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Determination of the optimal financial rotation period in poplar plantations

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  • University of Belgrade, Faculty of Forestry, Belgrade, Serbia

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Due to trends in the consumption of wood and particularly soft broadleaves, poplar cultivation has gained importance in Serbia and worldwide in the field of production, economics and environmental protection issues. The present study was performed to determine the optimal financial rotation lengths for hybrid poplar plantations (Populus Euramericana Gunier cv. I-214) in a selected area of Serbia. The aim of this study is to apply the method of assessment and calculation of the optimal production cycle length in order to determine the optimal production cycle length of poplar plantations in the localities of Serbia from a financial standpoint. The selected discount rate for the calculation is 6% (close to the maximum recorded internal rate of yield in the observed compartments). It was concluded that the production cycle length of poplar in the study area ranges from 12-19 years, depending on the soil type. The longest rotation is obtained for humofluvisol (alluvial semigley). The estimation based on the NPVs criterion determined a desired optimal production cycle length of about 16 years
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ISSN 2029-9230
673
2017, Vol. 23, No. 3 (46)
Introduction
Poplar plantations play one of the key roles in the
industrial wood supply in countries such as China, France,
India, Italy and Turkey, and each of them produces more
than 1 million m3 of poplar wood from specialised planta-
tions (Spinelli and Magagnotti 2011). Managed on 10 to
30 years rotations, some of the clones can produce ve-
neer logs (Hongyuan 1992).
Poplars are one of the most productive tree species
in Serbia, which production complexity requires rational
and well-planed management, whereby the site and spe-
cies potentials would be maximally used (Keèa and Pajiã
2010). Conventional poplar growing in Serbia is charac-
terized by the high costs of plantation establishment, as
it is common to use the technology of full ground and
soil preparation, with a lot of working operations (Keèa
and Pajiã 2015). Alluvial plains along the rivers Danube,
Sava, Tisa, Ibar and Morava Rivers are suitable for the
growth of several broadleaved tree species (Quercus
robur L., Fraxinus angustifolia Vahl., Populus spp.)
(Keèa et al. 2015). Serbias forest reserves, which cover
approximately 27% of the countrys land area, or about
two million hectares, are estimated to be containing 235
million m3 of the standing inventory (Keèa and Keèa
2015). About 36.000 ha of poplar plantations are located
in Vojvodina (Bankoviã 2009).
The controversy of optimal forest management has
a long history in forestry economics (Chladna 2007).
Determination of the Optimal Financial Rota-
tion Period in Poplar Plantations
LJILJANA KEÈA
Faculty of Forestry, University of Belgrade, Chair of Forestry Economics and Organisation, 1, Kneza Viðeslava
street, 11030 Belgrade, Serbia, Tel. +381641794648 and +381113053959, E-mail: ljiljana.keca@sfb.bg.ac.rs
Keèa, L. 2017. Determination of the Optimal Financial Rotation Period in Poplar Plantations. Baltic Forestry 23(1):
673682.
Abstract
Due to trends in the consumption of wood and particularly soft broadleaves, poplar cultivation has gained importance in
Serbia and worldwide in the field of production, economics and environmental protection issues. The present study was
performed to determine the optimal financial rotation lengths for hybrid poplar plantations (Populus Euramericana Gunier
cv. I-214) in a selected area of Serbia. The aim of this study is to apply the method of assessment and calculation of the optimal
production cycle length in order to determine the optimal production cycle length of poplar plantations in the localities of
Serbia from a financial standpoint. The selected discount rate for the calculation is 6% (close to the maximum recorded
internal rate of yield in the observed compartments). It was concluded that the production cycle length of poplar in the study
area ranges from 12-19 years, depending on the soil type. The longest rotation is obtained for humofluvisol (alluvial
semigley). The estimation based on the NPVs criterion determined a desired optimal production cycle length of about 16 years
Keywords: financial rotation, poplar, plantation, optimum
Many studies applying different methodologies have
been conducted in this area, and most of them are related
to stochastic optimal rotation models (Willassen 1998,
Alvarez and Koskela 2004). Nowadays, a lot of forest
economists believe that the net present value approach
is a true innovation in forest management and economics
science. The fact that a total of 313 papers with this topic
have been published since Faustmann speaks in favour
of its importance. However, over two-thirds of these pa-
pers (211) have come since 1985 (Newman 2002).
In short rotation plantation forestry, high biomass
productivity and economic profitability are given prior-
ity and harvest time usually coincides with the age when
mean annual increment is the highest (Tullus et al. 2012).
Therefore, the economic success of poplar plantations
usually depends on obtaining the largest possible
amount of top grade veneer logs, whose value can com-
pensate the high establishment and management costs
(Spinelli and Magagnotti 2011).
The aim of this research is to apply the method of
assessment and the method of calculating the optimal
production cycle length in order to determine the optimal
production cycle length (Keèa 2014) of poplar planta-
tions in the studied localities from an economic stand-
point.
The purpose of this research is to provide guide-
lines for forestry practices aimed at the improvement of
the situation in the field of assessment of the optimal
production cycle length in poplar plantations.
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
The research objects are: the number of trees, vol-
ume of trees and other elements that will be quantified
and numerically analyzed.
Material and methods
The method of assessment was used in the article to
prove the hypothesis that poplar achieved the best finan-
cial effects of production at the ages between 10 and 20
years. This problem comes down to the choice of the ap-
propriate criterion in financial analysis and the monitoring
of its trend for different lengths of the production cycle,
as well as finding the age when the value of the selected
criteria culminates. This is achieved by using regression
and correlation analysis. If statistical significance of the
regression model of the selected indicators trend is pro-
vided, we find the maximum of curves and determine the
time when the financial success is the highest.
The total net present value (NPV) and the average
net present value (NPVs) of wood production in the
analyzed poplar plantations were selected as the criteria
for the assessment of the financial effects, calculated
according to the method of the present value and the
resultant value and then expressed per unit area. The
basic principle on which the method of the present value
is based is that stand value is equated with the value of
timber of the selected trees (in this case poplar), in the
exact proportion that represented the assortment volume
of categories that at the time of assessment are present
in the market, reduced by the costs of forest utilization:
Vs = (V1·P1+ V2·P2++Vn·Pn) - Cs
where: Vs-value of the stand, V1,2,n - volume of the timber
assortment categories, P1,2,n prices of timber assort-
ment categories, Cscosts of forest utilization.
The investigated sample plots were established from
Populus × euramericana cl. I-214, with a 6 × 3 m (555 trees
per ha) planting spacing for technical wood production,
and they were located in the Northern province of
Vojvodina. Nineteen (19) compartments (52 stands) aged
24-42 years with a total area of 362.35 ha were investi-
gated. Soil types in these plots are: a / b-b gley; alluvial
semigley; fossil hydromorphic black soil on loess-alluvium
and fossil hydromorphic black soil (humosemigley) on
loess-alluvium. The research was carried out in poplar plan-
tations located in the area of the Sava River during the
2002  2014 period. Data pertaining to costs during years
0-5 (soil preparation, planting, care and protection, etc.)
were obtained from the archives of the forest enterprise
which managed the studied plantations, and also the data
from material books (Keèa 2010a). The costs of ground
preparation for afforestation are 2040.50 /ha in the start-
ing year. In the first year, the costs of maintenance and
protection of plants are 209.44 /ha. In the second year,
afforestation with rooted cuttings and maintenance and
protection of the plantation costs are 207.48 /ha. In the
third, fourth and fifth years, the costs of tending (inter-
row treatment and weed control) amount to 305.45 /ha.
The costs in the sixth year are 825.91 /ha, because of the
costs of schematic thinning and cutting, processing and
extraction of timber, and in the final year, the costs amount
to 3397.0 /ha. On the other hand, the revenues range be-
tween 11 088.3  23 676.36 /ha. Since all the studied stands
are state-owned and managed by the Public Forest Enter-
prise Vojvodinaðume, the value (cost) of the land (land
rent) did not enter into the calculations (Keèa et al. 2011).
Estimates were made separately for each soil type,
bearing in mind the possibility that different surfaces can
behave differently and the effects of financial trends ob-
served. The criteria for the assessment of the financial
effects were the selected total net present value (NPV)
and the average net present value (NVPs) of production of
poplar wood in the analyzed plantations, calculated ac-
cording to the method of the present value of felling ripe-
ness, and the resultant value then expressed per unit area.
The chosen discount rate to be used in the calcula-
tion was 6%. This discount rate is very close to the maxi-
mum recorded internal rate of return in the observed
stands, which amounts to 5.56% (Keèa 2010, Tullus et al.
2012). The return on investment from the stands at a cer-
tain age should be equal to the available alternative rate
of return on the capital invested (rather than percentage
changes in costs). Stands or trunks are only in this case
the financial mature (Duerr et al. 1956, Keèa and Keèa
2014). In forestry, the valuation of forests is performed
with the interest rate of capitalization (it is the basis for
the capitalization of rents, discounting and prolonging
of financing rents). Therefore, the basis for determining
interest rates in forestry is the rate of value growth. The
higher increment of a stand, the higher the interest rate
(Figuriã 1996).
The assessment was made separately for each soil
type in three variants. The first variant (M0) is based on
real data on costs and revenues created in the compart-
ments on the same ground, totally focused on them when
calculating total and average net present value of pro-
duction. Bearing in mind that in all cases it has reliable
information at the beginning of the production cycle (es-
tablishment and care of plantations  costs) and its end
(harvest and production assortments revenues and
associated costs).
The following two variants are created as an attempt
to compile an expert assessment of data about possible
values from the central segment of production cycle
length. In that way, the obtained data were incorporated
into the calculation. The assessment starts from the two
typical cases which form two clearly visible contradic-
tions. The second variant (M1) is based on an estimation
that in the period of culmination of the financial effects
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2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
there is no complex assortment structure, but at this age
stacked wood usually dominates in the assortment struc-
ture of the produced volume of poplar wood. It was taken
as an assumption that the entire realized production is of
simple assortment structure and belongs to the category
of cordwood.
The third variant (M2) is based on the assumption
that the assortment structure may still affect movement
of the culminating point of the observed criterion. How-
ever, at this moment there are no data related to complete
final felling at these ages in sample plots, remaining as
an opportunity to assess the income and expenses at
these ages. The estimation of revenues from timber, in
this case, is the most complex part of the assessment,
and is made through the assortment structure obtained,
based on the method of model tailoring of the trunks
(Nikoliã 1988). This method assumes that assortment
structure depends only on the dimensions of trunks and
does not take into account possible errors of the spin-
dles of tree trunks that affect the result of cutting in prac-
tice. Such a developed assortment structure can be con-
sidered ideal, and (theoretically) as a result brings the
highest revenues from the sales of wood.
In this way, there is the opportunity to compare the
results of three assessments (real  lack of data from
the central segment of the length of the production cy-
cle, minimalistic  the actual data associated data, where
income is assessed only on the basis of the least valu-
able assortments and maximalistic the actual data
associated the data were obtained on the basis of a
calculation of income based on the ideal assortment struc-
ture). Such access is provided to summarize the possible
similarities or differences in results and provide a more
precise definition of the age range at which the greatest
financial effects can be expected.
To conduct the calculation of missing data on in-
come in the variant M2, for stands at ages that are miss-
ing, in the field we required compartments to meet the
requirement that they include trees of such ages (rang-
ing between 9-23 years). Such departments are found in
each category of soil, but their number is not the same in
each of them. In the next step, data on the dimensions
(diameter and height) of all trees from each of the se-
lected compartments were collected and processed. The
dimensions of trees in the selected classes were obtained
from the Special plan of forest management of this area.
During data processing, it was noticed that trees in the
researched artificial poplar plantations at the same age
(same compartment) have approximately the same dimen-
sions (height variation coefficient is Ch = 5.23%, and the
thickness of Cd = 4.31%) (Table 1). That means it can be
operated with a single tree of average size (mean tree
as a representative of all trees in the department in which
the trees are of the same age (Bankoviã and Pantiã 2006).
Model tailoring based on the principle of maxi-
mum utilization (Nikoliã 1988) was applied for the selected
trees (Table 2), and a total of 33 trees of different ages
(from 12-28 years) were chosen.
Ta b l e 1 . Coefficients of variations of
dimensions of trees in plantations of
poplar with a 6×6 m planting space;
T  age of plantation, N  number of
stands, Cd  coefficient of variations
in diameter, Ch  coefficient of vari-
ations in height
T N Cd Ch
age % %
15
1 7,5 4,8
2 6,8 5,1
3 6,9 5,2
Average 7,1 5,0
20
1 7,1 4,6
2 7,5 5,3
3 5,2 4,2
Average 6. 6 4,7
25
1 5,8 4,1
2 7,0 4,4
3 6,4 4,7
Average 6, 4 4,4
Tab le 2. Age and number of stands whose derived trees
were used for the purposes of model tailoring
So il T ype Age of the stands Numb er of
stands year
* á / â-â gley 12, 14, 16, 18, 19, 23, 26, 28 8
*RC 13, 14, 1 5, 16, 1 7, 19, 23, 25, 26, 2 7 10
14, 15, 16, 18, 19, 22, 23 7
ASG 9, 1 2, 14 , 15, 16, 18, 23, 24 8
Ó / 33
As a result of the model tailoring, mean trees by
volume assortments were obtained in each selected de-
partment. These mean trees are the next step multi-
plied by the appropriate prices and the number of trees in
each of these departments, in order to obtain the value of
revenues by departments. These are dependent on the
assortment structure, soil type and the age of stands. In
the following calculation, the resulting value of income
is divided by the surface area of each department to ob-
tain the amount of revenue per hectare. So, as input data
for the assessment of income, we used data on the
number and size of trees in the selected departments on
the ground (to obtain the average dimensions of trees
and assess assortment structure), market prices assort-
ments for 2014 (the valid price list PE Vojvodinaðume)
and the area of the observed compartments. The whole-
sale prices of PE Vojvodinaðume (VAT is excluded) for
tree assortments are as follows: for class F, the price is
66.06 /m3, class L 51.75 /m3, class I 38.53 /m3 and class
II 30.28 /m3.
The present value of the income and expenses (with
a discount rate of 6%), total and average net present
value were calculated on the basis of the database, and
finally the time of their culmination was estimated. The
assessment of culmination was done in a way that data
were flat out (even) by a regression curve (cubic parable,
i.e. polynomial of third-degree). After that, we found the
maximum of the given function as the time of culmination
*RC-fossil hydromorphic black soil (humosemigley) on loess-al-
luvium, AS ASGalluvial semigley, LC-fossil hydromorphic black
soil on loess-alluvium, a / b-b gley
a / b-b
S
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2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
of the total and average net present income for the 4
researched types of poplar forests.
Finally, the criteria for the greatest financial impacts
were chosen. In order to compare the financial effects of
the total and average net present values, it is necessary
to reduce them to the same level. Therefore, procedures
are multiplying the average net present value with the
age at which the total net present value (tNPVmax) culmi-
nates. After that, we compared the result obtained in that
way between the results (NPVt) and the total net present
value (NPV), and the selected value that has a higher
validity (Rankoviã 1996). The formula for such a calcula-
tion would have the following form:
a choice when compared would be as follows:
 if the requirement that the NPVt ³ NPV is met, then
further analysis related to the average net present value
(NPVs would be a criterion for observation and analysis);
 if the opposite condition (NPVt £ NPV) is fulfilled,
then total net present value (NPV) is the criterion in rela-
tion to which further observation and analysis are to be
performed.
Results
According to the available data from the field on a /
b-b gley soil type, 8 stands aged 12, 14, 16, 18, 19, 23, 26
and 28 years (Table 3) were researched. They were evalu-
ated in terms of the size of NPV and NVPs presented by the
regression curve trend (cubic parabola) (Figures 1, 2).
tNPV
max
s
NPV NPV t
Tabl e 4. Optimal lenght of production cycle and the highest
value of NPV and NPVs
On the basis of these elements, it can be stated that
the estimation based on criteria NPVs represents the re-
quired optimum length of the production cycle and it is
17 years (Table 4).
y = -0,0066x3 - 1 ,4092x2 + 109,0 6x - 2688 ,7
R2 = 0,798 5
y = 0,1464x3 - 11,248x
2 + 252,7 7x - 1690,9
R2 = 0,860 7
-3000
-2500
-2000
-1500
-1000
-5 00
0
500
010203040
Figure 1. NPV and NPVs in estimation variant M1 (in all
figures NPV is in red, and NPVs is in blue)
y
= -0, 1458x3 + 6,415 8x2 + 26, 626x - 2521
R2 = 0,8733
y
= 0,1415x3 - 1 0,989x2 + 250,5 2x - 1687,4
R2 = 0,8637
-30 00
-25 00
-20 00
-15 00
-10 00
-5 00
0
500
1000
010203040
Figure 2. NPV and NPVs in estimation variant M2
Variant of
estim ation
Time of
culmination Maximum value Verification of
criteri a
NPV NPVs NPVmax
NPVsmax NPVsmax· tNPVmax
(tNPVmax=32)
year ·ha 1
M / / / / /
M 32 7 855, 72,82 2.33,2
M2 32 7 23,26 9,8 2.95,8 7
According to the data available from the field on RC
soil type was researched 10 stands aged 13, 14, 15, 16, 17,
19, 23, 25, 26 and 27 years (Table 5) (Figures 3, 4, 5).
On the basis of these elements, it can be said that
the estimation based on the NPVs criterion represents the
required optimum length of the production cycle, which
is 15 years (Table 6).
According to available data from the field, on LC
soil type was researched 7 stands of the following ages:
14, 15, 16, 18, 19, 22 and 23 years (Table 7) (Figures 6, 7).
Tab le 3 . Values of NPV and NPVs in three variants of esti-
mation
Age
year
Variants of estimation
M0 M1 M
2
NPV NP Vs NP V NPVs NPV NPV s
·ha1
1 2.040,48 2.04 0,4 8 2.040,48 2.040,48 2.040,4 8 2 .040, 48
2 2.238,06 1.11 9,0 3 2.238,06 1.119,03 2.238,0 6 1 .119, 03
3 2.422,72 807 ,57 2.422,72 807 ,57 2.42 2,7 2 807,57
4 2.516,46 629 ,12 2.516,46 629 ,12 2.51 6,4 6 629,12
5 2.593,22 518 ,64 2.593,22 518 ,64 2.59 3,2 2 518,64
6 2.665,63 444 ,27 2.665,63 444 ,27 2.66 5,6 3 444,27
7 2.227,16 318 ,17 2.227,16 318 ,17 2.22 7,1 6 318,17
12 / / 1.270,07 105,84 1. 392,1 5 116,01
14 / / 1.131,06 80,79 1 .133,4 2 8 0,9 6
16 / / 1.129,19 70,57 843,70 52,73
18 / / 1.077,86 59,88 273,23 15,18
19 / / 1.005,04 52,90 427,12 22,48
23 / / 1.117,19 48,57 784,25 34,10
26 / / 1.039,30 39,97 597,52 22,98
28 / / 1.144,09 40,86 326,94 11,68
43 1060,86 24,67 1.060,86 24,67 1.060,8 6 2 4,67
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2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
Age
year
Variants of es timat ion
M0 M1 M2
NPV NP Vs NPV NPV s NPV NPVs
·ha1
1 2040, 48 2040, 48 2040, 48 2040, 48 2040, 48 20 40,48
2 2238, 06 1119, 03 22 38,06 1119, 03 2238, 06 11 19,03
3 2422, 72 80 7,57 24 22,72 80 7,5 7 2422, 72 807,57
4 2516, 46 62 9,12 25 16,46 62 9,1 2 2516, 46 629,12
5 2593, 22 51 8,64 25 93,22 51 8,6 4 2593, 22 518,64
6 2665, 63 44 4,27 26 65,63 44 4,2 7 2665, 63 444,27
7 2227, 16 31 8,17 22 27,16 31 8,1 7 2227, 16 318,17
13 / /  1141,62  87,82 13 19,09 10 1,4 7
14 / /  1141,99  81,57 608,6 0 43 ,47
15 / /  1119,72  74,65 10 83,78 72 ,25
16 / / 90 3,1 9 56,45 10 29,56 64 ,35
17 / / 80 5,4 1 52,65 144, 58 8,50
19 / / 89 5,0 3 61,04 43 ,41 2,28
23 / /  1159,81  50,43 396,3 8 17 ,23
25 / /  1237,94  49,52 107,3 5 4, 29
26 / /  1205,75  46,38 443,7 9 17 ,07
27 / /  1158,08  42,89 569,7 0 21 ,10
29 27 5,6 0 9, 50 275,60 9,50 27 5,60 9,50
30 38,2 4 1, 27 38,24 1,27 38 ,24 1,27
32 31 5,8 9 9, 87 315,8 9 9,87 31 5,89 9,87
Tab le 5 . Values of NPV and NPVs in three variants of esti-
mation
y = -0, 4145x3 + 21,504x
2 - 212,72x - 1920,7
R2 = 0,9833
y = 0,3185 x3 - 20,686x2 + 401,73x - 2066,1
R2 = 0,9175
-3000
-2500
-2000
-1500
-1000
-500
0
500
0 5 10 15 20 25 30 35
Figure 3. NPV and NPVs in estimation variant M0
y = 0,058 5x3 - 3,9599x2 + 141,85 x - 2759,7
R2 = 0,7815
y = 0,2875 x
3 - 17,176x2 + 317,5 x - 1836
R2 = 0,9013
-3000
-2500
-2000
-1500
-1000
-500
0
500
1000
0 10203040
Figure 4. NPV and NPVsin estimation variant M1
y = -0,3082x3 + 12,069x2 - 12 ,088x - 2462,1
R2 = 0,8711
y = 0,2716x 3 - 1 6,519x2 + 312x - 1826,7
R2 = 0,9021
-3000
-2500
-2000
-1500
-1000
-500
0
500
0 5 10 15 20 25 30 35
Figure 5. NPV and NPVs in estimation variant M2
Tab le 6. Optimal lenght of production cycle
and the highest value of NPV and NPVs
Varian t of
estimation
Time of
culm inat ion Max imum value Verifi cation
of criter ia
NPV NPVs NPVma x NPV
year ·ha1
M0 28 15 116,83 380,44 10.652,32
M1 / 15 / 32,21 /
M2 26 15 34,67 53,18 1.382,55
Ages
year
Variants of estimation
M0 M1 M2
NPV NPVs NPV NPVs NP V NP Vs
·ha1
1 2.040,48 2.040,48 2.040,48 2.040,48 2.040,48 2.040,48
2 2.2 38,06 1.119,03 2.238,06 1.1 19 ,03 2.2 38, 06 1.119,03
3 2.422 ,72 807,57 2.422 ,72 8 07,57 2 .422,72 807,57
4 2.516 ,46 629,12 2 .5 16,46 6 29 ,12 2 .516 ,46 629,12
5 2.593 ,22 518,64 2.593,22 518,6 4 2.5 93,22 518,64
6 2.665 ,63 444,27 2.665,63 444,2 7 2 .665 ,63 444,27
7 2.227 ,16 318,17 2.227,16 318,1 7 2 .227 ,16 318,17
14 / / 1.358 ,64 97,05 1.168 ,11 8 3, 44
15 / / 1.259 ,21 83,95 8 11,7 1 5 4,11
16 / / 1.217 ,31 76,08 823 ,81 5 1, 49
18 / / 1.186 ,83 65,94 6 21,6 5 3 4,54
19 / / 1.114 ,57 58,66 804,19 42,33
22 / / 1.175 ,63 53,44 341,51 15,52
23 / / 1.199 ,77 52,16 339,48 14,76
25 237,3 5 9,49 237,35 9 ,49 2 37 ,35 9,49
Ta b l e 7 . Values of NPV and NPVs in three variants of esti-
mation
y = -0, 4224x3 + 1 8,2 99x2 - 138,56x - 2115
R2 = 0,8734
y = 0,62 95x3 - 30,339x2 + 4 53,32x - 2121,3
R2 = 0,9357
-3 00 0
-2 50 0
-2 00 0
-1 50 0
-1 00 0
-500
0
500
1000
0 10203040
Figure 6. NPV and NPVs in estimation variant M1
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677
2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
On the basis of these elements, it can be said that
the estimation based on the NPVs criterion represents the
required optimum length of the production cycle, which
is 12 years (Table 8).
According to the data available from the field 8 stand
at the AS ASG soil type of the ages: 9, 12, 14, 15, 16, 18, 23
and 24 years (Table 9), which were evaluated in NPV and
NVPs (Figures 8, 9, 10).
Table 8. Optimal lenght of production cycle and
the highest value of NPV and NPVs
y = -1, 2307x3 + 50,073x2 - 421,3x - 1587,4
R2 = 0,9482
y = 0,5867x3 - 28,713x2 + 439,51x - 2096,3
R2 = 0,9322
-3000
-2500
-2000
-1500
-1000
-500
0
500
1000
0 10203040
Figure 7. NPV and NPVs in estimation variant M2
Vari ant of
estimation
Time of
culm ination Maximum value Verific ation
of criteria
NPV NPVs NPVmax NPV
year ·ha1
M
0 / / / / /
M
1 25 12 742,13 3 7 , 5 0 937,50
M
2 22 12 274,8 4 56,97 1.253,34
Age
year
Variants of estimation
M0 M1 M2
NPV NP Vs NPV NPV s NPV NP Vs
·ha1
1 2.040,48 2.040,48 2.040,48 2.040,48 2.040,48 2.040,48
2 2.227,48 1.113,74 2 .23 8,06 1.11 9,03 2 .238, 06 1.119, 03
3 2.392,88 797,63 2.42 2, 72 807,57 2.42 2, 72 8 07,57
4 2.472,35 618,09 2.516,46 629,12 2.516,46 6 29 ,12
5 2.533,93 506,79 2.59 3, 22 518,64 2.593,22 518,64
6 2.588,92 431,49 2.665,63 444,27 2.66 5, 63 4 44 ,27
7 2.273,80 324,83 2.22 7, 16 318,17 2.22 7,16 3 18,17
9 / / 856,69 95,19 1.881,25 209,03
12 / / 859,78 71,65 1.64 6,98 137,25
14 / / 943,98 67,43 1.444, 57 103,18
15 / / 854,08 56,9 4 800 ,30 53,35
16 / / 833,39 52,09 411,19 25,70
18 / / 899,12 49,9 5 447,41 24,86
23 / / 1.011,41 43,97 527,92 22,95
24 / / 1.021,35 42,56 514,06 21,42
25 1.743,02 69,7 2 237,35 9,49 237,35 9,49
27 1.609,37 5 9,6 1 553,64 20,51 553,64 20,51
29 1.725,41 59, 50 335,17 11,56 335,17 11,56
30 1.896,30 6 3,2 1 363,49 12,12 363,49 12,12
38 1.999,57 5 2,6 2 124 ,02 3,26 124,02 3,26
43 2.161,99 50,28 1.097,84 25,53 1.097,84 25,53
Tab le 9 . Values of NPV and NPVs in three variants of esti-
mation
y = -0, 1078x3 + 6,5503x2 - 85,523x - 2130
R2 = 0,816
y = 0,1938x3 - 15,119x2 + 338,15x - 1913,6
R2 = 0,8898
-3000
-2500
-2000
-1500
-1000
-500
0
500
1000
-5 5 15253545
y = -0,0875x3 + 2,7829x2 + 79,488x - 2579,7
R2 = 0,7928
y = 0,1242x3 - 9,8204x2 + 233,07x - 1631,7
R2 = 0,8565
-3000
-2500
-2000
-1500
-1000
-500
0
500
1000
-5 5 15253545
y = -0,1758x3 + 7,3024x2 + 42,339x - 2621,7
R2 = 0, 8763
y = 0,117x3 - 9 ,399 1x 2 + 227,71x - 1627,8
R2 = 0,8666
-3000
-2500
-2000
-1500
-1000
-500
0
500
1000
0 1020304050
Figure 8. NPV and NPVs in estimation variant M0
Figure 9. NPV and NPVs in estimation variant M1
Figure 10. NPV and NPVs in estimation variant M2
ISSN 2029-9230
678
2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
On the basis of these elements, it can be said that
the estimation based on the NPVs criterion represents the
required optimum length of the production cycle ranging
from 16 to 19 years (Table 10).
According to the available data from the field, 19
compartments of different ages (1-7, 25, 27, 29, 30, 32, 38
and 43) were available on all soil types together, and they
were evaluated in the size of NPV and NVPs. If we analyze
the results of NVPs for the researched soil types (Table
11) and evaluation methods, it can be concluded that the
average value for all types of soil is 16 years. This sug-
gests that the estimated optimal length of the production
cycle is not dependent on the method of estimation. The
culminating point of NPVs is regularly the same, and does
not depend on whether the whole harvested volume is
treated as stacked wood (minimalistic variant) or used as
assortment structure obtained by model tailoring
(maximalistic variant). In other words, according to these
findings, and used methods of evaluation of the revenues
from timber, the time of NPVs (optimal length of the pro-
duction cycle) culmination is not sensitive to the assort-
ment structure between the ages of 10 and 20, although it
was found exactly at this segment of age (Figure 11).
Table 10. Optimal lenght of production cycle and
the highest value of NPV and NPVs
Variant of
estimation
Tim e of
culmination Max imum val u e Ve rifi cation
of criteria
NPV NPVs NPVmax NPV
year ·ha1
M0 32 16 1.692,62 420,14 13.444,48
M1 31 18 47,92 106,10 3.289,10
M2 30 19 474,03 108,18 3.245,40
Soil type
Variant of estim ation
M2 M0 M1
NPVs R
2 NPVs R
2 NPVs R
2
* á / â-â gley 17 0,87 / / 17 0,80
*RC 15 0, 90 15 0,92 15 0,90
12 0, 93 / / 12 0,94
ASG 19 0, 87 16 0,89 18 0,86
Average 16 / 16 / 16 /
sis can be used for project design, the selection of ap-
propriate size of the project, optimization of the timing of
activities and determination of the strategy of forest man-
agement. However, in addition to financial parameters,
decision-making on plantation establishment must take
other parameters into account, such as the interests of
local communities, government policy and environmen-
tal protection (Neumayer 2011, Perez 2004). Forests are
among the most valuable natural resources that human-
ity possesses, but it is difficult to make economic quan-
tification of their values. There are benefits of forests,
especially plantations, which cannot be quantified finan-
cially, such as their aesthetic, habitat, protective and anti-
erosion functions.
And finally, if a forest ecosystem has to fulfil all the
requirements it is facing (especially environmental pro-
tection, reduction of CO2 in the atmosphere (Holopainen
2008) and mitigation of the greenhouse effect), it is nec-
essary to establish the sustainability of their manage-
ment. According to some authors, for sustainable man-
agement it is necessary to size the plantations be at least
several hundred hectares (Rose et al. 1981, Medareviã
2006, Allen et al. 2008).
The optimal length of the production cycle in poplar
plantations may be treated as short, compared to the pro-
duction cycle of other economically important species
such as beech, spruce, oak and others. The duration of a
short rotation can be divided into three categories (Pope
Table 12. Optimal lenght of production cycle and the high-
est value of NPV and NPVs
Tab le 11 . The estimated optimal length of
the production cycle to NPVs and coeffi-
cients of the regression of model
a / b-b
On the basis of these elements, it can be stated that
the estimation based on the NPVs criterion represents the
required optimum length of the production cycle, which
is 16 years (Table 12).
Discussion
Financial analysis is an objective means by which
cost-intensive plantations can be compared to cultivat-
ing crops (e.g. agriculture) (Mitchell et al. 1999, Current
et al. 1995, Sharma 1996, Sabadi 1986, 1997). This analy-
y = -0, 2328x3 + 13,154x2 - 111,05x - 2161,4
R2 = 0,9408
y = 0,1745x3 - 14,025x2 + 325,41x - 1890, 8
R2 = 0,908
-3000
-2500
-2000
-1500
-1000
-500
0
500
010203040
Figure 11. NPV and NPVs in estimation variant Mo
Variant of
estimation
Tim e of
culmination
Maximu m
value
Verification
of c rite ria
Variant of
estimation
Tim e of
culmination
NPV NPVs
M0
32 16 132,52 445,26 14.693,58
M1 / / / / /
M2 / / / / /
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2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
and Dawson, 2005): (I) 5-10 years - of intense culture for
obtaining biomass; (II) 10-20 years - for receiving pulp-
wood (for paper, wood chips for the production of pan-
els, firewood, pallets, certain chemicals such as ethylene
glycol, and alcohols); (III) 20-40 years  for obtaining
technical wood (for construction, peeled veneer, produc-
tion of furniture). The largest poplar plantation areas are
intended for the production of veneer, peeling and cutting
logs, all of which (about 350,000 m3 round wood year-1) is
processed in Serbia and used in the production of pack-
aging, veneer, pallets, various types of board, furniture,
and other articles (Keèa et al. 2012). Short rotations (5-10
years) and the long ones (15 years) are different, both in
terms of cost-efficiency, and energy efficiency. Short ro-
tation plantations generate income earlier and more of-
ten. Due to shorter rotations, the risk of loss has not yet
been so great, and the occurrence of damages was not so
often. They allow the use of all technological advances
and frequent introduction of newly selected hybrids in
plantations (Rose et al. 1981). There are several factors
that significantly affect the length of production cycle,
but the most important are: the choice of the planting
site, planting density, the costs of establishing planta-
tions and the wood market conditions (Birler 1984).
The values obtained for the optimal length of the
production cycle ranged in the interval from 16 to 19 years.
The longest rotations in poplar plantations were obtained
for alluvial semigley. This is the most suitable soil of all
studied soils for the cultivation of poplar (Keèa and Keèa
2012), in addition to fluvisol and therefore the return that
is achieved can bear financial burden with an interest
rate of 6% (Keèa et al. 2011). A shorter length of rotation
was obtained on the black soil type. Similar results were
obtained by Kohn J.P. (1994), except that in hybrid pop-
lars with a 6 × 6 m planting space and different soil types
this interval ranges from 11 to 17 years (Chapman and
Meyer, 1947, Tahvonen and Seppo 1999). Researches
conducted in Turkey estimated the length of financial
rotation to 11 years (Engindeniz 2003). In the United
States, there is legislation (Forest Practice Act of 2008)
which exactly prescribes the production cycle length in
12-20 years old poplar plantations, depending on their
purpose. In Canada, van Kooten (1999) stated that the
optimal production cycle length for poplar ranged from 9
to 12 years.
It should be emphasized that the length of the eco-
nomic and financial rotation, generally do not overlap
(Anderson and Luckert 2006). The reason for this situa-
tion can be explained by the fact that the financial rota-
tion usually varies depending on the price of poplar wood
and interest rates (rate of interest), while the economic
changes if there is a change in the productivity of land
and habitat productivity (Kohn 1997).
Conclusions
The length of the production cycle for poplar in the
project area ranges from 10-20 years. The values obtained
for the length of financial rotation are in the range be-
tween 12 and19 years. The longest rotations were ob-
tained for alluvial semigley and they ranged between 16
and 19 years, depending on the applied methods. The
estimation based on the NPVs criterion represents the
required optimum length of the production cycle, which
is about 16 years for poplar plantations in Serbia. How-
ever, it has been noted that the better soil for growing
poplar (e.g. alluvial semigley) suffers a longer produc-
tion cycle (19 years) in the case of NPVs. According to
the optimal length of the production cycle for Euro-
American poplars, it is recommended to use the culmina-
tion of the average net present value. The statistical
analysis shows that the obtained results for the two re-
gression curves are characterized by high values of the
coefficient of determination and the parameters are the
most significant at the 0.05 level of significance, while
the parameters in NPVs in all variants are statistically sig-
nificant, so that the observations and reasoning based
on these regression models can be accepted as reliable.
The level of statistical significance is high (R2³0,91),
and the correlation coefficient is precisely calculated
(F=42.75).
In the future, private forest owners can be advised
to invest in such a production of poplar wood. On the
other hand, there is a state interest in poplar plantations.
Plantations are very efficient in CO2 consumption, as
shelterbelts, as well as in flood control, etc. Therefore, in
the future the state can stimulate forest owners to invest
in poplar production on river banks and on more quality
soil types, which tends to be more profitable.
Acknowledgement
Gratitude for the implementation of this research
authors suggest the Ministry of Education and Science
of the Republic of Serbia, which financially supported
this research within the project Sustainable manage-
ment of total resources of forests in the Republic of Ser-
bia  EVNo. 37008, and Forest plantations in order
to increase afforestation in Serbia EVNo. 31041 COST
Action FP1403 NON-NATIVE TREE SPECIES FOR EU-
ROPEAN FORESTS: EXPERIENCES, RISKS AND OP-
PORTUNITIES (NNEXT)".
References
Allen, D., Fraleigh, S., McKenney, D. and Yemshanov, D.
2008. An Assessment of Short Rotation Coppice Woody
Biomass to Heat Greenhouse in Southern Ontario, Cana-
dian Forest Service (4).
ISSN 2029-9230
680
2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
Alvarez, L.H.R. and Koskela, E. 2004. Optimal Harvesting
Under Resource Stock and Price Uncertainty. Discussion
Paper, vol. 31. Helsinki Centre of Economic Research.
Available at: http:// ethesis.helsinki.fi/julkaisut/eri/hecer/
disc/31.
Anderson, J.A. and Luckert, M.K. 2006. Can hybrid poplar
save industrial forestry in Canadas boreal forest?: A fi-
nancial analysis and policy considerations, Western For-
est Economist Meeting, Oregon, unpublished material
(36).
Bankoviã, S., Pantiã, D. 2006. Dendrometrija, Beograd, Ðu-
marski fakultet (556)
Bankoviã, S., Medareviã, M., Pantiã, D., Petroviã, N.,
Ðljukiã, B. and Obradoviã, S. 2009. The growing stock
of the Republic of Serbia - State and problems. Bulletin
of the Faculty of Forestry 100: 7-30 (in Serbian with
English summary).
Birler, A.S. 1984. The profitability of poplar growing sys-
tems in Turkey, 17th Session of International Poplar
Commission, Ottawa, Canada (http://www.fao.org/forest-
ry).
Chapman, H.H. and Meyer, W.H. 1947. Forest Valuation,
McGraw-Hill Book Company, Inc., USA (521).
Chladná, Z. 2007. Determination of optimal rotation period
under stochastic wood and carbon prices, Forest Policy
and Economics 9.8: 1031-1045.
Current, D., Lutz, E. and Scherr, S. 1995. Costs, Benefits,
and Farmer Adoption of Agroforestry, The World Bank,
Washington, USA, DC 20433 (15).
Duerr, W.A., Fedkiw, J. and Guttenberg, S. 1956. Finan-
cial maturity: a guide to profitable timber growing, U.S.
Dept. of Agriculture, p. 74.
Engindeniz, S. 2003. Determination of Economic and Finan-
cial Rotation Lengths of Hybrid Poplar Plantations: the
Case of Turkey, Pakistan Journal of Biological Sciences
6 (4): 325-330.
Figuriã, M. 1996. Uvod u ekonomiku ðumskih resursa, Sveuèi-
liðte u Zagrebu, Ðumarski fakultet, Zagreb (247).
Hongyuan, X. 1992. The culture history and breeding strate-
gy of poplar in Italy. Journal of Forestry Research, 3(2):
95-100.
Holopainen, J. 2008. Financing Sustainable Forest Manage-
ment, Tropenbos International, Wageningen, The Neth-
erlans (176).
Keèa, Lj. 2014. Determination of the optimal production
cycle length from the financial aspect in poplar planta-
tions on meadow semigley, Bulletin of the Faculty of
Forestry 110: 87-104. DOI: 10.2298/GSF1410087K.
Keèa, Lj. and Keèa, N. 2012. Commercial Profitability of
Poplar Plantation with Reference to the Damages Caused
by Fungi, SEEFOR, South-East European Forestry, In-
ternational Scientific Journal in field of forestry, 3(1): 23-
31.
Keèa, Lj. and Keèa, N. 2015. Market potential dynamics for
plantation-grown poplar forest products in Serbia. In:
Ivetic V., Stankovic D. (eds.) Proceedings: International
conference Reforestation Challenges. 03-06 June 2015,
Belgrade, Serbia. Reforesta. pp. 33-41.
Keèa, Lj., Keèa, N. and Pajiã, S. 2011. Investment Appraisal
of Poplar Plantations in Serbia, Baltic Forestry 17(2):
268-279.
Keèa, Lj., Keèa, N. and Pantiã, D. 2012. Net Present Value
and Internal Rate of Return as Indicators for Assessment
of Cost-efficiency of Poplar Plantations: a Serbian case
study, International Forestry Review 14(2): 145-157.
Keèa, Lj. and Pajiã, S. 2010. Financial Aspects of Restora-
tion in Poplar Plantations with Technology of Full Ground
and Soil Preparation, Global Change, challenges for Soil
Management, Advances in Geoecology No. 41. Editor:
Miodrag Zlatiã, Catena Verlag GMBH, (321-334)
Keèa, Lj. and Pajiã, S. 2015. Costs and revenues in poplar
plantations established using full ground and soil prepa-
ration in Serbia. In: Ivetic V., Stankovic D. (eds.) Pro-
ceedings: International conference Reforestation Chal-
lenges. 03-06 June 2015, Belgrade, Serbia. Reforesta: p.
234-241.
Keèa, N., Milenkoviã, I. and Keèa, Lj. 2015. Mycological
complex of poplars in Serbia, Journal of Forest Science,
61(4): 169174. doi: 10.17221/13/2014-JFS
Keèa, Lj. 2010. Assessment of cost-efficiency for wood pro-
duction in poplar plantations in Ravan Srem, based on
internal rate of return. Bulletin of the Faculty of Forest-
ry 102: 25-40.
Keèa, Lj. 2010a. Estimation of cost-effectiveness of poplar
wood production in Ravni Srem by applying the net
present value method. Bulletin of the Faculty of Forestry
101: 81-100.
Keèa, Lj. 2011. Estimation of cost-effectiveness of poplar
wood production in poplar plantations in Ravni Srem based
on the method of pay back period. Bulletin of the Facul-
ty of Forestry 103: 41-56.
Keèa, Lj. and Keèa, N. 2014. Investment Appraisal in pop-
lar Plantations in Serbia and its Relations with Sustaina-
ble Land Management, in Challenges: Sustainable Land
Management Climate Change, Advances in Geoecolo-
gy No. 43. Editors: Miodrag Zlatiã and Stanimir Kostadi-
nov, Catena Verlag GMBH, (287-297).
Kohn, J.P. 1997. The Ergonomic Casebook, CRC Press (240).
Medareviã, M. 2006. Planiranje gazdovanja ðumama, Ðumar-
ski fakultet u Beogradu [Forest management planning,
Forest Faculty in Belgrade]: 149-151 (In Serbian).
Mitchell, C.P., Stevens, E.A. and Watters, M.P. 1999.
Short-rotation forestry-operations, productivity and costs
based on experience gained in the UK, Forest Ecology
and Management 121: 123-136.
Neumayer, E. 2001. Greening trade and investment: environ-
mental protection without protectionism. Earthscan
(228).
Newman, D. H. 2002. Forestrys golden rule and the devel-
opment of the optimal forest rotation literature. Jour-
nal of Forest Economics 8(1): 5-27.
Nikoliã, S. 1988: Sortimentna struktura, Ðumarstvo, Èasopis
za ðumarstvo, preradu drveta, pejzaþnu arhitekturu i vo-
doprivredu erozionih podruèja 2(3): 19-26.
Perez, O. 2004. Ecological sensitivity and global legal plu-
ralism: rethinking the trade and environment conflict. Vol.
3. Hart Publishing.
Pope, P.E. and Dawson, J.O. 2005. Short-Rotation Planta-
tions, Central Hardwood Notes, North Central Forest
Experiment Station 5.09., Department of Forestry and
Natural Resources, Purdue University, West Lafayette,
Indiana (6).
Rankoviã, N. 1996. Ekonomika ðumarstva, Ðumarski fakultet
Univerziteta u Beogradu (362).
Rose, D., Ferguson, K., Lothner, D.C. and Zavitkovski, J.
1981. An economic and energy analysis of poplar intensive
cultures in the Lake States, North Central Forest Experi-
ment Station Forest Service, U.S. Department of Agricul-
ture, USDA Forest Service, Research paper NC-196 (44).
Sabadi, R. 1986. Ekonomika ðumarstva [Forestry econom-
ics]. Liber, Zagreb, 279 pp. (in Serbian).
Sabadi, R. 1997. Vrednovanje ðuma u njihovoj ukupnosti [Eval-
uation of forests in their totality]. Hrvatske ðume
[Croatian forests], Zagreb, 40 pp. (in Croatian).
ISSN 2029-9230
681
2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
Sharma, K.K. 1996. Agroforestry in farming system devel-
opment, Indian Forester 122(7), Agroforestry Systems 13:
235-257.
Spinelli, R., and Magagnotti, N. 2011. Strategies for the
processing of tree tops from hybrid poplar plantations.
Baltic Forestry, 17(1): 50-57.
Tahvonen, O. and Seppo, S. 1999. Optimal Forest Rotation
within Situ Preferences. Journal of Environmental Eco-
nomics and Management 37(1): 106-128.
Tullus, A., Lukason, O., Vares, A., Padari, A., Lutter, R.,
Tullus, T., Karoles, K. and Tullus, H. 2012. Econom-
ics of hybrid aspen (Populus tremula L.× P. tremuloides
Michx.) and silver birch (Betula pendula Roth.) planta-
tions on abandoned agricultural lands in Estonia. Baltic
Forestry, 18(2): 288-298.
van Kooten, G.C. 1999. Economic Dynamics of Tree Plant-
ing for Carbon Uptake on Marginal Agricultural Lands,
Working Paper 1999-18, For Internal Circulation Only
Sustainable Forest Management Network. University of
Alberta Edmonton, Alberta (19),
Willassen, Y., 1998. The stochastic rotation problem: a gen-
eralization of Faustmanns formula to stochastic forest
growth. Journal of Economic Dynamics and Control 22
(573596).
Received 23 October 2015
Accepted 24 February 2017
ISSN 2029-9230
682
2017, Vol. 23, No. 3 (46)
L. KEÈA
BALTIC FORESTRY
DETERMINATION OF THE OPTIMAL FINANCIAL ROTATION PERIOD IN POPLAR PLANTATIONS
... The short cutting age, the uniformity of the obtained wood grades, the ability to create and maintain an efficient transport infrastructure due to the fast payback -all this reduces the costs of wood production plantation and increases the efficiency of management [12]. At the same time, the priority for the forest business in plantation cultivation is not technical, but economic indicators [13]. For example, conventional poplar growing in Serbia is characterized by high costs of plantation establishment, as it is common to use the technology of full ground and soil preparation with a lot of working operations [14]. ...
... Structure of revenues in major felling in sample plots[13]. ...
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The article presents the economic aspects of growing poplar on plantations in Russia and Serbia. For Russia, the cultivation of poplar on forest plantations with a short turnaround is a promising activity which enables to get NPV 7 202 €/ha, taking into account the risks of forest plantations. In the creation of plantation crops the fundamental role is played by their density. To get timber the density of plantation should be from 3.0 to 5.0 thousand plants per 1 ha. Plantations with a 20-year rotation and planting density of 3.0 thousand plants per 1 ha are the most profitable and less risky ones. Similar results have been obtained on poplar plantations in Serbia. NPV revenues are in a range 11 088 to 13 676 €/ha when growing poplar plantations in Serbia. It is advisable to get not only industrial wood chips, but also wood assortment during the cultivation of poplar plantations with 20-year rotation in the conditions of Serbia. Positive financial effect can be reached in future by lowering the costs of poplar plantations establishing. Costs can be also reduced by finding out the solution in the field of soil preparation for afforestation, working operations which will show the higher level of economic efficient.
... ‫هززذٗشٗت‬ ‫التلززبد‬ ٕ ‫خٌگل‬ ‫ّب‬ ٕ ‫دػت‬ ‫وبؿت‬ ‫ّوزٔ‬ ‫فؼبل‬ ‫٘ز‬ ‫ت‬ ‫ّزب‬ ٕ ‫هزذٗشٗتٖ‬ ‫(هبًٌززذ‬ ‫ثشداؿززت‬ ٍ ‫داؿززت‬ ‫وبؿززت،‬ ‫وبؿززت‬ ‫ؿززخن،‬ ، ‫وٌتزشل‬ ‫آث٘زبسٕ،‬ ‫وَددّٖ،‬ ‫ػلزف‬ ‫ّزشص،‬ ‫تٌزه‬ ‫ػزبص‬ ٕ ٍ ‫ثش‬ ‫دس‬ ‫سا‬ ‫ثشداؿت)‬ ‫ه‬ ٖ ‫گ‬ ٘ ‫شد‬ ‫ثب‬ . ‫ا‬ ٗ ‫ي‬ ‫حبل‬ ، ‫صٗزبدٕ‬ ‫ؿوبس‬ ‫اص‬ ‫پظٍّؾ‬ ‫ّب‬ ٕ ‫داخلٖ‬ ٍ ‫خبسخ‬ ٖ ‫تٌْزب‬ ‫تؼ٘ز٘ي‬ ‫ثزِ‬ ‫فبكزلٔ‬ ‫وبؿت‬ ‫ٗب‬ ‫ػي‬ 1 ‫التلبدٕ‬ ‫كزٌَثش‬ ‫ثشداؿت‬ ‫پشداختزِ‬ ‫اًزذ‬( Olson & Lundgren, 1978;Engindeniz, 2003;Keča et al., 2012;Mohammadi Limaei et al., 2013;Adeli et al., 2016;Keča, 2017 ) ‫اػت‬ ‫ٍاثؼتِ‬ ٍ ‫فبكزلٔ‬ ‫وبؿت‬ ‫ًزَع‬ ‫اص‬ ‫تبثؼٖ‬ ‫ً٘ض‬ 1 ‫هحلزَل‬ 2 ‫ٗزب‬ ‫هحلزَل‬ ‫ّزب‬ ٕ ‫ّززذف‬ 3 ‫اػززت‬ (Amateis & Burkhart, 2012) ‫اص‬ . ‫ا‬ ٗ ‫ي‬ ‫سٍ‬ ، ‫ثْ‬ ٘ ٌِ ‫ػبص‬ ٕ ‫وبؿت‬ ‫فبكلٔ‬ ‫دٗگزش‬ ٍ ‫ثشداؿت‬ ‫ػي‬ ، ‫فؼبل‬ ٘ ‫ت‬ ‫ّب‬ ٕ ‫(هبًٌذ‬ ‫هذٗشٗتٖ‬ ‫وَددّ‬ ٖ ‫ثبٗذ‬ ‫تَدُ‬ ) ‫ثزشإ‬ ٍ ‫زخق‬ ‫هـز‬ ‫هحلزَل‬ ‫زذ‬ ‫چٌز‬ ‫ٗزب‬ ‫زه‬ ‫ٗز‬ ‫تَل٘زذ‬ ‫ثزِ‬ ‫زَست‬ ‫كز‬ ‫ّوضهبى‬ ‫كزَست‬ ‫پزز‬ ٗ ‫شد‬ ( Chang, 1983;Amateis & Burkhart, 2012;Halbritter & Deegen, 2015 .) ...
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This research aimed at determining the economic planting interval, planting pattern, and rotation age for high-yield black poplar in the West Azerbaijan Province, Iran. For this purpose, a decision support system called the bio-economic model was employed. The model simulates the dynamics of the stand’s bio-economic variables over time. The statistical population consists of poplar farmers and timber merchants in Orumiyeh and Naghadeh counties where black poplar plantations were highly concentrated. Biological data were collected using full calipering inventory (diameter) and systematic random sampling (height and wet wood density). The economic data (stumpage price and costs) were obtained through a field survey based on a semi-structured interview. Multiple regression analysis and OLS estimators were used to estimate the biological (e.g., growth and yield) and economic (e.g., planting cost) sub-models. By integrating sub-models within an Excel spreadsheet, a bio-economic the model was constructed for black poplar plantations. Finally, land expectation value (Faustmann formula) was simulated over a wide range of planting intervals, planting patterns, and rotation age. As a result, the economic planting interval/pattern and rotation age of average-fertility plantations appeared to be square, 2.52.5 meters and 12 years while the common standards are rectangular, 31 meter and 8 years, respectively. The results revealed that implementing economically optimal planting and harvest standards increase the per-hectare merchantable volume production, quadratic mean diameter, and land expectation value by 56, 46, and 143 percent, respectively. Further research will be required to model and optimize the growth response of poplar plantations to management activities (e.g., ploughing, fertilization, irrigation, vegetation control, and thinning).
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D ue t o t he t rends i n t he c onsumption o f w ood a nd p articularly s oft broadleaves, poplar cultivation gained importance in this country and worldwide during the last decade of the twentieth century. Many countries, primarily those with developed forestry (Canada, France, Italy, etc.), have recognized the importance of poplar cultivation in terms of production, economics and environmental protection. The aim of this study is to apply the method of assessment and the method of calculating the optimal production cycle length in order to determine the optimal production cycle length of poplar plantations in the studied localities of Ravni Srem (FE “Sremska Mitrovica”) from an economic standpoint. The purpose of this research is to provide guidelines for forestry practices aimed at the improvement of the situation in the field of assessment of the optimal production cycle length in poplar plantations. The research object a re: the number of trees, volume of trees and other elements that will be quantified and numerically analyzed. The initial hypothesis of the study was that the production cycle length of poplar in the study area ranges from 10-20 years, depending on the soil type. The production cycle length of poplar in the study area ranges from 15-19 years. It was calculated using three methods: Мо, М1 and М2. The assessment based on the NPVs criterion determined a desired optimal production cycle length of about 16 years on meadow semigley. When the optimum production cycle length of Euro-American poplar is concerned, it is appropriate for the analyses to use the maximization of the average net present value.
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Poplar plantations are a category of fixed assets in forestry, i.e. the assets with a biological character. They are related to their site, they are cultivated for a relatively long time and they have a relatively long utilisation cycle, with the yield development determined by the plantation growth and age. Plantations transfer their value gradually to the obtained products during the period of their harvesting, and, by the realisation of the products, the means invested in the plantation establishment are reproduced. The period of investments in poplar growing can be relatively long, and so is the period of harvesting. Therefore, it is important to determine the time of the return of the capital invested in these and similar plantations. This paper presents the analysis of commercial profitability of poplar cultivation according to the indicator for the assessment of projects in agriculture and forestry - pay back period. The application of pay back period (PBP) calculation can affect greatly the reliability of predicting the degree of economic effectiveness of investments, and also the potential risks for the investor in his decisions on the investments in poplar cultivation. The analysis of poplar clone I-214 plantations was carried out in the area of Ravni Srem, under different rotations and soil types. Based on the analysis of costs and receipts in different plantation ages, and using the method of pay back period, the objective of the study was to evaluate the possible pay back period of invested capital in wood production in poplar plantations. PBP is practically inacceptable by the investor under the discount rate of 6%. The most favourable situation is in the youngest stands, using the discount rate of 2%. The situation regarding the pay back period in the over-aged stands is utterly unfavourable, so the credit cannot be repaid under any conditions. This fact supports the idea that the production cycle length should be shortened.
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In conditions of increasing wood consumption and demand in the world, the aim of the majority of national economies is to intensify local resource production. Due to the fact that poplar rotation is one of the shortest in forestry, and as production of poplar wood requires rational and well-planned management, the potentials of sites and species must be maximally utilised. Favourable financial effects of such a production should be realized. The commercial profitability of poplar cultivation was analysed in an artificial poplar plantation in Serbia. The aim of the study was to validate the invested financial means in artificial poplar plantations, based on the analysis of costs and receipts in different rotation (25-42) years, on different fluvisols (alluvial semigley, humifluvisol, humogley and alpha/beta-beta gley), at different discount rates (4-12%). Methods of analysis of commercial profitability, especially some methods of dynamic investment calculation (net present value - NPV, internal rate of return - IRR, benefit-cost method - R and pay back period - PBP) were used. The investigated plantations were established from Populus x euramericana cl. I-214. with planting spacing 6 x 6 m. Thirteen study plots - management units (55 stands), with a total area of 331.05 ha were investigated in the period 2002-2010. For a discount rate r = 12%, all tested areas had a negative NPV of 11 088 to 23 676 (sic).ha(-1), regardless of age and site quality. The discount rate of 6% can be accepted by shorter production cycles in younger stands (to the age of 28 years) on better sites (alluvial semigley). IRRs varied in the range 4.32-6.94% (average 5.63%) at a discount rate of 12%. Internal rates were larger for plantations on good quality soil types and for shorter rotations and vice versa. The analysis showed that PBP is practically unacceptable for the investor under the discount rate of 6%. The most favourable situation is the discount rate of 2% in younger plantations. The average amount of R was 0.36 for all studied plots.
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Net Present Value and Internal Rate of Return were indicators used in the cost analysis of commercial poplar plantations in Serbia. The study was conducted on four types of sites under plantations of Populus x euramericana cl. I-214 aged 24–42 years. The aim was to examine the financial results of plantations of different ages at different discount rates. For a discount rate r = 12%, all the tested areas had a negative NPV, regardless of age and site quality. At r = 6%, shorter production cycles to up to 28 years of age on better site classes had positive NPV s (80–580 € ha −1
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Industrial poplar plantations represent a strategic source of wood products for many countries. Harvested after 10 to 30 years, they yield about 200 t ha(-1) of timber and 100 t ha(-1) industrial wood. The latter is obtained from poplar tops, which can be converted into chips, or a mix of pulpwood and chips. The study compared four options to process poplar tops. Alternatives derived from the intersection of two product strategies (pulpwood and chips, or chips only) with two pulpwood processing methods (manual or mechanized). Both mechanization and simplification (only one product) succeeded in reducing production cost, but the former had a stronger effect. The tests demonstrated that all options were cost-effective and could return some profits. However, the exclusive production of chips offered lower profits, compared to an articulate product strategy aimed at maximising value recovery. In the case of Italian poplar plantations, the price difference between pulp and chips is generally larger than the cost reduction obtained with integral chipping. Similar conclusions were reached by other authors working with spruce and beech in Central Europe. Of course, this is only true for the current price levels of pulpwood and chips: results may change, if this price balance will be altered by the growing demand for biomass fuel.
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Intensifying forest management has the potential to alleviate pressures of competing land uses, maintain global competitiveness in the face of increasing exotic plantations, and increase the value of the boreal forest resource. Yet such initiatives have largely been stymied in Canada's boreal regions because intensive forest management of native tree species is not financially viable. However, the yield curve estimation and financial analysis conducted in this paper suggests intensive management of hybrid poplar could be financially viable. The financial viability of such initiatives will depend heavily on the policy environment that governments create, such as priority zoning, to encourage or discourage such trends. But before reforming policy, decision makers will have to trade-off the environmental implications of industrial plantations of exotic species with the potential gains from priority zoning.
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Large-scale field trials of short-rotation coppice with willow and poplar have been studied since the mid-1980s in the UK. The information and results gained from these trials are presented, particularly with respect to operations, productivity and costs. Current methods for site selection, establishment, management practice, pests and diseases, harvesting and storage of short-rotation coppice crops are described and discussed. In the UK, the ability of short-rotation coppice to compete with conventional agricultural crops is still heavily dependent on the subsidies available for short-rotation coppice and the crop in question. Analysis of a wide range of data from field trials in Europe and North America showed that average levels of productivity ranged from 2 to 13.5odt/ha/year. The assumption that short-rotation coppice productivity increases from the first to second and subsequent rotations is not borne out in practice. Productivity levels may be increased in future through improved management practice and clonal materials, but it is unlikely that the predictions made in the early 1980s will be achieved in practice.