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J. Bio. & Env. Sci. 2015
289 | Moradi
RESEARCH PAPER OPEN ACCESS
Evaluation of systematic random sampling method for quantitative
estimation of rare and thick trees in Caspian Forests. (Case study:
Kheyroud-Kenar, Naushahr, Iran)
Sohrab Moradi
Agriculture Faculty of Payame Noor university, Iran
Key words: full callipering method, systematic random sampling (SRS), rare and thick trees, Gorazbon.
Article published on February 09, 2015
Abstract
Knowledge and recognition of existence or absence and real type and amount of rare and thick trees in natural
stands for studying silviculture, forest management, biodiversity, etc. can be useful. Recognition of number of
trees distribution in different diametric classes is necessary not only in the study of progress circumstance of
forest stand but also in composing database for value tables and growing stock. Study the importance of number
of trees distribution in different classes cannot be ignored in judgment quality of performed cultural operations,
method selection and cultural operations appropriate to forest stands in the future. In order to evaluate SRS
method for quantitative estimation of rare and thick trees, three compartments (312,313,319) of Gorazbon
district in Kheyroud -Kenar, Naushahr forest were selected. SRS was employed for estimation of number & basal
area per hectare in rare and thick species but full callipering methods for accurate measurement of the above-
mentioned attributes. Results of this study showed that SRS method has underestimated some species such as
Wild cherry (Cerasus avium), Mountain elm (Ulmus glabra Hudson), Cappadocian maple (Acer cappadocicum
Gled), Large-leaved lime tree (Tilia platyphyllos Scop.) and Velvet maple (Acer velutinum) and overestimated
others such as Chestnut-leaved oak (Quercus castaneifolia C.A.M.), Black alder (Alnus glutinosa (L.) Gaertn),
and Common hornbeam (Carpinus betulus L.) spices. SRS method did not have an accurate estimation for
number of trees distribution per hectare in diametric classes more than 100 for Chestnut-leaved oak,
Common hornbeam and Velvet maple spices.
*Corresponding Author: Sohrab Moradi  Moradi_4@pnu.ac.ir
Journal of Biodiversity and Environmental Sciences (JBES)
ISSN: 2220-6663 (Print), 2222-3045 (Online)
http://www.innspub.net
Vol. 6, No. 2, p. 289-296, 2015
J. Bio. & Env. Sci. 2015
290 | Moradi
Introduction
Forest cover about 12 million ha in Iran (Haidari et
al., 2013a; Haidari et al., 2013b; Hosseini et al., 2012;
Kalantari et al., 2012) which comprise 7.4% of the
whole country area. Considering this limited forest
coverage, logical management and planning seem to
be necessary (Hosseini et al., 2005). For optimal
management of these natural resources, enough and
accurate information is needed which are obtainable
through forest inventory. Nowadays, it has been
proved that any standard management and planning
enjoys proper information both qualitatively and
quantitatively. For this reason, forest inventory with
the purpose of present condition assessment and
future planning is in great importance (Eshagh
Nimvari et al., 2003). Each forest area, based on the
importance of the species and various forest stands,
acquires its respective inventory. One of the inventory
methods for assessment of various attributes of forest
trees located in the north of Iran, is SRS method. In
SRS method "any combination of sample plots
which have been designed in regular network with
respect to the number of sample plots and the area of
the related stand, has got an equal chance of being
selected". In this sampling method, Planning of
dimension network and determination of shape and
area of sample plots are very important (Zobeiri,
2002).
In this method, the Diameter at Breast Height (DBH)
of all trees exceeding the indicated counting limit in
the sample plot is measured. The point of measuring
the diameter, namely the breast height diameter, is
determined over the slope and the trees with
diameters over 7.5 cm are measured. Finally, the
results of measurements are recorded in special
forms.
The significance of natural species of forest stands has
nothing to do with their frequency rate and
accordingly conducting the studies towards the
species with high frequency is one of the causes of
gradual ruin of rare and valuable species in the north
of Iran (Namiranian, 2005). It is also worth
mentioning that the significance of study related to
the distribution of tree numbers in different diametric
classes should not be ignored in judgment of the
quality of applied tending operation and selecting
suitable method and tending operation for each stand
in the future (Namiranian, 1990). The research
hypothesis is that SRS method is not capable of
accurate estimation of the number and basal area per
hectare in rare and thick species. The reason is
claimed to be the small number of rare and thick trees
in the forest stands. On the other hand, the
significance of rare and thick trees in silviculture
investigation and biodiversity studies is absolutely
well known (Marvie Mohadjer et al., 2009). In
addition to, the knowledge and recognition of the
existence or lack of rare & thick species in natural
stands can be useful in forestry and silvicultural
planning (Moradi, 2005). For this reason, nowadays,
the attempts are made to preserve these species
against the danger of ruin and to use them as the
information sources of genetics and biodiversity. In
contribution to the goals of the present study, SRS
method as a common method of sampling in north
forests will be evaluated for estimation of number and
basal area per hectare in rare and thick species and
investigating the distribution of number per hectare
in diametric classes as well.
Some studies have been carried out on the
comparison between SRS method and other sampling
methods in Iran forests. Safi studied and compared
different inventory methods in Kheyroud -Kenar
forests in 1981 (Safi, 1981). Akhavan, in 2001,
evaluated and compared two methods of inventory,
SRS method and stratification method using aerial
images with respect to cost and accuracy (Akhavan et
al., 2001). Eshagh Nimvari, in 2000, has compared
two methods: SRS with circular sample plot and
transect methods in western oak trees having cost and
accuracy in mind (Eshagh Nimvari, 2000). Finally,
Namiranian in 1996 has investigated the way of
selecting network dimensions and sample plots in the
inventory of forest stands (Namiranian, 1996).
However, no study has been yet carried out on the
J. Bio. & Env. Sci. 2015
291 | Moradi
evaluation of SRS method in assessment of rare and
thick trees whether inside the country or outdoors.
The present study is the first one in this relevance and
hence it has no literature.
Materials and methods
Area of study
The region under study has been located in Gorazbon
district in Kheyroud -Kenar, Naushahr – (IRAN). This
district with area of 1022 has been located 18 kms
far from the east of Naushahr county and 23 kms from
the main road along the Caspian Sea. Gorazbon
district has been composed of 27 parcels with spaces
variable from 20 to 80 . As the forest area with
high diversity of species was needed for this study,
parcels of 312,313 & 319 were selected by forest
cruising. Fig. and table 1 shows the position, altitude
characteristics and the areas of the above-mentioned
parcels respectively.
Table 1. Altitude characteristics and the areas of the
parcels in the area study.
Maximum
altitude
Minimum
altitude
Parcel
area (ha)
Parcel
number
1218106033.52312
1300110049.67313
1265118040.89319
Fig. 1. Position of parcels in area of study.
Methodology
Considering that the aim of this paper is evaluating
SRS method to estimate the number and basal area of
trees per hectare in rare and thick species, initially
full callipering method was employed for achieving
real type and amount of number and basal area at
breast height in rare and thick trees. The next method
was SRS. It is worth mentioning that, in this study,
via forest cruising and initial studies, the species with
diameter over 100 cm were identified as thick species
and species of Wild cherry (Cerasus avium),
Mountain elm (Ulmus glabra Hudson), Large-leaved
lime tree (Tilia platyphyllos Scop.), Cappadocian
maple (Acer cappadocicum Gled) and Common ash
(Fraxinus excelsior) as rare ones.
Full callipering
In this method, all trees in the forest stand, the
diameter of which exceeds the indicated counting
limit, are measured (Zobeiri, 2000). The measuring
limit is 7.5 cm in this study. The inventory team
involved a leader and two measure men. The leader
recorded the measurements results in a special form
with respect to the different species. They ought to
measure the trees DBH the diameter of which
exceeded the indicated measuring limit. The
inventory indexes for each attribute were calculated
via the following equation:
Number per hectare: it is calculated through dividing
the total tree number on the area of the region under
study.

 

i
ii
S
nS
n
(1)
n is the average of tree number in the whole region
under study, is the area of each parcel and is the
number of trees per hectare in each parcel.
Basal area per hectare: this attribute is calculated
through dividing basal area of all trees on the area of
the region under study. It has been calculated per
hectare in isolation for each parcel and the whole
region under study as well.
J. Bio. & Env. Sci. 2015
292 | Moradi

 

i
ii
S
BAS
G
(2)
G is the average of basal area per hectare and the
whole region under study as well, iBA is the basal
area per hectare of each parcel per square meter.
SRS method
In this study, just like the previous and common
researches in the north forests, the shape and area of
the sample plot were decided circular and 10 Ar
respectively. Considering the aim and the area of the
region under study and also in order to have enough
sample plot in the region under study, it was decided
to obtain one sample plot per each hectare via forest
cruising and inspection of forest. Finally, 119 samples
were obtained. Fig. 2 shows the map of parceling and
the position of sample plots together with designed
network.
Fig. 2. Map of parceling and the position of sample
plots together with designed network.
In this method, the first sample plot or the start point
of inventory was selected randomly and finally the
inventory operation was carried out with the help of
forest network map. After determining the center of
sample plot, it was established in the forest with
respect to its circular shape. First, the maximum
slope of the sample plot was measured and was
obtained then the radius by means of which the
sample plot was established so that its horizontal area
is corresponded with the already determined area. To
measure out the trees, the diameter of those inside
the sample plot, the distances of which from the
sample plot were less than the radius of sample plot,
were measured via caliper or Diameter Tape ( for
trees having diameters over 100 cm). The point of
measuring the diameter was determined above the
slope. The trees with diameters above 7.5 cm were
gone under measurement and finally the results of
measurements were recorded in special forms.
In this inventory method, the statistic indexes for
each attribute were calculated through the following
equations:
Number per hectare
t
n
i
i
n
n
n

 1
(3)
n is the average of tree number in sample plot, is
the total of sample plots.
10 nN (4)
is the average of tree number per hectares.
Basal area
t
n
i
i
ip
n
BA
BA

 1
(5)
That ipBA
is the average of basal area in sample plot
per square meter.
10 ipBAG
(6)
G is the average of basal area in hectare per square
meter.
Results and discussion
The number and basal area per hectare for species of
Wild cherry, Mountain elm, Cappadocian maple,
Velvet maple and Large-leaved lime tree obtained
from SRS method are less than real amount (full
callipering). This difference is significant, so that SRS
method has not yield any results in number and basal
area for Wild cherry. In other word, in SRS method,
J. Bio. & Env. Sci. 2015
293 | Moradi
there has not been obtained any results for Wild
cherry in the region under study; while the number
and basal area obtained from full callipering method
for the above-mentioned species are 0.016 trees and
0.001 respectively. By generalizing these values
into the whole region under study (124.08 ha), we will
have 1.98 trees and 0.124 for number and basal
area respectively. The difference in number per
hectare for Mountain elm obtained from the various
inventory methods is 0.36 and the difference for basal
area is 0.007 . By generalizing these values into the
whole region under study, we will have 44.67 trees
and 0.87 for number and basal area respectively.
The lower values for basal area in these two species,
as compared with the values of number per hectare,
are due to their small diameters. The difference in
number per hectare for Cappadocian maple obtained
from the various inventory methods is 0.31 and the
difference for basal area is 0.021 . By generalizing
these values into the whole region under study, we
will have 38.46 trees and 2.06 for number and
basal area respectively. Considering that Cappadocian
maple possesses the higher diametric classes,
comparing with species of Mountain elm and Wild
cherry, the difference in basal area per hectare
obtained from full callipering and SRS methods is
significant. The difference in number per hectare for
Large-leaved lime tree obtained from the various
inventory methods is 0.224 and the difference for
basal area is 0.059 . By generalizing these values
into the whole region under study, we will have 27.79
trees and 7.32 for number and basal area
respectively. Considering that Large-leaved lime tree
possesses the higher diametric classes, comparing
with species of Mountain elm, Wild cherry and
Cappadocian maple, the difference in basal area per
hectare obtained from full callipering and SRS
methods is significant.
The number and basal area per hectare for Velvet
maple obtained from SRS method in diametric classes
above 100 are less than real (full callipering), But
the difference is not so significant. The difference in
number per hectare for the above-mentioned species
obtained from the various inventory methods is 0.04
and the difference for basal area is 0.06 . By
generalizing these values into the whole region under
study, we will have 4.96 trees and 7.44 for number
and basal area respectively.
The number and basal area per hectare for Chestnut-
leaved oak, Common hornbeam, Common ash and
Black alder species obtained from SRS method in
diametric classes above 100 are more than real
(full callipering). Although SRS method yields some
information about number and basal area per hectare
in the case of Chestnut-leaved oak, but the values of
the related attributes are different from the ones
obtained from full callipering method. The difference
in number per hectare for Chestnut-leaved oak
obtained from the various inventory methods is 0.014
and the difference for basal area is 0.208 . By
generalizing these values into the whole region under
study, we will have 1.74 trees and 25.8 for number
and basal area respectively. Considering that
Chestnut-leaved oak possesses the higher diametric
classes, comparing with species of Large-leaved lime
tree, Mountain elm, Wild cherry and Cappadocian
maple, the difference in basal area per hectare
obtained from full callipering and SRS methods is
significant.
The number and basal area per hectare for Common
hornbeam in diametric classes above 100 and
Common ash in different diametric classes, both
obtained from SRS method, are more than real (full
callipering) and the difference rate is significant here.
The differences in number per hectare for Common
ash and Common hornbeam obtained from the
various inventory methods are 0.21 & 0.054 and the
differences for basal area are 0.18 and 0.0004 . By
generalizing these values into the whole region under
study, we will have 26.06 & 6.7 trees and 22.33 &
0.05 for number and basal area respectively. The
reason of small difference in basal areas per hectare
obtained from various inventory methods for
Common ash is claimed to be the low diametric
J. Bio. & Env. Sci. 2015
294 | Moradi
classes of the related species in the region under
study.
The number and basal area per hectare for Black
alder obtained from SRS method in diametric classes
above 100 is more than real (full callipering). The
difference in number per hectare for the above-
mentioned species obtained from the various
inventory methods is 0.41 and the difference for basal
area is 0.36 . By generalizing these values into the
whole region under study, we will have 50.87 trees
and 44.67 for number and basal area respectively.
The number and basal area per hectare for different
species have been depicted in fig.s 3&4 respectively.
Fig. 3. Number of trees per hectare for different
species resulted from inventory methods.
Fig. 4. Basal area per hectare for different species
resulted from inventory methods.
SRS method neither yields accurate estimation of Large-
leaved lime neither tree, nor can calculate the
distribution of number per hectare precisely. The
diagram of distribution per hectare in different diametric
classes has been depicted in fig. 5 for Large-leaved lime
tree in different inventory methods. It is well inferred
from fig. 5 that the diagram of distribution of number
per hectare obtained from SRS method ranges only in
diametric classes of 15, 20, 25 & 30 but it ranges from
100 to 145 in most of diametric classes in the case of
full callipering method.
Fig. 5. Distribution of number of trees per hectare in
diametric classes of Large-leaved lime tree.
SRS method yields a rather reliable estimation of
number per hectare for Chestnut-leaved oak.
However, it fails to calculate the distribution per
hectare in different diametric classes. The diagram of
distribution of number per hectare in different
diametric classes has been depicted in fig. 6 for
Chestnut-leaved oak in different inventory methods.
It is well inferred from fig. 6 that the diagram of
distribution per hectare in diametric classes above
100 obtained from SRS method exists only in
diametric class of 210 , but in the equal condition,
the related values are 105,110,115,120,135 & 210 in
the case of full callipering method.
Fig. 6. Distribution of number of tree per hectare in
diametric classes of Chestnut-leaved oak.
J. Bio. & Env. Sci. 2015
295 | Moradi
In the case of Velvet maple, the distribution of
number per hectare obtained from SRS method in
diametric classes above 100 has a significant
difference from its counterpart obtained from full
callipering method. The diagram of distribution of
number per hectare in diametric classes above 100
has been depicted in fig. 7 for Velvet maple in
different inventory methods. It is well inferred from
fig. 7 that the diagram of distribution per hectare in
diametric classes above 100 obtained from SRS
method exists only in diametric classes of 105,110
&140 , but it ranges among the most of diametric
classes above 100 in the case of full callipering
method.
Fig. 7. Distribution of number of trees per hectare in
diametric classes of Velvet maple
Conclusion and recommendation
The results obtained from this study showed that, due
to the small number of rare and thick species in
natural stands, SRS method fails to yield an accurate
estimation of the type and quantity of the related
species in forest stand and most of the times either
there doesn't exist any estimation or in the case of any
estimation, it will be less or more than real. Although
in the few cases it may have estimation somewhat
close to the one in full callipering method, the
distribution of number per hectare in diametric
classes are not accurately calculated. Considering that
thorough knowledge on the distribution of number of
trees in different diametric classes, also presence or
lack of different tree species, is necessary not only in
the study of the development procedure of forest
stand, but also provide the basic data for value tables,
production quality and volume of Residual Stands.
Accordingly, the importance of investigating the
procedure of distribution in different diametric
classes, also information on the presence or lack of
rare & thick species cannot be ignored in the
judgment about the quality of applied tending
operation and also in the selection of the suitable
tending operation for each stand in the future.
Concerning the results of the present study and also
due to the significance of rare and thick species in
forestry and silvicultural planning, biodiversity
studies, etc. it is recommended to collate a
complementary method with SRS method in order to
evaluate the type and the quantity of species
accurately in the north forests of the country. For this
purpose, rare and thick trees should be measured
accurately through forest cruising and the results
should be substituted with the ones obtained from
SRS method.
References
Akhavan R, Zobeiri M, Namiranian M. 2001.
Study of Stratification method using for Volume
Estimation in Kheyroud -Kenar forest. Iranian
Journal of Natural Resources, Vol 54(3), p. 235-245.
Eshagh Nimvari J, Zobeiri M, Sobhani H,
Zangeneh HP. 2003. A Comparison of Randomized
Systematic Sampling with Circle Shape Plot and
Transect Method, Based on Precision and Cost, (Case
Study in Sorkhedizeh of Kermanshah). Iranian
Journal of Natural Resources, 56(4), p. 383-396.
Eshagh Nimvari J. 2000. A comparison of
systematic random sampling with circle shape plot
and transect method, base on precision and cost in
Zagros forests, Master of Science thesis, Faculty of
natural resources, university of Tehran.
Haidari M, Etemad V, Khosropour E. 2013a.
Study of tree regeneration in the grazed and non-
grazed areas in the Iran-o-Turanian Ecological Zones,
International journal of Advanced Biological and
Biomedical Research (IJABBR), Volume 1, Issue 1, p.
18-24.
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Haidari M, Rezaei D. 2013. Study of plant diversity
in the Northern Zagros forest (Case study: Marivan
region), International journal of Advanced Biological
and Biomedical Research (IJABBR), Volume 1, Issue
1, p.1-10.
Hosseini S.A, Sarikhani N, Soleimani K, Jalali
S.Gh, Hosseini S.M. 2005. An Investigation of
Effective Factors in Forest Road Selection Using GIS
(A Case Study in Nowshahr-Mazandaran Province),
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59-75.
Hosseini S.A.O, Haidari M, Shabanian N,
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Kalantari H, Fallah A, Hodjati S.M, Parsakhoo
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Marvie Mohadjer M.R, Zobeiri M, Etemad V,
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selection method at compartment level and necessity
for full inventory of tree species (Case study:
Gorazbon district in Kheyroud Forest), Journal of the
Iranian Natural Resources, Vol. 61, No. 4, p. 889-
908.
Moradi S. 2005. A comparison of full callipering
with systematic random sampling and systematic
random sampling along with forest cruising methods
in Caspian Forests. (Case study: Kheyroud – Kenar
NAUSHAHR), Master of Science thesis, Faculty of
natural resources, university of Tehran.
Namiranian M. 1990. The use of probability theory
in indicating the distribution of trees in different
diametric classes, Iranian Journal of Natural
Resources, Vol. 44, p. 93-108.
Namiranian M. 1996. The way of selecting network
dimensions and sample plots in inventory of forest
stands, Iranian Journal of Natural Resources, Vol.
48, p. 105-113.
Namiranian M. 2005. An Investigation of the Ash
species inventory at Gorazbon District in the
Educational and Research Forests of Kheyroud –
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57(4), p. 689-702.
Safi N. 1981. The survey and comparison of different
inventory methods in Kheyroud -Kenar forest (Patom
district), Master of Science thesis, Faculty of natural
resources, university of Tehran.
Zobeiri M. 2000. Inventory in forest. University of
Tehran press. Two editions.
Zobeiri M. 2002. Forest biometry. University of
Tehran press. First edition.

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Evaluation of systematic random sampling method for quantitative estimation of rare and thick trees in Caspian Forests. (Case study: Kheyroud-Kenar, Naushahr, Iran)

  • 1. J. Bio. & Env. Sci. 2015 289 | Moradi RESEARCH PAPER OPEN ACCESS Evaluation of systematic random sampling method for quantitative estimation of rare and thick trees in Caspian Forests. (Case study: Kheyroud-Kenar, Naushahr, Iran) Sohrab Moradi Agriculture Faculty of Payame Noor university, Iran Key words: full callipering method, systematic random sampling (SRS), rare and thick trees, Gorazbon. Article published on February 09, 2015 Abstract Knowledge and recognition of existence or absence and real type and amount of rare and thick trees in natural stands for studying silviculture, forest management, biodiversity, etc. can be useful. Recognition of number of trees distribution in different diametric classes is necessary not only in the study of progress circumstance of forest stand but also in composing database for value tables and growing stock. Study the importance of number of trees distribution in different classes cannot be ignored in judgment quality of performed cultural operations, method selection and cultural operations appropriate to forest stands in the future. In order to evaluate SRS method for quantitative estimation of rare and thick trees, three compartments (312,313,319) of Gorazbon district in Kheyroud -Kenar, Naushahr forest were selected. SRS was employed for estimation of number & basal area per hectare in rare and thick species but full callipering methods for accurate measurement of the above- mentioned attributes. Results of this study showed that SRS method has underestimated some species such as Wild cherry (Cerasus avium), Mountain elm (Ulmus glabra Hudson), Cappadocian maple (Acer cappadocicum Gled), Large-leaved lime tree (Tilia platyphyllos Scop.) and Velvet maple (Acer velutinum) and overestimated others such as Chestnut-leaved oak (Quercus castaneifolia C.A.M.), Black alder (Alnus glutinosa (L.) Gaertn), and Common hornbeam (Carpinus betulus L.) spices. SRS method did not have an accurate estimation for number of trees distribution per hectare in diametric classes more than 100 for Chestnut-leaved oak, Common hornbeam and Velvet maple spices. *Corresponding Author: Sohrab Moradi  Moradi_4@pnu.ac.ir Journal of Biodiversity and Environmental Sciences (JBES) ISSN: 2220-6663 (Print), 2222-3045 (Online) http://www.innspub.net Vol. 6, No. 2, p. 289-296, 2015
  • 2. J. Bio. & Env. Sci. 2015 290 | Moradi Introduction Forest cover about 12 million ha in Iran (Haidari et al., 2013a; Haidari et al., 2013b; Hosseini et al., 2012; Kalantari et al., 2012) which comprise 7.4% of the whole country area. Considering this limited forest coverage, logical management and planning seem to be necessary (Hosseini et al., 2005). For optimal management of these natural resources, enough and accurate information is needed which are obtainable through forest inventory. Nowadays, it has been proved that any standard management and planning enjoys proper information both qualitatively and quantitatively. For this reason, forest inventory with the purpose of present condition assessment and future planning is in great importance (Eshagh Nimvari et al., 2003). Each forest area, based on the importance of the species and various forest stands, acquires its respective inventory. One of the inventory methods for assessment of various attributes of forest trees located in the north of Iran, is SRS method. In SRS method "any combination of sample plots which have been designed in regular network with respect to the number of sample plots and the area of the related stand, has got an equal chance of being selected". In this sampling method, Planning of dimension network and determination of shape and area of sample plots are very important (Zobeiri, 2002). In this method, the Diameter at Breast Height (DBH) of all trees exceeding the indicated counting limit in the sample plot is measured. The point of measuring the diameter, namely the breast height diameter, is determined over the slope and the trees with diameters over 7.5 cm are measured. Finally, the results of measurements are recorded in special forms. The significance of natural species of forest stands has nothing to do with their frequency rate and accordingly conducting the studies towards the species with high frequency is one of the causes of gradual ruin of rare and valuable species in the north of Iran (Namiranian, 2005). It is also worth mentioning that the significance of study related to the distribution of tree numbers in different diametric classes should not be ignored in judgment of the quality of applied tending operation and selecting suitable method and tending operation for each stand in the future (Namiranian, 1990). The research hypothesis is that SRS method is not capable of accurate estimation of the number and basal area per hectare in rare and thick species. The reason is claimed to be the small number of rare and thick trees in the forest stands. On the other hand, the significance of rare and thick trees in silviculture investigation and biodiversity studies is absolutely well known (Marvie Mohadjer et al., 2009). In addition to, the knowledge and recognition of the existence or lack of rare & thick species in natural stands can be useful in forestry and silvicultural planning (Moradi, 2005). For this reason, nowadays, the attempts are made to preserve these species against the danger of ruin and to use them as the information sources of genetics and biodiversity. In contribution to the goals of the present study, SRS method as a common method of sampling in north forests will be evaluated for estimation of number and basal area per hectare in rare and thick species and investigating the distribution of number per hectare in diametric classes as well. Some studies have been carried out on the comparison between SRS method and other sampling methods in Iran forests. Safi studied and compared different inventory methods in Kheyroud -Kenar forests in 1981 (Safi, 1981). Akhavan, in 2001, evaluated and compared two methods of inventory, SRS method and stratification method using aerial images with respect to cost and accuracy (Akhavan et al., 2001). Eshagh Nimvari, in 2000, has compared two methods: SRS with circular sample plot and transect methods in western oak trees having cost and accuracy in mind (Eshagh Nimvari, 2000). Finally, Namiranian in 1996 has investigated the way of selecting network dimensions and sample plots in the inventory of forest stands (Namiranian, 1996). However, no study has been yet carried out on the
  • 3. J. Bio. & Env. Sci. 2015 291 | Moradi evaluation of SRS method in assessment of rare and thick trees whether inside the country or outdoors. The present study is the first one in this relevance and hence it has no literature. Materials and methods Area of study The region under study has been located in Gorazbon district in Kheyroud -Kenar, Naushahr – (IRAN). This district with area of 1022 has been located 18 kms far from the east of Naushahr county and 23 kms from the main road along the Caspian Sea. Gorazbon district has been composed of 27 parcels with spaces variable from 20 to 80 . As the forest area with high diversity of species was needed for this study, parcels of 312,313 & 319 were selected by forest cruising. Fig. and table 1 shows the position, altitude characteristics and the areas of the above-mentioned parcels respectively. Table 1. Altitude characteristics and the areas of the parcels in the area study. Maximum altitude Minimum altitude Parcel area (ha) Parcel number 1218106033.52312 1300110049.67313 1265118040.89319 Fig. 1. Position of parcels in area of study. Methodology Considering that the aim of this paper is evaluating SRS method to estimate the number and basal area of trees per hectare in rare and thick species, initially full callipering method was employed for achieving real type and amount of number and basal area at breast height in rare and thick trees. The next method was SRS. It is worth mentioning that, in this study, via forest cruising and initial studies, the species with diameter over 100 cm were identified as thick species and species of Wild cherry (Cerasus avium), Mountain elm (Ulmus glabra Hudson), Large-leaved lime tree (Tilia platyphyllos Scop.), Cappadocian maple (Acer cappadocicum Gled) and Common ash (Fraxinus excelsior) as rare ones. Full callipering In this method, all trees in the forest stand, the diameter of which exceeds the indicated counting limit, are measured (Zobeiri, 2000). The measuring limit is 7.5 cm in this study. The inventory team involved a leader and two measure men. The leader recorded the measurements results in a special form with respect to the different species. They ought to measure the trees DBH the diameter of which exceeded the indicated measuring limit. The inventory indexes for each attribute were calculated via the following equation: Number per hectare: it is calculated through dividing the total tree number on the area of the region under study.     i ii S nS n (1) n is the average of tree number in the whole region under study, is the area of each parcel and is the number of trees per hectare in each parcel. Basal area per hectare: this attribute is calculated through dividing basal area of all trees on the area of the region under study. It has been calculated per hectare in isolation for each parcel and the whole region under study as well.
  • 4. J. Bio. & Env. Sci. 2015 292 | Moradi     i ii S BAS G (2) G is the average of basal area per hectare and the whole region under study as well, iBA is the basal area per hectare of each parcel per square meter. SRS method In this study, just like the previous and common researches in the north forests, the shape and area of the sample plot were decided circular and 10 Ar respectively. Considering the aim and the area of the region under study and also in order to have enough sample plot in the region under study, it was decided to obtain one sample plot per each hectare via forest cruising and inspection of forest. Finally, 119 samples were obtained. Fig. 2 shows the map of parceling and the position of sample plots together with designed network. Fig. 2. Map of parceling and the position of sample plots together with designed network. In this method, the first sample plot or the start point of inventory was selected randomly and finally the inventory operation was carried out with the help of forest network map. After determining the center of sample plot, it was established in the forest with respect to its circular shape. First, the maximum slope of the sample plot was measured and was obtained then the radius by means of which the sample plot was established so that its horizontal area is corresponded with the already determined area. To measure out the trees, the diameter of those inside the sample plot, the distances of which from the sample plot were less than the radius of sample plot, were measured via caliper or Diameter Tape ( for trees having diameters over 100 cm). The point of measuring the diameter was determined above the slope. The trees with diameters above 7.5 cm were gone under measurement and finally the results of measurements were recorded in special forms. In this inventory method, the statistic indexes for each attribute were calculated through the following equations: Number per hectare t n i i n n n   1 (3) n is the average of tree number in sample plot, is the total of sample plots. 10 nN (4) is the average of tree number per hectares. Basal area t n i i ip n BA BA   1 (5) That ipBA is the average of basal area in sample plot per square meter. 10 ipBAG (6) G is the average of basal area in hectare per square meter. Results and discussion The number and basal area per hectare for species of Wild cherry, Mountain elm, Cappadocian maple, Velvet maple and Large-leaved lime tree obtained from SRS method are less than real amount (full callipering). This difference is significant, so that SRS method has not yield any results in number and basal area for Wild cherry. In other word, in SRS method,
  • 5. J. Bio. & Env. Sci. 2015 293 | Moradi there has not been obtained any results for Wild cherry in the region under study; while the number and basal area obtained from full callipering method for the above-mentioned species are 0.016 trees and 0.001 respectively. By generalizing these values into the whole region under study (124.08 ha), we will have 1.98 trees and 0.124 for number and basal area respectively. The difference in number per hectare for Mountain elm obtained from the various inventory methods is 0.36 and the difference for basal area is 0.007 . By generalizing these values into the whole region under study, we will have 44.67 trees and 0.87 for number and basal area respectively. The lower values for basal area in these two species, as compared with the values of number per hectare, are due to their small diameters. The difference in number per hectare for Cappadocian maple obtained from the various inventory methods is 0.31 and the difference for basal area is 0.021 . By generalizing these values into the whole region under study, we will have 38.46 trees and 2.06 for number and basal area respectively. Considering that Cappadocian maple possesses the higher diametric classes, comparing with species of Mountain elm and Wild cherry, the difference in basal area per hectare obtained from full callipering and SRS methods is significant. The difference in number per hectare for Large-leaved lime tree obtained from the various inventory methods is 0.224 and the difference for basal area is 0.059 . By generalizing these values into the whole region under study, we will have 27.79 trees and 7.32 for number and basal area respectively. Considering that Large-leaved lime tree possesses the higher diametric classes, comparing with species of Mountain elm, Wild cherry and Cappadocian maple, the difference in basal area per hectare obtained from full callipering and SRS methods is significant. The number and basal area per hectare for Velvet maple obtained from SRS method in diametric classes above 100 are less than real (full callipering), But the difference is not so significant. The difference in number per hectare for the above-mentioned species obtained from the various inventory methods is 0.04 and the difference for basal area is 0.06 . By generalizing these values into the whole region under study, we will have 4.96 trees and 7.44 for number and basal area respectively. The number and basal area per hectare for Chestnut- leaved oak, Common hornbeam, Common ash and Black alder species obtained from SRS method in diametric classes above 100 are more than real (full callipering). Although SRS method yields some information about number and basal area per hectare in the case of Chestnut-leaved oak, but the values of the related attributes are different from the ones obtained from full callipering method. The difference in number per hectare for Chestnut-leaved oak obtained from the various inventory methods is 0.014 and the difference for basal area is 0.208 . By generalizing these values into the whole region under study, we will have 1.74 trees and 25.8 for number and basal area respectively. Considering that Chestnut-leaved oak possesses the higher diametric classes, comparing with species of Large-leaved lime tree, Mountain elm, Wild cherry and Cappadocian maple, the difference in basal area per hectare obtained from full callipering and SRS methods is significant. The number and basal area per hectare for Common hornbeam in diametric classes above 100 and Common ash in different diametric classes, both obtained from SRS method, are more than real (full callipering) and the difference rate is significant here. The differences in number per hectare for Common ash and Common hornbeam obtained from the various inventory methods are 0.21 & 0.054 and the differences for basal area are 0.18 and 0.0004 . By generalizing these values into the whole region under study, we will have 26.06 & 6.7 trees and 22.33 & 0.05 for number and basal area respectively. The reason of small difference in basal areas per hectare obtained from various inventory methods for Common ash is claimed to be the low diametric
  • 6. J. Bio. & Env. Sci. 2015 294 | Moradi classes of the related species in the region under study. The number and basal area per hectare for Black alder obtained from SRS method in diametric classes above 100 is more than real (full callipering). The difference in number per hectare for the above- mentioned species obtained from the various inventory methods is 0.41 and the difference for basal area is 0.36 . By generalizing these values into the whole region under study, we will have 50.87 trees and 44.67 for number and basal area respectively. The number and basal area per hectare for different species have been depicted in fig.s 3&4 respectively. Fig. 3. Number of trees per hectare for different species resulted from inventory methods. Fig. 4. Basal area per hectare for different species resulted from inventory methods. SRS method neither yields accurate estimation of Large- leaved lime neither tree, nor can calculate the distribution of number per hectare precisely. The diagram of distribution per hectare in different diametric classes has been depicted in fig. 5 for Large-leaved lime tree in different inventory methods. It is well inferred from fig. 5 that the diagram of distribution of number per hectare obtained from SRS method ranges only in diametric classes of 15, 20, 25 & 30 but it ranges from 100 to 145 in most of diametric classes in the case of full callipering method. Fig. 5. Distribution of number of trees per hectare in diametric classes of Large-leaved lime tree. SRS method yields a rather reliable estimation of number per hectare for Chestnut-leaved oak. However, it fails to calculate the distribution per hectare in different diametric classes. The diagram of distribution of number per hectare in different diametric classes has been depicted in fig. 6 for Chestnut-leaved oak in different inventory methods. It is well inferred from fig. 6 that the diagram of distribution per hectare in diametric classes above 100 obtained from SRS method exists only in diametric class of 210 , but in the equal condition, the related values are 105,110,115,120,135 & 210 in the case of full callipering method. Fig. 6. Distribution of number of tree per hectare in diametric classes of Chestnut-leaved oak.
  • 7. J. Bio. & Env. Sci. 2015 295 | Moradi In the case of Velvet maple, the distribution of number per hectare obtained from SRS method in diametric classes above 100 has a significant difference from its counterpart obtained from full callipering method. The diagram of distribution of number per hectare in diametric classes above 100 has been depicted in fig. 7 for Velvet maple in different inventory methods. It is well inferred from fig. 7 that the diagram of distribution per hectare in diametric classes above 100 obtained from SRS method exists only in diametric classes of 105,110 &140 , but it ranges among the most of diametric classes above 100 in the case of full callipering method. Fig. 7. Distribution of number of trees per hectare in diametric classes of Velvet maple Conclusion and recommendation The results obtained from this study showed that, due to the small number of rare and thick species in natural stands, SRS method fails to yield an accurate estimation of the type and quantity of the related species in forest stand and most of the times either there doesn't exist any estimation or in the case of any estimation, it will be less or more than real. Although in the few cases it may have estimation somewhat close to the one in full callipering method, the distribution of number per hectare in diametric classes are not accurately calculated. Considering that thorough knowledge on the distribution of number of trees in different diametric classes, also presence or lack of different tree species, is necessary not only in the study of the development procedure of forest stand, but also provide the basic data for value tables, production quality and volume of Residual Stands. Accordingly, the importance of investigating the procedure of distribution in different diametric classes, also information on the presence or lack of rare & thick species cannot be ignored in the judgment about the quality of applied tending operation and also in the selection of the suitable tending operation for each stand in the future. Concerning the results of the present study and also due to the significance of rare and thick species in forestry and silvicultural planning, biodiversity studies, etc. it is recommended to collate a complementary method with SRS method in order to evaluate the type and the quantity of species accurately in the north forests of the country. For this purpose, rare and thick trees should be measured accurately through forest cruising and the results should be substituted with the ones obtained from SRS method. References Akhavan R, Zobeiri M, Namiranian M. 2001. Study of Stratification method using for Volume Estimation in Kheyroud -Kenar forest. Iranian Journal of Natural Resources, Vol 54(3), p. 235-245. Eshagh Nimvari J, Zobeiri M, Sobhani H, Zangeneh HP. 2003. A Comparison of Randomized Systematic Sampling with Circle Shape Plot and Transect Method, Based on Precision and Cost, (Case Study in Sorkhedizeh of Kermanshah). Iranian Journal of Natural Resources, 56(4), p. 383-396. Eshagh Nimvari J. 2000. A comparison of systematic random sampling with circle shape plot and transect method, base on precision and cost in Zagros forests, Master of Science thesis, Faculty of natural resources, university of Tehran. Haidari M, Etemad V, Khosropour E. 2013a. Study of tree regeneration in the grazed and non- grazed areas in the Iran-o-Turanian Ecological Zones, International journal of Advanced Biological and Biomedical Research (IJABBR), Volume 1, Issue 1, p. 18-24.
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