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Peter D. Clark
[CEO, PF Olsen Ltd. Paper compiled to provide information and views to the Climate Change Leadership
Forum. Compiled with input from others in the forestry sector but time available prohibits full consideration and
endorsement of this position by all forestry sector participants.]
Version 3, 23rd January 2008
The treatment of pre-1990 forests in the proposed NZ ETS:
It appears the primary driver of the ETS proposals for pre-1990 forest is to meet New Zealand s CP1 Kyoto obligations at least cost to the taxpayer. The Forum has been told as much. This least cost objective is achieved by mirroring closely the Kyoto forestry policies in our own domestic policies.
But it is widely acknowledged that the Kyoto artificial cut-off date of 1990 in respect of forests is flawed in respect of the environmental contribution of New Zealand s plantation forests. The 1990 fix was introduced at the eleventh hour in an attempt to address concerns related to northern hemisphere forests. It was agreed to by NZ negotiators against the recommendations of the NZ forest industry. So why would we lock in place a long-term domestic policy that mirrors a flawed five year international policy at the very time New Zealand is seeking changes to the international rules?
New Zealand is likely to become the only country in the world with a land-use change carbon liability imposed on forestry at a time when international consideration is being given to providing payment to developing countries to avoid deforestation. New Zealand should lead the world in introducing climate change policy which will reduce emissions and increase carbon sinks rather than slavishly implementing flawed elements of the old international rules which, at this very time, are being changed to become more effective.
As discussed, as a tiny emitter of greenhouse gases New Zealand s greatest contribution will be leadership in rational domestic policy instruments and fighting hard for those types of instruments to be adopted internationally.
The present CP1 Land Use Land Use Change and Forestry rules (LULUCF) only hold for the first commitment period and there is a good possibility that New Zealand can help bring about positive changes from 2012 through working with like-minded countries.
New Zealand has already shown leadership by being the first Kyoto country to include agriculture and forestry in our domestic climate change policies.
If these policies are to form the basis of our LULUCF negotiations and leadership role post 2012, then our CP1 policies must be rational from an environmental perspective and acceptable to private landowners.
Only if these criteria are met can we expect similar policies to be adopted in Australia, Canada, US or in South America or Asia that in turn could facilitate the next set of international agreements to cover these key sectors.
To be acceptable to the private sector, any government should be seeking to create a positive environment for:
(a) Retention of existing forest rather than penalties for removal of that forest, and
(b) Dramatically increasing total forest cover.
This concept is consistent with the trend towards rewarding avoided deforestation in developing countries that we also want to see included post-2012.
NZ plantation forests were first established to provide timber needs without further destruction of our indigenous forests. Unlike many countries, this outcome has been achieved with stunning success.
Most of our early forests were established on the scrubby CNI volcanic plateau (because at that time that land was unable to be used for pastoral farming), sand dune coastal strips and cleared but reverting farmland, or cleared but eroding hill country on the East Coast. In the 1990s a further 600,000 ha was established mostly on low-producing hill country pasture land throughout New Zealand.
When a forest is harvested it simply releases CO2 that has quite recently been captured from the atmosphere. Even if it is not replanted some of that carbon is stored in long-life applications like buildings, fences and furniture. Even under unrealistic Kyoto assumptions our forests are, at worst, carbon neutral. To the extent that we plant new forests, extend the rotation age or increase the rate of tree growth per hectare we create additional carbon sinks that can buy time for the world to adjust to a lower greenhouse gas emission economy.
Plantation forests also provide one of the greatest opportunities we have as an international community to produce low cost biofuels feedstock (via conversion of ligno-cellulose to ethanol ) to substitute for fossil fuels without impacting on global food supply, and to provide construction materials that replace more energy intensive building materials.
While announcements of a deforestation tax have played a part in bringing forward some deforestation, the fundamental driver is changes to the relative economics of pastoral farming (especially dairy) versus forestry. These economic drivers have become particularly evident in the last 2 or 3 years.
A forward-looking scenario suggests up to 200,000 ha of pre-1990 forest could usefully support higher and better land use, mainly dairy. It is probable however, that the rate of deforestation that has occurred over the last 3-4 years will be significantly less going forward. Moreover, it is likely that at least 200,000 hectares of land which is currently not in forestry would deliver a higher economic return if turned to forestry.
It is future opportunities that should be the basis of stranded asset compensation, not some historical level of deforestation that was based on very different economic fundamentals.
Key principles of our proposal are:
This proposal is a pragmatic one designed to meet the following objectives:
An amendment to the Bill to allow for domestic offset planting within New Zealand for any deforestation of pre-1990 forests on a hectare for hectare of equivalent carbon absorption capacity would:
(a) Preserve flexibility in land use, which is integral to a sustainable and prosperous primary sector;
(b) Slow the pre-2008 deforestation rate by requiring landowners to absorb the additional cost of offset planting; and
(c) Ensure that taxpayer expenditure on credits delivers long-term environmental benefits in the form of zero net loss of forest carbon volume;
(d) Be consistent with an environmentally defensible position for all plantation forests internationally that NZ may wish to promote in its CP2 negotiations.
Under this option taxpayers will carry a Kyoto obligation for the period 2008-2012.
However, this is a timing issue, because:
(a) The Government will receive additional Kyoto credits as the new trees begin to sequester carbon;
(b) The Government will receive additional tax revenue associated with the net economic benefits; and
(c) A favourable outcome of the current negotiations over the post- Kyoto agreement would remove the problem relating to pre-1990 forests after 2012, hence limiting the cost of the solution to the first five years.
Importantly, there are net economic, social and environment benefits (with associated net revenue benefits for the Government). CRA International undertook a comprehensive economic assessment of the conversion of forestry to pastoral land in June 2007 and found that for conversions such as those currently being done in the Central North Island, the net benefits to society of dairy farming exceed those from forestry by $767 per hectare per annum. In addition:
There will be more planting of new forests on land marginal for farming (often erosion-prone) under this proposal than under the Government s proposed solutions and this is most likely to result in net environmental benefits (the impact would be at least carbon neutral).
Landowners as the point of obligation will still face significant new costs for the establishment and management of an equivalent area of planting and compliance so there will not be conversion of marginal land except where there is a genuine and substantial economic benefit.
The taxpayers will receive better value for their money as the amendment will result in net economic benefits through best economic use of high value land.
There is no or minimal inequity between sectors as a result of offset planting.
Compliance and measurement of this approach could be readily undertaken within the terms of the proposed compliance and measurement regimes.
Land use flexibility will be enhanced delivering economic and environmental benefits to New Zealand
Our proposal for pre-1990 forests, as a transition towards full carbon accounting for all NZ plantation forests and the removal of the distinction between pre-1990 and post-1989 forests, is:
Some landowners (including Maori) are presently locked into lease or Forestry Rights arrangements with forest owners and have not been able to take advantage of early deforestation prior to 2008, and will not get access to their lands until current lease arrangements expire. CFL Maori land claimants are in a similar position, depending on the basis of their claim settlement and the land value impact on the quantum of land included in any settlement. There is a case that such landowners should be permitted to deforest their lands after hand-back, without the financial imposition of offsetting costs, as this would reduce the cash proportion of the settlement.
If the cost of land use change is to be kept low or nil (true compensation), then a specific NZ Deforestation Unit will need to be created because:
An annual on-line auction introduces a cost of carbon to the business as usual activities of landowners. The fact that the NZDU has no value other than for deforestation will discourage speculators entering into the auction process.
In theory the price bid for NZDUs should be low, given that supply and demand are expected to be matched.
The government s liability is capped at the level of NZDUs released to the market in any one period. While more deforestation may take place, this would need to be covered fully by the entities responsible through surrender of NZUs.
It is anticipated that 100% of the auctioned NZDUs would be taken up at auction. But some may be banked for future periods. Under this proposal the existing 21 million CP1 allocation would be maintained (see Current Expectations, page 11) and any NZDUs not taken up would be retained by the government, along with the proceeds from the sale of NZDUs.
Another important feature of the scheme, to give confidence to the forestry sector, will be a government commitment to fully covering (through annual allocation of NZDUs) deforestation of 200,000 ha over a 40 - 50 year period.
The net cost to government after 2012 will of course depend on what is negotiated internationally with respect to Land Use Change and Forestry. Carbon accounting for forests should be over much longer time periods (>25 years) reflecting that carbon stock changes in forests relate to rotational cycles over multiple decades.
It is broadly acknowledged that the compensation on offer for pre-1990 forest landowners is in respect of loss of land value (a stranded asset).
Within existing pre-1990 forest landowners there are two distinct groups:
Policies that enable land use change to continue to take place at reasonable cost will mitigate land value losses and reduce the case for land value loss compensation.
The government has signalled 21 million NZUs would be made available in CP1 on a simple land area basis to all pre-1990 forest owners. That is now the expectation of many pre-1990 forest owners, regardless of deforestation intentions. Our suggestion is that in terms of maintaining the good faith and confidence of those forest landowners, and in terms of supply of domestically available units to help cover emissions in other sectors from 2010, this 21 million CP1 NZU package be maintained, but that 25% of those units be specifically targeted towards land capable of high agricultural production as indicated by its Land Use Capability classification.
We recommend a new survey of CP1 deforestation intentions be carried out urgently, based on the offsetting pre-requisite condition to bidding for deforestation permits (NZDUs). The results of such survey would then form the basis of an additional allocation of NZDUs as per this proposal. The survey should also capture likely deforestation in future commitment periods up to 50 years from now. This would form the basis of a capped schedule of annual auction of NZDUs beyond 2012 should current Kyoto rules persist.
This proposal contains a number of separate elements that individually may have attraction to government but together do not. This proposal is presented with the intent that it be retained (no doubt with sensible improvements) as a total package. If component parts of the suggested policy is disaggregated then PF Olsen Ltd disclaims any individual element being attributable to its suggestion.
This proposal does not remove the differences in treatment between pre- 1990 and post-1989 forests. But it does acknowledge, in our domestic policy, that change in land use is both desirable and important to our national economy. This is a good starting point for post-2012 negotiations. It effectively creates a one-off transitional arrangement for pre-1990 forests for CP1. The eventual removal of that distortion is likely to be important for the adoption of forestry into the domestic climate changes policies of our major trading partners and competitors. It will also restore investment confidence in the NZ forest sector. The widespread international adoption of climate change policies that are similar to New Zealand is very important for our international competitiveness.
The proposal would ensure that land use flexibility was retained. In particular the ability to relocate forests without a net penalty could occur which would restore confidence and encourage new investment into the industry.
Land use flexibility has been a cornerstone of New Zealand s wealth creation since the first European settlements. This will remain the case as new technologies and Agricultural and Horticultural economic drivers change over time.
Kyoto Protocol deforestation liabilities should be met 100% by the NZ taxpayer, given that:
The devolvement of post-1989 carbon credits and liabilities under the ETS will encourage new planting. That this policy is effective is critical to generate domestically produced credits to offset forecast growth in transport (including aviation), stationery energy and agriculture emissions over the next 50 years. New planting is very capital intensive. The major constraint to new planting during CP1 will be land availability at reasonable cost. Pastoral land values will remain high as long as:
The contribution of the forestry sector to mitigate climate change will be enhanced by:
Supplementary policies around biofuels, transport weights and dimensions, port infrastructure, labour and skills, domestic wood use etc were aggressively pursued.
Delays and abandonment of previous climate change policies in NZ means that we have now reached January 2008 without any clear policies (let alone legislation) with respect to pre-1990 forests other than a very blunt instrument that has effectively halted deforestation activity. The flow-on economic impacts of this blunt instrument to both affected private landowners and to the NZ economy are not well researched or understood.
There is differing views within the forest sector as to what is best for their own interests and for NZ Inc. This paper has been developed without the benefit of input from many forest landowners, and has not been subject economic evaluation nor peer review.
The proposed legislative changes, in whatever form, will have a profound effect on the New Zealand economy. There will be winners and losers, and we cannot afford to get it wrong.
One sensible option may be to take a cuppa. In effect the current policy announcements (and therefore no deforestation) would apply while a better researched and more inclusive process involving affected parties was entered into over 9 -12 months in advance of legislation being passed in respect of pre-1990 forest lands. This would also enable NZ to get a better understanding of the likely post-2012 international position.