evolution of standing volumes by species in the lipova hills … 22(3) pdf... · 2019. 3. 1. ·...
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Volume 22(3), 73- 78, 2018 JOURNAL of Horticulture, Forestry and Biotechnology
www.journal-hfb.usab-tm.ro
73
Evolution of standing volumes by species in the Lipova Hills region using the Romanian National Forest Inventory’s methodology Dancea I. D.1*, Turcu D. O.1, Marin G.2
1National Research and Development Institute for Forestry “Marin Drăcea” – Timişoara branch;
2National
Research and Development Institute for Forestry “Marin Drăcea” *Corresponding author. E-mail: [email protected] Abstract The Lipova Hills region, located in Western Romania, is well covered by forests. The forest ecosystems are highly diverse regarding the tree species, about 25 different species being present in the upper canopy of the forests. Although most of the area is covered by mixed Quercus forests, in the Eastern part of the territory the European beech becomes more dominant. This study aims to roughly estimate the evolution of the standing volumes by tree species within the three Forest Districts from the region – Bârzava, Radna, Săvârșin – using the methodology and sample data from the Romanian National Forest Inventory (IFN). Within the first cycle of measurements (2007-2012), the mean volumes per hectare were respectively 371.653 m
3/ha for Bârzava Forest District, 256.865 m
3/ha for Radna and
332.709 m3/ha for Săvârșin. The values for the second cycle (2013-2018)
were respectively 374.212 m3/ha – Bârzava, 271.277 m
3/ha – Radna and
348.765 m3/ha – Săvârșin. The close similarity between the values from the
first cycle of inventory and the second cycle suggests a high stability of the forest ecosystems.
Key words Standing volumes, Lipova Hills, Romanian National Forest Inventory
The Romanian National Forest Inventory (IFN) was
established in Romania in 2006 (roifn.ro) as part of the
country’s accession to the European Union. The IFN is
an inventory based on modern methodologies and has
multiple aims: to evaluate the forest resources of the
country, to generate information for developing forest
policies, to generate information about the carbon
storage in the forest ecosystems and reporting under
the Kyoto Protocol, to gather information about the
biological diversity of the forests, etc. (roifn.ro).
The older forest inventories of Romania were
accomplished in the respective years 1973, 1980, 1984
using the information gathered by the forest
management planning system, without specific field
measurements. The modern IFN, established more than
a decade ago, continuously gathers information based
on a grid of sample plots; the first cycle of the
inventory was (2007) 2008-2012, and the second cycle
(2013-2018) will be completed at the end of 2018
(roifn.ro).
We used the data collected by the National Forest
Inventory, from 34 sample plots established in three
Forest Districts (Bârzava, Radna, Săvârșin) from the
Lipova Hills region. The raw information from IFN,
from both measurements (cycle I and II), was used
independently for calculations in order to express the
evolution of standing volume per hectare and by
species in the chosen region.
Material and Method
The National Forest Inventory uses permanent sample
plots (each of them with 4 sub-plots, Fig. 1.) which are
fully measured within a cycle of 5 years (*** 2007,
2013). The Inventory statistically covers the territory of
the country following a 4 x 4 km grid network in the
areas where the forest are well represented and 2 x 2
km in the areas where forests are rather scarce
(roifn.ro) (*** 2007, 2013).
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Fig. 1. The sample plot consisting of 4 sub-plots (roifn.ro)
Our study focuses on the hilly region in the nearby of
Lipova Town, Western Romania, on the Northern side
of the Mureș River (Fig. 2.), in the lowest part of its
basin, before its arrival in the Western Plains. This
hilly region’s specificity consists of oak forests which
are transiting to the East in beech dominated forests,
having a diversified range of species (taxons) which
establishes high biodiversity values.
Fig. 2. Study site – the Lipova Hills region (earth.google.com)
We used 34 sample plots (with 114 sub-plots) from the
National Forest Inventory, which cover the area of
three forest districts: Bârzava, Radna, Săvârșin. For all
trees (starting from diameter at breast height of 56 mm)
their respective positioning was recorded – polar
coordinates from the sub-plot center, then the
diameters at breast height (DBH, at 1.3 m) were
measured and recorded, total heights (H) were
measured using Vertex III device with high precision
(0.1 m) and recorded. All these measurements, together
with other measurements and qualitative information
about trees were recorded in the field in the specific
IFN software (roifn.ro).
The standing volume was calculated by aggregating the
individual volumes of all trees, which respectively
were computed using the following formula (Giurgiu et
Decei 1997):
log(v) = a0 + a1 log d + a2 log2 d + a3 log h +
a4 log2h
Where: v represents the individual volume of the tree
in m3, d represents the diameter at breast height in cm
and h represents the total height of the tree in m.
The parameters of the equation for the species found in
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our sample plots are shown in Table 1 (Giurgiu et Decei 1997):
Table 1
Parameters of the volume equation (Giurgiu et Decei 1997)
Species a0 a1 a2 a3 a4
Acer campestre -3.22096 1.58409 0.13567 -0.08677 0.313054
Acer platanoides -3.48668 1.00128 0.40669 0.74812 -0.013734
Acer pseudoplatanus -4.06012 1.81478 0.07283 0.76688 0.006155
Acer tataricum -3.45646 1.94746 0.01879 -0.16420 0.342355
Betula pendula -4.16999 2.27038 -0.21540 0.30765 0.368258
Carpinus betulus -4.23139 2.15204 -0.00988 0.59652 0.112810
Cornus mas -3.22096 1.58409 0.13567 -0.08677 0.313054
Corylus avellana -3.22096 1.58409 0.13567 -0.08677 0.313054
Crataegus sp. -3.45646 1.94746 0.01879 -0.16420 0.342355
Fagus sylvatica -4.11122 1.30216 0.23636 1.26562 -0.079661
Fraxinus excelsior -3.53048 1.26636 0.31105 0.52368 0.082743
Fraxinus ornus -3.53048 1.26636 0.31105 0.52368 0.082743
Malus sylvestris -3.50736 1.91195 0.02764 -0.28831 0.432403
Picea abies -4.18161 2.08131 -0.11819 0.70119 0.148181
Pinus nigra -4.01698 1.96342 0.01241 0.57848 0.094783
Pinus strobus -4.36966 1.55475 0.14981 1.40295 -0.157352
Pinus sylvestris -3.84672 1.82103 -0.04107 0.35677 0.334910
Populus tremula -4.22131 1.76256 0.05900 1.04105 -0.009430
Prunus avium -3.59371 1.95047 0.04086 -0.12835 0.374948
Prunus domestica -3.59371 1.95047 0.04086 -0.12835 0.374948
Pseudotsuga menziesii -4.29910 1.90710 0.02841 1.01819 -0.055894
Pyrus pyraster -3.96965 2.11784 -0.03021 0.32199 0.127335
Quercus cerris -3.68707 2.03534 -0.06747 -0.15871 0.500372
Quercus frainetto -4.25185 2.03370 -0.02026 0.93727 -0.022033
Quercus petraea -4.17315 2.27662 -0.09084 0.57596 0.093429
Quercus robur -4.13329 1.88001 0.04880 0.95371 0.063638
Quercus rubra -3.60162 2.03988 0.00783 -0.13348 0.337740
Robinia pseudoacacia -3.37551 1.80802 0.02827 -0.33554 0.512150
Salix alba (vegetative regeneration) -4.19326 1.58473 0.01938 0.93588 0.144451
Salix caprea -4.01470 1.72202 0.08639 0.85987 -0.009759
Sambucus nigra -3.22096 1.58409 0.13567 -0.08677 0.313054
Sorbus domestica -4.31485 2.58064 -0.21693 0.55092 0.025773
Sorbus torminalis -4.31485 2.58064 -0.21693 0.55092 0.025773
Tilia sp. -4.80605 1.92424 0.02214 1.96408 -0.452969
Ulmus sp. -4.49118 2.18244 -0.10324 1.20293 -0.124978
Results and discussions
The total number of trees measured for the 34 sample
plots within the first cycle of IFN was 3246 (by Forest
District, repectively: Bârzava 826, Radna 965, Săvârșin
1455 trees). Within the second cycle of IFN, the total
number of trees measured was 3027 (respectively:
Bârzava 793, Radna 875, Săvârșin 1359 trees). The
new trees recorded for the second cycle are 179
(Bârzava 49, Radna 53, Săvârșin 77 trees). During the
5 years interval between the two recording cycles, a
total number of 398 trees were lost (Bârzava 82, Radna
143, Săvârșin 173 trees) due to multiple causes: natural
elimination of some trees due to competition, normal
tree harvesting, tree break under 1.3 m, in rare cases
some trees were not accesible in the firts cycle, also in
rare cases some trees were not inside the plot any more
(horizontal distance from the sub-plot center to the tree
is larger than the sub-plot radius, mainly caused by
landslides). The volume gain through the “new” trees
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is respectively 5.351 m3/ha for Bârzava Forest District,
6.945 m3/ha for Radna and 5.468 m
3/ha for Săvârșin.
The volume “lost” by dissapearance/cutting of trees is
represented respectively by: 2.792 m3/ha for Bârzava, -
7.466 m3/ha for Radna and -10.587 m
3/ha for Săvârșin,
the last two negative values meaning that actually the
volume extracted/dissapeared is more than the
increment of the standing trees combined with the
volume gained by the “new” trees.
The mean standing volume per hectare for the studied
area for the first cycle was 320.409 m3/ha. For the
second cycle the average standing volume is 331.418
m3/ha, increasing by a rate of 3.44% compared to the
first cycle. By Forest District, the average standing
volume is 371.653 m3/ha for Bârzava for cycle I and
374.212 m3/ha for cycle II (increasing by 0.69 %); in
Radna, cycle I totalizes 256.865 m3/ha and cycle II
totalizes 271.277 m3/ha (increasing by 5.61 %); in
Săvârșin, the mean of cycle I is 332.709 m3/ha and the
mean of cycle II is 348.765 m3/ha (increasing by 4.83
%) (Fig. 3).
Fig. 3. Evolution of total standing volume per hectare, Cycle I and Cycle II
The evolution of standing volumes by species within the three Forest Districts is shown in Fig. 4, Fig. 5, Fig. 6:
Fig. 4. Evolution of standing volume per hectare by species, Bârzava Forest District
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The evolution of the standing volume per hectare in the
Bârzava Forest District shows a slight increment, if we
consider all the species (0.69 %) (Fig. 4.). At
individual species though, there are strong relative
increments – Salix alba by 42.69 %, Tilia sp. by 36.03
%, Pyrus pyraster by 33.53 %. There are also strong
relative decreases – Quercus robur by 100 %, Fagus
sylvatica 28.92 %, Populus tremula 21.9 %. Other
species, like Quercus petraea, showed a very small
evolution between the two cycles of the Inventory.
Fig. 5. Evolution of standing volume per hectare by species, Radna Forest District
Within the Radna Forest District, the evolution of the
standing volume per hectare shows an increment of
5.61 %, considering all species (Fig. 5.). The highest
positive evolution is represented by the following
species: Fagus sylvatica – 49.71 %, Sorbus domestica
– 41.12 % and Pyrus pyraster – 32.94 %. The relative
decreases are lead by Acer campestre – 69.14 %,
followed by Salix caprea – 67.47 % and Robinia
pseudoacacia – 36.91 %. Quercus petraea and
Quercus frainetto have shown a relative constance in
volume through the two cycles of the Inventory.
Fig. 6. Evolution of standing volume per hectare by species, Săvârșin Forest District
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The standing volume of the forests from the Săvârșin
Forest District show a small tendency of increasing
between the two cycles of the IFN (4.83 %) (Fig. 6.).
The positive evolution tendency is lead by Sambucus
nigra – 172.25 %, followed by Fraxinus ornus– 61.41
% and Robinia pseudoacacia – 42.14 %. The relatively
negative tendency is shown by the following species:
Corylus avellana – 92.36 %, Salix caprea and Acer
tataricum – both with 100 %. Fagus sylvatica, which
becomes one of the dominant species in this area,
shows a remarcable constance tendency (1.52 %
increment).
Conclusions
The mean standing volume per hectare (considering all
three Forest Districts) was 320.409 m3/ha for the first
IFN cycle, very close to the national average standing
volume per hectare which is 321.925 m3/ha (roifn.ro),
while for the second cycle was 331.418 m3/ha
(increasing by 3.44%). The evolution of standing
volume for all of the three studied Forest Disticts
showed a light increasing tendency, respectively
Bârzava by 0.69 %, Radna by 5.61 % and Săvârșin by
4.83 %.
The evolution of the standing volume per hectare by
species shows great increases in Salix alba, Tilia sp.
and Pyrus pyraster in Bârzava Forest District, Fagus
sylvatica, Sorbus domestica and Pyrus pyraster in
Radna Forest District and Sambucus nigra, Fraxinus
ornus and Robinia pseudoacacia in Săvârșin Forest
District. On the other hand, some species show great
volume decreases between the two cycles, like Quercus
robur, Fagus sylvatica and Populus tremula in Bârzava
Forest District, Acer campestre, Salix caprea and
Robinia pseudoacacia in Radna Forest District and
Acer tataricum, Salix caprea and Corylus avellana in
Săvârșin Forest District. Some species show a
remarcable constance in volume, like Quercus petraea
in Bârzava Forest District, Quercus petraea and
Quercus frainetto in Radna Forest District and Fagus
sylvatica in Săvârșin Forest District.
The evolution of standing volumes by species, studied
within the three Forest Districts, leads to the
conclusion that from West towards East, the
importance of the oak species decreases and the beech
is more and more dominating. The high stability of the
studied forest ecosystems is indicated by the close
similarity between the observed standing volumes from
the first cycle of inventory and the ones from the
second cycle.
Acknowledgements
The author D. O. Turcu was supported by the project
PN 18040401.
References
1. Giurgiu, V.; Decei, I., 1997: Biometria arborilor din
România. Metode dendrometrice / Biometry of the
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4. www.earth.google.com
5. www.roifn.ro