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Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants • MISA • VWI •BREKKE & STRAND akustikk as °Miljøanalyser 16.03.22

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Page 1: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Environmental analysis HSR Phase 2

Asplan Viak AS with subconsultants

• MISA

• VWI

• BREKKE & STRAND akustikk as

°Miljøanalyser

18.04.23

Page 2: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Task

Develop methods for assessment of:

• Landscape (AVAS)

• Intervention effects (natural environment, water resources) (AVAS)

• Noise (AVAS, Brekke & Strand akustikk)

• Energy (VWI)

• Climate (MISA)

Main challenge: High level analysis at a large geographical scale with relevant documentation and advices for the project and later IA.

18.04.23

°Miljøanalyser

Page 3: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Landscape study and Intervention effects

Legislative and Regulatory Framework; a selection:

– European Conventions regarding landscape and biological diversity– The EU Water Framework Directive

» implemented in Norway through Norwegian legislation» the main goal of the Water Framework Directive is to achieve a so-called “Good

ecological standard” for the quality of surface water and groundwater.” – Water resources are regulated through e.g. ”Lov om vassdrag og grunnvann

 (Vannressursloven)”– Norwegian Nature Diversity Act – Norwegian Planning and Buliding Act, and requirements for Impact Assessment at

different planning stages– Regulations– Handbooks

18.04.23

°Miljøanalyser

Page 4: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Landscape study and Intervention effects

Approach to Method Development:

• Review existing methods for analysis and assessment of landscape and environmental intervention effects, and

• Identify aspects of existing methods which could be adapted for high level analysis at a large geographical scale.

18.04.23

°Miljøanalyser

Page 5: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Landscape study and Intervention effects

Scope of work:

– Litterature study– Identification and review of digital datasets– Identification of existing value classification of datasets– Identification of need for supplementing information and the need for additional/

supporting data and qualitative assessments– Description of methodology and description of GIS-model

18.04.23

°Miljøanalyser

Page 6: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Landscape study and Intervention effects

Recommendations so far:

• ”Wide” defenition of landscape also including visible cultural heritage

• Inclusion of natural resources and outdoor activities despite this not being covered by JBVs initial scope of work

• The proposed approach consists broadly of the following stages:To describe the character of the area under each topicTo describe a value/ importance/ sensitivity to the characteristics of the areaTo describe how proposals will impact on these characteristicsTo derive an overall assessment score/ measure of conflict potential

Derived from : [TØI, 2000] Miljøhåndboken, Trafikk- og miljøtiltak i byer og tettsteder, [STATENS VEGVESEN 2010] Konseptvalgutredning Grenland. Vurdering av ikke-prissatte virkninger , [STATENS VEGVESEN 2008] Konseptvalgutredning E18 Langangen – Grimstad. Vurdering av ikke-prissatte virkninger

18.04.23

°Miljøanalyser

Page 7: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Landscape study and Intervention effects

• GIS-model

• Data unevenly

registered

18.04.23

°Miljøanalyser

Page 8: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Natural environment

18.04.23

°Miljøanalyser

Naturbase (DN) – important nature

Regionally collected

Classified according to national, regional or local interest/ level of protection

8

Page 9: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Noise

• DIRECTIVE 96/48/EC — INTEROPERABILITY OF THE TRANS-EUROPEAN HIGH SPEED RAIL SYSTEM : Likely to be a guideline also for Norwegian HSR

Limiting values LpAeq,T for the stationary noise of rolling stock: 68 dB for train setsStarting noise for electric trainsets: Class 1/Class 2 = 85/82 dBPass-by noise has different limits at different speeds, se table below. Measured 25 m from centre of track, 3.5 m above ground in a non reflecting environment.

Practical situation: Limits are hard to achieve for rolling stock available today.

18.04.23

°Miljøanalyser

Page 10: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Findings from the NOEMIE project (NOise Emission Measurements for high speed Interoperability in Europe –EU)

• The TSI noise emission limits are difficult to keep, current HS-TSI levels can be considered to be very demanding limits, however, trainsets have come on the market since then.

• The combined roughness of rail and wheels is the dominant contribution to the track side noise emission up to train speeds of 300 kph.

• First at speeds beyond 300 kph, the aerodynamic noise tends to dominate

• A takeout from NOEMIE project is that Nordic noise calculation method is expected to be applicable for higher speeds than earlier envisioned.

18.04.23

°Miljøanalyser

Page 11: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

A summary of pass-by noise levels

Results from NOEMIE project compared with TSI values

Results from new models of trainsets should be obtained and compared

18.04.23

°Miljøanalyser

Page 12: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Important takeouts at this stage:

• Noise limits set in the TSI for rolling stocks will be difficult to achieve

• Nordic noise calculation metod can likely be used for most practical cases up to 300 kph based upon current findings

• Around and beyond 300 kph, the nose of the train, the first boggie and the pantograph creates the main noise sources and the pantograph present a noise challence at these speeds, especially because it may create noise with significant content of ”sinusiodal” character, implying a + 5 dB more stringent noise requirement according to T-1442

• Vibrations seems mainly to follow the solutions seen by ordinary tracks

• Structural noise will present a greater challenge than today, especially where buildings are located above tunnel openings or close to the tunnel

• Tunnels with irregular shape (”blasted tunnels”) have significantly less vibrational problems than ordinary, round tunnels.

• Tunnels, tracks and power lines must be included in noise assesment

18.04.23

°Miljøanalyser

Page 13: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Infrastructure Scenarios Technical Data Results Summary

Institute of Transportation Research Stuttgart (VWI) 13

Infrastructure scenarios General and train specific technical data and assumptions

• General assumptions• Train specific technical data• Efficiency degree of the tractive system

(Intermediate) Results• Passenger load factor effects• Gradient and permitted track velocity impact• Tunnel impact on specific energy consumption• „Straight but steep“ vs. „Flat but with a detour“

Energy Consumption

Page 14: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Infrastructure Scenarios Technical Data Results Summary

Institute of Transportation Research Stuttgart (VWI) 14

Infrastructure Scenarios

Based on the attributes above, 1,650 different infrastructural combinations – and thus far too many – can be found. Passenger load factors included, the number rises to 9,900. Consequently, the calculations are limited to reasonable scenarios, only.

Infrastructure scenarios

Attributes Values

Track Length [km] 500

Track Gradient [‰] 0 ±12.5 ± 20.0 ± 25.0 ± 30.0 ± 35.0

Permitted Track Speed [km/h] 220 250 280 300 330

Passenger Load Factors [%] 0 10 20 50 67 100

Curves None

Tunnel lengths [km] 0 2 5 10 20 40

Number of Intermediate Stops 0 1 2 5 10

Page 15: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Infrastructure Scenarios Technical Data Results Summary

Institute of Transportation Research Stuttgart (VWI) 15

Technical Data

Efficiency Degree as a function of

Train Speed and Tractive/Braking Effort

Efficiency degree () of the tractive system

Page 16: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Infrastructure Scenarios Technical Data Results Summary

Institute of Transportation Research Stuttgart (VWI) 16

Results

Permitted track speed impact and train comparison

Page 17: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Infrastructure Scenarios Technical Data Results Summary

Institute of Transportation Research Stuttgart (VWI) 17

Results

Tunnel impact on specific energy consumption

Page 18: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Motivation for assessment of climate related effects

• Is High Speed Rail an environmentally good solution, and for what time horizon?

• Importance of infrastructure is often omitted in discussions of transport modes

• Importance of infrastructure phase versus operation phase• HSR in Norwegian topography

– More tunnels and bridges? What are the consequences?– Consequences of topography on operation?

• Decision making support– Building module based system to assess various corridor

characteristics – open sections, tunnels, bridges• Only climate related effects are considered in this part

Page 19: Environmental analysis HSR Phase 2 Asplan Viak AS with subconsultants MISA VWI BREKKE & STRAND akustikk as °Miljøanalyser 28.04.2015

Air

Road: car & bus

Market analysisAlternatives A-D

Demand for individual transport modes

Component-based emission inventories

High speed rail: A, B, C, D

HSR

Rolling stock OperationInfrastructure

Time (year)

CO2e

Alt. 1Alt. 2

Alt. 3

Emission profiles (to be made)

Physical planningAlternatives A-D

Energy use dataAlternatives A-D

Open stretch Tunnels Bridges

Materials, processing, energy, transport …

National emissions Emissions abroad

Time (year)

CO2e