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STFFN newsletter - Winter 2005
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Replanting
ACT Forests – update
In recent
weeks, ACT Forests and the ACT Government have come under some public
pressure not to replant Pinus radiata plantations in the Cotter
Catchment following the 2003 bushfires. Some criticism has come
from people who were originally supporters of the plan to replant
the Cotter catchment with pines, and now appear to have changed
their opinion.
The 2003 bushfires
burnt 10,500 hectares of pine plantations. A comprehensive plan
has been prepared to replant 8,000 hectares of this area. The remainder
will become parks, some residential development, and streamside
buffers. The plan incorporates a re-designed roading network to
lessen erosion, and native streamside riparian zones to enhance
water quality. The proposed plan was endorsed in the “Shaping the
Territory’s Future” report, and was found to have sound land management
principles, and also made good fiscal sense.
Greening Australia
formed a partnership with ACT Forests for the planting of native
trees and shrubs in the riparian zone, and also on steeper slopes
where it was considered that future harvesting of pine plantations
was not a viable option. Greening Australia has also come under
some unjust, ill considered and unwarranted criticism for the role
they are playing. Greening Australia has used over 1,000 volunteers
for this planting, and the efforts of the volunteers and Greening
Australia have been unfairly denigrated.
Although the
private plantation industry has been able to supply the ACT processing
industry at present, the ACT processing industry will require the
ACT Forests plantation estate to be replanted to ensure its long
term ongoing existence. The long term ongoing existence of the ACT
processing industry is also essential for the private growers in
the Southern Tablelands region who have young plantations they will
wish to market in future years. Thus replanting the ACT Forests
estate will have long term economic, social and environmental benefits
for the region.
For these reasons,
STFFN has written to the ACT Government and the Greens urging that
the plantations must be replanted. A positive response has been
received from the ACT Chief Minister giving an assurance that the
pine plantation estate will be replanted in the ACT.
To allow members
to observe first hand what is being undertaken by ACT Forests, it
is intended that the 2005 STFFN Annual General Meeting will be a
tour of ACT Forests work in the Cotter catchment, looking at the
roading re-alignment work, riparian zone planting with native species
and the replanting of the pine estate. The tour will then look at
the proposed Stromlo Forest Park, including the new arboretum site,
and the heritage listed cork oak plantation. Details will be in
the next newsletter.
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Direct seeded
windbreaks on the Southern Tablelands of NSW: effectiveness and
development
Background
STFFN has long
recognised the commercial potential of direct seeded windbreaks
in the Southern Tablelands region. To investigate the potential
commercial benefits from direct seeded windbreaks, STFFN sponsored
an ANU Forestry honours student, Meghan Whitbread, to undertake
to this important study. The following is the abstract from Meghan’s
honour thesis.
Abstract
The importance
of having trees on farms has been recognised by landholders for
centuries. Trees can offer shade and shelter for the protection
of livestock, crops and pastures, reduce soil losses from erosion,
stop unwanted weeds from neighbouring properties, reclaim barren
landscapes and offer the potential for the production of farm timber,
to mention some advantages.
Direct seeding
of windbreaks in Australia has been used as an efficient and economic
way of revegetating the landscape to deal with a wide range of objectives.
Direct seeding is a way of directly sowing seeds into prepared ground.
In this study, direct seeding has been used to establish native
mixed species windbreaks to provide shade and shelter, with the
possibility of obtaining timber from the stands.
Previous research
has shown that the maximum shelter benefit of a windbreak is related
to porosity and tree height. Porosity is the proportion of space
that is taken up by vegetation or left as open gaps. To achieve
an optimum windbreak there needs to be a balance between the vegetation
and open gaps. If the windbreak is too dense (all vegetation) it
acts as a barrier and turbulent eddies form on the lee side. If
the windbreak is too porous (many gaps) it does not reduce wind
speed to a great extent and stock and pastures will not be as protected.
Optimal windbreak porosity for reducing wind speed is one that has
uniform porosity across the windbreak to a value of approximately
35% to 45% (optical porosity).
Experimental
sites were established in windbreaks on farms at stand ages 4,5,6,8,9,12,
and 16 years old. Photographs were taken to obtain an estimate of
optical porosity, total tree height and Diameter at Breast Height
measurements were taken, and presence and absence data was collected
on each species sown at each site.
It was demonstrated
in this study that none of the windbreaks had uniform optical porosity
across the upper, middle and lower layers of the windbreak. Vegetation
was concentrated in the middle layer and did not occupy multiple
growing spaces across the height ranges. The consequence is the
creation of gaps. Over time the windbreaks are not maintaining sufficiently
even stand structure to optimally provide shade and shelter for
pastures and livestock, while maintaining the possibility of farm
timber.
The sample of
windbreaks used in this study is small, however it does demonstrate
that the age classes sampled do not follow the usual successional
trend in native forest stands of acacia species dominating early,
slowly being replaced by eucalypts. Although this trend occurs distinctly
between the 4 and 16 year old windbreaks, others between these ages
do not follow this trend. Possible differences in site factors and
environmental conditions at the time of sowing could be reasons.
Thus a manager cannot assume that because acacias are usually pioneer
species and faster growing than most eucalypts, that acacias will
dominate a stand early on.
The younger
age classes (years 4,5 and 6) have a distinctly different species
composition than the older windbreaks (years 8,9 and 12).
Essentially the species composition change occurs around age 7.
Younger sites are dominated by Acacia mearnsii and Eucalyptus ovata,
whereas older sites are dominated by E. blakelyi, E. mannifera,
E. melliodora, A. implexa, A. cardiophylla, A. boormanii, A. falciformis,
and Callistemon citrinus. However, Eucalyptus viminalis and Acacia
decurrens occur in every site.
Revegetation
programmes should take into account the competitive aggressiveness
of the latter two species if the outcome is to encourage a diversity
of species. The ability of these species to out compete all other
neighbours provides evidence of their capacity to dominate revegetation
areas. When determining species mixes the competitive nature of
some should be considered and they should be sown at lower densities
to ensure the resulting plant communities are diverse.
In direct seeding
projects the resultant vegetation is not completely representative
of the seed mixture. Dominance by any one species varies from site
to site. This may be influenced by rainfall events in combination
with environmental and site conditions (availability of light, water,
soil and nutrients) both at time of sowing and subsequently. There
is the potential for farm timber options in direct seeded windbreaks.
However, whether the farm timber operations will be economically
viable or not is another matter and needs to be the subject of further
research on farms. Important factors include access for management
options, particularly harvesting, access to markets and potential
buyers.
Windbreaks can
be planted for many multiple benefits, including shade and shelter
for pastures and livestock, enhancing farm aesthetics, increasing
biodiversity, creating a fodder resource and can be used to diversify
income through farm timber. This study has shown that all of these
outcomes are unlikely if the stand is left unmanaged. Early management
will be critical to maintain the integrity of the windbreak so that
the original goals set by the landowner can be achieved during the
later stages of stand development. Future research on management
of direct seeded windbreaks of native Australian plants is needed,
particularly on optical porosity and thinning trials.
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Forestry reports
will bring balance to timber debate
Australian
Forestry and Conservation Minister Senator Ian Macdonald has launched
three new reports on the important issues of sustainability, the
barriers to investing in timber plantations and the availability
of plantation grown hardwood sawlogs.
The publications,
Eucalypt Plantations for Solid Wood Products in Australia, Impediments
to Investments in Long Rotation Timber Plantations and Forests for
Tomorrow were launched at the Regional Forestry Workshop for Central
and North Queensland in Mackay.
Senator Macdonald
said recent media claims incorrectly suggesting there is enough
plantation grown hardwood available to replace those logged in native
forests proves the need for facts in the debate.
“These
reports clearly dispel some of the myths being pushed by the radical
Green groups,” Senator Macdonald said. “In fact, the Eucalypt Plantations
for Solid Wood Products in Australia report highlights that by 2035,
plantation logs are likely to make up only about 18% of the total
log availability.”
“The report
brings together all the information on Australia’s hardwood supply,
as well as its potential for value added timber products. It recommends
a greater focus on research, particularly in the areas of:
Senator Macdonald
said the second report, Impediments to Investments in Long Rotation
Timber
Plantations,
identifies the barriers to investing in these types of plantations,
and ways of overcoming them.
“The right
investment environment is crucial to any industry’s long term growth
and survival,” he said. “The Australian Government believes it is
especially important with regard to long rotation timber plantations,
and we contributed $20,000 towards this report in the hope some
of the recommendations will help the industry move forward.”
The final publication,
Forests for Tomorrow, examines how timber products are used and
produced, and also provides a range of views on the important issue
of sustainability. “As the report states, people love wood, and
love forests, but sometimes struggle to agree on how to have both,”
Senator Macdonald said.
“These
three reports make an important contribution to the debate on sustainability
in Australia’s forest and wood products industry, the investment
climate during a very capital intensive period, and the future of
the plantation hardwood sector.”
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Impediments
to investment in long rotation timber plantations
This article
is the Executive Summary from a document of the same name prepared
by the Forest and Wood Products Research and Development Corporation.
Over the last
decade in Australia investment in short rotation plantations has
greatly exceeded investment in long rotation plantations. URS Forestry
estimates that only around 20% of the estimated 450,000 hectares
of new plantation established in Australia over this period was
for long rotation plantations. There is already emerging evidence
that lack of investment in long rotation plantations will
result in insufficient supplies to meet the future demand of processors.
The aim of this
study is to assess whether or not there are impediments that are
resulting in under investment in long rotation plantations. The
study does not aim to recommend actions that would lead to preferential
treatment of long rotation plantations versus short rotation investments,
but rather to identify different factors that have acted to limit
investment and to propose a series of measures to overcome impediments
that are assessed to be distortionary from a national economic point
of view.
The most significant
development in generating investment in new plantations in Australia
in the last decade has been the very rapid expansion of the hardwood
plantation estate. The most important driver of this investment
has been the growth of the Managed Investment Schemes (MIS) that
have successfully provided a mechanism for attracting retail investors
to plantation investments. Most of this investment has been in short
rotation plantations and it appears that retail investors are less
interested in long rotation investments.
The other major
development has been the entry of the Timberland Investment Management
Organisations (TIMOs). These companies have responded to market
opportunities presented by the privatisation of publicly owned plantations
as well as the desire by processing companies to move out of plantation
ownership. There is also a growing interest by institutional investors
generally in plantation investments. These wholesale investors are
generally more interested in existing plantation assets than new
plantation establishment, although there is evidence of an increasing
interest in new plantation establishment by larger institutions.
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Major Impediments
The study
included a survey of the existing literature on impediments, ranking
of those impediments, and targeted consultation with relevant stakeholders
including institutional investors, asset consultants, MIS companies,
financial advisors, state governments, forest product processors
(industry) and equity and debt providers for plantation investments.
This consultation component culminated in a workshop for selected
stakeholders that focussed on taxation issues relevant to the functioning
of secondary markets for plantations and the potential for alternative
investment vehicles for long rotation plantations.
The key factors
identified as inhibiting investment in establishment of green field
long rotation plantations were:
Limited development
of secondary markets for plantation – secondary markets refer to
the sale of plantations between parties during the rotation. Although
there is a developing secondary market in plantation sales in Australia,
the market is characterised by relatively few trades of larger assets.
This limited nature of secondary markets reduces the liquidity of
plantation investments and makes long term forestry less attractive
as part of an investment portfolio, particularly for wholesale investors.
The lack of secondary markets also limits the ability of plantation
owners to value their maturing plantation assets over the life of
a rotation which is more important for long rotation plantations;
Lack of readily
available market information – compared to other countries and other
commodities there is relatively little available information on
log transaction prices in Australia. This makes assessment of plantation
investments difficult and creates uncertainty;
Non market based
log pricing and allocation – reliance on non market based mechanisms
for log pricing and allocation adds to the uncertainty created by
lack of log price information;
Limited understanding
of investor needs and the forest sector – there is a limited understanding
by potential investors of the forest sector and the nature of plantation
investments. Similarly, many participants in the forest industry
do not have a good understanding of investor needs, and;
Limited knowledge
of hardwood sawlog plantations – while the technical aspects of
softwood and short rotation hardwood plantation establishment are
well understood the technology associated with long rotation hardwood
establishment is much less well developed in Australia.
In addition
to these “primary issues” other issues that were identified as potentially
inhibiting investment in long rotation plantations included the
limited development of markets for environmental services and perceived
sovereign risk associated with a lack of certainty over rights to
harvest planted forests in Australia.
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Secondary markets
and taxation
The limited
nature of secondary markets for forest plantations is largely a
reflection of the size and structure of the industry. While there
has been a small number of sales of both large public and private
resources in Australia in recent years, there has been a less active
market in smaller plantations.
The potential
of the taxation system to discourage secondary trade in plantations
has received considerable attention. Review of that information
and consultations conducted as part of this study suggest that the
Tax Ruling 2000/8 and in particular Paragraph 48 of that ruling,
act specifically to prevent MIS companies from offering long rotation
products that include secondary sale. Paragraph 48 is interpreted
by MIS companies to mean that of long rotation plantation investment
that involve sale of the plantation prior to harvest will not qualify
for an ATO Product Ruling.
Failure of MIS
to get a Product Ruling prevents investors in plantations from accessing
the primary producer deductibility provisions thereby removing a
major attraction of the scheme to retail investors. As Paragraph
48 is part of a Tax Ruling it represents an ATO interpretation and
addressing this issue does not require a change in tax legislation.
It appears that changes in the plantation investment sector have
removed many of the concerns that originally motivated Paragraph
48. It is therefore proposed that the forest industries approach
the ATO to seek re-interpretation and issue of a revised ruling.
To remove the
bias against long rotation investment, it is suggested that the
forest investment should be owned for a specified time (say, 10
years) prior to sale. A 10 year minimum period would prevent tax
driven “round robin” sales of plantations and effectively achieve
neutrality between long rotation and short rotation investment decisions.
The taxation
treatment of profit-a-prendre has also been raised in the past as
a dis-incentive to development of secondary markets. Profit-a-prendre
is the name given to a common law provision that originated in the
United Kingdom that allows the partitioning of rights to land. It
can be used in plantation investments to separate ownership of trees
from the land on which they stand and has proved a useful tool for
the development of markets for environmental services.
For example,
a number of states have legislated to allow separate registration
of the title for carbon on land titles. It has been suggested that
the taxation treatment of profita-prendre discourages use of this
instrument, thereby effectively reducing the scope for secondary
sale of trees in this way. It is argued that the full value of the
asset created by profit-a-prendre could become subject to capital
gains tax in the year created even if no payment is made at the
time, and subsequently income tax may be payable on any income derived
from the right in the future.
However, there
is evidence of considerable use of profit-a-prendre in new plantation
development in recent years and there is no known incidence of actual
imposition of such double taxation.
In addition,
none of the commercial operators contacted during this study expressed
concern over the taxation treatment of profit-a-prendres. This contrasts
with the interest shown in other tax issues, such as Paragraph 48,
which was repeatedly mentioned. Given that profit-a-prendres are
being entered into voluntarily in increasing numbers and are reported
helping to provide investors with tradeable plantation rights, there
would seem to be little to gain at this stage from pursuing changes.
Another taxation
related issue that deserves attention is the sunset clause applying
to the “12 month prepayment rule.” This rule was introduced in 2002
and under existing legislation is due to end on 30th June 2006.
It allows a plantation manager a maximum of 12 months (or no longer
than the end of the following financial year) to secure land and
carry out “seasonally dependant agronomic activities” associated
with plantation establishment for which the grower has paid and
claimed the business tax deduction. These arrangements are very
important for the effective and efficient operation of MIS. Further,
the perceived need for the sunset clause was misguided, since the
12 month rule provides no special incentive or subsidy, for either
the grower or the manager. Rather, the 12 month pre-payment rule,
as legislated, is merely a timing mechanism that enables the plantations
to be established in a seasonally appropriate manner, and does so
without an attributable cost to public revenue.
If the 12 month
rule is terminated it is highly likely to substantially reduce the
current rate of plantation establishment (both short and long rotation),
as well as the replanting of areas as they are progressively harvested.
Continuing uncertainty about the future of the 12 month rule will
also discourage new entrants to the MIS plantation sector, including
those with an interest in establishing and managing long rotation
plantations. Since the MIS plantation sector is currently driving
most new plantation investment, it is imperative that that this
investment is not threatened or impeded by adverse changes in tax
treatment.
Lack of information
and clear market signals for log pricing and allocation The lack
of availability of log price information arises out of the structure
of the forest sector in Australia. The relatively small number of
buyers and sellers, together with the fact that logs are generally
sold by long term contract, means that log pricing information is
commonly commercial-in-confidence.
While the situation
has improved with the publication of the Australian Pine Log Price
Index (APLPI), there is considerable scope to improve the extent
and availability of log price information to plantation investors.
While public agencies have taken considerable effort to introduce
more market based pricing for log sales, a large proportion of plantation
log sales are still based on administratively determined prices
with allocation based on long term contracts that exceed what would
be expected in more freely operating markets.
It is also argued
that the methodologies used by some state agencies to determine
stumpage prices have little or no relevance to the market factors
that would affect private growers. For example, the Western Australian
Forests Products Commission has used a “cost of growing” methodology
to price native hardwood sawlogs and other states also have heavily
administered price systems for both native and plantation sawlogs.
These issues
have been addressed over time through corporatisation and privatisation
of government owned plantation agencies. For instance, changes have
included auctioning of increased log volumes, shorter term contracts,
more accurate statement and commitment to log specifications and
more commercially oriented log supply contracts.
However, in
general there is considerable room for improved commercial orientation
in these areas. The following actions are proposed as means of enhancing
market signals for potential plantation investors:
Extend the APLPI
to cover all major growers and examine the scope for illustrating
regional log price differences;
Develop a similar
index for hardwood logs. This will be more complex as a result of
the various grades but benchmarks should be possible; and
Promote increased
transparency and ongoing market orientation of log prices and allocation
by government agencies through ongoing expansion of the use of a
combination of short term tenders and long term supply agreements.
These actions
would require co-operation between existing private and public sector
growers and there is no existing formal organisation with responsibility
to drive these changes. In the case of plantation softwood log prices
the APLPI is prepared through co-operative arrangements between
major public and private forest growers in southern and eastern
Australia and any extension of these arrangements would require
consideration of existing participants as well as new participants.
Given the mix of public and private growers it is suggested that
the Australian
Plantation Products
and Paper Industry Council (a3p) drive the proposed extension to
APLPI.
For hardwood
sawlogs the vast majority of sales are from public agencies. It
is therefore suggested that the proposal to prepare a hardwood sawlog
index be further considered and driven by the Forestry and Forest
Products Committee of the Primary Industries Ministerial Council.
Similarly, this Committee would appear to be the appropriate body
to promote increased transparency and ongoing market orientation
of log prices and allocation by government agencies.
In addition,
it is recommended that state governments give consideration to ongoing
commercialisation and preferably privatisation of government owned
plantation assets. The sale of publicly owned plantation assets
offers the opportunity to substantially increase investment in long
rotation plantations and thereby build familiarity with the sector
among investors. It is also considered that increased private ownership
of plantations has the potential to provide significant economic
benefits by providing more commercially focussed management and
log pricing mechanisms.
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Understanding
investor needs and forest sector characteristics
As part
of the stakeholder consultations it has become clear that several
participants in the forest industry (including MIS companies) that
have been actively seeking funds from institutions such as superannuation
companies do not adequately understand the industry with which they
were trying establish a business relationship. Similarly, there
was strong interest in the plantation sector from the investment
community but a lack of understanding of its financial drivers.
It is important
to note that the decision makers within financial institutions and
their advisors (asset consultants) are not proactive in seeking
investments, whether they are in forestry or other sectors. The
number and quality of proposals presented to these organisations
are such that staff are fully employed evaluating proposals that
come across their desks. There can be significant differences in
the investment philosophies of various organisations and it is therefore
critical that any plantation manager that is making a “pitch” for
funding takes time to understand the objectives and philosophies
of the particular institution.
Examples of
approaches by the forestry sector that did not progress for reasons
other than underlying financial returns included reasons such as
inappropriate investment structures, inadequate understanding of
assessment and reporting procedures, and corporate culture.
The lack of
understanding between industry participants and investors is already
being addressed to some extent through increasing contact between
the sectors via projects such as this and industry conferences that
have greater appeal to the investment sector. As an example, the
International Investment Seminar as part of Austimber 2004 specifically
targeted the domestic and international investment community. However,
there is scope for the forest industry to put a greater emphasis
on providing information to potential investors and there is a role
for industry associations to organise a combination of formal (eg
seminars) and informal gatherings to facilitate this
change.
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Hardwood plantations
Research
and development into long rotation softwood and short rotation hardwood
plantations is well developed in Australia, as well as other regions
where the same species are grown. However, the Australian forestry
industry has previously enjoyed access to a public native hardwood
estate and the same research effort has not been extended to the
establishment and management of long term hardwood plantations.
Senate Rural
and Regional Affairs and Transport Committee inquiry into Australian
forest plantations – A Review of Plantations for Australia: The
2020 Vision highlighted the need for a co-ordinated approach to
research and development in the hardwood sector that focuses on
a broad range of issues including plantation health, wood quality
characteristics, and silvicultural systems that shorten the rotation
and technologies that utilise small logs. While this has not occurred
in Australia, there is a considerable body of research available
on long rotation hardwood plantations, particularly in South America
and South Africa.
There appear
to be opportunities for the establishment of plantation eucalypts
in Australia from a market perspective, but the level of technical
knowledge suggests a need for caution in the creation of any specific
incentives that promote the rapid establishment of a broad scale
long rotation hardwood estate. Emphasis should be placed on a coordinated
effort to undertake the research and development necessary to make
well considered forestry and investment decisions.
While some of
the information gaps can only be filled by establishing long term
trials and breeding programmes, it appears that considerable progress
could also be made through a co-ordinated review of the available
data sets from existing plantations and by collating relevant research
from overseas. It is understood that the Forest and Wood Products
Research and Development Corporation (FWPRDC) is currently funding
a study that should provide a useful first step by assessing available
research and development relevant to producing solid wood products
from hardwood plantations. It is also understood that the report
of that study will identify a need for coordinated research and
development. It is therefore proposed that the FWPRDC consider further
funding for cooperative approaches to relevant research and development
for long rotation hardwood plantations.
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Markets for
environmental services
The environmental
services that can be provided by plantations are of interest to
potential investors with the sustainability of forestry investments
often highlighted as an attraction to investing. However, markets
for environmental services in Australia are only in their infancy
and subject to considerable uncertainty, which in turn inhibits
investment. A diverse range of market based schemes has been introduced
in Australia over the previous few years, including transferable
water entitlements, renewable energy tradeable certificates and
tax rebates for landcare. Markets for environmental services for
land under forestry are less advanced, however there has been some
recent interest in investment resulting from the NSW Greenhouse
Gas
Benchmarking
Scheme, the potential for carbon trading, and the increasing social
and environmental awareness of organisations. There has also been
a pilot salinity credit
trade where
downstream irrigators paid for additional transpiration by re-afforestation
projects. The commercial environmental forestry project currently
being undertaken by CSIRO and funded by the Commonwealth Government
offers potential for further definition and evaluation of the environmental
benefits of planting trees in lower rainfall regions for environmental
benefits.
Regardless of
current Australian government policies and emissions trading systems,
it is understood that a number of industrial companies currently
have funds available for investments that may provide a carbon offset
against industrial activities. Some of these investors have been
looking closely at the forest sector as a means of providing a commercial
return and sequestering carbon. There is also a strong preference
for plantation investments that provide other environmental benefits.
However, in most cases such investments do not meet minimum rates
of return for investors. Providing a subsidy to corporate investors
that are prepared to establish plantations in particular regions
that have defined environmental benefits could better leverage government
funds currently being spent directly on environmental tree planting
activities.
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Sovereign
risk
The two
main aspects of sovereign risk relating to long rotation plantation
investments are the lack of certainty over rights to harvest planted
forests in Australia; and inconsistent government regulations for
plantation establishment, particularly with respect to codes of
practice and local government regulations.
Forest rights
legislation has now been implemented in all Australian states but
there are no such rights in the territories at this stage. Despite
this, there is some concern that long rotation plantations of native
species will at some stage be exposed to environmental protection
claims. Australian Forest Growers (AFG) cites examples in NSW, and
a Hardwood Sawlog Forum conducted by the Victorian Government in
2002 also expressed the same concerns. However, there is little
evidence that this is a major limitation on new plantation investment.
Local government
regulations can act as a significant restraint on plantation development
and the issue has been raised at a number of forest industry regional
investment workshops over the last 18 months. These workshops have
been convened on behalf of the Forest and Forest Products Committee
of the Primary Industries Ministerial Council. In addition, the
report of the Senate Rural and Regional Affairs and Transport Committee
inquiry into Australian forest plantations – A Review of Plantations
for Australia: The 2020 Vision, clearly recognised the potential
impact of local government regulations on plantation development.
A number of submissions to the inquiry also raised the issue eg,
the Forest and Forest Industries Council of Tasmania list local
government obstacles as the critical impediment to achieving the
aims of the 2020 Vision in Tasmania. The council claimed that local
government manifests the uncertainty created by anti plantation
and that planning and zoning ordinances are inflexible and excessively
regulated. Submissions from other states to the Senate inquiry also
listed local government as a major obstacle to plantation development.
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Recommendations
for action
While
governments are investing in some expansion of the long rotation
plantation estate, it is clear that the private sector will be more
important to the expansion of the plantation estate in Australia
than it has been in the past. The MIS companies have been very effective
in mobilising retail investment in short rotation plantations but
their investors have less interest in long rotation plantations.
At the same time TIMOs and other institutional investors have a
strong interest in long rotation plantations but have a preference
for purchasing established plantation estates.
These preferences
create a logical pattern of ownership throughout the rotation that
utilise both retail and wholesale sources of investment funds. MIS
investors could establish the long rotation plantation and this
could be on-sold to a TIMO or financial institution during the rotation.
From the primary investors point of view the transaction needs to
be no different to that of an investor in a short rotation plantation,
except that they are selling standing timber rather than harvested
logs.
There are two
initiatives that could be taken immediately to address this and
create opportunities for increased investment in long rotation plantation:
Firstly, redressing
the issues associated with Paragraph 48 of TR2000/8 would result
in MIS companies preparing investment projects to raise retail investment
funds for green field long rotation plantations on a similar basis
to short rotation plantations. It is expected that this would lead
to a significant increase in retail investor interest in long rotation
plantations; and
Secondly, there
is potential to capitalise on the growing interest by wholesale
investors in green field plantation establishment. Improving the
availability of regular market information could most readily facilitate
this, and ongoing development of market based pricing and allocation.
In addition,
the potential application of the sunset clause for the 12 month
pre-payment rule applying to MIS runs the risk of severely reducing
their ability to attract investment in both short rotation and long
rotation plantations. Action to remove the sunset clause must be
taken immediately.
Specific priorities
for action to achieve these outcomes are:
-
Preparation of a whole of industry submission
to the ATO co-ordinated by AFG/TIMA and a3p seeking re-interpretation
of Paragraph 48 of TR2000/8;
-
Organise through the auspices of a3p an
initiative to extend the APLPI to cover all major growers and
examine the scope illustrating regional log price differences;
-
The Forestry and Forest Products Committee
of the Primary Industry Ministerial Council to consider: a)
the development of a log price index for hardwood logs; and
b) Preparation of a plan for promoting increased transparency
and ongoing market orientation of log prices and allocation
by government agencies.
-
The plantation industry should make representation
to the Australian government through AFG/TIMA seeking the immediate
removal of the sunset clause currently applying to the 12 month
pre-payment rule for MIS;
-
The forest industries and governments
consider jointly funding provision of enhanced market and industry
data relevant to the plantation sector;
-
The FWPRDC consider the scope for additional
funding for co-operative research relevant to long rotation
hardwood plantations; and
-
State governments should consider enhanced
commercialization and preferably privatisation of government
owned plantation assets.
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Discussion
paper for the plantations and water roundtable
The National
Water Initiative (NWI), as agreed by COAG (except Tasmania and Western
Australia), and the requirement on State Governments to develop
implementation plans to achieve the objectives of that agreement,
present a significant number of challenges for Australia’s plantation
sector. Paragraph 55 of the Intergovernmental Agreement for the
NWI identifies large-scale plantation forestry as a landuse change
activity occurring without a water access entitlement, but with
the potential to intercept a significant volume of surface and/or
ground water. The agreement goes on to state that the impacts of
plantation forestry should be assessed and, where necessary, appropriate
planning, management and/or regulatory measures should be introduced
by catchment managers to protect the integrity of the current and
future budgeted water access entitlements (paragraph 56).
While there
appears to be no justifiable reason for having plantations or native
forests recognised as a significant interceptor of water, the NWI
is quite clear in its content.
A change in
landuse to large-scale plantation forestry will be regulated by
catchment managers through a process that is similar to the management
of water interception by farm dams.
There is no
doubt that plantations, like all other dryland activities, use water.
However, the impact of plantations on catchment water yields is
extremely variable and there continues to be little recognition
of the many economic, social and environmental benefits that can
be generated by supporting the future growth of the plantation sector.
In lower rainfall areas, for example, it is more than likely that
plantations will deliver a more efficient use of the available water
than other agricultural activities.
The National
Water Commission will therefore have an important role in determining
whether the treatment of plantation forestry, to be presented in
the State’s implementation plans, is consistent with the objectives
of the NWI. Governments should not attempt to over-regulate the
plantation sector by detailing the species that can be grown or
the silvicultural practices, and when introducing rules which refer
to plantation planning approvals, that there is some means for assessing
the economic and social impacts of those regulatory controls.
The Plantations
and Water Roundtable will consider definitions for some of the terms
contained in the NWI, the options for using a balanced approach
to assist catchment managers determine how water should be distributed
across each landuse, and the options for securing credits arising
from more efficient water use or improvements in water quality.
It is anticipated that these important matters can be drawn together
in an industry position statement on plantations and water, and
will be pursued by an industry working group after the Roundtable.
The following draft statement is provided for discussion during
the course of the Roundtable.
The plantation
sector is willing to assist water regulators and catchment managers:
-
to develop the means for assessing and
weighing up the economic, social and environmental impacts and
benefits of each landuse before establishing any new system
of water entitlements within their jurisdictions;
-
to help them understand the related policy
implications and potential environmental benefits from plantations
before regulating the water entitlements for this landuse;
-
to recognise that the industry is already
committed to improvements in water use efficiency from certification
and the legislated codes of forest practice; and
-
by identifying the initial research questions
that need to be addressed as priority issues to help meet the
expectations and objectives of the NWI during its implementation.
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Background
on the National Water Initiative (NWI) and National Water Commission
The NWI
as agreed on 25th June 2004, established the objectives, outcomes
and actions to be completed as part of the national water reform
process. This agreement identified the need for reform in water
access entitlements and planning, integrated catchment management,
water resource accounting, building improved knowledge, and establishing
a system of community partnerships and adjustment.
It is intended
that this process of reform will optimize the economic, social and
environmental outcomes from the nation’s water use, based around
a transparent and legislated system for water planning in each State
and Territory, and facilitate efficiency improvements in the use
of water.
As part of the
NWI, large-scale plantation forestry was recognised as a significant
interceptor of water with the water use entitlements for this landuse
to be considered separately from the entitlements for all other
dryland landuses. The State Government processes for regulating
plantation forestry should therefore be contained in the draft implementation
plans that the States will present to the National Water Commission
by mid-2005. In the first instance, the Commission will be required
to undertake an initial assessment of Australia’s water resources
and water management practices.
Two additional
roles for the Commission will be advising COAG on progress with
the implementation of the NWI and the administration of the Australian
Water Fund. There will be two programs under the Australian Water
Fund – Water Smart Australia and Raising National Water Standards.
Water Smart Australia will accelerate that introduction of new water
use technologies and practices. The Raising the National Water Standards
program is designed to improve Australia’s capacity to measure,
monitor and manage its water resources.
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Plantations
and Water – an overview
The opinions
surrounding the level of water use by plantations has been over-simplified
to a point where there is a commonly-held perception that plantations
use 1-2ML per hectare per annum more water than the pastures they
replace. This additional interception of water may lead to a reduction
in stream flow, leaving a smaller amount of water available for
other water users and the environment.
At the present
time, each State’s Code of Forest Practice provides an important
link between forestry and water policies. In each Code of Practice,
the planting of trees around drainage lines, creeks and rivers,
is heavily restricted. For example, in Victoria, the Code of Practicecontains
a ‘water yield protection requirement’ that may require plantation
managers to protect water yields by adopting longer rotations, controlling
stand density by thinning, or by placing limits on the area that
can be harvested each year. Unfortunately, the new management and
design requirements contained within the Codes of Practice are not
fully reflected in the current models of plantation water use, which
use data from older plantation designs that are likely to over-estimate
the amount of water being intercepted.
It is important
that catchment managers are aware that plantation water use is driven
by a number of factors that extend well beyond the area or proportion
of a catchment that contains plantations. Research from the CRC
for Catchment Hydrology has indicated that there are significant
differences in plantation water use between the uplands and lowlands
of catchments.
In some cases,
as in the Commercial-Environmental Forestry project being undertaken
for the Goulburn-Broken catchment (Victoria), it is predicted that
plantation establishment can be targeted in the landscape to deliver
a significant reduction in the volume of saline groundwater discharged
into rivers while having a limited impact on surface water run-off.
For other catchments,
such as the Denmark River catchment in southwest Western Australia,
a change in landuse from agriculture to plantations is leading to
improvements in the river’s salt loads. Although it will take some
time for the water quality to return to potable levels in that catchment,
there is a long-term positive trend associated with the expansion
of the plantation resource.
While there
is little doubt that plantation use water, the correct assessment
of how much water is intercepted, whether it is significant and
whether that use of water has other positive benefits, has only
been assessed in a small number of cases. If in the major plantation
regions around Australia, tree crops cover less than 10% of the
agricultural land area, but produce up to 30% of its economic output
and provide more than 25% of its employment, should this be viewed
as a good use of water? If so, should this water use be supported
through legislation and catchment management plans that reflect
such benefits?
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How should
the water entitlements for each landuse, including plantations,
be determined?
Improvements
in water quality must be considered alongside the impacts on water
yields, government policy priorities and other regional economic
and social outcomes, when assessing the water use and entitlements
for plantation growers. For example, the Victoria’s draft Plantation
Investment Strategy
recognises the importance of having a viable and growing timber
industry in that State. However, with the reduced access to native
forest resources in that State, the industry will become increasingly
dependent on plantation resources, which may in turn, impact on
water yields and run-off. It is therefore important for State Governments
and catchment managers to recognise and resolve the conflicts between
water use and other policy priority areas.
Reviews of the
current literature on plantation water use indicate that the impacts
of plantations on stream flow are specific to their respective region
and ecosystem. For example, in some areas plantations use less water
than native forests (Leon Bren, personal communication) while in
others, plantations use groundwater from shallow water tables (Richard
Benyon and Tanya Doody, CSIRO Technical Report No. 148, 2004). Given
the specificity of these research results, decisions on water allocations
for particular landuses, such as plantation forestry, should be
made at the Water Management Planning level based on the principles
of a nationally-consistent framework, rather than through prescriptive
State Government legislation and regulations.
However, at
this time, no government or catchment has developed a system that
will help guide the decisions of catchment managers over their water
allocations, entitlements and management options for all of the
landuses within their jurisdictions. A comprehensive approach for
assessing the water needs and setting entitlements is outlined in
Figure 1. By taking account of all these factors, it may then be
possible to determine what are efficient uses of water, what is
significant interception and what is largescale plantation forestry.
During the Plantations
and Water Roundtable, there will be some consideration of the processes
that catchment managers could utilise to assess the amount of water
being used and to determine the sustainable water entitlements across
the various landuses within their jurisdictions.
The processes
adopted by catchment managers should have the capacity to take into
account the:
-
Catchment-based water management planning
objectives;
-
Economic, social and environmental outcomes
from each water use;
-
Regional development strategies and planning
priorities; and
-
State and Federal Government policy objectives.
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Certification
is another means for improving the efficiency of plantation water
use
If the
plantation sector can be guaranteed access to a certain volume of
water within each catchment, then issues over water use efficiency,
species selection and silvicultural options become of strategic
importance to the future growth of the industry. Forest managers
who have achieved certification are already required to consider
these matters as part of their commitment to on-going improvements
within their sustainable forest management practices.
For example,
under the Australian Forestry Standard, one of the indicators is
for forest managers to work with relevant landholders and water
managers to monitor the impacts of forest management activities
on water yields. Appropriate actions for forest managers may include
increasing water yields by thinning or by maintaining a mosaic of
age classes across catchments. However, some thought may need to
be given to the impacts on water yields where a substantial proportion
of any one catchment is planted with tree crops across one or two
years.
The requirements
of certification, in addition to the requirements stipulated in
the State’s codes of forest practice, have the potential to drive
improvements in water use efficiency. Other options for improving
water yields may be to leave the plantation sites fallow for a year
(and sell the increase in surface water run-off for that period)
or to include late-age fertilisation as a means of increasing the
volume of timber grown for each megalitre of water consumed by plantations.
Unless water
managers and regulators are properly informed about current water
use, projected use and the options for improving the efficiency
of water use across all landuses, it will be difficult to derive
an equitable and consistent system for allocating water entitlements.
In this context, the research priorities of the plantation sector
which need to be completed to assist this process, will be discussed
during the Plantations and Water Roundtable.
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Water regulation
driven by various sources of legislation
Clauses
55 and 56 of the NWI clearly identify water interception by plantations
as an important issue that needs to be addressed. In addition to
the water resources legislation in each State and Territory, it
is possible for plantation water entitlements to be regulated through
a range of other mechanisms which have been designed to minimize
any threats to ground and surface water yields, including:
-
the preparation
of regional water resources planning frameworks
-
the development
of water and stream flow management plans
-
the declaration
of water supply protected areas
-
integrated
catchment management strategies
-
river health
strategies
-
regional
landcare plans
-
nutrient
management plans
-
native vegetation
management and protection plans
-
salinity
management plans
-
biodiversity
management plans
-
environment
protection policies and legislation
-
State and
local government planning policies and guidelines, and
-
forestry
legislation and codes of practice.
This list indicates
that there are many different ways to control the impacts of plantations
on surface water run-off and catchment water yields. In addition,
there is already some talk of introducing new measures that could,
if not thoughtfully implemented, have a significant and unnecessary
impact on the future growth of the plantation sector.
These new measures
might include mandatory water efficiency or water-saving targets,
set on a catchment-by catchment basis. However, they should not
be introduced until they can be applied to all landuse activities
within the respective catchments.
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Will the improved
management of water resources lead to new opportunities for the
plantation sector?
To improve
the returns from plantation forestry projects, one option is for
catchment managers to consider the development of salinity credits.
These credits could apply to some of the multi-purpose plantations
that will be established in areas such as the Denmark River and
Goulburn-Broken catchments. In addition to the salinity credits,
catchment managers might also consider supporting some positive
economic returns for the introduction of practices that lead to
a more efficient use of water.
In the Pratt
Water Murrumbidgee Project, The Business of Saving Water, it is
stated that ‘our water crisis does not stem from an overall shortage
of water. Our water crisis arises from our failure to make better
use of the water resources we have.’ Instead of the water debate
focusing on a choice between agricultural growth and the environment,
there is a requirement to have a national water policy and trading
system to ensure that water flows to its highest-value uses, which
should also incorporate the unique and lengthy growth periods of
the forestry sector.
The Pratt Water
Project provides some examples of the water savings that could be
delivered from a better use of our existing water resources. Out
of the 4.3 million ML of water conveyed through the Murrumbidgee
catchment each year, around one-third of the water is lost from
the system without generating any economic, social or environmental
benefit. It has been estimated that up to 945,000 ML of these water
losses could be saved and used for productive purposes and environmental
flows.
If these water
savings can be delivered, it will open up the potential for a range
of new agricultural investments in this particular catchment, including
the establishment of additional plantations. The report indicates
that at least 30,000 hectares of new plantations are required to
meet the growing demands of the region’s timber processing sector
and should be established over the next 10-
15 years. Even
if these plantations were to use 1ML of water each year over and
above the amount of water used by the pasture they replace, this
would only represent around 3% of the possible water savings for
the catchment.
There also continues
to be some discussion on the introduction of water saving targets
for catchments and the introduction of a trading system for ‘saved
water certificates’, which could be recognised as a new and tradeable
category of water. For plantation growers, it may be possible to
be part of this system if water-saving certificates can be generated
through changes in silviculture or by leaving the plantation
areas fallow for an extra year between harvesting and replanting.
In this latter case, plantation growers could receive water-saving
certificates for the increase in water run-off that occurs during
the fallow period.
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Industry working
group on plantations and water
It is
anticipated that the Roundtable will identify priority actions to
be pursued in working with the National Water Commission and water
regulators. These actions will include defining a number of key
terms contained in the NWI, outlining a process for determining
water entitlements across all landuses on the basis of the economic,
social and environmental outcomes they produce, outlining the options
for salinity or water-saving credits, and identifying the research
priorities for plantation managers.
Nominations
will be sought from people attending the Plantations and Water Roundtable
for the establishment of an industry working group on plantations
and water. Terms of reference for guiding the activities of this
working group on plantations and water issues will be based on the
outcomes of the Roundtable.
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Estimating
site index for Pinus radiata on the Southern Tablelands, NSW
Background
STFFN
has been providing advice to potential plantation growers in the
Southern Tablelands area since 1996. Although there have been some
maps available indicating potential growth, these have been very
generalised maps lacking in detail. In 2004, STFFN sponsored and
ANU Forestry honours student, Andrew Ford, to undertake a plantation
suitability study for the Southern Tablelands region. The result
is that STFFN now has a detailed map showing site index for all
land in the STFFN area, and also showing site index on cleared agricultural
land.
The map and
report can now enable STFFN to provide an indication to private
land holders the potential growth of Pinus radiata in their area.
It is intended to undertake further study by providing an economic
analysis of the STFFN area, and then to extend the original work
to show the growth potential of native species that could be established
on a commercial basis.
Introduction
The productivity,
or quality, of a site is an important factor in the evaluation of
plantation establishment investment. Site Index, an index of site
productivity, is one of the most important silvicultural parameters
influencing plantation profitability. Thus, it is useful to have
and estimate of the Site Index of a new plantation before it is
planted.
A number of
models have been developed to spatially estimate the quality of
a site using climate and soil factors.
However, the
input data and technical understanding required to initialise and
run the models can limit their application. For this reason, the
honours project aimed to determine whether the Forest Productivity
Model, developed by the Australian Greenhouse Office to indicate
growth potential of native forests across Australia, can be used
to estimate Site Index across the Southern Tablelands region. The
land capability and suitability assessments completed in this project
should greatly assist potential plantation investors to identify
the most productive areas of land for plantation establishment.
Summary
The Forest
Productivity Model, developed by the Australian Greenhouse Office,
was trialed as an indicator of site quality for Pinus radiata plantations
across the Southern Tablelands region of NSW. A significant correlation
was found between Site Index, an index of actual site quality, and
the modeled 25 year average Forest Productivity Index. However,
strong regional variations were found in the relationship between
these two indices.
A regression
model including parameters for Forest Productivity Index value and
region yields a strong correlation for the regions of Tumut, Tallaganda,
Lake George and Bombala Tablelands. However, the cause of the regional
variation is unknown, thus defining regional boundaries was problematic.
The Lake George and Bombala Tablelands regions are similar in their
relatively low rainfall and undulating topography. The Tumut and
Tallaganda regions both have relatively high, orographically influenced
rainfall. The marked variation in rainfall (influenced by topography)
between regions is suggested as the cause of the regional variation.
Under this assumption, regional boundaries for Tallaganda and Tumut
were delineated according to altitude.
The regression
models and regional boundaries were applied to the 25 year average
Forest Productivity Index layer using Geographical Information System
software. The resulting map provides and indication of potential
Site Index for P. radiata plantations, and forms the basis of a
land capability assessment.
Areas that were
considered to be unsuitable for plantation establishment, such as
existing woody vegetation and National Parks, were masked out to
complete a land suitability assessment. The predicted areas available
for plantation establishment in each Site Index class were calculated
and tabulated. Out of 4,742,000 hectares considered in the land
capability assessment, approximately 2,749,000 hectares was cleared
land suitable for plantation establishment. Of this area, 34,000
hectares were in the top Site Index class, and was mostly in the
Tumut region.
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Preparing for
a dry planting season...
Those
Southern Tablelands tree farmers already committed with tree seedlings
for this years planting season will certainly be worried about the
dry conditions. As seedling survival could well be at the mercy
of dry soil conditions, measures may need to be taken for those
who absolutely need to plant this year. Some of us have seedlings
on order with nurseries and the like and are committed to planting
with either pines this winter and/or natives this spring. In light
of this, there are measures in which one could take to help reduce
the effect of drought in the early development stage of seedling
establishment.
Some of these
include;
-
Firstly
consider the site or sites on your property where you had planned
to plant trees this year. If it is possible to concentrate new
tree establishment projects on the more protected sites rather
than the exposed sites may in it’s self, positively impact overall
establishment successes this year. Exposed sites, meaning shallow,
gravelly, rocky or sandy soils, especially on hill tops or north/
west facing slopes should be avoided if at all feasibly possible.
The more protected sites are more likely to retain soil moisture
better than the exposed ones.
-
Mulching
seedlings at the time of planting is an obvious step in limiting
soil moisture evaporation from the soil surface directly around
individual seedlings. A nice, deep, mulchy layer, at around
a half a metre radius around seedlings without being too massed
around the seedling stem itself is a good measure to take, although
the costs in material and labour needs also to be taken into
account. Many vegetative organic substrates can be effective
as mulch around young seedlings, but measure should be taken
to ensure that the material is adequately shredded and dry for
ease of application. Green, slushy material that has not been
adequately composted can be undesirable on young seedlings,
as it can be too rich in nutrients, possibly setting back and
sometimes killing young seedlings. Hay, pea straw and mulched,
heaped n’ dried garden waste are the most obvious substrates
for mulching trees at planting time. Avoid manures, especially
around native seedlings like eucalypts and wattles, as the high
phosphorus levels in many manure’s can retard native seedling
development.
-
Organic
materials that are fairly small in size may also be easily applied
to the soil at shovel depth, at the time of planting. Composted
leaf material and such like, without being too high in nutrients
like veggie garden compost, could theoretically be incorporated
into the soil at the direct location of planting. In practice,
a handful or two of organics from a bag or a shovel full from
a wheel barrow could be applied to each individual planting
site. Organic material at some depth round seedlings will become
a store and sponge for spare soil moisture, as well as providing
a more richly organic soil pocket, directly on hand for the
root system of the newly developing seedling. Organics are particularly
important for sandy soils where soil moisture holding capacity
is typically poor.
-
Water crystals
available from nurseries and hardware stores have been used
with mixed levels of success for establish young tree seedlings
in the field. Peat moss is also another material that can be
added to the soil at shovel depth, which has the capacity to
swell and store water, whilst making water available for plant
root absorption. Cost though may again be an important consideration,
especially for broadacre application.
-
Grazing
animals such as rabbits, hairs, kangaroos and wallabies are
also going to be increasingly hungry, especially if we
don’t get any rain soon to freshen things up. This means it
will be especially important to protect seedlings with tree
guards and possibly make timely interruptions to pest, grazing
animal populations. It is certainly the right climatic conditions
now, to effectively and significantly impact localised pest
animal populations with various forms of integrated pest control.
-
Most importantly
though, water your seedlings in well at planting time, using
several litres per tree if possible. Plant seedlings in deep,
not being afraid to cover and inch or two of the seedling stem
with soil, even when a generous dish is formed with the tree
planting shovel, at the time of planting. Make sure seedlings
still waiting to be planted are vigilantly well moistened on
the planting day, to avoid seedlings being in any moisture stress
in the first place. Preferably, don’t plant on hot or windy
days to lessen the impact of planting stress. Planting stress
can also mean over-handling the root ball, or having the seedling
exposed (such as seedlings taken out of their container and
left to sit next to the planting hole, while it or other holes
are being dug) to outside conditions for any length of time
than is absolutely necessary.
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Wagga Wagga
effluent plantation project: sustainble water and nutrient management
The Problem
In recent
years, the growth of large blooms of toxic blue-green algae in our
rivers has been a problem in many parts of Australia. One cause
is the over abundance of nutrients in rivers, particularly phosphorus
and nitrogen, some of which comes from the discharge of treated
sewerage effluent. Not only does this discharge contribute to a
major pollution problem, but river disposal of municipal effluent
is a waste of a resource that can be used to promote the growth
of trees in plantations. Each year, towns in the Murray Darling
Basin generate sufficient effluent to irrigate up to 25,000 hectares
of fast growing plantations that otherwise would be unable to survive
or produce useable wood products due to low rainfall or lack of
nutrients.
Recently, environmental
pressures have required the implementation of methods other than
river discharge to treat sewerage effluent. Irrigation of tree plantations
for wood production has become one of the most popular methods for
land treatment of effluent.
The area of
tree plantations for this purpose has grown to more than 2,000 hectares
over a five year period.
The Project
In 1991,
CSIRO established the Wagga Wagga Effluent Plantation Project in
conjunction with the Wagga Wagga City Council at a site called Flushing
Meadows. The purpose was to study the processes of water use, nutrient
cycling and salt management in plantations that are irrigated with
effluent. The aim was to ensure that the treatment could be sustained
without causing serious degradation to soil, rivers or groundwater.
The outcome will be authoritative guidelines to help design, establish
and manage sustainable effluent irrigated plantations under a variety
of Australian effluent, soil and climatic conditions.
By irrigating
eucalypt and pine plantations at various rates with treated sewerage
effluent, the project aimed to:
-
Measure
the water balance and develop appropriate irrigation scheduling
strategies.
-
Determine
the fate of phosphorus and nitrogen applied in the effluent
and the effect of irrigation on nitrogen and phosphorus already
in the soil.
-
Quantify
changes in soil properties, including salinity, sodicity, acidity
and permeability.
-
Study tree
growth, nutrient accumulation, wood quality and water use and
develop appropriate silvicultural strategies.
-
Identify
genetically superior clones of Pinus radiata and screen a range
of native species for use in effluent irrigated plantations.
Awards
In 1995,
the Wagga Wagga Effluent Plantation Project was awarded the BHP
Landcare Research
Award for NSW
for outstanding achievement in land and water conservation research.
In 1996, the
project was honoured with the Australian Banksia Environmental Award
for Land Management for protecting existing land and water systems
from degradation and developing new land management practices that
contribute to the sustainable fertility and productivity of that
land.
In 1997 the
project won the Theo Charles-Jones Tree Award for conservation and
sustainable development from the Murray Darling Association.
Communication
This research
has lead to the development of a substantial body of technical knowledge
that has been widely disseminated throughout the Australian water,
wastewater, forestry and environmental industries. In 1994, the
first of three stages of the guidelines, entitled Green Rivers or
Green Trees was published and 20,000 copies were distributed nationally.
In 1994, a comprehensive technical report summarising the first
three years results was published. In 1995, a manual entitled Effluent
Irrigated Plantations: Design and Management was launched and 10,000
copies were distributed. Final guidelines are being prepared.
Communication
of the results has focused clearly on the target customers, for
example:
-
Annual open
days and industry workshops.
-
Group visits
for more than 3,000 people, including federal and state politicians,
as well as school students.
-
More than
40 TV and radio interviews and over 50 newspaper articles.
-
A 10 minute
documentary on the ABC TV programme, A Question of Survival.
-
Twenty articles
in popular and semi technical journals.
-
Thirty five
scientific and technical papers in national and international
journals and conference proceedings.
Key outcomes
-
Quantified
rates of mineralisation of nitrogen in the soil, rates of accumulation
in the trees, litter fall and decomposition and rates of nitrogen
removal by gaseous losses and leaching to groundwater.
-
Quantified
rates of plantation water use and these have been extrapolated
nationally into the WATERLOAD2 model.
-
Demonstrated
that effluent irrigated plantations can be managed sustainably
with respect to salt, nitrogen and phosphorus effects on soils.
-
Identified
potential long term risk of sodium accumulation in the soil
which can cause structural degrade if effluent irrigated land
is reverted to rain fed agriculture.
-
Identified
best eucalypt species and Pinus radiate clones for effluent
irrigated plantations and quantified differences in salt sensitivity
between flooded gum (Eucalyptus grandis) and Pinus radiata.
-
Developed
an economic evaluation model (WATCOST) for effluent irrigated
plantations.
-
Pulpwood
thinning harvested at age 6.
-
Integration
of all the information for use by the general public in an Issues
Manual, National Guidelines, and models.
Note: The Flushing
Meadows site is now managed by the Wagga Wagga City Council
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Forestry investors
20 years on: still no money
(From
the Sydney Morning Herald, 10th March 2005.)
Investors in
a pine forest planted in the Oberon area could see some money back
from an investment made two decades ago, following orders handed
down in the NSW Supreme Court that the scheme be wound up.
Justice Peter
Young has declared that the scheme, known as Lot 3 Hai Welyki, an
unregistered investment scheme under the Corporations Act and appointed
a trustee to sell the assets.
The scheme was
run by Pine Forests of Australia Pty. Ltd.
The investors,
represented by law firm Maurice Blackburn Cashman, owns the land
as tenants in common, in lots divided into 500 interests. The minimum
investment was $3000, but one investor
put in $158,000.
Maurice Blackburn Cashman partner Andrew Quiqley said that the pine
forest scheme could extend beyond the area that is the subject of
the court order, and ultimately could involve thousands of investors
who sank money into various schemes in the 1980s and have seen no
return on their investment.
Justice Young
noted that the investors appeared to have entered the contracts
as a result of the activities of a salesman who provided them with
brochures. He noted “They contain a lot of puffery and pretty pictures
of forests against an attractive skyline, happy plantation owners
gathered around a camp fire, etc, as well as statements from people
who indicate they have qualifications in the forestry industry,
extolling the virtue of growing Pinus radiata, milling it and marketing
it. The brochures also pointed out the taxation advantages in investing
in pine forests, an advantage that would be reaped wholly in the
tear of payment.”
Lot 3 Hai Welyki
is one of 12 adjoining plantations in the Oberon/Jenolan area 200
km west of
Sydney. “The
plaintiffs must be disappointed that so far they have only received
$243 by way of income over the last 20 years, and are justified
in feeling that there has been misconduct in the operation of the
plantation,” Justice Young said.
They are also
peeved that ASIC would not assist them in any way in seeking justice.
After the judgement, Mr. Quigley said “This is the first step to
try and recover a return on the investment for our clients and we
are pleased to see that the Supreme Court has moved to protect the
investor’s interests.” He said investors have received little or
no profits from the scheme for several decades.
Mr. Quigley
believes more than 3000 investors could have contributed up to $9
million in the various pine forest schemes in the area. “We have
been contacted by a number of disgruntled investors who have received
no return on their investment since the 1980s. The decision will
greatly assist those investors who are relying on the original investment
to partly provide a retirement fund,” he said.
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