Breakout Session presentations ‘Infrastructure Planning, Mike Simpson, University of Oxford'

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Evaluation of Strategies and Interdependencies at the National Scale Water in Future Cities | Infrastructure Planning | RCUK Showcase 2015 Mike Simpson [email protected]

Transcript of Breakout Session presentations ‘Infrastructure Planning, Mike Simpson, University of Oxford'

Evaluation of Strategies and Interdependencies

at the National Scale

Water in Future Cities | Infrastructure Planning | RCUK Showcase 2015

Mike Simpson

[email protected]

• How can we build a complete picture of water resource

infrastructure and its interaction with other infrastructures when

facing deep uncertainties?

• Where will new water infrastructure be

needed to 2050?

• What are the significant interactions with

other infrastructures and resources?

• How can we use a scenarios and strategies

approach to explore a range of future conditions?

Evaluation of Strategies and Interdependencies at the National Scale

• We modelled 130 water resource zones/megazones across mainland Great Britain

• We generated transient projections of available water in each zone for each of 11

Future Flows climate scenarios (Prudhomme et at 2012), taking into account

groundwater, river and reservoir sources

• A demand model estimates future demand on the basis of existing per capita

consumption, non-domestic use and leakage coupled with 3 scenarios of population

growth

Modelling Water Systems

• A regression model of infrastructure options identifies costs and maximum/minimum

asset sizes for eight management options

• Where shortfalls in supply/demand are identified, best options for new infrastructure

are selected

Infrastructure Decisions

Surfaces of Lifetime/Water

Supply/Cost for five option types

AR – Aquifer Recharge

DE – Desalination

DR – Demand Reduction

ER – Effluent Reuse

LR – Leakage Reduction

Central Growth

High Flow Climate Scenario

Central Growth

Central Flow Climate Scenario

Central Growth

Low Flow Climate Scenario

Low Growth

Central Flow Climate Scenario

Central Growth

Central Flow Climate Scenario

High Growth

Central Flow Climate Scenario

Balance (ML/d)

Scenarios

Strategies

Minimum

Intervention

Total Cost (£m)

Capacity

Expansion

System

Efficiency

System

Restructuring

Interdependency

Tran, M., Byers, E., Blainey, S., Baruah, P., Chaudry, M., Eyre, N., Jenkins,

N., Qadrdan., M., (2015) Quantifying interdependencies:

transport-energy and energy-water, In Tran, M., Hall, J., Hickford,

A., Nicholls, R., eds. Planning Infrastructure for the 21st Century: A

Systems-of-Systems Methodology, Cambridge University Press:

Cambridge

How can we build a complete picture of water resource infrastructure and its

interaction with other infrastructures when facing deep uncertainties?

• A system-of-systems approach allows us to compare the changing needs for

infrastructure to 2050.

• Building the requirements for other infrastructure types into our model allows the

needs for and requirements of water to be evaluated.

• Uncertainties can be considered using a non-probabilistic scenarios approach.

Where will new water infrastructure be needed for the coming century?

• Scenarios and strategies influence where and how soon water will be required.

• Demand management is a common solution across many scenarios but it does not solve

the problem alone.

• Many scenarios show a shortfall in the South and the West Midlands by 2050.

Outcomes

Outcomes

What are the significant interactions with other infrastructures and resources?

• We assess interdependencies across other infrastructures.

• We find that energy demand for water is the most important interdependency.

• A carbon capture and storage future suggests the highest demand for water due to its

continued support for hydrocarbon power.

How can we use a scenarios and strategies approach to explore a range of future

conditions?

• The 11 climate scenarios and 3 demand scenarios allow us to consider possibilities

under these deep uncertainties.

• The strategies are implemented across each infrastructure and interpreted for each

system.

• We will next explore a scaled sensitivity approach to deep uncertainty.

Further Work

We will incorporate other abilities within the Environmental Change Institute including

pathways-driven approaches and social/environmental factors

• Further refine our representation of water supply

• Move beyond supply/demand to a fully risk based approach

• Incorporate non-technical criteria to better represent the decisions which are

made

• Look at multi-dimensional decision scaling to evaluate sensitivity across changes

in drought autocorrelation/drought intensity/non-domestic demands/leakage

• Consider composite strategies

• Investigate green infrastructure solutions

• Investigate how robustness to drought can vary depending on the units of

management

Please contact me for further information or questions -

[email protected]

Simpson, M., Ives, M. C., Hall, J., Kilsby, C., (2015), Water supply systems assessment

In Tran, M., Hall, J., Hickford, A., Nicholls, R., eds. Planning Infrastructure for the 21st Century:

A Systems-of-Systems Methodology, Cambridge University Press

Prudhomme, C., Dadson, S., Morris, D., Williamson, J., Goodsell, G., Crooks, S., Boolee, L., Davies, H., Buys, G., Lafon, T. (2012). Future

flows climate data. NERC Environmental Information Data Centre. http://doi.org/10.5285/bad1514f-119e-44a4-8e1e-442735bb9797

Figures make use of BGS and OS data from EDINA Digimap, which are Ordnance Survey/ British Geological Survey/EDINA supplied

services © Crown Copyright/Database Right 2015.