2.2 Seed data and assumptions

2.2 Seed data and assumptions Bruno Prior Mon, 14/12/2020 - 21:59

2.2.1 The need for seed data

  1. An hourly model must do its best to represent a realistic scenario hour by hour. It will need to either accept hourly seed data or generate its own.
  2. It is not realistic to generate the data. Key factors like weather and demand are neither random nor regular. They are not unrelated but not determinant (e.g. temperature and wind affect demand, but so do other human factors). The output of any model based on artificially-generated data would primarily reflect the assumptions used to generate that data.
  3. The seed data must be based on historic data to provide a realistic pattern of irregular variability amongst several key components, which creates the challenge to balance supply and demand.
  4. That historic data must be used raw and not aggregated to produce “typical” figures for each period. The aggregate would not be typical. It would be an average that radically dampened the inter- and intra-temporal variability that represent the key challenge in real-life operation.
  5. The model must encompass all energy, not just electricity as many previous models have done. Net Zero is about recognising that decarbonisation has to cover a lot more than the electricity sector.
  6. Many of the favoured solutions (e.g. electrification, hydrogen and bioenergy) create large overlaps between what were previously regarded as largely discrete sectors: electricity, transport, heat and non-energy carbon sources. The model and the seed data need to encompass these overlaps, to allow for the allocation of scarce means between alternative uses.[1]
  7. Which factors are primarily exogenous and require seed data?

2.2.2 Weather

2.2.2 Weather Bruno Prior Mon, 14/12/2020 - 22:03
  1. The external temperature is the most important factor in the levels of heat demand. But the relationship between temperature and heat demand is revealed primarily by comparing temperatures with the use of the primary heating fuel: gas. Unfortunately, unlike electricity, most gas is not metered on a frequent basis. Two academic studies attempted to overcome this by estimating daily profiles that could be applied to the daily figures for gas-use available from National Grid to generate synthetic granular heat-demand data:
    • Image
      The ground-breaking research of Robert Sansom at Imperial College London generated the first profile of half-hourly heat demand, reflected in the chart to the right that has become famous in energy-policy circles for illustrating the challenge of matching heat demand to inflexible sources:[1]
    • Image
      Recently, Watson, Lomas and Buswell of Loughborough University made some well-founded modifications to Sansom’s model that reduced its “peakiness”.[2] The observation that heat demand would be spread more widely over the day in cold conditions with high demand (rather than simply increased pro rata in each period) is both intuitive and consistent with the large dataset that they used. The difference with Sansom is illustrated in the chart from their paper to the right.
       

      We adopted their “less-peaky” heat-demand profiles to convert National Grid’s daily gas-demand figures into reasonable synthetic hourly figures.[3] The somewhat-flattened profile reduces the balancing challenge, but comparing the two charts above should illustrate that heat demand remains significantly larger and more variable than electricity demand (the grey line in Sansom’s chart).

  2. Temperature is important not only to the heating demand, but also to the cooling demand. This is currently modest in the UK, but is a key determinant of the demand profile in hotter countries, and is likely to become more significant in the UK if the climate warms and if we wish to reduce the number of excess deaths during hot periods. Data are limited, but we have an estimate of the capacity of non-domestic air-conditioning units (a large proportion of the total) from the work done to estimate the contribution of “RAAHPs” (see above) to our renewable heat. We may assume their output for their primary purpose, cooling, is also significant, but have to adjust for the fact that the estimated heat is not the electricity consumption, but the large figure assumed to be produced on the basis of their heating sCOP. Very roughly, this suggests an equivalent usage in summer that might amount to 5 TWh of electricity (1.7% of total electricity demand). It is unlikely to be more, because even this small amount would be quite prominent in the electricity demand figures for the limited number of periods that require cooling in the UK. We allocate this total (which is an input that can be adjusted in the model) to hourly periods according to the extent the temperature exceeds a threshold temperature for cooling, on the basis of Met Office hourly temperature data.[4] We then subtract these synthesised figures from the electricity demand figures, to estimate the demand for conventional uses (lighting, equipment etc) so that the combined total is consistent with Elexon’s demand figures.
  3. The wind is another key weather input, as wind power is expected to play such a large part in the UK’s future electricity supplies. Fortunately, half-hourly electricity data are available in a cornucopia of details from Elexon’s website.[5] Wind output from Elexon is better as seed data than any figure for UK wind speeds, as it reflects the reality of where wind farms are actually located, and how their output responds (not linearly) to wind strength.
  4. UK solar capacity has become large enough for insolation to be another important weather variable. Figures for solar power connected to the transmission network are also available from Elexon, but this is complicated by the fact that the majority of solar is embedded. That has a double effect:
    • The available solar figures do not reflect national output, and
    • The embedded solar is treated as negative demand and affects Elexon’s demand figures

    However, the profile of grid-connected solar output is probably reasonably reflective of the profile of total solar output (although the embedded solar is probably somewhat less optimally positioned on average). So we can use Elexon’s solar figures for the hourly solar profile whilst discarding the absolute figures as only a fraction of the true figure. In our model, we treat solar as one homogeneous lump of capacity (undifferentiated as grid-connected or embedded), and likewise electricity demand as a gross figure exclusive of any embedded power, to minimise complexity. That means that the model figures for electricity demand will not match the metered figures and the figures in national statistics. But reverse-engineering these figures (by applying the solar profile to an estimate of embedded capacity based on subtracting the public figures for total capacity from Elexon’s figures for grid-connected capacity) should be reasonably accurate, and produce the same net effect.

  5. We do not incorporate other weather factors, such as rainfall, which have some impact (e.g. on hydro output and heat demand). These should be internalised approximately in the figures we use to estimate these components.

[4] We extracted this data while the Met Office had made their APIs freely available to the public, enabling us to download hourly data for their measurement points around the country. Unfortunately, they closed the public access in 2019, which is why our model uses data for the years 2016-2018, which were the years for which we obtained complete datasets before the API was closed.

2.2.3 Energy supply and demand (human behaviour)

2.2.3 Energy supply and demand (human behaviour) Bruno Prior Mon, 14/12/2020 - 22:20
  1. The other key exogenous factor is human behaviour, as reflected in patterns of usage.
  2. We have already explained how we generate estimates for hourly gas demand. To convert this into heat demand, we need to adjust for the other heat sources. Not all heat sources are used equally for the different uses of heat (e.g. space heating, hot water, cooking and industrial uses). Gas, as the predominant form of space heating in the UK, skews more heavily to space heating than some of the other heat sources. We cannot simply therefore apply the gas figures pro rata to the other technologies.
  3. One of those heat sources (oil) appears from national statistics to have a similar seasonal profile to gas, and we treat accordingly.
  4. Another heat source (wood fires and stoves) is used almost exclusively for space heating. The Domestic Wood-Use Survey of 2015 identified that (a) very few fires and stoves had back boilers (i.e. they were limited to space heating) and (b) around 40% of their heat was produced in summer, even though the respondents defined the summer period as the months when they did not burn wood.[1] These two “facts” are irreconcilably conflicting. We choose to believe the credible one: that most appliances do not have back boilers and therefore supply heat according to the profile for space-heating demand that can be extracted from the gas figures, not 40% in summer. This is actually an important factor in reducing the stresses of balancing the system, because wood burning is playing the role in this model that it plays in real life – helping to supplement the primary heat source during the coldest periods, when those primary heat sources would otherwise be under greater pressure.
  5. The other technologies show much less seasonality in the national statistics. There is not great variation between their quarterly splits, and we treat them homogenously. We estimate the residual hourly heat after subtracting gas, oil and wood’s shares on the above basis, and then divide it for each technology and hour pro rata to that technology’s share of the total and the balance between space heating (highly seasonal) and other heating (much flatter) within those residual figures. This is a broad assumption, but as reasonable a basis to allocate figures that are not available hourly as any other way that we could conceive.
  6. We apply conversion factors to each heating technology to estimate their fuel-use. This is an important difference from the conventional way of dealing with heat in the national statistics. Heat is traditionally treated as synonymous with the fuel used to produce it, in contrast to electricity, which is measured as the output of the conversion process after losses. The difficulty with treating heat this way is that differences in efficiency between some technologies are significant (e.g. heat pumps at one extreme and wood fires at the other), so one cannot simply switch their fuel consumption from one to the other. But it is an important part of the model to test different contributions from various heating technologies. We therefore reverse-engineer figures for heat outputs, i.e. the heat actually used, not the fuel used to produce it, applying reasonable conversion efficiencies for each technology and the hourly shares described above. The default heat demand figures therefore look smaller than in the national statistics, because they are net of conversion losses. When the model is run, it re-applies the conversion efficiencies to the hourly figures calculated from the seed data and the modeller’s choices, to calculate the usage of each fuel.
  7. For the electricity technologies (direct heating, air-source and ground-source heat pumps) this fuel usage under the default assumptions is deducted from the total demand figures to estimate conventional demand net of heat (and cooling, see below) in the seed data, so that changes to the use of electric heating can be reflected separately in the total electricity figures.
  8. Electricity demand is based on Elexon’s figures. Their out-turn figures (INDO and ITSDO) are the longest half-hourly series available. They are imperfect representations of demand, but the best we have for demand upstream and downstream of the transmission network.
  9. Interconnector flows are also based on Elexon’s data. This is a difficult area because the flows are determined not only by the UK’s needs but also by those of our counterparts at the other ends. Flows may be into the UK because we need the electricity and/or because a neighbour (e.g. France) needs to dump its excess. The best we can do is treat the historical figures as an indication of the elasticity (e.g. high export means either the UK really needed to shed load or the neighbour really needed the imports). We marry this to our model’s generated balance taking into account all the other variables, and assume that flows will reflect a balance of the factors. For example:
    • If we were historically exporting strongly in a period but our model predicts under different conditions that we would have a high need to import in that period, we assume that the UK would not choose to export, but the neighbour would have its own requirements that prevented substantial export to us, and treat it as a wash.
    • If historical flows were not large up or down in a period, and the model calculates that the UK needs to import or export heavily in that period under different conditions, we assume that the neighbour was not stressed and would be able to accommodate the UK’s requirements.
    • If the model predicts that the UK will not be under significant stress in a period, but a neighbour (most often Ireland) was relying heavily on us historically in that period, the model assumes that we will continue to accommodate that.
  10. Another difficulty of interconnectors is predicting the flows where they are planned with other neighbours for whom we have no historic data. The model accepts as an input the assumed capacity of each of the five existing routes under the conditions being modelled (e.g. the modeller can assume that each interconnector has been expanded or closed). It does not (yet) offer a means to add another interconnector with a different profile because there is no obvious way to generate that profile. This will obviously not mirror the real world when these new interconnectors arrive. It is just one more example of the limitations of modelling. Other models may use assumptions to address this problem, but their output will then be significantly conditioned by their assumptions rather than by the data and the model. Garbage In, Garbage Out.
  11. We have already covered most of the inflexible generation technologies: onshore and offshore wind and solar. We treat two other technologies as inflexible, i.e. their output is determined by their operation more than by demand.
    • Nuclear is the key one. Although it can be varied, its economics mean that it rarely is. It does, however, occasionally experience step changes when one of the units has to shutdown for maintenance. Each unit is so large that these steps are material. We reflect this by using Elexon’s figures for nuclear output to determine nuclear’s output profile in the model.
    • Biogas (e.g. anaerobic digestion, sewage gas and landfill gas) also tends to run relatively flat, not because it also couldn’t be varied (storage for a few hours of gas would not be too expensive or technically complex), but because of the incentives created by the subsidy regimes make it uneconomic to do anything other than export as the power is produced. We therefore use Elexon’s figures for this technology in the same way as for nuclear.

    To date, it is so rare for the output of inflexibles to exceed total demand that there is not a great issue of contention. But it has started to occur, and increasing capacity of some of these technologies means that it is likely to become a significant issue. The model therefore needs a method to decide how the output of inflexibles will vary where there is insufficient demand. Our merit order, based on the economics and engineering issues of de-rating and up-rating the technologies and the history of how this has been handled in the relatively rare cases to date is: nuclear, biogas, solar, onshore wind, offshore wind. This is another case where the assumption is highly imperfect (for instance, in reality, it will vary within technology depending whether the projects are embedded or grid-connected) but some method must be chosen, and no other seems superior.

  12. The other generation technologies are treated as dispatchable, even though some (e.g. solid biomass) have been in a halfway house to date, created by the tension between their incentives (produce baseload to maximise subsidy) and the network requirements (marginal costs are higher than the inflexibles, so when the latter’s output approaches total demand, biomass has to de-rate). Our cost data (covered below) differentiates between capital, flat-operating (£/period) and variable-operating (£/MWh) costs, and the model can therefore estimate marginal costs for the generating technologies treated as dispatchable (gas, oil, coal, solid biomass and hydro). We do not use seed data for these technologies, as their output has to be treated as one of the key ways to balance the inflexible elements of supply and demand.
  13. Large volumes of intermittents mean increasing periods where some output has to be constrained. The subtly-different concepts of “load factor” and “capacity factor” both refer to outcomes, not potential. In order to differentiate between what technologies would deliver unconstrained and what they actually deliver having been constrained, the model uses a concept we have termed “availability factor”, meaning the load factor that they would achieve if they were not constrained. We use this to estimate what each technology would like to supply if not constrained. We then apply constraints according to our assumed merit order. Over a year, the load factor is the constrained availability factor. To allow for technical improvements, we differentiate between the historic availability factor for existing capacity and the availability factor for new capacity. The default availability factors for new capacity of most technologies is materially higher than the historic. They can be varied by the modeller.
  14. There is limited storage in our energy systems at present, but this will be one of the key factors in balancing our future energy systems. The model allows the modeller to specify MW, MWh and round-trip efficiency for each of three technologies: pumped-hydro, batteries and compressed-air storage. But no seed data are used beyond reasonable defaults for these values, as these technologies by definition will be used to respond to the balance, which is a key output of the model.
  15. Transmission and distribution losses are treated as a function, not as an input. Comparison of Elexon’s INDO and ITSDO data reveals that losses are greatest as a proportion when demand is lowest. Losses are calculated by spreading an assumed annual average loss factor (combined for transmission and distribution) across each hourly figure according to a simple formula that reflects this historic behaviour. The loss factor can be varied by the modeller.
  16. Heat demand is not only a function of the weather, but also of investments that may be made in future, whether in energy-conservation or the construction of more heat uses (e.g. homes or businesses). There has been a tendency in some models in the past to treat improvements in this factor as a way of magically resolving some of the tensions, by treating demand components as inputs for the user to specify.
  17. We wanted to ensure a more realistic approach, as this is an important and often-abused factor. The model therefore treats the demand from various uses not as an input, but as an output determined by inputs such as:
    • the proportion of the existing building stock that has been improved to modern standards with regard to loft, cavity-wall and solid-wall insulation, and glazing, with an indication of the current proportions that are considered easy or difficult to improve, and
    • the number of new houses and flats that have been built and the standards to which they have been built.
    • the number of existing buildings demolished can also be accommodated by reducing the total figures under the section for existing buildings. The model relies on the modeller to choose realistic figures for the combined number of existing, demolished and new-build buildings. An unrealistic modeller could skew outcomes by assuming that we shall all live five to a flat in future. But they will then have to explain how that is desirable and deliverable in a democracy.
  18. These calculations rely on seed data for the cost and efficacy of building improvements and standards, drawn from government statistics, set out in a blog piece on the C4CS website.[2]

2.2.4 Costs

2.2.4 Costs Bruno Prior Mon, 14/12/2020 - 22:24
  1. Our generating-cost data are drawn from a number of sources, and incorporate a significant amount of judgment as the information is rarely consistent. We differentiate between the costs of existing capacity and costs of new capacity to allow the modeller to test learning-curve assumptions. In the case of technologies dominated by old installations (nuclear, biomass, hydro and coal), the existing capital costs reflect an estimated book value, as their main use will be to estimate the cost of decommissioning them. For gas, “existing” is assumed to be CCGTs, but “new” is assumed to be OCGTs or similar, for market reasons, and to allow to differentiate within the model.
  2. The defaults can be adjusted by the modeller. The variable cost incorporates the fuel cost (after conversion losses), and is therefore likely to be an important factor for sensitivity testing.

    Technology

    Capital (£/kW)

    Fixed (£/kW/yr)

    Variable (£/MWh)

     

    Existing

    New

    Existing

    New

    Existing

    New

    Solar

    1300

    1000

    10

    10

    0.05

    0.05

    Biogas

    4000

    3500

    300

    300

    -10

    -10

    Nuclear

    1300

    6000

    150

    140

    11

    10

    Onshore wind

    1500

    1250

    30

    25

    0.05

    0.05

    Offshore wind

    3600

    3200

    100

    65

    0.05

    0.05

    Biomass

    200

    3500

    40

    60

    90

    110

    Hydro

    100

    3200

    5

    5

    0.05

    0.05

    Gas

    500

    350

    17

    10

    45

    65

    Coal

    300

    1000

    10

    10

    25

    25

    Oil

    300

    300

    10

    10

    135

    135

  3. Defaults for transmission/distribution costs provide the basis for estimates of network costs in choices that increase maximum or change total flows. These currently cannot be modified, simply because we have not provided the interface. They are easy to adjust within the model, and we will provide an interface in due course. For now, they are:

    Capacity (MW)

    Capital (£/kW)

    Fixed (£/kW/yr)

    Variable (£/MWh)

    Existing

    New

    Existing

    New

    Existing

    New

    Existing

    New

    60000

    0

    450

    1000

    100

    150

    5

    6

    We do not yet incorporate equivalent costs for the gas network. This is a significant omission that needs correcting.

  4. Storage costs are based on published claims from a variety of sources. With so little deployment, these figures must be regarded as highly speculative, particularly for compressed-air storage for which there are almost no cost data from the sustained operation of substantial installations. We have naively accepted the developers’ claims for wont of a reasonable alternative approach, but these figures should be treated with great caution until proven in sustained operation. Pumped storage and batteries have more of a track record, but are limited in the UK and (in the latter case) limited at scale across the world. We do not yet know how learning curves would balance against resource pressures if they are widely deployed beyond the already-massive scale expected for transport. Treat with caution, but FWIW, these are our defaults:

    Technology

    Capital (£/kW)

    Capital (£/kWh)

    Fixed (£/kW/yr)

    Variable (£/MWh)

    Existing

    New

    Existing

    New

    Existing

    New

    Existing

    New

    Pumped storage

    15

    160

    160

    1000

    10

    10

    0.1

    0.5

    Batteries

    300

    240

    300

    240

    10

    5

    0.5

    0.05

    Compressed air

    1500

    1000

    40

    30

    2

    1

    0.1

    0.05

  5. Two components of capital cost are given for storage because, unlike other aspects of our energy systems, storage capacity is defined in terms of both power (kW, momentary flow) and energy (kWh, sustained flow). These components are additive in the model; e.g. if the capital cost is £1500/kW and £40/kWh, a storage unit rated at 1 MW and 6 MWh costs £1,740,000.
  6. As for nuclear, hydro etc above, the capital-cost values for pumped storage are an estimate of the book value/decommissioning cost, as the main use of the figure is to estimate the cost if the units were closed down.
  7. The variable operating costs do not include round-trip losses, which are calculated separately based on the import and export prices generated by the model and the assumed round-trip efficiency for the technology. These are one of the most significant factors in the economics of storage systems.
  8. The model assumes each technology is half-full at the start of the year, to allow for some charging or discharging, depending on the initial conditions.
  9. The supplier’s margin is a significant component of the total energy cost. For electricity, we incorporate the following defaults that cannot currently be modified, based on the Big Six’s Consolidated Segmental Statements. The same comments apply as in the previous section, vis-à-vis the interface and the need for equivalent figures for other fuels. These are total costs to be spread over the whole system. This implies no change in the suppliers’ combined costs if volumes change significantly (e.g. with electrification), which is obviously an unsafe assumption. But there are insufficient data to judge how they might vary, and the magnitudes within a probable range are not so large that this imprecision is likely to weigh heavily on the outcomes. One would expect significant economies of scale from electrification. It is not obvious why there are substantial capital costs in the supply business, but that’s what their accounts say. It’s a large number, but small when amortized.
    • Capital cost: £4bn
    • Fixed cost: £1.5bn p.a.
    • Variable cost: £10/MWh
  10. We provide defaults for two cost factors that have wide ramifications:
    • The Weighted Average Cost of Capital: 8%
    • The Cost of Carbon: £50/tCO2e
  11. The construction and operating costs above do not include a cost of carbon, which is applied separately so it can be seen as a separate component, to compare the costs of the chosen options with their carbon value. That comparison can be viewed two ways if it is not favourable:
    • The investment may not be justified by the carbon benefit, or
    • The assumed price for carbon is incorrect if necessary investments are not justified by their notional carbon saving.
  12. If the latter, the modeller can adjust the carbon price accordingly. This will propagate through all aspects that engender a carbon cost/saving.
  13. The modeller should not adjust the carbon price to suit their favoured technologies and ignore the impact on other technologies whose economics may be improved even more by the change. This should avoid perhaps the most common way that energy-system models produce skewed outcomes: by treating different components as though they have different carbon values. We can argue about the true cost of carbon, but whatever it is, it must apply equally to all emissions or sequestrations of carbon. The climate does not care where the greenhouse gases come from, and how they are engendered makes no difference to the harm that they do.
  14. To convert cost elements into hourly costs/prices, the model assumes that (a) over a year, each technology must cover its costs including the amortized capital cost and cost of money, but (b) the price for output from each technology in each hourly period is a function of (i) its operating costs and (ii) whether the market is long or short (given the technology’s position in the merit order list). The price in long (i.e. over-supplied) conditions is the marginal operating cost. The price in short conditions is the operating cost plus an apportionment of the fixed/capital costs sufficient (when combined over all long-market periods) to achieve (a) over the year. The overall price of electricity in each period is the cost of the marginal technology in that period, given the merit order. For example:
    • If the market is short and some gas-fired generation is required, the price of electricity in that period is the price of gas-fired electricity, and as the market is short, the price of gas-fired electricity is its operating cost plus an apportionment of its fixed/capital costs. If gas’s annual load factor is depressed because of high inflexible capacity producing many periods when gas is not required, the cost of gas-fired electricity in the periods when it is required will increase as the fixed/capital costs are spread over fewer periods.
    • If the output from inflexible generators exceeds demand, the market is long, and the price is determined by the marginal operating cost of the last technology in the merit order required to meet that demand (typically offshore wind). The marginal operating costs of wind and solar are considered to be very low, so the marginal price of electricity in a long market is typically in this model very low. These are favourable assumptions for the deployment of storage, but hopefully realistic (i.e. the world towards which we are being driven is one in which storage should be able to buy electricity cheaply and sell at a high price).
  15. We do not take account of any government incentives in the cost calculations. The model is intended to explore the true underlying economics. Government incentives (other than a carbon tax) skew the economics of different technologies significantly. If the pricing generated by this model differs significantly from the real world, this is the biggest reason, and gives a measure of the skew.

2.2.5 Operational assumptions

2.2.5 Operational assumptions Bruno Prior Mon, 14/12/2020 - 22:34
  1. We provide defaults for the existing installed capacity and availability factors. These are based on figures from around the turn of 2018/19, when we were developing this model. In some cases (wind and solar), these figures are materially out of date. They can be adjusted by the modeller. We have chosen not to modify the defaults to the current position because to some extent they are aligned to the hourly seed data, although this is not a major factor as the seed data is used for the profile, not for absolute figures. The model is primarily about the future, so most of these values will be taking fresh inputs anyway, so the starting point is not significant, except that the base case for comparison will be roughly 2016-18, not 2020.
  2. The current reported capacities of the UK’s five interconnectors (one of them internal, to Northern Ireland) are given as the defaults, but can be modified to model increased interconnection capacity. We do not attempt to model the costs of interconnection. We do not have good data, and the national share of the costs would depend on the balance of import and export, which may vary depending on model assumptions. They arguably lie outside our system boundaries, although if an interconnector were built mainly to satisfy the UK’s needs, we should take account of that cost within overall system costs.
  3. The only aspect of transport fuel consumption that the model currently attempts to estimate on an hourly basis is that component that is electrified, in order to contribute to the overall electricity figures. It is in the nature of most forms of transport that there is no regular metering of usage, so granular data are not available. Longer-frequency estimates suggest a fairly predictable rhythm to road usage. We estimate hourly usage on the basis of reasonable and simple rules-of-thumb, e.g. usage is higher during the week than at weekend, highest around the rush hours, and marginally higher in summer than winter, but that this will be combined in the case of electric transport with choices to charge off-peak as far as possible.
    • The annual usage of fossil fuels and electricity are inputs with defaults based on current usage. They are allocated to hourly periods on the above basis.
    • An important constraint is that the model recognises the significant differences in on-vehicle conversion efficiency between Internal Combustion Engines (ICE) and electric motors, and tries to ensure that an adjustment to one is balanced by an equivalent adjustment to the other, such that the total post-conversion energy is not altered by a change to one component, though that total can be adjusted by the modeller. For example, given that electric motors are assumed by default to be 3.4 times more efficient than ICE on average, if we increase electricity’s share of road transport by 1 TWh, we reduce the non-electric component by 3.4 TWh and the total by 2.4 TWh. These default efficiency assumptions can also be varied by the modeller. The default efficiency for electric vehicles may look relatively low to proponents of the technology, but this is intended to reflect not only the efficiency in motion, but also inefficiencies in the charging process. We believe this is more realistic than the utopian figures sometimes used for electric-vehicle efficiency, but the modeller can apply their own assumptions. We have also seen lower efficiencies used by electric-vehicle sceptics.
    • Another important assumption in the model is that users have some but not unlimited ability to choose to charge their electric vehicles when other electricity demands are low and prices are then presumably also low, and conversely avoid charging during peak demand periods. In other words, we assume that electric vehicles will provide a significant degree of demand smoothing to help with balancing, but that this will be largely preset according to behavioural patterns and expectations, and not responsive to unexpected system pressures outside expected patterns.
    • There is a lot of talk of using vehicle batteries for electricity-system demand responsiveness. It seems to us that, whereas this might be true on the crude basis described above, it is fanciful on a more directed, on-demand basis. For example, few people will choose not to charge their car overnight so that they are unable to go to work the next day, no matter how much the system might need them to. This would have to be imposed against their will, and would be political suicide for any government attempting to instigate the capability. It is not inconceivable in this world of overmighty bureaucracies and misanthropic advisers, but we choose to assume a more benign, if less exactly-managed, world.

2.2.6 Carbon

2.2.6 Carbon Bruno Prior Mon, 14/12/2020 - 22:37
  1. Carbon emissions are another output of the model. They are based on figures for carbon intensity that rely heavily on the UK government’s Greenhouse Gas Conversion Factors and related statistics, although it was necessary to cast the net more widely to encompass online articles for estimates of the construction emissions. These assumptions cannot currently be varied by the modeller. They are also affected by the efficiency assumptions.
  2. To make a fair comparison between technologies with high energy inputs at the construction phase but low fuel consumption in operation and those that have the reverse pattern, we attempt to take account of both the operating emissions (e.g. fuel combustion) and also the construction emissions. However, we do not attempt to combine them into lifecycle emissions.
  3. The operating emissions are taken into account within the annual system costs, but the infrastructure emissions are recorded as a separate item, both in their own right and under the investment heading as the carbon element of the capital components of costs. Our assumptions are in the table to the right/below.

Technology

Operating emissions (tCO2e /MWh of fuel consumed)

Construction

/embodied emissions (tCO2e/MW)

Gas

0.2

45

Oil

0.25

35

Coal

0.33

380

Biomass

0.015

380

Biogas

0.0002

35

Liquid biofuels

0.0035

-

Hydro

0

500

Onshore wind

0

730

Offshore wind

0

840

Solar

0

1700

Nuclear

0

1250

Pumped storage

-

40

Batteries

-

40

Compressed air

-

20

Interconnection

-

10

Transmission

-

21

2.2.7 Demand-side management

2.2.7 Demand-side management Bruno Prior Tue, 15/12/2020 - 09:47
  1. Demand-side management (i.e. encouraging people not to use energy when the systems are stressed) will be an important tool to maintain system stability in a world where energy is less dispatchable. There is little historic data on which to base assumptions about the cost of demand shedding. But a few simple economic basics suggest a model:
    • The minimum cost must be more than people are paying for their electricity, or they would not be using the electricity.
    • Willingness to curtail demand will be marginal. We may find a few users willing to curtail at the minimum cost, but as the scale of curtailment grows, people’s willingness to pay not to be curtailed (i.e. to pay for power, which equates to the opportunity cost of curtailment) will increase.
    • This applies both to the scale and the frequency, i.e. each extra GW of curtailment in each period will be more expensive than the previous, and also each time someone has to curtail, it will be a bit more expensive to them than the last. Consider a manufacturing business asked to limit its electricity usage for one hour in the year. At a price, the cost is probably not too significant (depending on circumstance). Now consider if that business is asked to curtail for a week. It would at least be difficult and could be enough to put them out of business. They might accept a reasonable offer for the first, but would want a very high offer for the second.
  2. Our model assumes that the minimum cost of demand shedding is £200/MWh. Each additional GW that has to curtail in a period is 10% more expensive than the last. And each time a GW tranche has to curtail in the year, the cost is 1% more expensive than previously. For example, if we need to curtail 1 GW in one period and then 2 GW in another period:
    • The 1st period is 1 GWh x £200/MWh = £200,000
    • The 2nd period is (1 GWh x £202/MWh) + (1 GWh x £220/MWh) = £422,000
    • Total cost of demand shedding for the two periods: £622,000
  3. The effect is roughly what one would expect: small amounts of demand shedding lead to a modest cost. At this scale, it is quite likely a more economic solution for marginal circumstances than providing additional generating capacity or storage to meet the last few GWh of occasional demand (where there is insufficient dispatchable capacity). But, if the system needs frequent and large amounts of demand-curtailment, the cost would rise exponentially. The 3-day week was a lot more expensive than simply the cost of the missing energy.
  4. These costs would apply whether demand-side management were achieved contractually, or were imposed by the system operator. That simply changes the parties on whom the costs fall: on the operator in the first case, and on the users in the second case. The opportunity cost is the same. In the first case, the cost ends up falling on all consumers via the system operator’s charges. In the second case, a significant part of the cost cascades to government coffers (and taxpayers) because of the hit to taxes and welfare. There is no such thing as a free lunch. Rationing is simply a less responsive means of allocating resources than the market.

2.2.8 Other elements

2.2.8 Other elements Bruno Prior Tue, 15/12/2020 - 09:53
  1. The model does not currently accommodate hydrogen, whose profile has risen disproportionately to its credibility since we started putting together this model. This is an omission that we shall have to rectify.
  2. The model also does not yet incorporate carbon-sequestration technologies, whether mechanical/chemical Carbon Capture and Storage (the “U” for “Use” in the trendy recent variant, CCUS, does not constitute sequestration and does not need to be accommodated) or natural methods such as afforestation. This also needs remedying in due course, to the extent that there is any point pursuing the illusion of perfection in this kind of exercise (see the Introduction).