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† Ante Krstinic 1, Joso Gracan
2 and Davorin Kajba1
1 Faculty of Forestry
University of Zagreb, 10000 Zagreb, Croatia
2 Forest Research Institute, 10450 Jastrebarsko, Croatia
Foreword
At the second meeting of the
EUFORGEN Noble Hardwoods Network held in Laurizan, Spain from 23 to
25 March 1997, it was concluded that is necessary to work on
European gene conservation strategy for the genus Alnus. This
task was given the participants from Croatia (Ante Krstinić and
Joso Gračan). This strategy document was planned to be finished
for the third meeting in Sagadi, Estonia, 13 to 16 June 1998.
However, at the meeting it was noted that the strategy for this
species could not yet be presented, and it would be discussed at the
next one.
Black alder (Alnus
glutinosa /L./ Gaertn.) is very important forest tree species in
Croatia, especially in the floodplain ecosystems along the Sava and
Drava rivers. Because that black alder is very variable and fast
growing species found all over Europe, in our opinion it can be used
as a example for Conservation strategy models of gene resources for
other species of genus Alnus.
Introduction
The genus Alnus
includes about 36 species mostly located in the Northern Hemisphere.
Generally, alders grow in the regions of floodplain forests, even
though in mountains of central Europe they occur along water flows
up to 2800 m above sea level. Species of this genus grow either as
bushes or high trees, showing great variability in their
morphological and physiological properties.
Black alder is becoming a more
and more interesting forest tree species due to its multiple uses
both in the forestry and wood industry. It is known as a fast
growing and meliorative species, which has the ability of fixing
atmospheric nitrogen. Black alder stands with longer rotations can
produce logs of very good quality for wood industry, but in short
rotation (cycles) in so-called special-purpose plantations it is
very desirable for biomass production (Krstinić 1994). The
basic function of these black alder plantations is a reduction of
the pressure on natural forests of valuable hardwoods species (oak,
beech, ash, maple), conservation of genetic resources and effect on
global climate changes. Owing to these characteristics black alder
proved to be very suitable for tree cultivation either in the form
of pioneer plantations or in mixed plantations with other coniferous
and deciduous tree species which grow better than in monocultural
plantations (Hansen and Dawson 1982; Heilman and Stettler 1983;
Krstinić and Komlenović 1986).
As the natural distribution of
black alder is not compact but markedly disjunct and widely spread
both in the horizontal and vertical directions, the natural
populations of this species exist in different edaphic conditions,
and it should be supposed that climatic, edaphic and altitudinal
races are differentiated. This hypothesis is proved by the results
of provenance research which have showed very distinct genetic
differences in survival and biomass production (Krstinić et al.
1992.). The genetic differences between provenances are found not
only at the European level but also at a broader one. As a result of
what was mentioned above there is a need to protect existing
biodiversity of natural populations and to spread the range of black
alder by establishing plantation on suitable sites.
Distribution
Species of the genus Alnus
are widely spread in the Northern Hemisphere from Northern Africa in
the South up to 70o N in Europe and Asia. In south
America, species of the genus Alnus occur south from the
equator in Peru as well as in the northern part of Argentina up to
the latitude of 25o S. They usually grow in cold and
moderate climate conditions, but they can be also found in the warm
regions of the Mediterranean. Alders grow on the banks of streams
and lakes in a humid habitats, although their occurrence in dry
sites have been observed too. Most species prefer rich, moist but
well drained soils with a high water table. Stagnant waters are
tolerated well by some species only.
Black alder is spread all over
Europe from Ireland in the west to western Siberia in the east, as
far as northern Africa in the south and up to 65o in the
north. It has been introduced in the Azores and in the United States
of America. Its range both in Europe and Africa is not compact but
markedly disjunct. In the mountainous regions of the central Europe
it reaches altitudes between 1500 and 1800 m. Its preferred climate
is moderate to cold one, it grows best in deep soils where the water
table is high. Optimum amount of precipitation is from 800 to 860 mm
per year. It does not tolerate stagnant water or high soil acidity
(Fig. 1).
Alnus glutinosa /L./
Gaertn. belongs to the genus Alnus, of the Betulaceae
family. Some 36 species of the genus Alnus are divided
into various number of subgenera, subspecies or varieties.
In its natural range in
Europe, black alder usually reaches the height of 25 m and in some
rare cases up to 40 m. Diameters in old trees normally are between
35 to 40 cm, but a maximum diameter at breast height of 175 cm was
found. Black alder is a highly variable forest tree species,
therefore, it has been the subject of research carried out by many
scientists.
Importance for forestry and
environmental protection
Black alder is becoming an
increasingly interesting forest species due to its multiple uses
both in the forestry and wood industry. It is a known as a
meliorative species which, owing to a symbiotic actinomycete, Frankia
alni, located in nodules, has the ability of fixing atmospheric
nitrogen. The nodules act not only as a nitrogen fixatives but also
as regulators of photosynthetic products (Wheeler and Lawrie 1976).
This ability makes it very suitable for tree cultivation either in
pioneer plantations or in mixed plantations with other coniferous
and decidous tree species which grow better than in monocultural
plantations (Hansen and Dawson 1982; Heilman and Stettler 1983;
Krstinić and Komlenović 1986, and others).
Black alder may also be used
as a pioneer species in establishing common oak plantations, common
ash tree plantations and black poplar plantations. However, our
experiences have shown that the establishment of mixed plantations
with mentioned species is not easy since black alder fast outgrows
common oak. Therefore, pioneer plantations for this purpose should
be used mainly for biomass production and soil enriching with
nitrogen, that will then improve the growth of oaks and ash.
Black alder wood is used in
mechanical and chemical processes. Thus, it is used in mining and
hydraulic engineering, in production of veneer, utility plywood and
joinery boards, and for the pulp and paper and furniture industry.
It is also used in many crafts, musical instruments, models, toys,
barrel stopcorks, wooden shoes, etc. Being very sensitive to the
presence of SO2, black alder may find an application as a
bio-indicator in case of air pollution by this chemical compound. By
cultivating black alder in mixed or pioneer plantations, the use of
nitrogen fertilizers is avoided and the biological control of weed
vegetation is ensured by shading thus making the application of
herbicides unnecessary. In this way, it protects the soil and
underground water (Trinajstic et al. 1991).
Growth of black alder is very
intensive between the fifth and the tenth year, as well as between
fifteenth and twentieth year (Mlinsek 1960, Ehrenberg 1979,
Nemesszeghy 1986.). After reaching the age of 20, a stagnation of
growth in height occurs while diameter growth remain satisfactory in
old age. In the Table 1, data describing black alder production in
Sweden, Germany and Croatia for various age and different habitat
are given according to several authors. In this table the data show
that the number of standing trees per ha depends in the first place
upon the age (Schwapach 1902, Rauš 1971, Vidakovic and Krstinic
1984). According to the some authors, at the age of 40 the number of
trees per ha varies from 568 to 1352, but at the age of 60 from 363
to 595 trees/ha.
The annual average volume
increment of black alder stands is lowest in the north but becomes
higher towards to the south. The maximum volume increment per annum
in Sweden is 3,9 m3/ha, in Germany 6,4 m3/ha,
in Slovenia and Croatia from 7,7 to 9,7m3/ha.
The first records of the black
alder plantations originate from eastern Germany (Ehrenberg 1979).
Later, plantations of this species have also been established in
other countries where black alder is autochtonous as well as in
countries where it is cultivated as an exotic species (USA, Canada).
In order to improve its cultivation, special of black alder breeding
have been prepared in several countries in Europe in States and in
Canada (Hall 1985). When establishing black alder plantations, it
must be taken into consideration that this species is very sensitive
to unsuitable sites (the environmental stress) and to some
arboricides (Tordon 10 k), also it is sensitive to NaCl and to
herbicides.
Table 1: Black alder
production (Alnus glutinosa /L./ Gaertn)
|
Country |
Soil
quality |
Age in
years |
Average
height in m |
Average
breast diameter in cm |
Number
of stranding trees/ha |
Wood
stock m3/ha |
Average
annual in crease m3/ha |
Stand/plantation
type |
Author |
|
Croatia |
III |
5 |
5 |
4 |
15.000 |
- |
- |
Posavina,
pure, natural |
Rauš,
1971 |
|
Croatia |
III |
10 |
11 |
8 |
5.000 |
- |
- |
" |
Rauš,
1971 |
|
Croatia |
III |
40 |
26 |
30 |
- |
- |
- |
- |
Rauš,
1971 |
|
Slovenia |
I |
21 |
17.0 |
15.6 |
1.435 |
204 |
9.7 |
Pomurje,
mixed, natural |
Mlinššek,
1962 |
|
Slovenia |
I |
40 |
21.0 |
28.0 |
670 |
365 |
9.1 |
" |
" |
|
Slovenia |
I |
59 |
23.0 |
34.0 |
595 |
521 |
8.8 |
" |
" |
|
Croatia |
I |
48 |
20.0 |
25.5 |
500 |
250 |
5.2* |
Natural
popult., Podravina |
Vidaković
& Krrtinić, 1984 |
|
Croatia |
I |
70 |
28.5 |
36.0 |
400 |
538 |
7.7* |
" |
" |
|
Croatia |
III |
50 |
19.5 |
24.0 |
_ |
_ |
_ |
Natural
popul., Posavina |
" |
|
Croatia |
IIII |
75 |
21.2 |
29.6 |
_ |
_ |
_ |
" |
" |
|
Germany |
I |
20 |
14.5 |
11.7 |
1.529 |
140 |
7.0 |
Natural
stand |
Schwappah,
1902 |
|
Germany |
I |
40 |
20.9 |
21.7 |
677 |
281 |
7.0 |
Natural
stand |
" |
|
Germany |
I |
60 |
24.1 |
27.4 |
476 |
359 |
6.0 |
Natural
stand |
" |
|
Germany |
I |
20 |
15.1 |
11.5 |
1.578 |
110 |
5.5 |
Pure
plantation |
Schober,
1975 |
|
Germany |
I |
40 |
20.8 |
20.8 |
665 |
228 |
6.4 |
Pure
plantation |
" |
|
Germany |
I |
60 |
24.7 |
29.0 |
363 |
283 |
5.2 |
Pure
plantation |
" |
|
Germany |
I |
90 |
28.8 |
40.1 |
190 |
351 |
3.9 |
Pure
plantation |
" |
|
Sweden |
I |
11 |
5 |
2.7 |
2.168 |
4 |
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