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Conservation of
Norway spruce gene resources in Finland
Veikko
Koski
The Finnish Forest Research
Institute, FIN-01301 Vantaa, Finland
Norway spruce (Picea abies
L. Karst.) is a relatively new tree species in most parts of the
country. After the latest glaciation spruce returned later than
birch and pine. Probably spruce occurred sporadically earlier, but
no more than 5500 years ago it began to spread from the east. It
took some 3000 years to reach the western and northern parts of
Finland. It is also worthwhile to mention that a large proportion of
the present land area has risen from the sea rather recently. Later
on, some 100 to 200 years ago, human impact on forests, especially
pine and spruce forests, used to be exploitive. Shifting agriculture
with prescribed burning, deliberately ignited forest fires, tar
burning, grazing of cattle, and merciless cuttings resulted in
treeless areas, which primarily turned to broadleaved forests. Owing
to early legislation, education and silviculture, forests recovered
and are now a dominating component of the Finnish landscape.
The total area of forest land
of Finland is 20 million hectares, which is 66% of the total land
area. Norway spruce is the second in abundance, after Scots pine
(Table 1). In terms of growing stock the proportions of tree species
in 1983-1993 were as follows (Yearbook of Forest Statistics 1994):
Pinus sylvestris 45.6%
Picea abies 36.8%
Betula spp. 14.5%
Other broadleaved 3.1%
The earlier land use,
mentioned above, had favoured broadleaved species. More recently
spruce has reoccupied fertile sites, and even penetrated to rather
poor `pine sites'.
For the time being nothing
seems to threaten Norway spruce and its genetic resources. However,
gene conservation is a matter for the unforeseeable future. Our tree
populations are close to the northern margin C
the tree line of many species goes across Finland. Thus, in respect
to climatic adaptability the populations must represent extreme
variants of the species in question. On the other hand, a wide
genetic variation has been revealed within populations. The goal of
gene conservation is to ascertain that this kind of natural resource
is neither accidentally nor deliberately lost. The global change of
environment is a potential threat to genetic resources. Cultivated
forests with foreign seed sources and genetically improved material
will gradually alter gene frequencies, if there are no
counteractions. The need for gene conservation was recognized by
forest geneticists as early as the 1970s. Consequently, the number
of trees subject to breeding has been large since the beginning. The
establishment of gene reserve populations did not get started until
the Strasbourg Ministerial Conference and UNCED had an impetus.
As the first step,
establishment of a network of in situ gene reserve forests
was started in 1992. By March 1995 we have registered six spruce
forest areas, the total area being 886 ha (Fig. 1). The distribution
and coverage of the gene reserves is not satisfactory yet. The
target is to find and establish some 10 more gene reserve forests,
especially in the southwestern part of the country. There are also
gene reserve forests of Pinus sylvestris, Betula pendula
+ B. pubescens, and even of Tilia cordata. The total
number over all species is 29, and their area 5188 ha (March 1995).
Besides gene reserve forests, genetic diversity has been stored in
clonal archives. There are altogether close to 1600 clones, both
plus trees and special forms in the clonal archives.
Table 1. Proportions
of species according to their dominance in forests (Yearbook of
Forest Statistics 1994)
|
Region |
Forest area (x 1000 ha) |
Proportion (%) |
| |
|
Treeless |
Pine |
Spruce |
Other conif. |
White birch |
Downy birch |
Other broad leaved |
|
Whole
country
|
20 058 |
1.8 |
64.6 |
25.5 |
0.1 |
1.3 |
6.0 |
0.6 |
|
South
Finland
|
11 499 |
1.6 |
56.8 |
33.2 |
0.1 |
2.2 |
5.1 |
1.1 |
|
North
Finland
|
8 559 |
2.1 |
75.0 |
15.2 |
0.1 |
0.2 |
7.2 |
0.2 |
Fig. 1. Gene reserve
forests of Norway spruce (nos. 1-6 refer to breeding zones, see
Table 2)
Table 2. Gene reserve
forests of Norway spruce in Finland, registered by 1 January 1995
|
Code no. |
Locality |
Latitude, N |
Longitude, E |
Area (ha) |
|
3 |
Lapinjärvi |
60E 39' |
26E 08' |
250 |
|
4 |
Luopioinen |
61E 23' |
24E 48' |
80 |
|
9 |
Tervola |
66E 09' |
26E 01' |
190 |
|
10 |
Kittilä |
68E 01' |
25E 25' |
150 |
|
18 |
Puolanka |
64E 39' |
28E 03' |
112 |
|
25 |
Posio |
65E 54' |
27E 48' |
120 |
A national long-term tree
breeding program of 1989 suggests establishment of long- term
breeding populations for all main species by breeding zones. For P.
abies six breeding zones have been delineated in Finland. The
basic material of these breeding zones would be phenotypically
selected plus trees. The designing of the factual populations is
still underway.
Finland is in the fortunate
position that the genetic resources of the main forest trees, P.
sylvestris, P. abies and B. pendula + B. pubescens,
are not subject to direct threat. The challenge of gene conservation
is how to justify necessary actions now in order to maintain the
wealth even in the far future. Biodiversity and gene conservation
are favourite issues, as long as your own money is requested. After
a few years people may have new topics in their minds and selling
the idea of gene conservation may be much harder than it is today.
The main stream of gene
conservation is by means of gene reserve forests. Based on the
conditions of efficient pollination and the need of parcels of
various age classes the minimum area of one unit ought to be 100 ha,
i.e. 1 km2. Finding this large area of naturally
originated forest in public ownership is not always easy. In the
southern part of Finland forests are mainly privately owned and
consist of rather small holdings. Plantings with transferred, and
even unknown, origins interfere with the natural population
structure. The frequency of nonindigenous provenances and
genetically improved stock will gradually increase in the future.
Rather than giving up the
purity requirement and the target area of 100 ha, we could start
with smaller `kernels' and then later on enlarge the population with
plantings. Seed must, of course, originate from the nucleus. Extra
costs of artificial enlargement may cause difficulties, and it
requires sincere effort to carry through this kind of action. The
advantage of gene reserve forests is that they are managed and
merchantable timber may be harvested, as well as seed.
For the time being we do not
see urgent research needs in our spruce gene reserves. I consider
the project a practical operation, where we must not waste any more
time. Selection and documentation of the missing samples is the main
goal. Characterization of populations by means of genetic markers
would be desirable, but is out of the question because of economic
restrictions. On the other hand, gene reserves provide excellent
reference and study material for genetic studies.
Public concern on nature
protection and biodiversity has been efficiently promoted by the
mass media. An emotional attitude readily leads to an all-or-nothing
approach to conservation. The need for gene conservation is
certainly well accepted and understood. Some contradiction occurs as
regards the methods of conservation. Old forests and strict nature
reserves appeal to laymen, whereas forest geneticists prefer
actively managed genebanks.
We have to keep on saying that
conservation of forest genetic resources is the duty of the present
generation. We still have large areas of native (spruce) forests in
our country. As the first step a covering network of in situ
gene reserve forests should be established. A guidebook for the
handling of gene reserve forests is anticipated.
The establishment of ex
situ long-term breeding populations is still on the planning
desk. Breeding zones have been delineated, and there are sufficient
numbers of phenotypically selected plus trees in each zone. Every
breeding zone will have a breeding population of its own. As the
composition and the physical location of the breeding populations
determine the mode of action into the far future, the planning has
been thorough and time consuming. The choice between closed or open
systems, large entities or substructures, basic population versus
nuclei, are under discussion. Information on possible experiences on
Small Multiple Population Breeding Systems or other advanced models
of breeding/conservation would be useful.
To my mind, gene conservation
proper and effectively functioning breeding populations do not
necessarily cover each other. After a few generations of selection a
broad variation in breeding populations may become a `genetic load'
instead of a `hidden treasure'. My final statement is: Let us start
with simple and inexpensive measures, such as gene reserve forests,
now. If we wait for a perfect universal method, it may be developed
too late.
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