Planning a 100 percent renewable electricity system

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Transcription:

Planning a 100 percent renewable electricity system Andy Philpott Electric Power Optimization Centre University of Auckland www.epoc.org.nz (Joint work with Michael Ferris) INI Open for Business Meeting, Cambridge, January 23, 2019.

Open for Business This talk is about formulating models to advise government policy. What is the role of mathematics in this process? What is the role of planning and plans? How do we think about uncertainty? How should we represent business decisions in our plan? Disclaimer: This talk presents some preliminary results obtained from the authors model of the New Zealand electricity system under some plausible assumptions about model parameters. The results should not be interpreted as representing the views of the New Zealand Climate Commission or as reflecting New Zealand Government policy.

New Zealand: How to implement Jacinda s deal Confidence and Supply Agreement between Labour Party and Green Party, October 2017. (https://www.greens.org.nz/sites/default/files)

New Zealand greenhouse gas emissions [https://emissionstracker.mfe.govt.nz] Total GHG emissions in 2016 were 80 M t CO2 equivalent.

New Zealand greenhouse gas emissions [https://emissionstracker.mfe.govt.nz] Total CO2 emissions in 2016 were 30 M t.

New Zealand greenhouse gas emissions [https://emissionstracker.mfe.govt.nz] Total CO2 emissions from electricity in 2016 were 3 M t.

New Zealand s electricity system in one slide 55% of New Zealand electricity comes from hydro generation. New Zealand cannot import or export electricity (aluminium excepted). Hydro reservoirs hold about 8 weeks of storage if plant run at full capacity. Electricity system currently has ample generation and transmission capacity, but...... electricity system is susceptible to risk of seasonal low inflows ( dry winter ).

A mathematical modelling approach to planning Build and solve a social plannning model that optimizes electricity capacity investment with constraints on CO2 emissions. Social planning solution should be stochastic: i.e. account for future uncertainty Social planning solution should be risk-averse: because the industry is. Approximate the outcomes of the social plan by a competitive equilibrium with risk-averse investors. Compensate for market failures from imperfect competition or incomplete markets.

Summary 1 Introduction 2 Stochastic optimization models 3 Some results 4 Conclusions

Summary 1 Introduction 2 Stochastic optimization models 3 Some results 4 Conclusions

Uncertainty is experienced at different time scales Demand growth, technology change, capital costs are long-term uncertainties (years). Seasonal inflows to hydroelectric reservoirs are medium-term uncertainties (weeks). Levels of wind and solar generation are short-term uncertainties (half hours). Very short term effects from random variation in renewables and plant failures (seconds).

Scenario analysis for long-term planning 14 scenarios for electricity demand and generation mix in 2050 under different assumptions.

Computing the right capacity mixture Needs modelling at finer time scales. Find the optimal mix of capacity so as to enable optimal releases from hydroelectric reservoirs with uncertain inflows. meet demand with random variations in wind and solar. spinning reserve capacity to deal with random plant failures Building more capacity costs more, but makes operations cheaper - seek a least-cost sweet spot.

Simplified two-stage stochastic optimization model Capacity decisions are x at cost K (x). Operating decisions are: generation y at cost C (y), loadshedding q at cost Vq. Random demand is d(ω). Minimize capital cost plus expected operating cost. P: min K (x) + E ω [C (y(ω)) + Vq(ω)] s.t. y(ω) x, y(ω) + q(ω) d(ω), y(ω), q(ω) 0.

More realistic model Plant k has current capacity U k, expansion x k at capital cost K k per MW, maintenance cost L k per MW, and operating cost C k. Minimize fixed and expected variable costs. Here t = 0, 1, 2, 3, is a season and w(t) is reservoir storage at end of season t. P: min ψ = k (K k x k + L k z k ) + t E ω [Z (t, ω)] s.t. Z (t, ω) = b T (b) ( k C k y k (t, ω, b) + Vq(t, ω, b)), x k u k, z k x k + U k, y k (t, ω, b) µ k (t, ω, b)z k, b T (b)y k (t, ω, b) ν k (t, ω) b T (b)z k + w(t 1) w(t), q(t, ω, b) d(t, ω, b), d(t, ω, b) k y k (t, ω, b) + q(t, ω, b), w(t) W, y, q, w 0.

Operating costs are random Plant k has current capacity U k, expansion x k at capital cost K k per MW, maintenance cost L k per MW, and operating cost C k. Transfer energy w(t) from season t to season t + 1. Minimize fixed and expected variable costs. Here T (b) is the number of hours in load block b of annual load duration curve. P: min ψ = k (K k x k + L k z k ) + t E ω [Z (t, ω)] s.t. Z (t, ω) = b T (b) ( k C k y k (t, ω, b) + Vq(t, ω, b)), x k u k, z k x k + U k, y k (t, ω, b) µ k (t, ω, b)z k, b T (b)y k (t, ω, b) ν k (t, ω) b T (b)z k + w(t 1) w(t), q(t, ω, b) d(t, ω, b), d(t, ω, b) k y k (t, ω, b) + q(t, ω, b), w(t) W, y, q, w 0.

Shedding load incurs VOLL penalties Plant k has current capacity U k, expansion x k at capital cost K k per MW, maintenance cost L k per MW, and SRMC C k. Transfer energy w(t) from season t to season t + 1. Minimize fixed and expected variable costs. P: min ψ = k (K k x k + L k z k ) + t E ω [Z (t, ω)] s.t. Z (t, ω) = b T (b) ( k C k y k (t, ω, b) + Vq(t, ω, b)), x k u k, z k x k + U k, y k (t, ω, b) µ k (t, ω, b)z k, b T (b)y k (t, ω, b) ν k (t, ω) b T (b)z k + w(t 1) w(t), q(t, ω, b) d(t, ω, b), d(t, ω, b) k y k (t, ω, b) + q(t, ω, b), w(t) W, y, q, w 0.

Capacity of wind and run-of-river is random in a season Plant k has current capacity U k, expansion x k at capital cost K k per MW, maintenance cost L k per MW, and SRMC C k. Minimize fixed and expected variable costs. P: min ψ = k (K k x k + L k z k ) + t E ω [Z (t, ω)] s.t. Z (t, ω) = b T (b) ( k C k y k (t, ω, b) + Vq(t, ω, b)), x k u k, z k x k + U k, y k (t, ω, b) µ k (t, ω, b)z k, b T (b)y k (t, ω, b) ν k (t, ω) b T (b)z k + w(t 1) w(t), q(t, ω, b) d(t, ω, b), d(t, ω, b) k y k (t, ω, b) + q(t, ω, b), w(t) W, y, q, w 0.

Energy input from reservoir inflows is random in a season Plant k has current capacity U k, expansion x k at capital cost K k per MW, maintenance cost L k per MW, and SRMC C k. Minimize fixed and expected variable costs. P: min ψ = k (K k x k + L k z k ) + t E ω [Z (t, ω)] s.t. Z (t, ω) = b T (b) ( k C k y k (t, ω, b) + Vq(t, ω, b)), x k u k, z k x k + U k, y k (t, ω, b) µ k (t, ω, b)z k, b T (b)y k (t, ω, b) ν k (t, ω) b T (b)z k +w(t 1) w(t), q(t, ω, b) d(t, ω, b), d(t, ω, b) k y k (t, ω, b) + q(t, ω, b), w(t) W, y, q, w 0.

Accounting for CO2 emissions Some capacity x k, k N, is non renewable". Some generation y k (ω), k E emits β k y k (ω) tonnes of CO2. For a choice of θ [0, 1] constraint is either: E ω [ k E β k y k (ω)] θe ω [ k E β k y k (ω, 2017)], (reduce CO2 emissions compared with 2017) E ω [ k N y k (ω)] θe ω [ k N y k (ω, 2017)], (reduce non-renewable generation compared with 2017) k N x k θ k N x k (2017), (reduce non-renewable capacity compared with 2017)

How to find a solution? With a finite number of scenarios our model is a large-scale linear programming problem We solve it using the commercial package Gurobi in the GAMS environment. (Alternatives are PuLP (Python), AMPL, JuMP(Julia), Solver Studio.)

Summary 1 Introduction 2 Stochastic optimization models 3 Some results 4 Conclusions

More about New Zealand

Non renewable capacity reduction can increase emissions Many instances of the model where a reduction of non-renewable plant capacity ceteris paribus increases average emissions. Hydro-reservoir inflows are susceptibe to dry winter risk. With high nonrenewable plant capacity, dry winters can be dealt with just before they have an effect, so reservoir levels in summer need not be full. With low nonrenewable plant capacity, can t wait till last minute and reservoir levels in summer need to be close to full just in case. Burning fuel to achieve this increases emissions.

Output from simulation of optimal reservoir policy [Fulton, 2018] Optimal reservoir storage trajectories under status quo at Huntly

Output from simulation of optimal reservoir policy [Fulton, 2018] Reservoir storage trajectories with no coal plants at Huntly

Compare CO2 emissions from reduction strategies Since (renewable) geothermal and CCS emit some CO2 100% renewable yields modest reductions in CO2 emissions.

Compare cost of reduction strategies as theta increases Cost of actually reaching zero CO2 emissions (without geothermal or CCS) increases as we approach the limit.

Technology choices as theta increases Wind and batteries increase modestly as well as CCS (renewable) as 100% approaches.

Technology choices as theta increases Investments in wind and batteries increase with reductions in geothermal.

Risk-averse solutions for 95% NR energy reduction Risk aversion modelled using (1 λ)e [Z ] + λavar 0.90 (Z ), for λ = 0, λ = 0.5, λ = 0.8.

Summary 1 Introduction 2 Stochastic optimization models 3 Some results 4 Conclusions

Conclusions 100% renewable electricity system has several interpretations with different implications. Policy should choose the objective function not the action: e.g. reducing thermal capacity ceteris paribus can increase average emissions. Uncertainty in the model makes a difference. Electricity system has uncertainties at many time scales. Can include these in a single model with some approximations. If geothermal and CCS are renewable then 100% renewable is feasible, but emission reduction is modest. Next steps: A multistage model, and its competitive equilibrium counterpart.

The End THE END

References Bishop, P. and Bull, B., The future of electricity generation in New Zealand. In 13th annual conference of the New Zealand Agricultural and Resource Economics Society, Nelson, New Zealand (pp. 28-29), 2008. Ferris, M.C., Philpott, A.B., Dynamic risked equilibrium, EPOC technical report, 2018. Fulton B. Security of Supply in the New Zealand Electricity Market, Engineering Honours Thesis, 2018. Girardeau, P. and Philpott, A.B., GEMSTONE: a stochastic GEM. In EPOC Winter Workshop, 2011.

References Philpott, A.B., Ferris, M.C. and Wets, R.J-B., Equilibrium, uncertainty and risk in hydrothermal electricity systems, Mathematical Programming B, 157,2, 483-513, 2016. Kok, C., Philpott, A.B. and Zakeri, G., Value of transmission capacity in electricity markets with risk averse agents, EPOC technical report, 2018. Wu, A., Philpott, A. and Zakeri, G., Investment and generation optimization in electricity systems with intermittent supply. Energy Systems, 8(1), pp.127-147, 2017. All references and this talk can be downloaded from www.epoc.org.nz