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Gene
conservation of Norway spruce (Picea abies) in Poland
Jan Matras
Forest Research Institute,
Department of Genetics and Physiology of Woody Plants,
00973 Warsaw, Poland
Introduction
The network connected with
gene conservation of forest tree species started in 1991 when the
Programme of gene conservation and tree breeding for 1991-2010 was
formally confirmed by Officials. This Programme was mainly prepared
for conservation of genepools of the species in economical forests
(State Forests). In this Programme the strategic aims of gene
conservation were estimated. Conservation of the forest gene
resources is necessary to sustain:
- continuity of
fundamental ecological processes,
- maintenance of forests
and utilization of ecological systems,
- restitution of forests
destroyed by anthropogenic factors,
- preservation of
biological and genetic variety for future generations,
- increased natural
resistance of the future forests.
To the main factors causing
threats to genetic variety of native populations belong:
- decrease of
participation of same species in next generations by their
substitution by foreign provenances or species,
- pollen contamination of
other provenances or species,
- biotic factors causing
forest decline (insects, fungi, game),
- abiotic factors
(greenhouse effects, air pollution).
Methods
Depending on the threat to the
forests it is planned to use different methods of gene conservation.
For these reasons the forests (areas) are classified in three
groups:
Areas without threat
(mainly in situ
preservation)
- choose the stands and
trees for gene conservation,
- initiate natural
regeneration in these stands,
- provide additional
protection of very old stands and trees,
- provide secondary
protection where necessary on ex situ plots,
- progeny plantations,
- seed orchards,
- clonal archives,
- seeds in genebank.
Areas of medium threat
(in situ and ex situ
preservation)
In situ
- initiation of natural
regeneration in chosen stands,
- choose threatened
populations and trees for preservation ex situ.
Ex situ
- progeny plantations,
- seed orchards,
- seedling seed orchards,
- clone collections,
- long-term storage of
seeds, pollen and parts of plants.
Areas of total decline of
forests
(ex situ preservation)
- vegetative propagation
of populations and single trees by cuttings and tissue cultures,
- progeny plantations,
- seed orchards from
vegetatively propagated materials,
- long-term storage of
plant materials.
Results
Spruce exists in Poland in
three subranges (or regions Giertych), separated by areas where
spruce does not occur naturally. It is probably connected with
glacial epoch and spruce refugial regions from which spruce migrated
mainly in northerly and westerly directions. Spruce growing in
northeast Poland (northeast subrange) is connected with the northern
and eastern ranges of this species in Lithuania, Latvia and
Byelorusia. Hercynian West Carpathian subrange is the part of
natural range connected with spruce growing in Germany, Czech
Republic and part of Slovakia. Spruce growing in the southeast part
of Poland belongs to the southeast Carpathian subrange.
On the basis of this
macrodivision were delimited the areas where existing natural
populations of spruce should be included in a long-term gene
conservation programme. Between these populations there are also
well-known and valuable Polish provenances such as: Bystrzyca,
Ldek, Istebna, Wis»a, Nowy Targ, Tarnawa, Zwierzyniec, Bia»owieńa,
Augustowo, Knyszyn and Borki.
Apart from these populations,
other spruce stands located in central and northwest Poland were
included in the programme of long-term gene conservation of spruce.
In total, 52 populations (stands) of spruce were chosen for gene
conservation in Poland (Table 1). All of these stands will be
managed as normal stands and at the proper time the natural
regeneration for establishing in situ progeny plantations
will be started.
Parallel ex situ
progeny plantations were established artificially from seeds
collected in these stands. The size of the work connected with ex
situ gene conservation of spruce in Poland is shown in Table 2.
Until 1993, 623.7 ha in situ and ex situ progeny
plantations had been established.
Also, clones of spruce (about
500) existing in seed orchards are treated as an additional source
of genes for conservation.
Short-term activities in gene
conservation of spruce are connected with the threat of populations
growing in Sudety region.
For this reason, field work
was done, which let us choose natural or probably natural stands in
11 Forest Districts (about 670 ha) for ex situ gene
conservation. In these stands 2 years ago was begun the first clone
collection and 49 samples of seeds (1.5 kg each) were put in a
genebank for long-term storage (Table 3).
Additionally, a special
short-term programme for gene conservation of spruce for the oldest
natural stands and trees growing in our protected areas is managed
by Dr A. Korczyk in northeast Poland, mainly for Bia»owieńa
National Park.
In the first phase of this
work one natural stand of different ages (40-240 years) and 73 trees
older than 200 years, growing in different soil conditions, were
chosen for conservation of our premanagement natural population of
spruce. These trees were used for establishing ex situ clone
collections (4.16 ha) in two different places.
[Table 1] Not
available
[Table 1. cont'd.] Not
available
Table 2. Areas of in
situ and ex situ progeny plantation established up to
1993
|
Regional Forest District |
Area (ha) |
|
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17 |
Bialystok
Gdańsk
Katowice
Kraków
Krosno
Lublin
Lódz
Olsztyn
Pila
Poznań
Radom
Szczecin
Szczecinek
Toruń
Warszawa
Wroclaw
Zielona Góra |
16.1
82.0
226.0
8.5
80.9
80.9
80.9
69.0
34.4
34.4
34.4
34.4
9.7
9.7
9.7
97.1
623.7 |
Research
At the same time as networks
connected with gene conservation were started, the Gene Bank
Laboratory was created in the Department of Genetics and Physiology
of Woody Plants of the Forest Research Institute. This laboratory
carries out the studies which are necessary for practical
realization of gene conservation, including:
- genetic diversity of
natural populations of spruce in Poland,
- influence of the
anthropogenic factors on genetic structure of populations,
- methods of long-term
storage of seeds and pollen,
- consequences of
long-term storage of seeds on genetic structure of seed samples,
- methods of propagation
by:
- cuttings,
- organogenesis,
- embryogenesis,
- somaclonal variation of
seedlings from somatic embryos,
- cryopreservation of
embryos, callus and `artificial seeds',
- monitoring changes in
stored seed, pollen and embryo samples.
Table 3. Spruce stands
where cones were collected for long-term storage in genebank
|
Forest District |
Altitude (m) |
Plot number |
Age (yrs) |
|
701 |
Šwieradów |
490-570
550-630
550-680
880-930 |
224 g
263 a
277 c
411 f |
90
90
85-90
80 |
| |
Szklarska Porźba |
600
670-700 |
240 i, 134 l
116 c |
110
134 |
| |
Kamienna Góra |
600-800 |
278 ac |
- |
| |
Wabrzych |
500-550
520-550
520-600
520-600
520-600
550-620
620-640
600-800
600-800
600-800 |
117 j
126 a, 127 a
117 c
117 i
126 f
127 b
291 f
216 k, 217 b
337 ab
281 d |
140
130
140
140
100
105
95-100
83
-
140 |
|
702 |
Jugów |
550-810
590-790
730-870
740-940
790-940 |
41 f
34 c
9 c
212
224 f |
110
95
120
95
115 |
| |
Zdroje |
480-500
630-700
500
510-650
690-720
760-960 |
34 c
23 h
152 a
52 a
129 g
295 h, 297 c |
110
115
145
100
135
115 |
|
703 |
Miźdzylesie |
520-630
680
680
750
690-780
780-830
840-910
990-1060
1120
940
1250 |
146 f
199 b
132 i
192 c
166 c
138 c
163 c
154 bf
17 c
23 l
220 d |
158
128
117
120
112
112
122
133
132
112
150 |
| |
Lodek Zdrój |
400-600
450
700-800
800
820
900
800-950 |
280 d
50 d
240 b
151 a
197 i
312 g
314 lf |
145
140
110
100
105
140
160 |
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