There are a number of different national policies that could be applied to manage greenhouse gas emissions from landfills. These range from continued guidance, economic instruments, climate projects, national environmental standards, through to the 'do nothing' and status quo.
The following sections set out these options and look at their appropriateness for achieving the stated objectives for landfill gas emissions.
In order to find the most appropriate option for controlling landfill gas emissions, the Ministry has considered a list of potential options. These have been analysed, and for the purposes of this report only the following options have been considered in detail:
Prior to the introduction of the Resource Management (Energy and Climate Change) Amendment Act 2004, the majority of regional councils were requiring large landfills to collect and destroy methane. However, the Amendment Act removes the ability of regional councils to consider the effects on climate change from air discharges, which means there is no certainty that regional councils will continue to place controls on landfill gas emissions.[Note that regional councils could still require management of landfill gas for health and safety and nuisance impacts.]
For the purpose of this analysis, 'status quo' refers to the Government continuing with its promotion of best practice through advocacy of the Centre for Advanced Engineering's Landfill Guidelines, and regional councils not being able to consider the effects of climate change from air discharges.
Tables 1 and 2 set out two types of analysis. Table 1 examines the advantages and disadvantages of the option while Table 2 looks at whether the option achieves the stated objectives.
Table 1: Advantages and disadvantages of the status quo option
|
Advantages |
Disadvantages |
|---|---|
|
There would be no extra monetary costs for all parties. |
The amount of methane emitted from landfills could rise. |
|
No new regulation is required. |
New Zealand may not be able to meet its climate change commitments under the Kyoto Protocol. |
|
There would be no formal control of landfill gas except for health and safety and odour issues. |
Table 2: Assessment of status quo against the objectives
|
Objective |
Does this option meet this objective? |
|---|---|
|
To help New Zealand meet its obligations under the Kyoto Protocol |
No |
|
To establish nationally based landfill gas management for greenhouse gas emissions |
No |
|
To provide certainty for the waste management industry |
No |
|
To encourage the diversion of organic waste from landfills into composting and other uses |
No |
This option clearly does not achieve the stated objectives. However, the use of this option as a baseline in the analysis is crucial in comparing the benefits and costs of other options.
This is similar to the status quo, but with the inclusion of the climate change project mechanism. The climate change project system means applicants can apply for a grant of carbon credits if they have a project that will decrease the amount of greenhouse gas that would have otherwise been emitted into the atmosphere when compared to business as usual. In turn, these project operators can sell these credits to other nations who produce more carbon than their quota, thus generating income. A number of landfill operators have recently received credits, and this option assumes that a similar process continues into the future.
Tables 3 and 4 set out two types of analysis for this option. Table 3 examines the advantages and disadvantages of this option, while Table 4 looks at whether the option achieves the stated objectives.
Table 3: Advantages and disadvantages of the 'status quo plus projects' option
|
Advantages |
Disadvantages |
|---|---|
|
There would be relatively low costs (dependent on the extent of funding of projects). |
This option may create an incentive for landfill operators to exaggerate their estimated emissions to receive more carbon credits. |
|
No new regulation is required. |
It does not fully address the issue of emissions growth. |
|
Landfills that currently capture and flare landfill gas are unlikely to qualify for carbon credits. There is no certainty that the Government will continue to offer carbon credits through the Climate Change Projects Mechanism. |
Table 4: Assessment of 'status quo plus projects' against the objectives
|
Objective |
Does this option meet this objective? |
|---|---|
|
To help New Zealand meet its obligations under the Kyoto Protocol |
Partially |
|
To establish nationally based landfill gas management for greenhouse gas emissions |
No |
|
To provide certainty for the waste management industry |
No |
|
To encourage the diversion of organic waste from landfills into composting and other uses |
Partially |
This option is not appropriate because it does not meet the crucial objective of establishing nationally based landfill gas management greenhouse gas emissions.
This option would involve placing a tax or charge on landfill gas emissions, whereby a polluter is forced to pay a certain amount of money for every unit of pollutant emitted. The aim of such an option is to provide an economic incentive for landfill operators to minimise emissions and in this case divert organic waste or collect and flare their gas. This option may also form the basis of a tradable permit scheme.
The RMA supports investigating imposing financial charges, but the Act, on its own, would not facilitate the use of charges. Changes to existing legislation would likely to be needed. A question also remains over the ability to trade discharge permits.
Tables 5 and 6 set out two types of analysis for this option. Table 5 examines the advantages and disadvantages of this option, while Table 6 looks at whether the option achieves the stated objectives.
Table 5: Advantages and disadvantages of the 'economic instruments' option
|
Advantages |
Disadvantages |
|---|---|
|
The charge could raise revenue that is then recycled to encourage the further reduction of greenhouse gas emissions. |
Methane quantities from individual landfills are difficult to measure because they require a high level of accuracy. This would inevitably result in the use of estimates, which can create large differences when emission charges are high. |
|
A tradable permits regime offers a method to encourage efficiency and cost savings. |
The charge would be costly to implement due to the high measurement and verification costs. The charge would need to be very high (higher than the cost of infrastructure) to actually encourage methane capture. This option may require alternative legislation or an amendment to the RMA - a costly and time-consuming process. |
Table 6: Assessment of 'emissions charge' against objectives
|
Objective |
Does this option meet this objective? |
|---|---|
|
To help New Zealand meet its obligations under the Kyoto Protocol |
Yes |
|
To establish nationally based landfill gas management for greenhouse gas emissions |
No |
|
To provide certainty for the waste management industry |
No |
|
To encourage the diversion of organic waste from landfills into composting and other uses |
Yes |
This option is not appropriate for a number of reasons. There are questions over its feasibility (particularly under the RMA in its existing form), and it does not meet the objectives of establishing nationally based landfill gas management greenhouse gas emissions to provide certainty for the waste management industry. If a tradable permit approach were found to be feasible, there would still need to be some sort of emissions cap (to establish a 'cap and trade' programme, for example). To sum up, as a stand-alone option the use of charging or a trading regime will not achieve the stated objectives.
The Resource Management (Energy and Climate Change) Amendment Act 2004 specifies the use of national instruments to control greenhouse gas emissions. The Act makes explicit mention of national environmental standards in this regard:
New section 70A removes the power of regional councils, in making rules on the discharge of greenhouse gases into air, to have regard to the effects of a discharge on climate changes ... new section 70B permits regional councils to make rules as necessary to implement a relevant national environmental standard made by regulation under section 43.
New section 104F provides, as a further exception to the prohibition in new section 104E, that regional councils may determine the specified applications that are necessary to implement a relevant national environmental standard made by regulation under section 43, but must be no more or less restrictive than the national environmental standard being implemented.
Due to the specific reference to national environmental standards within the Amendment Act, consideration of national instruments is restricted to the consideration of a national environmental standard, and not other alternatives such as national policy statements.
National environmental standards are regulations that set a national technical standard that all operators in the country are required to meet. The proposed standard sets a consistent national approach by specifying the requirement to collect and destroy landfill gas emissions for landfills over a million tonnes in capacity, unless the landfill contains less than 5% organic matter.
Tables 7 and 8 set out two types of analysis for this option. Table 7 examines the advantages and disadvantages of this option, while Table 8 looks at whether the option achieves the stated objectives.
Table 7: Advantages and disadvantages with the 'NES' option
|
Advantages |
Disadvantages |
|---|---|
|
Ensures that greenhouse gas emissions from landfill sites are controlled. |
Regulations can be costly and time consuming to implement - less so in this case. |
|
Sets a national approach to the management of greenhouse gas emissions from landfill sites. |
Additional resourcing requirements would be placed on regional councils and landfill consent holders to implement and enforce the NES. |
|
Gives regional councils the ability to control greenhouse gas emissions from landfill sites (removed by the RMA amendment). |
|
|
All landfill sites in New Zealand will be treated the same, setting a level playing field. |
|
|
Allows regional councils flexibility to introduce additional instruments to ensure the standard is achieved (eg, tradable permits, emission charges, education, etc.) |
Table 8: Assessment of 'landfill NES' against objectives
|
Objective |
Does this option meet this objective? |
|---|---|
|
To help New Zealand meet its obligations under the Kyoto Protocol |
Yes |
|
To establish nationally based landfill gas management for greenhouse gas emissions |
Yes |
|
To provide certainty for the waste management industry |
Yes |
|
To encourage the diversion of organic waste from landfills into composting and other uses |
Yes |
From the above it can be seen that this option meets the stated objectives and has a number of advantages. This option will, therefore, be taken forward the next step for further analysis.
The appropriateness test has assessed a range of options, setting out their relative advantages and disadvantages and whether each option can meet the stated objectives.
We found that only one option has the ability to meet the stated objectives: the national environmental standard option. This option is considered to be the most appropriate from the range of option assessed. Further analysis of this option will determine its effectiveness and efficiency.
As further support for the national environmental standard option, a number of events have led to calls from stakeholders for the Ministry to consider the introduction of standards.
Given the above tests and taking into account calls from stakeholders, the national environmental standards option has been taken forward for more detailed analysis. This is not to suggest that this is the only viable option, but it is the only option that meets the current stated objectives.
In order to test the effectiveness and efficiency of the national environmental standard option, the proposed standard is set out in summary in section 4. Section 5 then examines the costs and benefits associated with this option in order to determine its efficiency. The benefits will measure the effectiveness of this option to reduce greenhouse gas emissions from landfill sites.