Genetic
Dialectic:
The Biological Politics of Genetically Modified Trees
by Viola Sampson
and Larry Lohmann
The
Cornerhouse - Briefings Nº 21
The attempt to engineer trees
genetically belongs to a centuries-old tradition of state and corporate
efforts at drastic simplification of large wooded landscapes for
specialized purposes. Fraught with internal contradictions, this
tradition is also under challenge from interests defending local
diversity. An effective response to the dangers of genetically modified
(GM) trees will go beyond exposes of their biological effects by
contributing to alliance-building among these interests.
Most contemporary systems of
forest stewardship of established, sustained productivity, fertility
and value to local people are based on diversity. Difficult to interpret
or administer from outside, such systems often include a mixture
of forests, woodlands, agricultural fields, and gathering or hunting
grounds arranged in spotty, periodically-changing, seemingly-irregular
patterns which fit local topography and community convenience. They
typically feature trees planted or maintained for a variety of purposes
including food, shade, erosion control and protection for livestock;
fruit, vegetables and wood for humans; and water, nutrients and
protection for crops. This diversity of uses generally reflects
a local politics in which no single production interest is able
to exclude all others. It has a number of beneficial effects --
for example, shielding insect species from the monolithic selection
pressures they would encounter in a monoculture, which often turn
them into devastating pests.
A
MODERN DIVERSITY-BASED FORESTRY SYSTEM
Among
at least 400 modern "community forest" systems
in the hilly upper Northern region of Thailand is that of
Mae Khong Saai village in Chiang Dao district of Chiang
Mai province. The system features 57 hectares of agricultural
fields in which at least 10 different types of paddy rice
are grown in stepped fields in the valley bottoms. Some
10 varieties of dryland rice are also cultivated in hill
fields, which rotate on a cycle of 3-5 years.
Some
643 hectares of community use forest are carefully distinguished
from 980 hectares of protected forest, between them encompassing
six different native forest types. Some 58 herbal medicines
on which villagers depend are locally cultivated, some in
a protected pharmaceutical garden in the middle of the forest.
Altogether, forest food and medicine yield the equivalent
of US$700 per year for each of the village’s 22 households.
As well as providing wood for local use, the forests also
help preserve the nature of the streams that lace the area,
which provide water for agriculture and drinking as well
as the 17 carefully-conserved species of fish which supplement
the local food supply.
All
aspects of the system -- agriculture, community-use forest,
protected forest, fisheries -- are interdependent. The whole
pattern, meanwhile, relies for its survival on local villagers’
protection. For example, the use of fire is carefully controlled
by locals so that devastating blazes don’t strike the local
forest, as they often do the surrounding region’s monoculture
tree plantations. Regular monitoring, together with a newly-formalized
system of rules and fines covering forest, stream and swidden
use, helps maintain the local biotic mosaic. Political vigilance
is also crucial. In 1969, locals teamed up with concerned
government officials to stave off a threat by commercial
loggers to devastate the area. Today, Mae Khong Saai villagers
are fighting a 1993 government decree ordering them out
of the Wildlife Sanctuary which was established in 1978
on the land they inhabit and protect.
Mae
Khong Saai’s insistence on local stewardship is obviously
good for the area’s biodiversity. A recent rapid wildlife
survey in and around the village resulted in sightings of
many species -- including a flock of Oriental Pied Hornbills
(Anthracoceras albirostris) – that indicate that
the area is one of the most biologically diverse in Thailand.
Animals including bear, dear, gibbon, boar and various wild
cats, as well as over 200 species of birds, take advantage
of the tapestry of local ecosystems.
Thoroughly
integrated with lowland economies, polities and cultures,
Mae Khong Saai couldn’t be further from the romantic cliché
of a completely isolated, self-sufficient community. As
well as marketing forest products, many community members
periodically take jobs far outside the community, some in
distant cities. In their defense of local livelihoods and
the biodiversity they rely on, moreover, Mae Khong Saai’s
residents depend partly on alliances they have fashioned
not only with similar communities across Thailand’s northern
mountains but also with urban-based NGO movements. Arguably,
the community owes even its current identity and way of
life on the periphery partly to the history of uneasy relations
between the Karen people who inhabit it and the modern,
nationalistic, racialist Thai state which has developed
over the past century. Whatever successes its forest stewardship
system achieves will owe much to the way it is able to converse
and negotiate with lowland and international powers in renewing
its strategies for local control.
|
In enduring tension
with such systems, and with itself, is a forestry tradition, at
least two centuries old, of centralized control which attempts to
create large, simplified wooded landscapes easy to administer from
offices for single, specialized purposes. This tradition stems from
the efforts of both early modern European states and large commercial
concerns to calculate probable yields from timber extraction, using
techniques such as exhaustive statistical field surveys of the species
and sizes of forest trees. This narrow focus on quantifying sustainable
wood volume led naturally to attempts to create, as if from a blueprint,
a more uniform forest that was both more legible to bureaucrats
and their employees and more "efficient" in its production
of a single commodity. Systematic seeding, planting and cutting
brought into being the ideal bureaucratic or commercial "forest",
with its grid pattern of similar trees manageable according to globally-applicable
techniques and free of "extraneous" vegetation or human
activity. Such "forests" -- and the industrial plantations
which followed on -- became rigidly separated off from agriculture.
(See BOX: The Industrial Plantation Tradition.) The multiple functions
of ordinary forests were reconceptualized as symptoms of untidiness
and disorder. Non-wood uses of forests were recast as, at best,
"minor forest products", while trees whose growth rates
had ceased to justify their survival in economic terms were dismissed
as "overmature". Flora and fauna which reduced timber
output were classified as weeds or pests. This redefinition of forests
was accompanied by a redefinition of rights, as forest societies
were also partly disassembled. Complicated webs of local rights
of access to woods and their varied contents -- firewood, mushrooms,
fodder, nuts, gravel, peat, game, poles, moss and so on -- were
curtailed as authorities and firms sought to gain more sweeping
legal controls over their productive domains. As seeding, planting,
nutrients, growth rates and dates of harvest all came under the
control of landowners and industry, a backlash, both biological
and social, became evident. Growth rates dropped after first rotations
of trees had been harvested; pest infestations increased as genetic
diversity dropped; wildlife vanished, and local farmers deprived
of part of their livelihoods took to resistance and sabotage. All
of these, however, were played down as problems which could be "mitigated"
through the application of further centrally-administered techniques.
Examples included chemical fertilizer and pesticide application;
distribution of nesting boxes to replace the hollow trees which
birds had previously used; and state repression.
|
THE
INDUSTRIAL PULPWOOD PLANTATION TRADITION
The factory-like order
of industrial pulpwood plantations, with their ranks of
even-aged trees of the same species marching over large
landscapes, is closely tied to the political development
of the factory itself. The basic design for the paper machine
used today was developed in the 1790s largely as an attempt
to transfer control over paper-making knowledge from restive
artisans to factory owners. The new device encouraged increased
plant scale, increased consumption and increased physical
centralization. It also encouraged the use of wood -- which
was more easily stored, more available and more easily transportable
than agricultural wastes or rags, as well as being less
labor-intensive -- as raw material. Reliance on wood in
turn encouraged the already-existing trend toward state
control over forests. It also helped foster reliance on
large, heavily-mechanized and -capitalized, water- and energy-intensive
mills. One outcome was large-scale deforestation and the
creation of vast, simplified catchment areas of uniform
raw materials -- industrial plantations, or "fields
of fibre". Increasingly sited in the South, where land
is cheaper, growth rates faster, and regulation less restrictive,
such enclaves are intolerant of other land uses such as
agriculture, gathering, grazing or wildlife preservation.
Requiring centralized legal, political and biological control,
they also provide few jobs for local people and have provoked
local resistance in countries ranging from Indonesia and
Thailand to Portugal and Chile.
The grand scale of pulp
and paper operations makes state subsidies indispensible,
whether these come in the form of free infrastructure, tax
breaks, cheap land, suppression of local opposition, or
low-cost university research services. The enormous size
of each factory added to the sector, meanwhile, fosters
savage boom-and-bust cycles which encourage periodic increases
in demand. Paper executives insist that this scale is necessary
for "efficiency". But even if the issue is disregarded
of whether any industry so subsidized can be regarded as
"efficient", obvious questions remain. Who or
what is this "efficiency" for? A typical US citizen
uses 60 times more paper than an average Vietnamese, yet
the literacy rates of the two countries are virtually the
same. (See TABLE: Efficient Paper Production for Whom and
for What?) In fact, some 58 per cent of current world paper
production has nothing to do with writing and printing,
but is used instead in packaging, tissues, and other uses;
and even a large proportion of writing and printing papers
go toward junk mail and other types of advertising. The
scale of the industry and its associated need to simplify
landscapes and entrench high demand are products not of
some disembodied need for "efficiency" but of
a wider politics and culture.
|
Table:
"Efficient" Paper Production for Whom and for What?
| Country |
Apparent
Paper Consumption 1999 kg/person |
Pulp
Production 1999 - kg/person |
Approximate
Literacy Rate
(rounded to nearest 5) |
| USA |
347 |
209 |
95 |
| Japan |
239 |
87 |
100 |
| Taiwan |
231 |
17 |
95 |
| Italy |
179 |
10 |
95 |
| Malaysia |
107 |
7 |
90 |
| Portugal |
98 |
176 |
85 |
| Chile |
53 |
193 |
95 |
| South
Africa |
40 |
49 |
80 |
| Thailand |
31 |
14 |
95 |
| China |
28 |
13 |
80 |
| Bulgaria |
19 |
6 |
100 |
| Indonesia |
15 |
18 |
85 |
| Egypt |
15 |
1 |
50 |
| Vietnam |
6 |
2 |
95 |
| Nigeria |
4 |
<1 |
55 |
| Nicaragua |
3 |
0 |
65 |
Sources:
Pulp and Paper International, Asian Week, UNESCO
Genetically Modified Trees Enter the Scene
Politically and institutionally,
the genetic engineering of trees is directed mainly at shoring up
this beleaguered tradition of giant-scale industrial operations,
corporate power over the countryside, and biologically homogenized
landscapes.
Two trends are in evidence.
The first aims at industrial quality control at a new, molecular
level. One example is from the pulp and paper industry. As long
as papermakers were dependent on diverse types of wood waste for
raw materials, they had to rely mainly on manufacturing processes
to ensure uniform paper quality. With pulpwood plantations, however,
variability in the raw material itself could be reduced through
choice of species, site, inputs, spacing, provenance, hybridization,
cloning, macro- and micro- propagation and DNA analysis. The genetic
engineering of trees is merely another step in this standardizing
"process of linking genes to tree, pulp and paper characteristics".
Robotics systems developed by the Australian biotech company ForBio
-- currently in liquidation -- provide a way of producing the large
numbers of cloned GM trees necessary. Pulp and paper industrialists
now envisage vast plantations not only of trees of single species,
but of trees which have all been genetically modified in exactly
the same way.
One of the most important targets
of current research is lignin -- the strengthening and protective
substance of woody plants. In the production of high-quality paper
from cellulose fibres, lignin gets in the way and must be removed
with a high expenditure of chemicals and energy. By manipulating
the genes which instruct woody plants to manufacture the building
blocks of lignin, biotechnologists hope to reduce the proportion
of the substance in pulpwood trees, or change it to a less ‘troublesome’
type. Reducing lignin by as little as one per cent would result
in savings of many millions of dollars for the industry and would
also be useful environmental public relations, since less water,
energy and chemicals could be used in pulp recovery. Several US
patents have been taken out on GM low-lignin trees. (See TABLE:
Selected Life Patents.)
Genetic engineers also aim to
increase the wood density of trees destined for construction materials
or paper pulp manufacture; to curb the tendency to branch in trees
grown for furniture; to boost growth rates in fuelwood trees; and
to engineer fruit trees for altered taste, different ripening characteristics
or pharmaceutical production. One biotech company has been set up
to market a caffeine-free GM coffee bush which is billed as a means
of avoiding industrial processes of manufacturing decaf coffee.
The second tweak which tree
biotechnologists give the monoculture tradition is to try to repair
some of its inherent contradictions without questioning its nature
or the power relationships that sustain it. For example, large monoculture
plantations are notoriously vulnerable to insect and disease infestations,
since they offer a gigantic feast all in one place to any insect
or microorganism able to evolve to exploit them. Applying pesticides
may ultimately make the problem even worse, since they cull the
target organism’s natural enemies while simultaneously causing it
to evolve resistance. Instead of addressing these problems at their
root, however, genetic engineers apply the Band-Aid of trying to
make trees manufacture their own insecticides (see discussion in
section below). Among the first genes forest biotechnologists exploited
were those encoding insecticidal toxins from the soil bacterium
Bacillus thuringiensis. Bt genes have been engineered
into a wide range of species, including poplar, European larch,
white spruce and walnut. Other genes that have been selected to
confer insecticidal properties on trees include protease inhibitor
genes (from rice and potatoes) that disrupt insect digestion. In
order to counter diseases that cut into the yield of fruit tree
plantations, meanwhile, biotechnologists are attempting to engineer
resistance to plum pox and papaya ringspot viruses. Researchers
are also exploring the possibility of creating GM trees that are
resistant to fungal disease, such as leaf rust and leaf spot diseases
that affect poplar and white pine plantations.
By the same token, genetic engineering
is being applied to the problem of soil salinification associated
with industrial plantations, particularly those in Australia --
not by undertaking to decrease salinification, but by adjusting
plantation trees’ genomes in a way which allows them to survive
on the spoiled land. One of the areas of greatest current interest
for forest biotechnologists, finally, is the engineering of broad-spectrum
herbicide resistance. Industrial tree monocultures are typically
established by ploughing up existing vegetation – an expensive process
which also results in soil erosion. If broad-spectrum herbicides
could be used to clear land without affecting plantation species,
and to keep it free of understorey, business could save an estimated
US$975 million per year. Biotechnologists are thus racing to create
herbicide-friendly plantation trees, particularly hardwoods, which
are more vulnerable to herbicides commonly used in forestry than
pines. Among the trees that have already been grown in field trials
are chestnut, sweetgum and poplar engineered with genes to confer
resistance to glyphosate, chlorosulfuron and glufosinate-ammonium
(see TABLE: Releases of GM Trees in OECD Countries). A number of
patents have also been taken out.
Promising to bypass the need
for conventional breeding (a particularly long and costly process
with trees due to their long life cycles), genetic engineering is
also attractive to wood industries in that it extends the breeder’s
palette to include a range of previously-unavailable traits from
other species. Genes from bacteria, for example, can be used to
boost trees’ resistance to insects, and genes from pine to increase
nitrogen uptake and growth rates in poplar. This is another reason
why genetic engineering is biased against biodiversity: it may make
it appear that the need to conserve native genetic resources essential
to breeders is less of a priority, and thus cut support for forest
conservation.
Following the Money
A glance at who is instigating,
funding, patenting and testing the genetic modification of trees
confirms that the technology is strongly biased in favour of the
conflict-plagued industrial monoculture tradition -- and against
more progressive diversity-based systems of forest livelihood and
stewardship.
Some research is being carried
out directly by transnational corporations committed to the industrial
plantation tradition. One of the biggest efforts toward making genetic
engineering in forestry a reality was a US$60 million joint venture
announced in April 1999 between Monsanto and pulp and paper manufacturers
International Paper, Westvaco and Fletcher Challenge. The last three
companies all have miserable reputations among environmentalists
or affected people for their forestry operations, toxic releases,
or both, while Monsanto is a well-known promoter of large agribusiness
monocultures worldwide. The objective of their alliance was to make
wood easier to pulp. Although Monsanto has now backed off, restricting
its role in the deal to that of a technology provider, the other
partners remain in the hope that the new "designer trees"
will reduce mill costs. In January 2000 they were joined by the
New Zealand company Genesis Research and Development (which specializes
in pharmagenomic drug discovery and therapeutic vaccines as well
as forestry genomics). Fletcher Challenge and Genesis have been
in partnership for five years to develop herbicide tolerance in
plantation trees such as eucalyptus, poplar and pine. The two firms
have also been granted a US patent to alter the lignin content of
trees. (See TABLE: Selected Life Patents.) Further north, Japanese
paper and auto firms are also carrying out research into the genetic
manipulation of trees. In addition, transnational corporations are
stumping up money to pay university researchers in a number of countries
to carry out investigations into tree biotech.
The bulk of basic research,
however, is likely to be funded by corporate-friendly government
agencies working together with industry associations and universities.
This better suits the conservative orientation of many wood industries,
who favour the time-tested corporate strategy of shifting research
costs off on the public sector wherever possible. In the mid-1990s,
for example, the American Forest and Paper Association, an industry
group dominated by giant transnationals with control over vast areas
of land, launched a "collaborative research effort" with
the United States Department of Energy to increase US wood production.
Under the scheme, the US government provides tax dollars to government
laboratories or universities for genetic engineering research which
the corporate sector can then take advantage of, with supplementary
support from companies such as Georgia-Pacific, Rayonier, Union
Camp and Westvaco. Researchers at the Tree Genetic Engineering Research
Cooperative (TGERC) based at Oregon State University, meanwhile,
who are responsible for researching and testing trees genetically
modified for improved fibre production, herbicide tolerance and
resistance to fungus and insects, receive funding from the US Department
of Energy Biofuels Program, the US Department of Agriculture, and
the US Environmental Protection Agency; paper and timber companies
such as International Paper, Weyerhaeuser, Boise Cascade, Georgia-
Pacific, Union Camp and MacMillan Bloedel; the Electric Power Research
Institute, a utility industry association; other firms such as Monsanto
and Shell; and Oregon State University itself. Providing technical
and logistical support are the US and Canadian Forest Services,
Mycogen, the University of Washington, and Washington State University.
This wide collaboration, in TGERC’s own words, results in a "leverage
factor of nearly 40-fold for individual industrial members".
Tree biotechnologists at Michigan
Technical University, meanwhile, have benefited both from money
from the state of Michigan and from collaboration with plantation
companies such as Champion. Their colleagues at the University of
Washington have received funding from not only the US Departments
of Agriculture and Energy but also the National Science Foundation,
as well as various wood corporations and universities. The Department
of Energy and the National Science Foundation are also bankrolling
research on genetic manipulation of organisms to alleviate global
warming and a Plant Genome Research Program which could lay the
groundwork for GM pines. In Canada, too, although a joint venture
called Arborgen has been formed by transnational forestry companies
to work on GM trees, the government is playing a central role in
developing tree biotech through the Canadian Forest Service.
The more money is available
for tree biotech research, of course, the less incentive foresters
will have to study other areas -- a heavy irony, given that while
the complexity of forest ecology and tree genetics is well recognised,
they are poorly understood and starved of research funding.
The Technofix Dilemma
The genetic engineering of new
traits into trees, in short, can be expected only to deepen the
familiar environmental and social contradictions of the industrial
monoculture tradition:
- Lignin-reduced trees are
likely to have multiple deleterious effects given that lignin
functions in forests in so many ways. Lignin reduction may weaken
trees structurally, and some researchers have reported stunted
growth and collapsed vessels, leaf abnormalities or
an increase in vulnerability to viral infection. Because lignin
protects trees from feeding insects, low-lignin trees are also
likely to be more susceptible to insect damage, leading to pressures
to increase pesticide use. Low-lignin trees will also rot more
readily -- affecting soil structure, fertiliser use, and forest
ecology -- and will release carbon dioxide more quickly into the
atmosphere.
- GM trees that produce their
own insecticide
are virtually certain to cause non-pest species to evolve into
pests as GM pesticides eradicate their competitors. The target
insects themselves, meanwhile, will evolve resistance to the GM
pesticide, leading straight back to the application of conventional
pesticides. In addition, some newly-resistant insects could simultaneously
evolve a capability to expand their feeding range to previously
less-susceptible plant species. Unexpected
pesticide contamination of ecosystems is also possible. The insecticidal
Bt which certain agricultural crops have been engineered
to produce, for example, has unexpectedly been found to be capable
of being exuded through roots and binding with soil particles,
persisting in the soil for 243 days and remaining toxic for very
long periods. Non-target insects essential to healthy ecosystems
may also be vulnerable to the GM insecticides. Finally, as long
as they enjoy an advantage over trees susceptible to insect feeding,
insecticide-producing trees will be able to invade wilder systems
with ease, disrupting their insect population dynamics.
- Trees genetically engineered
for resistance to disease,
especially when deployed in simplified landscapes, are likely
to cause fresh epidemics. For one thing, genetic diversity within
stands is well-recognised as essential to tree health in sustainable
forestry. Yet with the advent of cloned GM trees, genetic diversity
will be lower than ever in commercial plantations. Extreme vulnerability
is bound to engender extreme methods of disease control. Second,
fungicide production engineered into GM trees to help them counter
such afflictions as leaf rust and leaf spot diseases may dangerously
alter soil ecology, decay processes and the ability for the GM
trees to form mycorrhizal interactions essential for nutrient
uptake and soil structure. Third, GM virus resistance may accelerate
the evolution of new diseases. Biotechnologists have engineered
several tree species, including plum and papaya, with genes from
viruses which instruct the trees to make viral proteins. For reasons
not fully understood, these proteins confer some resistance to
infection by that particular virus and often its close relatives.
Yet infecting viruses can acquire and use viral genetic information
carried on some GM plant chromosomes in a process known as viral
recombination. In the absence of genetic engineering, viral recombination
will occur only on the rare occasions when two similar viruses
have infected an organism simultaneously, but because every cell
of GM virus resistant plants contains viral genetic material,
any viral infection can be considered as in effect a simultaneous
infection. Laboratory experiments have confirmed that viral recombination
involving engineered viral genes in plants can indeed increase
viruses' virulence and expand the range of hosts they are capable
of attacking.
- Trees genetically engineered
to be tolerant of herbicides
will further entrench the use of the chemicals in corporate and
state attempts to create wooded landscapes free of "extraneous"
species. The consequences will be multiply detrimental. Broad-spectrum
herbicides damage soil structure and fertility through changes
in root systems, soil insect populations and soil food webs. As
bacteria and fungi which promote soil health decline, vegetation-damaging
bacteria and fungi move in. Ultimately,
the use of other pesticides to combat fungal diseases may increase.
Herbicides are also dangerous to birds and other animals that
rely on a diversity of plants for food and shelter. Their use
over prolonged periods diminishes food sources for the species
dependent on them and provides ideal conditions for the evolution
of herbicide-tolerant plants and the need for higher doses and
even more hazardous chemicals. Herbicide use has also been shown
to increase agricultural crops' susceptibility to disease.
Despite manufacturers' claims of 'environmental friendliness',
moreover, glyphosate, the active ingredient of favoured plantation
herbicides (including Round-Up), binds to soils in the same way
as inorganic phosphates and may remain undegraded for years, endangering,
through runoff, aquatic life. Glyphosate also disrupts the healthy
balance of soil life and kills beneficial insects including wasps,
lacewings and ladybirds. GM glyphosate-tolerant
trees have been grown in field trials throughout the 1990's, in
USA, Europe and South Africa.
- Trees genetically modified
for faster growth are
likely to use up water even faster than the fast-growing trees
currently used in industrial plantations, exacerbating problems
of dryout and salinification which undermine the agricultural
or fisheries livelihoods of people living on adjacent land. Such
trees will also suck up nutrients at a higher rate, necessitating
the application of an ever-increasing volume of chemical fertilisers.
Hence fast-growing GM trees may speed up the process by which
previously rich land is impoverished -- thus increasing, not reducing,
plantations' demand for land and their threat both to agricultural
livelihoods and to native forests. Trees genetically modified
for fast growth will also be highly invasive of ecosystems for
which they were not intended, quickly overtaking slower-growing
non-GM trees in the competition for light and nutrients. They
will thus threaten not only wild and endangered tree populations
but also the plants, insects, fungi, animals and birds that have
evolved to fill specialist niches dependent on those populations.
For example, Swedish researchers engineered aspen with a gene
from oats which controls the response of plants to day length.
The resulting tree was able to grow in winter daylengths (with
as little as six hours of daylight daily) as well as summer (when
daylight may extend to 15 hours or more). Had the GM aspen not
lost its ability to withstand cold, it would have had a huge advantage
over other trees in extreme latitudes where day length limits
tree growth. Fast-growing trees with improved ability to take
up nitrogen compounds from soil can also be an invasive ecological
threat. A (non-GM) nitrogen-fixing tree introduced to Hawaii provides
one cautionary example. The tree has pumped a normally nutrient-impoverished
lava ecosystem so full of nutrients that a number of diverse and
specially-adapted native plant communities have been driven out.
Recent proposals by the US Department
of Energy and others to use carbon-dioxide absorbing GM trees to
counter climate disruption highlights in another way the complex
connections between genetic engineering and the attempts of central
authorities to re-engineer large landscapes for single purposes.
At their most grandiose, such proposals call for genetically "manipulating"
terrestrial ecosystems so that they can temporarily store several
times more carbon than at present, in order to make possible "continued
large-scale use of fossil fuels". One result could be the creation
of vast plantations of trees genetically engineered for both faster
growth (to absorb more carbon dioxide from the atmosphere) and higher
lignin content (for more stable storage of the sequestered carbon).
The consequences would include not only the social effects associated
with the seizure and degradation of huge areas of forest lands and
their soils, but also the entrenchment of a wasteful energy economy
elsewhere. If allowed to decay or used for fuel or paper, of course,
the trees would quickly release the carbon they had temporarily
sequestered back to the atmosphere.
Genetic Colonisation
Nowhere are the contradictions
of the GM "fix" clearer than in the controversy over how
to prevent genetic modifications from spreading from industrial
to neighbouring ecosystems.
The need to prevent GM trees
and their genes from invading native ecosystems is clear. Low-lignin
trees have the potential to disrupt the forest composting cycle
responsible for unique soil structures and nutrient cycling systems.
An influx of low-lignin trees vulnerable to damage from insects
and other herbivores, moreover, could result in pest population
explosions. Insect-resistant GM trees have the potential to disrupt
insect population dynamics and also are likely to enjoy an invasive
advantage over forest tree species. More generally, invasions of
GM trees could threaten the diversity of the forest gene pool from
which trees are selected for conventional breeding -- a reservoir
already reduced by selective logging practices. Because trees are
even more genetically compatible with their wild relatives than
highly-bred agricultural crops, GM "escapes" are especially
worrisome in forestry.
Although the need to keep GM
and non-GM trees separate meshes neatly with industrial incentives
for simplifying land use to a single species or variety of tree,
the problem is that isolation is virtually impossible in practice.
For one thing, plantations often border wild forest systems, and
indeed are often set up on land cleared of old-growth forest. For
another, tree pollen can travel vast distances. On the treeless
Shetland Islands, pollen was found from forests more than 250 km
away across the sea. In Northwest India, windborne pine pollen was
found 600 km from the nearest pine trees. Crucial forest pollinators
including flies, butterflies, ants, beetles, aphids, bumblebees
and honeybees are also notably indifferent to posted boundaries
between GM and non-GM domains. Seeds are equally difficult to limit
to a single geographical area, some being carried around by fruit-eaters
while others are wind-borne or water-borne. In fact, it is seed
or vegetative fragments which feature in the best-documented cases
of long-distance gene flow, for example the establishment of plants
on new continents. Many trees can also spread through the distribution
of broken twigs, while others send suckers up from their root systems.
A single aspen in Utah, for example, boasts 47,000 trunks springing
from its root system, and covers 42 hectares. Trees can also grow
from stumps left after felling. In sum, trees may be even more adept
at spreading their progeny than crops, and once in the wild, a single
GM tree could survive for hundreds (perhaps thousands) of years.
A Cascade of Higher-Order
Technical Fixes
One measure of the power of
the tradition of industrial landscape simplification is that for
each fresh contradiction created by attempts to "fix"
one of its problems, there is always funding to research yet further,
higher-order fixes. The result is a continuous cascade of ingenuity-absorbing
technical tweaks fated to generate still further contradictions.
Thus one "solution"
to the dilemma of genetic invasion is to attempt to engineer trees
for sterility (see BOX: GM Sterility). Making GM trees sterile,
the reasoning goes, will prevent gene flow. Predictably, however,
this second-order fix leads immediately to difficulties requiring
a third-order fix, and so on. GM sterility, for example, cannot
be guaranteed to be permanent over generations and through environmental
changes and disease stresses. Nor does engineered sterility prevent
gene flow through horizontal transfer (for example to bacteria and
fungi), or through vegetative propagation, such as twig and stump
re-growth or suckers. Moreover, stands of sterile trees devoid of
birds, insects or mammals that rely on tree seeds, pollen or nectar
for food could disrupt population dynamics (pollinators are of particular
concern), with severe repercussions for neighbouring wild systems.
|
GM
STERILITY
There are several
approaches to engineering tree sterility, including manipulation
of hormonal messaging systems, alteration of flower- and pollen-related
enzyme production, or cell ablation technology. The latter
can involve the engineering of several genetic triggers together
with a toxin gene, such as the diphtheria toxin gene, under
the control of a promoter that instructs the tree to use the
gene only in the cells destined to become reproductive structures.
The production of the toxin in these specific cells leads
to their death.
Additional advantages
which biotechnologists see in the prevention of flowering
and seed production include the possibility that sterile trees
will divert more energy and nutrients to timber production
and thus increase financial returns. Other benefits foreseen
by the forestry industry include reduction in management costs
associated with the removal of competitive seedlings following
seed dispersal, and an increase in the commercial value of
timber that is not marked by indentation and formation of
cone stems in some commercially important pine species. |
Current regulatory requirements for risk assessment constitute a
further example of an attempt at a higher-order technical fix. This
attempt, too, is quickly beset by its own limitations and dilemmas.
For one thing, much of the data which adequate risk assessment of
GM trees demands is unobtainable. For instance, in practice it is
not possible to measure accurately to what extent GM plants or their
genes might spread, simply because of the sheer size of the area
which would need to be thoroughly examined for migrants. Studying
small-scale, short-term experimental GM releases, moreover, holds
few lessons for the large-scale, long-term releases to which GM
forestry is committed, and long-distance migration and its effects
will be different for every release. Second, serious risk assessment
would exclude GM trees from precisely those uses for which they
are being principally developed. For example, Professor Kenneth
F. Raffa at the University of Wisconsin's Forestry Department suggests
that risks connected with the evolution of insect resistance can
be limited if large or homogenous plantations are avoided -- a recommendation
inherently at odds with the requirements of the large-scale forestry
industry. The team also recommends close monitoring of plantations
for a rise in insect resistance, but such monitoring is expensive
and difficult in the remote locations in which plantations are often
established.
In addition, the long life cycles
of trees and the range of seasonal and other environmental stresses
that they have to withstand entail that any genetic modifications
made to them may be unstable. This too militates against reliable
risk assessment. Each stage of a tree's lifecycle is characterised
by a cascade of previously unused genes or gene combinations --
those that act in concert to direct flower formation or fruit ripening,
for example. Determining how these interact with the engineered
gene could take several years to ascertain -- a timescale unlikely
to be acceptable to shareholders or even many environmental risk
assessors. Unforeseen results are common. Aspen, for instance, will
usually not flower before its seventh year, and German authorities
gave consent for a five-year open field trial of GM aspen trees
on the assumption that they would not flower before the trial had
finished. Unexpectedly, however, one of the GM trees started flowering
in its third year, despite pre-trial findings hinting that GM aspen
would grow even more slowly than non-GM aspen. Although all the
trees were derived from the same gene clone, in other words, they
did not all flower at the same time. Even in agricultural crops,
engineered genes have been shown to be less stable than originally
expected.
Given the threat to the development
of forestry biotech which thoroughgoing and rational assessment
would pose, it is small wonder that proponents such as Simon Bright
of Zeneca Agrochemicals are driven on occasion to articulate the
defensive and unscientific demand that questions about GM trees
be "framed in a way that gets a positive answer, or that a
positive answer is allowed". Fortunately or unfortunately,
the agencies currently undertaking risk assessment of GM trees are
often the ones with a vested interest in supplying just that "positive
answer". Thus in Canada the Canadian Forest Service both promotes
GM research and checks for risks, while Oregon State University's
TGERC program, whose future lies in promoting GM trees, is precisely
the body the US Environmental Protection Agency has chosen to assess
the dangers of the technology. This pattern hardly bodes well for
forest ecosystems and the people whose livelihoods depend directly
on them.
Conclusion
The processes through which
genetically engineered trees are being developed are profoundly
biased against social arrangements which promote and rely on biological
diversity. These processes are also riven by dilemmas and destructive
tendencies which chains of technical refinements, no matter how
long, are likely to be powerless to overcome. Tackling the challenge
GM trees pose means tackling the industrial and bureaucratic tradition
which seeks the radical simplification of landscapes. That entails
alliance-building with groups working against and outside that tradition.
In these respects, the issues
raised by GM trees are similar to those raised by GM crops. Yet
in many ways, genetic modification in forestry is an even more serious
issue than genetic engineering in agriculture. Trees' long lives
and largely undomesticated status, their poorly understood biology
and lifecycles, the complexity and fragility of forest ecosystems,
and corporate and state control over enormous areas of forest land
on which GM trees could be planted combine to create risks which
are unique. The biosafety and social implications of the application
of genetic engineering to forestry are grave enough to warrant an
immediate halt to releases of GM trees.
|