /s discharge 15m 3 /s discharge 15m 3 /s discharge 15m 3 /s discharge 15m 3 /s discharge
16 4. step: photo scenario development Habitat measure Stream flow adjustment (3,6 or 15 m 3 /s) Parameter wetted area water level Type of inputdata/model used Data from field work Miljødesign Mandalselva HEC-RAS* 1D model & GIS (HEC-GeoRAS) ** Data from field work Miljødesign Mandalselva HEC-RAS 1D model & GIS (HEC-GeoRAS) ** (yes/no) water velocity water depth water surface structure light,colour,shadow Data from field work Miljødesign Mandalselva HEC-RAS 1D model & GIS (HEC-GeoRAS) ** Qualitative expert knowledge (Hans-Petter Fjeldstad) *HEC-RAS: Hydrologic Engineering Centers River Analysis System. **expert knowledge (H-P. Fjeldstad) also used for data gaps
17 4. step: photo scenario development Changes in wetted area, water velocity and water depth: HEC-GeoRAS modeling Modeling illustration examples of data input to photo scenario development Source: H.-P. Fjellstad, P. Zinke, A.A. Bustos, S.E. Gabrielsen: Foreløpig SINTEF Energi AS Rapport TR F7450 (2014): «Fjerning av terskler ved Laudal i Mandalselva»
18 4. step: photo scenario development Fossekilen weir weir 3 weir 4 weir 5 Klevland bru weir original 6 m 3 /s* w/o weir 6 m 3 /s w/o weir 3 m 3 /s w/o weir 15 m 3 /s * The original discharge was 2 m 3 /s; 6 m 3 /s scenario exists Scenarios: Bjørnar Dervo, 3D smia
19 Klevland bru original, with weir 6 m 3 /s Photo: Berit Kohler
20 Klevland bru without weir 6 m 3 /s Scenario: 3D smia
21 Klevland bru without weir 3 m 3 /s Scenario: 3D smia
22 Klevland bru without weir 15 m 3 /s Scenario: 3D smia
23 Weir 5 original, with weir 6 m 3 /s Photo: Berit Kohler
24 Weir 5 without weir 6 m 3 /s Scenario: 3D smia
25 Weir 5 without weir 3 m 3 /s Scenario: 3D smia
26 Weir 5 without weir 15 m 3 /s Scenario: 3D smia
27 Fossekilen weir original, with weir 2 m 3 /s Photo: Berit Kohler
28 Fossekilen weir without weir 3 m 3 /s Scenario: 3D smia
29 Fossekilen weir without weir 6 m 3 /s Scenario: 3D smia
30 Fossekilen weir without weir 15 m 3 /s Scenario: 3D smia
31 EcoManage: use of photo scenarios Mandalselva 5. step: application in focus group interviews with local stakeholders 3 m3/s 6 m3/s 15 m3/s Best=9 Worst=1 Ex. question: «Please rank the following scenes on a scale from 1 (worst) to 9 (best) according to how attractive they are for you!» Slide adapted from: David N. Barton (work in progress)
32 EcoManage: use of photo scenarios Mandalselva in MCDA 5. step: application in focus group inteviews with local stakeholders 3 m3/s 6 m3/s 15 m3/s 0 scaled impact 1 Q: How do we scale impact in MCDA? Slide adapted from: David N. Barton (work in progress)
33 EcoManage: use of photo scenarios Mandalselva in MCDA Without weir 3m 3 /s With weir 6m 3 /s Without weir 6m 3 /s Without weir 15m 3 /s wetted area = 4,86 m 2 wetted area = 40,33 m 2 wetted area = 7,77 m 2 wetted area = 14,67 m 2 Interviews stakeholders Wetted area (m 2 intervals) input tabel Hugin/BBN scaled impact (0-1) Slide adapted from: David N. Barton (work in progress)
34 Fossekilen weir scenario 6m3/s Visualisation of habitat measures by means of photo scenarios Thank you! Comments, questions? Scenario: 3D smia
35 Industrial partners
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