Archived publication
This publication is no longer current or has been superseded.
Ministry of Economic Development, April 2008
This report covers emissions from energy and industrial processes. Energy emissions covered are those associated with electricity generation, transport and direct use in the residential, commercial and industrial sectors.
Industrial process emissions are the non-energy emissions ie, those that occur during:
The energy sector contributes around 40 per cent of New Zealand’s total greenhouse gas emissions.
On average, around two-thirds of New Zealand’s annual electricity needs are met by hydro-electric generation. The balance is provided by fossil-fuelled thermal generation using natural gas and coal, and other renewable sources such as geothermal and wind.
Around 40 per cent of energy emissions are from the transport sector. Emissions for this sector have grown significantly since 1990, averaging over three per cent growth per annum. The growth in transport emissions is largely due to the increased use of petrol and diesel as well as increased use of aviation fuels.[New Zealand's Greenhouse Gas Inventory 1990-2006, Ministry for the Environment, April 2008, http://www.mfe.govt.nz/publications/climate/greenhouse-gas-inventory-overview-apr08/index.html] Recent increases in the price of liquid transport fuels appear to have resulted in a reduction in the growth rate of demand for liquid transport fuels.
Industrial processes contribute around six per cent of New Zealand’s total greenhouse gas emissions, with most emissions coming from the metal industry.
In general, changes in energy emissions in New Zealand are linked to the overall rate of consumption within the economy. Emissions therefore tend to increase steadily over time, driven by economic growth.
There can be significant year-to-year fluctuation in emissions from electricity generation, with increased thermal generation in a ‘dry’ hydro year.
Historically, fluctuations in the price of liquid transport fuels have had a limited impact on consumption and emissions. However, the very large recent increases in the price of liquid transport fuels appear to have resulted in a reduction in the growth rate of demand, and therefore emissions from the transport sector.
Projections of emissions from energy (including transport) and industrial processes are largely derived from the Ministry of Economic Development’s Supply and Demand Equilibrium Model. SADEM is a collection of models, each representing the supply of a form of energy, or the demand from a sector of the economy. The sub-models buy and sell from each other just like in a real market. The Ministry has used SADEM since the early 1990s for internal policy analysis and to make projections of New Zealand’s energy supply, demand, prices and emissions.
Modelling CO2 emissions from combustion is fairly straightforward, since the output of CO2 depends on the amount of each type of fuel being burned. Emissions of other greenhouse gases and of CO2 from non-combustion activities, eg, industrial processes, are more complicated to estimate and depend both on the amount of fuel and on the way the fuel is used.
Since the Net Position 2007 report, a number of enhancements have been made:
This section provides an overview of the key assumptions used. An effort has been made to align modelling assumptions across government, and with the assumptions underpinning the New Zealand Energy Strategy. Macroeconomic assumptions are in line with Treasury projections, milk solids projections are supplied by the Ministry of Agriculture and Forestry (MAF) and fuel price assumptions are consistent with those recommended by the Energy Data and Analysis Coordination Group (EDAC).[Recommended Input Assumptions, MED, 7 January 2008, http://www.med.govt.nz/templates/MultipageDocumentPage____33244.aspx. (The horizontal rule in each MED web address represent four underscore characters)]
Table B1: Most likely scenario for key macro-economic assumptions for CP1
| Year | Economic growth |
Exchange rate |
Oil prices |
|---|---|---|---|
2007 (actual) |
3.00 |
0.736 |
100 |
2008 |
2.09 |
0.738 |
100 |
2009 |
2.73 |
0.697 |
100 |
2010 |
2.67 |
0.652 |
100 |
2011 |
2.87 |
0.622 |
100 |
2012 |
2.87 |
0.607 |
100 |
The government has decided in principle that New Zealand will use an emissions trading scheme (ETS) as its core price-based measure for reducing greenhouse gas emissions and enhancing forest carbon sinks. The government has also proposed a staged entry of different sectors into the ETS:
Coal prices are based on import parity prices around $4.00 per GJ.
The rate of new gas discoveries is assumed to average 60 PJ/year with production from new discoveries starting in 2012.[http://www.med.govt.nz/templates/MultipageDocumentPage____33244.aspx]
Methanex is the gas-to-methanol operation in Taranaki. Based on recent announcements by Methanex, it is assumed that it will increase production at Motonui from 2008 and that the smaller Waitara Valley plant will continue operating until mid 2008.
Energy efficiency measures included in Net Position 2008 are those evaluated as part of the Benefit Cost Analysis of the New Zealand Energy Strategy. These are assumed to be 100 per cent implemented in the most likely case, and 120 and 80 per cent in the low and high emissions scenarios. An “upside” factor has been incorporated to account for increased energy use resulting from the greater uptake of electrical appliances, eg, heat pumps, and take-back effects not included in the models, eg, purchase of larger plasma televisions.
An approximate saving of 2,100 kWh per unit per year from the solar water heating programme is assumed. The programme is funded for three-and-a-half years, therefore we assume no additional solar water heating units installed as a result of the programme beyond 2010.
The Projects to Reduce Emissions (PRE) programme allows firms to receive tradable emissions credits for each tonne of carbon emissions saved. Credits have been awarded for a number of projects, with the majority of eligible projects in the electricity generation sector.
The heavy industries section is under continuing review and sector-specific discussions take place at various times. Key assumptions are:
It is assumed that energy use and emissions from the New Zealand Refinery Company will be steady over time, with a step change occurring following the expected 20 per cent capacity expansion in 2009. This is consistent with Net Position 2007.
In projecting transport emissions it is assumed that the proposed Biofuel Sales Obligation levels are met, which will require biofuels sales of at least 3.4 per cent of total diesel and petrol sales by 2012.[Cabinet Decision, http://www.mot.govt.nz/biofuels-440-index/] It is assumed that this fuel will be used by the transport sector; tail-pipe CO2 emissions produced from this fuel are not included in the Net Position. CH4, and N2O emissions produced from this fuel are included.
Bio-diesel is assumed to supply 30 per cent of the sales obligation and from bio-ethanol 70 per cent.
In Net Position 2007, the Ministry of Agriculture and Forestry’s dairy herd projections were used to project the dairy sector’s energy demand. Enhancements had been made to SADEM for Net Position 2008 whereby MAF’s milk solids production projections are used to project energy demand.
MAF’s projections take account of the recent drought conditions which have significantly reduced projected milk solids production, resulting in a decrease in the dairy sector’s energy demand over CP1.
The Vehicle Fleet Emissions Model (VFEM) has been used for the transport projections. The VFEM models changes to New Zealand’s on-road vehicle fleet, including the number of vehicles, kilometres travelled per vehicle and average fuel economy and adds a level of refinement to estimates of on-road transport energy demand. It also allows an improved estimate to be made of the off-road and non-motor vehicle uses of petrol and diesel. This time series is itself projected forward to give a total projection of future land transport energy demand.

The schematic illustrates an overview of the transport emissions modelling. All of the details in the figure are contained within the paragraph above.
The Ministry of Economic Development models carbon dioxide emissions from industrial processes, which is then adjusted to account for non-carbon dioxide greenhouse gases. A multiplier of 17.6 per cent is used.
Table B2: Energy demand sectors and modelling techniques used
| Major demand sector | Sub-sector |
Model |
|---|---|---|
Residential demand |
Residential |
Multivariate, GDP, price, heating and cooling degree days, lagged demand |
Industrial and commercial demand
|
Forestry |
Industry-specific forecasts |
Petrochemicals and refining |
Company forecasts |
|
Metals |
Industry-specific forecasts |
|
Dairy |
MAF forecasts (as input) |
|
Other industrial |
Multivariate, GDP, lagged demand |
|
Commercial |
Multivariate, GDP, lagged demand |
|
Transport demand
|
Land |
On road: Vehicle Fleet Emissions Model MoT/MED forecast |
Off road: Multivariate |
||
Sea |
Ordinary least squares |
|
Aviation |
Ordinary least squares |
The impact of two new policy measures have been incorporated into the modelling for Net Position 2008.
In September 2007, the government announced its in-principle decision that New Zealand will use an emissions trading scheme (ETS) as its core price-based measure for reducing greenhouse gas emissions and enhancing forest carbon sinks.
The impact of introducing an emissions price on energy and industrial process activities has been incorporated into the projected emissions over CP1.
The government is considering regulatory options to limit investment in baseload fossil-fuelled thermal electricity generation. The projections generated for Net Position 2008 do not include the commissioning of any new baseload thermal electricity generation capacity over CP1.
The New Zealand Energy Efficiency and Conservation Strategy (NZEECS) was released in October 2007. It contains a range of measures to improve energy efficiency throughout the economy, and the impact on emissions of these measures has been incorporated into Net Position 2008.
Total emissions from energy and industrial processes are projected to be 163.7 Mt of carbon dioxide equivalent for the first Kyoto Commitment Period.
Table B3: Emissions by sector during the First Commitment Period (kt CO2-e)
| Year | Energy |
Transport |
Industrial Processes |
Total |
|---|---|---|---|---|
2008 |
18,759 |
14,346 |
4,330 |
37,434 |
2009 |
18,632 |
14,287 |
4,361 |
37,280 |
2010 |
18,483 |
14,170 |
4,393 |
37,046 |
2011 |
18,128 |
14,147 |
4,427 |
36,702 |
2012 |
18,374 |
14,326 |
4,461 |
37,161 |
Total CP1 |
92,377 |
71,274 |
21,972 |
185,623 |
Projected emissions from electricity generation are around 5 per cent lower than for the 2007 Net Position.
This is primarily due to:
Transport sector emissions are projected to be 8.9 million tonnes CO2-e lower over CP1 than projected in 2007. The primary reasons for this are:
Projected emissions from industrial processes are effectively unchanged from the 2007 projections.
The following is a non-exhaustive list of conditions that could affect actual emissions over the First Commitment Period:
The ‘high’ and ‘low’ emissions scenarios provide an indication of the range of uncertainty in the projections. The table below presents the results of these two scenarios, compared to the 2008 ‘most likely’ scenario:
Table B4: High and Low emissions scenarios, and assumptions made
| Scenario | Assumptions |
Total emissions from Energy and Transport during CP1 (CO2-e) |
|---|---|---|
Low Emissions Scenario |
Low GDP growth Low population growth Carbon price $NZ50 per tones of CO2-e Low milk solids production numbers Methanex not operating after 2010 Biofuels obligation exceeded Energy efficiency gains increased Wet hydrological conditions |
152.2 Mt (–11.4 Mt compared to 2008 ‘most likely’ case) |
High Emissions Scenario |
High GDP growth High population growth Carbon price $NZ15 per tonne of CO2-e High milk solids production numbers Methanex Motonui plant running during CP1. Waitara Valley plant running between 2013 and 2020 No biofuels No energy efficiency and conservation No solar water heating programme Dry hydrological conditions |
179.2 Mt (+15.6 Mt compared to 2007 ‘most likely’ case) |
In conclusion, the projected balance of emissions from energy and transport during CP1 lies in the range between 152.2 and 179.2 with the most-likely scenario of 163.7 million tonnes of carbon dioxide equivalent. This compares with a range from 162.8 million tones to 187.7 million tones in 2007 Net Position