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Climate Change Leadership Forum report number: 13
Briefing for the Climate Change Leadership Forum
Prepared by the Emissions Trading Group
Date: 8 April 2008
This paper provides:
The Leadership Forum has previously received and discussed alternative proposals (developed by Ngai Tahu and PF Olsen1) for including forestry in the ETS. At the Forum’s request, these proposals have now been independently reviewed by the University of Waikato (Professor Frank Scrimgeour) and Covec (Dr Tim Denne).
At the time of writing this note, the University of Waikato / Covec report was still only a final draft. It had been provided to a range of key stakeholders for comment, including representatives of Ngai Tahu, PF Olsen and the Flexible Land Use Coalition. In turn, PF Olsen had sought an independent review of it. Those comments had not been provided at the time of writing. A summary of them, along with the finalised University of Waikato / Covec report and any independent analysis of it, will be provided at a later date.
PF Olsen recommends an alternative solution for the treatment of deforestation of pre-1990 forests. There are two elements that apply to land owners of these forests:
Flexible Land Use Alliance
The Flexible Land Use Alliance (FLUA) proposal is substantially similar to that of PF Olsen. It proposes an offset scheme that requires planting of land to compensate for any deforestation. This proposal has not been analysed separately. But the University of Waikato / Covec report expects the results of the analysis of the PF Olsen proposal to apply to the FLUA proposal also.
Ngai Tahu provided two alternative solutions, relating both to the treatment of pre-1990 and post-1989 forests.
Option 1 is focussed on promoting afforestation. It includes the following elements:
Option 2 introduces a wider set of obligations on deforestation. The components of this option include:
The report’s overall conclusion is that:
“… the emissions trading system (ETS) as currently specified has greater net benefits than the other options. This result occurs because the ETS ensures that deforestation occurs only when the net benefits are greater than the costs of the emission units that need to be surrendered as a result of the deforestation. Surrendering emission units is a real cost to the nation that the other proposals do not pass on to landowners. The other options result in a greater level of deforestation, and the additional area deforested has higher costs than benefits.”
The reports’ estimates of the overall benefit of the pre 1990 forestry components of the ETS (relative to a base case scenario where no policies are introduced to manage New Zealand’s deforestation emissions) are shown in Table 1 below. Those benefits stem from a reduction in deforestation levels, and a resulting reduction in the costs New Zealand is expected to face in order to meet its commitments under the Kyoto Protocol.
Table 1 Estimated Benefit of the ETS
Unit price |
ETS |
$15/t |
$100 – 219 |
$30/t |
$480 – 623 |
$50/t |
$1,184 – 1,361 |
In turn, the reports’ estimates of the cost of the different options relative to the ETS are shown in Table 2.
Table 2 Net Costs of Policy Options Relative to Current ETS Design
Unit price |
PF Olsen/FLUA |
Ngai Tahu 1 |
Ngai Tahu 2 |
$15/t |
$76 – 167 |
$60 – 132 |
$60 – 132 |
$30/t |
$384 – 499 |
$320 – 416 |
$320 – 416 |
$50/t |
$832 – 956 |
$704 – 809 |
$704 – 809 |
The report goes on to note that there is an irreconcilable trade-off when designing the ETS between minimising costs to landowners, and costs to the economy as a whole:
It concludes that “it is this trade-off that leads to the ETS approach of passing on the full cost so that the national benefit is greatest but designing a compensation package to offset landowner costs”.
With regard to the adequacy of the approach the government has previously proposed for compensation, the report concludes that:
“If there is a desire to compensate, then the ideal approach is to provide lump sum compensation to those that are most likely to face costs, and for the level of compensation to any individual landowner to be independent of the decision to deforest. This ensures that it does not reduce the effective emission price faced by landowners.
The difficulty faced by the government is to identify these participants. It is easy to identify deforesters, after they have deforested. But ex-post compensation of those that do deforest (and presuming that they know compensation is coming) is equivalent to these landowners not facing the full price of emissions—rates of deforestation would rise and the nation would face higher net costs. The compensation needs to be lump-sum and this is what the proposed regime seeks to achieve.
The problem is, it is poorly targeted. But the targeting problem is not easily resolved. The only way to be sure of providing adequate compensation is to increase total compensation levels. However, in the absence of a clear way to target compensation, this would need to be spread widely thus increasing total costs to the government substantially.
The government is left with a clear policy dilemma: an efficient outcome that results in high costs being passed on that cannot easily be compensated, or not without high costs; or less efficient outcomes that pass lower costs on to landowners but result in increased deforestation and greater national costs.”
For the reasons discussed in the University of Waikato / Covec report, Ministers do not favour changing the way that forestry is included in the ETS. However, after considerable discussion with a broad range of stakeholders, Ministers are now proposing a revised approach to freely allocating NZUs to Pre 1990 forest owners. That revised approach, and the rationale behind it, is discussed below.
The Emissions Trading and Renewable Preference Bill (the Bill) provides for an allocation of New Zealand units free of charge to owners of pre 1990 forest (with the exception of those whose land has been declared exempt under the 50ha participation threshold). The total number of units freely allocated will be equal to 55m NZUs, less the number required to meet the cost of the 50ha threshold and the ongoing 2ha deforestation exemption.
In the ETS engagement material put out by the government in September 2007, the government proposed that this total number of units be apportioned on an equal pro rata basis across all landowners. No differential was proposed to take account of whether landowners purchased their land before or after the date when the government first announced its intention to introduce deforestation controls (October 2002). It was estimated that this approach would provide each landowner with an allocation of 39 units per hectare (it is not possible to calculate this figure with certainty until applications for the 50ha participation exemption have been received).
In that engagement material, units allocated in respect of Crown Forest Licence (CFL) land not yet passed to successful Treaty claimants were to be received by the government. The approach set out in the engagement material therefore was expected to lead to the allocation shown in Table 2.
Table 2: Allocation Approach Proposed in the 2007 Engagement Material
Owners of Pre 1990 Land Purchased Prior to October 2002 |
39 NZUs per ha |
Owners of Pre 1990 Land Purchased After October 2002 |
39 NZUs per ha |
The Crown (for CFL lands) |
39 NZUs per ha |
Future successful Treaty claimants |
Nil (but could be part of a negotiated settlement quantum) |
This approach has received considerable criticism from stakeholders in the forestry sector. The key argument has been that the approach does not adequately target assistance to the parties that are likely to face the greatest costs under the ETS, and does not provide sufficient compensation to those parties that have real opportunities to introduce alternative land uses.
As noted in the University of Waikato / Covec report, the targeting problem is not easily resolved. However, the government now believes that it is possible to improve the proposed approach to some degree, in a way that better targets those parties that are likely to be most heavily affected.
As noted, Ministers are now proposing a revised approach to freely allocating NZUs to Pre 1990 forest owners. This revised approach differs from the previously proposed approach in three key ways:
This new option is summarised in the table below (with the original approach from the 2007 engagement material provided for comparison).
Table 3: Summary of Proposed Revised Approach to Forestry Sector Allocation
|
Original Approach (in 2007 Engagement Material) |
Suggested Revised Approach |
Owners of Pre 1990 Land Purchased Prior to October 2002 |
39 NZUs per ha |
60 NZUs per ha |
Owners of Pre 1990 Land Purchased After October 2002 |
39 NZUs per ha |
39 NZUs per ha |
The Crown (for CFL lands) |
39 NZUs per ha |
Nil |
Future successful Treaty claimants |
Nil |
18 |
Other key points to note about this new proposed approach are that:
As noted, this new proposed allocation approach provides an increase in assistance to owners who bought their pre 1990 land prior to October 2002 (‘pre 2002 Owners’) and future Maori owners of CFL land (‘iwi yet to settle’).
The government first announced its intention to introduce deforestation controls in October 2002. Owners that bought their land after that date, or purchased a company which owned forest land, would/should have known about New Zealand’s Kyoto obligations and the government’s policy to limit its exposure to deforestation liabilities. They therefore had the ability to factor these commitments into their purchase price and other management arrangements so as to account for the increased limitations on alternative land uses.
On the other hand pre 2002 owners could not have anticipated Kyoto and the associated limitations of land use change. A number of these owners now have much more constrained options and opportunities than they had anticipated. This argues for the pre 2002 owners receiving a higher value allocation of NZUs than 39 units per hectare.
Turning to iwi yet to settle, officials’ previous analysis noted where iwi opt to take CFL land as part of a settlement, the ‘price’ they pay for that land will be reduced, where relevant, to reflect the fact that it is covered by the ETS and has restrictions on its future use. This will clearly reduce the impact of the ETS on iwi yet to settle. However, the Iwi Leadership Group has argued that it does not mean that they will not face any impact. Had those settlements been completed earlier, claimants would have had the opportunity to take advantage of the recent rises in land values, and/or the opportunity to convert forest to farming operations in advance to the ETS coming into force. In such cases the claimants may not have ‘paid’ a land value much different to forest only valuations – since these additional opportunities have only arisen fairly recently.
The proposed allocation of 18 units per hectare for iwi yet to settle reflects this lower, but non-zero, impact.
The government has not yet made an unconditional decision to introduce this new allocation approach. Its final decision will be taken after:
1 A further proposal has also been developed by the Flexible Land Use Alliance, but is in practice equivalent to the PF Olsen proposal.
2 Over time a greater portion of forest land will be post-1989 forest and thus eligible to receive RMUs under the Kyoto Protocol (assuming that the rules continue as are). Thus the ratio of NZUs awarded to CO2 absorbed will trend over time towards 1:1