Subscribe Now Subscribe Today
Research Article
 

Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran



Raza Basiri
 
Facebook Twitter Digg Reddit Linkedin StumbleUpon E-mail
ABSTRACT

In this study, Quercus libani Oliv.’s site in Sardasht has been studied phytosociologically. The vegetation has been carefully studied in Braun-Blanquet method. The relationship between environmental factors including topography and some of the most current physicochemical features of soil and plant associations was researched by means of multiple discriminant analysis. Based on AFC and CAH methods, 8 associations and 1 sub-association were achieved including: Trifolio stellati-Quercetum brantii, Pistacio atlanticae-Quercetum brantii, Violo modestue-Quercetum brantii, Trifolio campestri-Quercetum brantii, Quercetum brantii, Thalictro sultanabadensi-Quercetum libani, Quercetum libani-acerotosum cinerascens, Quercos boissieri-Quercetum libani and Quercetum libani. These plant associations belong to Quercetea persicae class and Quercetalia persicae order. The effective environmental factors in division of plant associations based on multiple discriminant analysis include respectively: pH, landform index, Terrain shape index and aspect.

Services
Related Articles in ASCI
Similar Articles in this Journal
Search in Google Scholar
View Citation
Report Citation

 
  How to cite this article:

Raza Basiri , 2010. Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran. Journal of Applied Sciences, 10: 1667-1683.

DOI: 10.3923/jas.2010.1667.1683

URL: https://scialert.net/abstract/?doi=jas.2010.1667.1683
 
Received: February 18, 2010; Accepted: May 27, 2010; Published: June 26, 2010



INTRODUCTION

Like other sciences, vegetation description and analysis shall be studies under a special logic and system (Kent and Coker, 1992). In the recent years, the study of plant associations has made great developments in perception, summarization and facilitation of environment-vegetation relations and the studies consider two major goals:

(1) To provide a state-of-the-art overview of all vegetation types in its territory that are dominated by vascular plants; (2) To give a detailed assessment of these types for conservation purposes (Dengler et al., 2005).

Many methods have developed into different schools to describe characteristics of plant association, among which Zurich-Montpellier school is of special importance (Kent and Coker, 1992). The general goal of BRAUN-BLANQUET method is classification of plant associations based on floristic composition which is performed by ordering floristic data in phytosociology tables (Mueller-Dombois and Ellenberg, 1974). Braun Blanquet used association expression for characteristic species which is a basic unit for describing vegetation (Pignatti et al., 1997). Plant associations are changeable and can be seen as mosaic of vegetation units. This changeability relates to environmental variants at any time (Cook and Irwin, 1992; Comstock and Ehleringer, 1992). The analysis of species-environment relationship has always been considered as a central axis in the studies of ecology (Guisan and Zimmermann, 2000).

Physicochemical features of soil and topography have been discriminated as effective environmental factors on growth of species (Barnes et al., 1998; Barbour et al., 1999; Abd El-Ghani et al., 2003; Solon et al., 2007; Hee et al., 2007). Quercus libani Oliv.’s site in Sardasht is located in the North West of Iran in the range of north Zagros mountains (Maroofi, 2000; Fattahi, 2000). Considering distributed ecology in Quercus libani site indicates a general description of quality of the relationship between vegetation types and environmental factors such as topography and soil in a wide (Maroofi, 2000). Quercus libani is one of species which have been in Iran and Tourani and merely seen in North Zagros (Sardasht in West Azerbaijan province, Baneh and Marivan in Kordestan province). The West Azarbayejan with 69% distributional area of this species, it is very important (Maroofi, 2000). The current study is to recognize and manage vegetation of this region to protect, restore and progress of plant associations of Quercus libani and covers the following major goals.

Discriminating and dividing plant associations and sub-associations based on Braun-Blanquet method to gain detailed information about vegetation progress in Quercus libani’s site.

Quantity analysis of relationships between these associations and environmental factors, topography and common factors of soil chemistry by means of multiple-discriminant analysis.

MATERIALS AND METHODS

The study area: The study area is located in North West of Iran in West Azerbaijan; between (45E and 16’ and 52’’) and (45E and 29’ and 58’’) Eastern longitude and (36° and 9’ and 45’’) and (36° and 25’ and 45’’) Northern latitude (Fig. 1). The considered study site covers an area of 320 ha. The altitude of the study area is from 1400 to 1950 m above sea level. The slope in the area differs from 25 to 60% and most of mountain peaks are made of alkaline and andesite. Distribution of vegetation types can be divided into two major types in the entire area: Quercus libani type in the northern side and Quercus brantii Lindl. type in the southern side at importance value idex of : 146.3 and 160.3 accordingly (Basiri, 2003).

Methods of vegetation sampling: The study area was measured by the method of preferential sampling (Botta-Dukat et al., 2007) in 2007. First, plant formations were distinguished based on physiognomy and then by means of floristic standard, the vegetation type was carefully selected and then in each unit, 56 releves were picked. Releves with an area of 256 3 were found suitable. Species and Abundance were considered as measuring standards for vegetation (Okland, 1990). In this method, abundance dada was converted into Braun-Blanquet scale (Braun-Blanquet, 1932).

Method of sampling from soil and factors of topography: The sampling was performed in all releves at the depth from 0 to 20 cm; that is, a sample was taken from the entire thickness of 20 cm of the soil (Robertson et al., 1999). Some of the most important chemical and physical variables such as pH, EC at3, organic materials (%), nitrogen (%), C/N, phosphorus (mg kg-1), potassium (mg kg-1), calcium (mg kg-1), magnesium (mg kg-1), iron (mg kg-1), manganese (mg kg-1), copper (mg kg-1) and soil content were measured. In each releve, topography variables of the altitude (m) and aspect were converted by means of Beers et al. (1966). The percentage of the slope, the slope position and slope-aspect, were applied by means of formula of Brosfske et al. (2001), landform index, (McNab, 1993) and Terrain shape index (McNab, 1989).

The method of vegetation data analysis: To discriminate plant association, Anaphyto Ver.95 was used (Briane, 1995). In this software, first AFC ordination (Analyse Factoriell des Correspondance) was used and it resulted in 5 axes of coordinates for releve and species. For the purpose of clear division of groups, CAH classification (Classification Ascendant Hierarchique) was used. To discriminate subgroups, Partial Analysis was performed. In this system, after discrimination of main groups, each group was individually analyzed for the second time. This phase continues until no other division of groups is possible. Based on the resulted groups, first, the raw table and then synthetic table were formatted and releve and species in them were arranged based on previous analysis (CAH and AFC) and constancy coefficient and eventually, the final phytosociological table was drawn up based on professional knowledge of botany and ecology by introducing characteristic species and transgrasive character species and association and subassociation were identified according to naming regulations in Phytosociology (Barkman et al., 1986).


Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Fig. 1: Situation of the study area

Multiple discriminant analysis method: To discover the relationships between environmental factors and plant association, multiple discriminant analysis method was applied. To study the power of environmental variables in discrimination of plant groups, One-way ANOVA test was used. After performing the above hypothesis and One-way ANOVA test, a composition of the environmental variables which have the least collinearity and the most Hit ratio were selected for multiple discriminant analysis. Based on Johnson (1998), the Stepwise method was used for determining the discriminant model. In this method, the best effective independent variables in discrimination and classification or prediction of group membership are recognized. After calculating the function of discrimination, Wilks lambda statistic was used to test the significant level of functions (Hair et al., 1995). To calculate the power of discriminant function, the classification matrices were used. The matrix presents the Hit ratio which is equal to the R-square coefficient in multiple regressions. The Hit ratio was approved by benefiting from the proportional by chance accuracy rate. If the Hit ratio is 25% more than the proportional by chance accuracy rate, it is acceptable. The Press'sQ statistic was applied to test the predictive accuracy of discriminant functions. By comparing the measured Q with the quantity of chi-square for the degree of freedom on a special error level, if the measured Q is more than crisis ratio of Chi-square, the predictive accuracy is statistically approved (Hair et al., 1995).

RESULTS

Results of AFC ordination: The result of AFC ordination for releve on axis of multiple coordinates indicates that the studied releve, especially those on axis (1 and 2) discriminate 3 major groups: group 1, 2 and 3 (Fig. 2). Axis 1 indicates 39.3%, axis 2 shows 24.8% of the total variances. The reason of discriminating these three groups, as the species in releve indicates, is the effective ecological factors.


Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Fig. 2: Ordination of releve for axes 1 and 2 (-: group1 Quercetum brantii association, ^: group2 Quercetum libani association, +: group3 Thalictro sultanabadensi-Quersetum libani- acerotosum cinerascens subassociation)

Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Fig. 3: Ordination of species for axes 1 and 2 (TSQB: Trifolio stellati-Quercetum brantii, PAQB: Pistacio atlanticae-Quercetum brantii, VMQB: Violo modestue-Quercetum brantii, TCQB: Trifolio campestri-Quercetum brantii, QB: Quercetum brantii, TSQL: Thalictro sultanabadensi-Quercetum libani, QLAC: Quercetum libani-acerotosum cinerascens, QBQL: Quercus boissieri-Quercetum libani, QL: Quercetum libani)

Considering axis of species and coordinating it with axis of releve, it is understood that species such as Pistacia atlantica, Quercus brantii and Guandelia tournifortii in group 1 and species such as Quercus libani, Quercus infectoria and Euphorbia denticulata in group 2 with different ecological features are located next to each other and it is resulted by the existence of smaller groups in these two major groups. Axis 1 and 2 with the highest eigenvalue was used for achieving the results. Based on axis 1, groups 1 and 2 are discriminated with 13.088 eigenvalue and based on axis 2, group 3 is discriminated from group 2 with 8.272 eigenvalue. Group 3 is not divisible to smaller groups (Fig. 3). To discriminate subgroups in groups 1 and 2, each of the groups were individually studied in details. The results of the first partial analysis indicate that there are 5 subgroups in group 1. Axis 1 indicates 32.8%, axis 2 shows 29.1% of the total variances. Axis 1 and 2 with the highest eigenvalue was used for achieving the results. Based on axis 1, subgroups 1 and 2 are discriminated with 10.2 eigenvalue and based on axis 2, subgroups 3,4 and 5 is discriminated from group 1 with 6.42 eigenvalue (Fig. 4). The results of partial analysis in major group 2, 3 subgroups are discriminated. Axis 1 indicates 27.5%, axis 2 shows 22.6% of the total variances. Axis 1 indicates 25.9%, axis 2 shows 20.8% of the total variances. Axis 1 and 2 with the highest eigenvalue was used for achieving the results. Based on axis 1, subgroups 1 and 3 are discriminated with 8.2 eigenvalue and based on axis 2, subgroups 2 is discriminated from group 2 with 6.89 eigenvalue (Fig. 5).

Results of CAH classification: Analysis of classification of ascending hierarchy for releve and species indicates adaptation of discriminated groups with discriminated groups in AFC ordination (Fig. 6).

Dendrogram of CAH classification for species was very long thus relinquished it.

Results of phytosociological table: Synthetic table of Phytosociology was made according to data obtained from the two above methods (AFC, CAH). In the table, the ordination of releve and species has the same hierarchy as CAH diagrams. A few changes were made in the rows and columns of the final table based on the data obtained in AFC ordination, environmental knowledge and available resources. The Phytosociological table was drawn up based on falling ordination of abundance coefficients B overcome of species in either one of plant groups and also falling hierarchy of species considering ratio of presence (Table 1). After discriminating syntaxons in the shape of association and sub-association and naming them, the growing units were introduced with companion species based on characteristic species.

Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Fig. 4: Ordination of releve in partial analysis of axes 1 and 2 for group1>Quercetum brantii association’ by eliminating groups 2 and 3:(-: Subgroup1: Trifolio stellati-Quercetum brantii, *: Subgroup2: Pistacio atlanticae-Quercetum brantii, +:Subgroup3: Violo modestue-Quercetum brantii, Λ: Subgroup4: Trifolio campestri-Quercetum brantii, /: Subgroup5: Quercetum brantii)

Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Fig. 5: Ordination of releve in partial analysis of axes 1 and 2 for group2 Quercetum libani association’ by eliminating groups 1 and 3 (+: Subgroup1: Thalictro sultanabadensi-Quersetum libani-acerotosum cinerascens, -: Subgroup 2: Querco boissieri-Quercetum libani and /: Subgroup3: Quercetum libani)

Table 1: Phytosociological table of sardasht district (West Azerbaijan)
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran

Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Fig. 6: Dendrogram of CAH classification for releve

Table 2: Statistical results for variables in discriminant function
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran

Table 3: Statistical results for discriminant functions
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran

Results of multiple discriminant analysis in regard to plant association:
Major analysis for 3 groups: According to the result of plant association analysis, first 3 groups (of association) were discriminated. Based on Table 2, variables of pH, landform index, Terrain shape index and aspect were placed in discriminant function in order for importance in group discrimination and all of them were placed on the significant level of 1%.

The two discriminant functions which were the outcome of the four above variables both were significant. The first function which was formed based on variables of pH and aspect indicated canonical correlation of 79%. This function allocated 77.6% of the aforementioned variables of the two functions. The second function which was formed based on variables of landform index and terrain shape index, indicated 60% canonical correlation. This function allocated 22.4% of the aforementioned variance by the two functions (Table 3).

Correlation of variables entered into the model with each of the functions showed that pH and aspect are significant with function 1. Also; landform and terrain shape indices are significant with function 2. pH and aspect variables were more effective in distinguishing associations (Table 4).

This analysis proves that discriminant functions can be produced by means of 4 environmental variables and generally, these functions indicate 87.7% predictive accuracy in classification of variables; that is, based on environmental variables, about 87.7% of 3 classified groups are accurately classified.


Table 4: Structure matrix between environmental variates and discriminant functions
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
*Indicates significant correlation at level of 0.01. (ns) Indicates non-significant at level of 0.05

Table 5: Results of One-way ANOVA for variables in discriminant functions model
Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran

The predictive accuracy was proved in Press'Q statistic (Q = 66.4 and p<0.01). Cohen's Kappa standard was applied for reliability of classification. Measuring Kappa of 72.4% and its significant level (p<0.01) indicates that the classification was performed based on the method of Phytosociology and it is in discriminant analysis.

The results of One-way ANOVA for the above 4 environmental variables indicates that there is a difference between 3 groups in significant level of 1% (p<0.01) (Table 5).

Results of Duncan test for pH showed that the Quercetum brantii association was more significant than other associations (Fig. 7a). Results of Duncan test for Terrain shape index and landform index, showed that the Talictro sultanabadensi-Quercetum libani-acerotosum cinerascens association was more significant than other associations (Fig. 7b, c). Results of Duncan test for aspect showed that the Quercetum brantii association was more significant than other associations (Fig. 7d).

Partial analysis for group 1: To gain smaller groups, partial analysis was used, after eliminating group 2 and 3 in Fig. 2 and 3, the partial analysis was performed for group 1 and totally 5 subgroups were discriminated. In multiple discriminant analysis, no environmental variables played a role in discriminating these 5 subgroups.


Image for - Phytosociological Study in Quercus libani Oliv.’s Site by Analyzing Environmental Factors in West Azerbaijan, Iran
Fig. 7: Bar chart of environmental variables in discriminant functions for 3 major groups (the written numbers on columns shows mean and standard deviation), (a) pH variable, (b) terrain shape index variable, (c) landform index variable and (d) aspect variable

Partial analysis for group 2: By eliminating group1, 3 subgroups were discriminated in group2 (Fig. 5). In multiple discriminant analysis, no environmental variables played a role in discriminating these 3 subgroups.

Description of association and subassociation
The association (I) (subgroup 1): Trifolio stellati-Quercetum brantii.

Characteristic species include: Trifolium stellatum, Ceratocephalus testiculatus, Anemone coronaria, Ornithogalum cuspidatum, Teucrium polium, Muscari caucasicum, Callipeltis cucularis.

The association (II) (subgroup 2): Pistacio atlanticae-Quercetum brantii.

Characteristic species include: Pistacia atlantica.

The association (III) (subgroup 3): Violo modestae-Quercetum brantii.

Characteristic species include: Viola modesta

The association (IV) (subgroup 4): Trifolio campestri-Quercetum brantii.

Characteristic species include: Trifolium campestre.

The association (V) (subgroup 5): Quercetum brantii

Characteristic species include: Quercus brantii, Anthemis hassknechtii, Gundelia tournifortii, Alkea kurdica, Colchicum speciosum, Picnomon acarna, Smyrnium cordifolium, Euphorbia azerbajdzhanica, Trifolium dasyurum, Hordeum bulbosum, Bryonia aspera, Aristolochia bottae, Serratula cerinthifolia, Bryonia aspera.

The association (VI) (subgroup 1): Thalictro sultanabadensi-Quercetum libani.

Characteristic species include: Thalictrum sultanabadense, Astragalus piranshahricus, Campanula involucrata, Tragapogon gramifolius, Sonchus asper subsp.glaucescens, Hesperis kurdica, Allium scabricapum, Cotoneaster nummularioides, Agropyrum panormitanum, Euphorbia denticulate, Arum conophalloides, Fibigia macrocarpa, Ranunculus cicutarius.

The subassociation (I): Thalictro sultanabadensi-Quersetum libani- acerotosum cinerascens.

Characteristic species include: Acer monspesulanum subsp.cinerascens, Scrophularia nervosa subsp.nervosa, Smyrniopsis aucheri, Rosularia sempervivoides, Fritialaria persica, Astragalus cariolobus.

The association (VII) (subgroup 2): Querco boissieri-Quercetum libani.

Characteristic species include: Quercus infectoria subsp.boissieri, Rumex conglomeratus, Rhaponticum insigne.

The association (VIII) (subgroup 3): Quercetum libani.

Characteristic species include: Quercus libani, Chaerophyllum macrospermum, Dactylis glomerata subsp. glomerata, Centaurea behen, Veronica polita, Viola odorata, Lamium album subsp. Album, Aethionema memberanaceum, Silene chlorifolia, Euphorbia condylocarpa, Cruciata taurica, Symphytum kurdicum, Lepyrodiclis holosteoides, Ferula orientalis, Mentha longifolia, Astragalus lovensis, Astragalus compactus, Dactylorhiza umberosa, Astragalus tortuosus, Comperia comperiana, Ornithogalum oligophyllum, Steptorhamphus persica and Melica persica subsp.persica.

Transgrasive and characteristic species and class: Galium aparine, Poa bulbosa subsp. vivipara, Geranium tuberosum subsp. micranthum, Ranunculus arvensis, Vicia variabilis, Alyssum linifolium subsp. linifolium, Bunium elegans, Ziziphora capitata subsp. Capitata, Arabis caucasica subsp. caucasica, Bellevalia longistyla, Ficaria kochii, Achillea millefolium subsp. millefolium, Tragopogon retriculatus, Bromus tectorum var. tectorum, Crepis sancta subsp. sancta, Eremopoa persica var. persica, Crataegus pontica, Cerastium inflatum, Salvia suffruticosa, Onosma sericeum, Valerianella carinata, Pyrus syriaca, Trifolium pilulare, Milium pedicellare, Chardiana orientalis, Echinops orientalis, Gentiana olivieri, Inula thapsoides, Cerasus microcarpa, Falcaria vulgaris, Ranunculus pinardi, Phlomis olivieri, Allium eriophyllum var. eriophyllum, Lonicera nummularifolia, Helianthemum ledifolium, Holosteum umbellatum, Hypericum scabrum, Senecio vernalis, Bongardia chrysogonum, Lactuca serriola, Geranium rotundifolium, Silene ampullta, Chaerophyllum macropodon, Eremostachys lacinata, Taraxacum montanum, Echium italicum var. italicum, Lallemantia peltata, Pterocephalus plumosus, Nasturtium officinale, Medicago regidula, Ferulago stellata, Eremorus spectabilis subsp. spectabilis, Orobanche aegyptica, Papaver dubium, Rosa canina, Adonis sp., Trifolium arvense var. arvense, Lens orientalis, Lens cyanea, Vicia narbonensis var. narbonensis, Torilis leptophylla, Gladiolus kotschyanus, Onopordon acanthium, Lathyrus cicera, Scandix pectin-veneris, Sorbus persica, Prangus ferulacea, Chamaegron oligocephalus, Onosma microcarpum, Conringia perfoliata, Alopecurus myosuroides var. myosuroides.

DISCUSSION

Kurdo-Zagrosian site in Iran with open forest and shrub lands is part of a mountain range at latitude of 4000 m parallel to Zagros (Kordestan and some parts of Azerbaijan) (Zohary, 1973). Flore of this area has been studied by many researchers (Guest, 1953; Pabot, 1960). Zohary (1973) considers the vegetation of this area of Quercetea brantii type while Mobayyen and Djavanshir (1971) consider these societies of Quercetea persicae type and have introduced two orders of Quercetalia infectoria and Quercetalia persicae. The first order includes various species of Quercus brantii Lindl. and characteristic species of this order is Quercus infectoria which covers the area from the North of Kermanshah to Oroumiyeh forests; the second order covers the area from Kermanshah to around Shiraz and its main species is Quercus brantii var. persicae. Quercus infectoria is never seen in this order. The first order indicates the Mediterranean and relatively mild climate and covers most of forests in the west of Iran and in the areas where the sunshine is at its most, it covers the foot of mountain toward the north where it is cooler and more humid while the second order is placed at the low longitude and includes species resistive to dry climate and it is seen in the southern and southwestern terrains where semi-dry climate joins the subtropical regions. The soil in the areas of the first order is very much alkaline while the soil in the areas of the second order is made of sandy-clay soil. Some of the reported forest associations in these areas include the following:

Quercetum libani, Quercetum infectoria, Quercetum brantii, Querceto-pistacietum (Sabeti, 1976; Djavanshir, 1999; Fattahi, 2000; Asri and Mehrnia, 2001; Browicz, 1994; Zohary, 1973).

Based on the results achieved in this research, the gained 8 associations are included in the class of Quercetea persicae and order of Quercetalia persicae; except for 3 associations: Quercetum libani, Quercetum infectoria and Quercetum brantii which have been reported in different sources, in other cases because of shortage of information, they are considered documentary merely based on real observations in the nature, phytosociologists and unpublished studies. Based on the final table of phytosociology, characteristic species have been introduced for each association; it shall be taken into consideration that characteristic species of alliance based on observations in the areas and phytosociologists and until comprehensive and accurate information on all areas of Zagros have not been obtained in this regard, no certain claim can be made. Meanwhile based on the above reasons, some of the species such as Pyrus syriaca and Crataegus pontica which are characteristic order and class and accompanied with such species so that in the future comprehensive studies in these areas, comments can be given on them.

The initial analysis of major groups (Fig. 2, 3) indicates that 82.4% of the releves are correctly classified; that is, the releves belong to those groups that existed in the phytosociological classification analysis. Variables which were significant at 5% error level in this analysis include: pH, landform index, terrain shape index and aspect. pH in group 2 (Quercetum libani) and groupe 3 (Thalictro sultanabadensi-Quersetum libani- acerotsum cinerascens) indicated significant difference in comparison with group 1 (Quercetum brantii) (p<0.01). Brosfske et al. (2001) and Gough (2001) have considered acidity as an important factor in dispersion and distribution of associations. Based on the studies, Quercetum libani exists on soils with pH of nearly acid (Maroofi, 2000; Varol and Tatli, 2001; Abella and Springer, 2008) and it is true according to the achieved results in this research. Group 1 exists on soil with pH of nearly alkaline and the presented reports indicate the result (Talebi et al., 2006).

The landform index in group 3 (Thalictro sultanabadensi-Quersetum libani-acerotosum cinerascens) indicated significant difference in comparison with two other groups (p<0.01). The much landform index for group 3 (0.34), indicates the position of this group near the edge while the quantity of this index for other two groups (0.27 for group 1 and 0.25 for group 2) indicates the position of these two groups at the median of altitude. Several studies have indicated that the effect of landform index on distinguishing of vegetation (Odom and McNab, 2000; McNab et al., 1999; Ford et al., 2002; Abella, 2003). The studies by Assareh in 2005 indicated the existence of tree characteristic species of group 3; that is Acer monspessulanum subsp. Cinerascens in mountainous areas and edges. The tree characteristic species of group 1; that is, Quercus brantii Lindl. exists in all types of landform shapes including valleys, slope and edges, but tree characteristic species of group 2 (Quercus libani Oliv.) are reported to be available on reported middle slope and the results accords with the result of this research (Assareh, 2005).

Terrain shape index indicates a significant difference between group 2 (Quercetum libani) and group3 (Thalictro sultanabadensi-Quersetum libani- acerotosum cinerascens) (p<0.01). Several studies are on the effect of this index in distinguishing of associations (McNab, 1989; McNab et al, 1999; Abella, 2003). The (+) sign in the quantity of this index for group 3 (+0.068) indicates convex site of group 3. The subassociation is located upper slope (on the edge); the landform upper slope is usually concave (Barnes et al., 1998) and accords with the achieved results. The (-) sign in the quantity of this index for group 2 (-0.016) indicates concave site of group 2. Concave shape in ecological point of view indicates concentration of moisture and nutrients in the site (Barnes et al., 1998); on the other hand, this association requires such a desired conditions (Fattahi, 2000; Maroofi, 2000). The quantity of this index for group 1 (Quercetum brantii) is (+0.011) that has no significant difference with group 2 and also this association has a great ecological endurance (Fattahi, 2000) and can exist in undesirable conditions as well. Adaptation of oak associations with moisture gradient has been identified in several studies (Seng and Deil, 1999).

The aspect in group 1 (Quercetum brantii) indicated a significant difference from two other groups (p<0.01). Several studies have been done about the effect of aspect on separation of plant associations (McNab et al., 1999; McEvan et al., 2005; Zhang et al., 2006; Collins and Carson, 2004). The existence of Quercetum brantii in the southern direction and Quercetum libani in the northern direction has been reported in many of the studies (Fattahi, 2000; Sagheb-Talebi et al., 2005; Zohary, 1973). group 3 is mostly seen in the humid regions, valleys and stony grounds in the northern and Northeastern terrains (Zohary, 1973; Assareh, 2005).

Partial analysis of vegetation in group 1 (Quercetum brantii) proved the existence of subgroups (Fig. 4). The partial analysis on group 1 (Quercetum brantii) resulted into 5 subgroups. But due to the destructive condition, open condition of the forest and overgrazing of cattle on this association, no environmental variables indicated having a role in the taking a part.

The partial analysis on group 2 (Quercetum libani) proved the existence of 3 subgroups. Multiple discriminant analysis indicated effectiveness of altitude variable and the C/N in this distinguishing. The studies in the site of Zagros indicated the effectiveness of altitude and C/N in Quercetum libani association's separation (Heydari and Mahdavi, 2009; Jazerehei and Ebrahimirastaghi, 2003). The existence of three associations of Quercus boissieri-Quercetum libani, Quercetum libani and Thalictro sultanabadensi-Quercetum libani has been specified in group 2. The association of Quercus boissieri-Quercetum libani has been severally reported to exist at lower altitude in comparison with Quercetum libani association (Browicz, 1994; Maroofi, 2000; Assareh, 2005). Thalictro sultanabadensi-Quercetum libani with its characteristic species such as Hesperis kurdica (1150-2200 m), Fibijia macrocarpa (1000-2400 m), Campanula inolucrata (2300-3100 m), Cotoneaster nummularioides (800-2800m) and Agropyron panormitanum (550-1625 m) (Nazarian et al., 2004; Onal and Behset, 2007; Malekmohammadi et al., 2007; Gucel et al., 2008) indicate the existence of species of this association at different altitudes.

The existence of Quercetum libani association at middle altitude (mean altitude = 1650 m) with slope at mean of 45% which makes it impossible for cattle to climb up, causes high density of forest (in most of places of this association, 90% cover has been seen) and ecological needs of Quercus libani including high moisture of soil and nutritious soil (Maroofi, 2000; Assareh, 2005; Zohary, 1973; Heydari and Mahdavi, 2009), all are because of significant of C/N in this association in comparison with other subgroups. Generally, Christine and McCarthy (2005) stated that C/N has correlation with distribution of herbaceous species. Based on researches by Oner and Oflas (1977), the plant association (Quercus boissieri-Quercetum libani) grows on fertile sites and high water table. In this area, because of growth of this association at low altitude (mean altitude =1590 m), cattle and people living there have more access to it and it caused knocking of the soil, reducing of organic materials and decreasing of C/N and finally, it has led to significant with Quercetum libani (Tabatabai and Ghasriani, 1992).

CONCLUSIONS

Based on AFC and CAH methods, experiences and literature review, 8 associations and 1 sub-association were achieved including: Trifolio stellati-Quercetum brantii, Pistacio atlanticae-Quercetum brantii, Violo modestue-Quercetum brantii, Trifolio campestri-Quercetum brantii, Quercetum brantii, Thalictro sultanabadensi-Quercetum libani, Quercetum libani-acerotosum cinerascens, Quercos boissieri-Quercetum libani and Quercetum libani. These plant associations belong to Quercetea persicae class and Quercetalia persicae order.

On the bases of discriminant analysis, the effective and significant environmental factors in division of plant associations include respectively: pH, landform index, Terrain shape index and aspect.

ACKNOWLEDGMENT

Generally, ecology studies are very hard and in temporal and spatial point of view, they require a great effort; therefore, such researches can not be made by one person and in any phase of performance, guidance and cooperation of specialists, scientists and relevant authorities in different centers appear as great assistance.

As a result, I find it necessary to express sincere gratitude and thanks to all those who have provided me with their help and dedication.

REFERENCES
1:  Abella, S.R. and J.D. Springer, 2008. Canopy-tree influences along a soil parent material gradient in Pinus ponderosa-quercus gambelii forests, northern Arizona. J. Torrey Bot. Soc., 135: 26-36.
Direct Link  |  

2:  Abella, S.R., 2003. Quantifying ecosystem geomorphology of the southern Appalachian mountains. J. Phys. Geogr., 24: 488-501.
Direct Link  |  

3:  Guisan, A. and N.E. Zimmermann, 2000. Predictive habitat distribution models in ecology. Ecol. Model., 135: 147-186.
CrossRef  |  Direct Link  |  

4:  Barkman, J.J., J. Moravec and T.S. Rauschert, 1986. Code of phytosociological nomenclature. Vegetation, 67: 145-195.

5:  Assareh, M., 2005. Plant Variety in Iran. Publication of Research Institute of Forests and Pastures, Belem, Para, Brasil.

6:  Barnes, B.V., D.R. Zak and S.H. Spurr, 1998. Forest Ecology. 4th Edn., John Wiley and Sons Inc., New York, ISBN: 9780471308225, pp: 774.

7:  Barbour, M.G., J.H. Burk, W.D. Pitts, F.S. Gilliam and M.W. Schwartz, 1999. Terrestrial Plant Ecology. 3rd Edn., Wesley Longman Inc., Boston, MA, USA.

8:  Basiri, R., 2003. Identification and analysis of forest types regarding aspects in Ghamishleh. Marivan Res. Constr. J., 60: 50-68.

9:  Beers, T.W., P.E. Dress and L.C. Wensel, 1966. Aspect transformation in site productivity research. J. For., 80: 493-498.

10:  Botta-Dukat, Z., E. Kovacs-Lang, T. Redei, M. Kertesz and and J. Garadnai, 2007. Statistical and biological consequences of preferential sampling in phytosociology: Theorertical considerations and case study. Folia Geobotanica, 42: 141-152.
CrossRef  |  Direct Link  |  

11:  Braun-Blanquet, J., 1932. Plant Sociology: The Study of Plant Communities. 1st Edn., McGraw Hill Book Co. Inc., New York, USA., Pages: 439.

12:  Briane, J., 1995. A Software for Data-processing in Phytosociology, Anaphyto, Labratorie de Systeatique and Ecologie Vegetales. Universities Orsay, Paris.

13:  Brosfske, K.D., J. Chen and T.R. Crow, 2001. Understory vegetation and site factors: Implications for a managed Wisconsin landscape. For. Ecol. Manage., 146: 75-87.
Direct Link  |  

14:  Christine, J.S. and B.C. McCarthy, 2005. Relationship of understory diversity to soil nitrogen, topographic variation and stand age in an eastern Oak forest USA. For. Ecol. Manage., 217: 229-243.
Direct Link  |  

15:  Collins, R.J. and W.P. Carson, 2004. The effects of environment and life stage on Quercus abundance in the eastern deciduous forest, USA: Are sapling densities most responsive to environmental gradients?. J. For. Ecol. Manage., 201: 241-258.
Direct Link  |  

16:  Comstock, J.P. and J.R. Ehleringer, 1992. Plant edaptation in the great basin and colorado plateau. Western North Am. Natur., 52: 195-215.
Direct Link  |  

17:  Cook, J.G. and L.L. Irwin, 1992. Climate-vegetation relationships between the great plains and great basin. Am. Midl. Nat., 127: 316-326.
Direct Link  |  

18:  Dengler, J., C. Berg and F. Jansen, 2005. New ideas for modern phytosociological monographs. J. Ann. Bot., 5: 51-66.
Direct Link  |  

19:  Djavanshir, K., 1999. History of Natural Resources Sciences of Iran. Research Organization Publication, Education and Extension of Agriculture, Washington, DC, USA.

20:  Browicz, K., 1994. Chorology of Trees and Shrubs in South-West Asia. Vol. 10, Bogucki Publishers, Poznan.

21:  Fattahi, M., 2000. Management of Forests in Zagros (Studied area: Darbadam Forests in Kermanshah). Vol. 1, Publication of Forests and Pastures Research Institute, Jabalpur, Madhya Pradesh, India.

22:  Ford, W.M., M.A. Menzel and R.H. Odom, 2002. Elavation, aspect and cove size effects on southern appalachian salamanders. J. Southern Nat., 1: 315-324.
Direct Link  |  

23:  Gough, L., G.R. Shaver, J. Carroll, D.L. Royer and J.A. Laundre, 2000. Vascular plant species richness in Alaskan arctic tundra: The importance of soil pH. J. Ecol., 88: 54-66.
CrossRef  |  Direct Link  |  

24:  Gucel, S., K. Ozkan, S. Celik, E. Yucel and M. Ozturk, 2008. An overview of the geobotanical structure of turkish Pinus sylvestris and Carpinus betulus forests. Pak. J. Bot., 40: 1497-1520.
Direct Link  |  

25:  Guest, E.R., 1953. The rustam herbarium, Iraq: Part VI. General and ecological account. Kew Bull., 8: 383-404.
Direct Link  |  

26:  Hair, J.F., R.E. Anderson, R.L. Tatham and W.C. Black, 1995. Multivariate Data Analysis. 4th Edn., Prentice Hall, Upper Saddle River, New Jersey, USA.

27:  Hee, M.Z., J.G. Zengh, X.R. Li and Y.L. Qian, 2007. Environmental factors affecting vegetation composition in the Alxa Plateau China. J. Arid Environ., 69: 473-489.
CrossRef  |  

28:  Heydari, M. and A. Mahdavi, 2009. The survey of plant species diversity and richness between ecological species groups (Zagros, Ecosystem, Ilam). J. Applied Sci., 9: 745-751.
Direct Link  |  

29:  Jazerehei, M.H. and M. Ebrahimirastaghi, 2003. Zagros Silviculture. 1st Edn., University of Tehran Press, Tehran, Iran pp: 560 (In Persian).

30:  Johnson, D.E., 1998. Applied Multivariate Methods for Data Analysts. Higher Education Press, USA., pp: 319-396.

31:  Kent, M. and P. Coker, 1992. Vegetation Description and Analysis (a Practical Approach). John Wiley and Sons Publication, New York.

32:  Malekmohammadi, L., A. Mahmoudzadeh and A. Hassanzadeh, 2007. Ecological study in forest reserve of Ghasemloo (Shohada) Valley and it’s adjacent areas, Urmia-Iran. J. Biol. Sci., 10: 3254-3265.
CrossRef  |  PubMed  |  Direct Link  |  

33:  Maroofi, H., 2000. Study of requirements of the site of Quercus libani in Kordestan province. Master Thesis, Imam Khomeini Higher Education Center.

34:  McEvan, R.W., R.N. Muller and B.C. McCarthy, 2005. Vegetation-environment relationships among woody species in four canopy-layers in an old-growth mixed mesophytic forest. J. Castanea, 70: 32-46.
Direct Link  |  

35:  McNab, W.H., 1989. Terrain shape index: Quantifying effects of minor landforms on tree height. For. Sci., 35: 91-104.
Direct Link  |  

36:  McNab, W.H., 1993. A topographic index to quantifying the effect of mesoscale landform on site productivity. Can. J. For. Res., 23: 1100-1107.
Direct Link  |  

37:  McNab, W.H., S.A. Browning, S.A. Simon and P.E. Fouts, 1999. An unconventional approach to ecosystem unit classification in Western North Carolina, USA. For. Ecol. Manage., 114: 405-420.
CrossRef  |  

38:  Mobayyen, S. and K. Djavanshir, 1971. Yasooj Forests. Publication of Forestry Faculty, Tehran University, Tehran.

39:  Abd El-Ghani, M.M. and W.M. Amer, 2003. Soil-vegetation relationships in a coastal desert plain of Southern Sinai. Egypt J. Arid Environ., 55: 607-628.
CrossRef  |  Direct Link  |  

40:  Mueller-Dombois, D. and H. Ellenberg, 1974. Aims and Methods of Vegetation Ecology. 1st Edn., John Wiley and Sons, New York, USA., ISBN-13: 978-0471622901, Pages: 570.

41:  Nazarian, H., A. Ghahreman, M. Atri and M. Assadi, 2004. Ecological factors affecting parts of vegetation in North Iran (Elika and Duna watersheds) by ploying eco-phytosociological method. Pak. J. Bot., 36: 41-64.
Direct Link  |  

42:  Odom Jr., R.H. and W.H. McNab, 2000. Using digital terrain modeling to predict ecological types in the Balsam Mountains of western North Carolina. USDA Forest Service Research Note SRS-8. pp: 12. http://www.treesearch.fs.fed.us/pubs/viewpub.jsp?index=1769.

43:  Okland, R.H., 1990. Sommerfeltia Supplement 1 (Vegetation Ecology: Theory, Methods and Applications with Reference to Fennoscandia). Botanical Garden and Museum, University of Oslo, Norway.

44:  Onal, M. and L. Behset, 2007. Flora of Pirresit mountain (van, Turkey). Turk. J. Bot., 31: 193-223.

45:  Oner, M. and S. Oflas, 1977. Plant succession on the Kula volcano in Turkey. Vegetatio, 34: 55-62.
CrossRef  |  Direct Link  |  

46:  Pabot, H., 1960. Rapport au Khuzistan developpement service sur la vegetation naturelle et son ecologie dans les bassins versants du Khuzistan, Io maps and diagrams. Tehran-Ahwaz (Mimeogr).

47:  Pignatti, S., E. Dominici and S. Pietrosanti, 1997. European vegetation survey-from the methodological discussion to the first approximation. Ann. Bot., 45: 5-16.

48:  Robertson, G.P., D.C. Coleman, C.S. Bledsoe and P. Sollins, 1999. Standard Soil Methods for Long-Term Ecological Research. Oxford University Press, NewYork, USA.

49:  Sabeti, H., 1976. Forests, Trees and Shrubs of Iran. Agriculture and Natural Resources Research Organization Press, Iran, Pages: 874.

50:  Sagheb-Talebi, K.H., T. Sajedi and F. Yazdian, 2005. A Look at Forests in Iran. Publication of Forests and Pastures Research Institute, Boulder, CO USA.

51:  Seng, M. and V. Deil, 1999. Forest vegetation types in the serra de monchique (portugal): Anthropogenic changes of oak forests. Silva-Lusitana (Portugal), 7: 71-92.
Direct Link  |  

52:  Solon, J., M. Degorski and E. Roo-Zielinska, 2007. Vegetation response to a topographical-soil gradient. Catena, 71: 309-320.
CrossRef  |  

53:  Talebi, M., K.H.S. Talebi and H.J. Goojani, 2006. Study of site requirement and some of quality and quantity characteristics of Quercus brantii Lindl in forests of Chahar Mahal Bakhtiari Province. Sci.-Res. Seasonally J. For. Spruce Res., 14: 67-79.

54:  Tabatabai, M. and F. Ghasriani, 1992. Natural Resources in Kordestan (Forests and Pastures). Publication of Cultural Office of ACRCE, The Netherlands.

55:  Varol, O. and A. Tatli, 2001. The vegetation of Cimen mountain (Kahramanmaraß). Turk. J. Bot., 25: 335-358.
Direct Link  |  

56:  Zhang, X., M. Wang, B. She and Y. Xiao, 2006. Quantitative classification and ordination of forest communities in Pangquangou National Nature Reserve. Acta Ecologica Sinica, 26: 754-761.
CrossRef  |  

57:  Zohary, M., 1973. Geobotanical Foundation of the Middle East. Vol. 1, Gustav Fisher Verlag, Stuttgart, New York.

58:  Asri, I. and M. Mehrnia, 2001. Study of plant associations in the central part of protected zone of Sefid Kooh. Iran Natl. Resourc. J., 4: 423-443, (In Persian).

©  2021 Science Alert. All Rights Reserved