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ORIGINAL ARTICLE
Plant species and communities assessment in
interaction with edaphic and topographic factors; an
ecological study of the mount Eelum District Swat,
Pakistan
Murad Khan a
, Shujaul Mulk Khan b,*, Muhammad Ilyas c
, Abdulaziz A. Alqarawi d
,
Zeeshan Ahmad b
, Elsayed Fathi Abd_Allah d,e,*
a
Department of Botany, Hazara University Mansehra, Pakistan
b
Department of Plant Sciences, Quaid-i-Azam University Islamabad, Pakistan
c
Department of Botany, Islamabad Model College for Boys G10/4 Islamabad, Pakistan
d
Department of Plant Production, College of Food & Agricultural Sciences, P.O. Box 2460, Riyadh 11451, Saudi Arabia
e
Seed Pathology Department, Plant Pathology Research Institute, ARC, Giza 12511, Egypt
Received 2 August 2016; revised 29 November 2016; accepted 30 November 2016
Available online 9 December 2016
KEYWORDS
Canonical Correspondence
Analysis (CCA);
Characteristic species;
CANOCO;
PC-ORD;
Eelum;
Plant communities;
Swat Pakistan
Abstract The current analyses of vegetation were aimed to study the different effects of environ-
mental variables and plant species and communities interaction to these variables, identified threats
to local vegetation and suggestion for remedial measures in the Mount Eelum, Swat, Pakistan. For
assessment of environmental variability quantitative ecological techniques were used through quad-
rats having sizes of 2 Â 2, 5 Â 5 and 10 Â 10 m2
for herbs, shrubs and trees respectively. Result of
the present study revealed 124 plant species in the study area. Canonical Correspondence Analysis
(CCA) was used to analyze the ecological gradient of vegetation. The environmental data and spe-
cies abundance were used in CANOCO software version 4.5. The presence absence data of plant
species were elaborated with Cluster and Two Way Cluster Analysis techniques using PC-ORD ver-
sion 5 to show different species composition that resulted in five plant communities. Findings indi-
cate that elevation, aspect and soil texture are the strongest variables that have significant effect on
* Corresponding authors at: Department of Plant Sciences, Quaid-i-Azam University Islamabad, Pakistan – 45320 (S.M. Khan). Department of
Plant Production, College of Food & Agricultural Sciences, P.O. Box 2460, Riyadh 11451, Saudi Arabia (E.F. Abd_Allah).
E-mail address: elsayed_22@yahoo.com (E.F. Abd_Allah).
Peer review under responsibility of King Saud University.
Production and hosting by Elsevier
Saudi Journal of Biological Sciences (2017) 24, 778–786
King Saud University
Saudi Journal of Biological Sciences
www.ksu.edu.sa
www.sciencedirect.com
http://dx.doi.org/10.1016/j.sjbs.2016.11.018
1319-562X Ó 2016 The Authors. Production and hosting by Elsevier B.V. on behalf of King Saud University.
This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).
species composition and distribution of various communities shown with P value 0.0500. It is rec-
ommended to protect and use sensibly whole of the Flora normally and rare species particularly in
the region.
Ó 2016 The Authors. Production and hosting by Elsevier B.V. on behalf of King Saud University. This is
an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).
1. Introduction
The study of plant communities is the best way to learn about
habit, habitat, niche and vegetation structure (Khan et al.,
2016a; Malik, 1986) as well as various interaction among the
plants in an ecosystem. Forest ecosystems in the world have
a history of fragmentation due to activities of human advance-
ment (Chabrerie et al., 2013). The deforestation mask the
greenery, created ecological disturbance, drastic change in soil
chemistry, physical weathering and denudation of rocks which
leading to floods and changed almost the natural structure of
vegetation. The important zone of ecological study is to deter-
mine the interaction between different biotic and abiotic com-
ponents of an ecosystem (Rahman et al., 2016; Tavili and
Jafari, 2009). Abiotic variations are well known characteristics
both in space and time which effect plant communities and
population. The plant communities highlight changes in
response to various factors not only related to its zone of ori-
gin but also to its ecology (Afzal et al., 2000). The most simply
interpretable sign of biological variation is species richness
which highlight by different environmental characters (Khan
et al., 2016b; Shrestha and Vetaas, 2009). Researchers study
several factors (abiotic and biotic) basically which interact in
community structure formation. These factors contribute to
comprehend distribution, composition and diversity of plant
species and communities (Brown, 1984). Variations in plant
species composition along altitude and latitude is well estab-
lishment phenomenon (Kitayama, 1992; Lieberman et al.,
1985; Shaheen et al., 2012) and one of the ultimate effect in
restricting plant species and communities types in mountain-
ous regions (Khan et al., 2011a). Furthermore soil is an envi-
ronmental factor that also determines plant growth which is
influenced by organisms, climate, topography, time and parent
material (Hoveizeh, 1997). Climate is affected by topography
such as slope, elevation and aspect, in addition to affect of
evapotranspiration and temperature that as a whole result rich
vegetation in the northern aspects as compared to southern
ones (Ordon˜ ez et al., 2009). Furthermore, the quantitative
analysis has a strong back ground and a lot of different field
scientist have contributed to use it (Shaheen and Shinwari,
2012). Quantitative measure updates the feature of vegetation
because of its obvious effects on all types of associated life to
vegetation communities. Ecologists use multivariate approach
for seeking and summarizing ecological set of plants data
regarding with environmental variables. The statistical study
of these data help in finding actual position of plant species
in the field (Curtis and McIntosh, 1950). The multivariate sta-
tistical analytical programs assists the ecologists to analyse the
effects of environmental variables on whole numbers of species
and to know structure in the data set (Anderson et al., 2006).
Canonical Correspondence Analysis (CCA) shows the
relationship amongst the species as linear combinations of
environmental variables graphically (Green, 1979). So this
technique interrelates with different types of reciprocal averag-
ing with multiple regression techniques together (Ter Braak,
1986, 1987). Canonical Correspondence Analysis (CCA) is a
type of direct gradient analyses which show the difference
among vegetation patterns under the influence of environmen-
tal variables (Al-Qarawi, 2011).
The purpose of present study is to attain realistic prototyp-
ical form of vegetation and its interaction due to location of
Eelum hills – a rich floristic zone, its distant peaks inaccessibil-
ity and harsh terrain evaluation. It has been planned to evalu-
ate vegetation variability in relation to environmental factors
through advanced analytical analyses (CCA, PC-ORD). It is
specially intended to quantify the vegetation of the region with
various edaphic and physiographic factors to get knowledge
about microclimate of each and every plant species. Particu-
larly, present research work carried to find out the indicator
species of diverse communities through multivariate analyses
and the anthropogenic activities as threat to local flora.
2. Materials and methods
The Swat has always remained self-sufficient in its natural and
agricultural resources (DiPietro et al., 1999). The mount
Eelum located on southern watershed of the Murghuzar Valley
in famous mountain range with altitude of 9273 feet (Altimeter
data). It belts a natural boundary between district Swat and
Buner. Agriculture is common practice in the outskirts of
Mount Eelum, with typical crops of maize (1069 ton), wheat
(3.5 metric ton), rice (2.5 ton), onion and Trifolium, while in
fruits, the area is dominated by plum, persimmon and pears.
The present study was carried out to find the Indicator species,
plant communities, species composition, distribution and
abundance with a special relation or interaction to edaphic fac-
tors and various threats to flora in the Eelum hills Swat, Pak-
istan. The quantitative ecological techniques (Quadrate
methods) were carried out for assessment of plant species
and environmental variability. The various transects were
placed from lower to higher elevations at regular interval of
100 m. Quadrates having sizes of 2 Â 2 m2
for herbs,
5 Â 5 m2
for shrubs and 10 Â 10 m2
for trees were placed ran-
domly at systematically established stations. For all quadrates
phytosociological attributes i.e., density, frequency, cover, rel-
ative density, relative frequency, relative cover and importance
values (IVs) were recorded. The plant specimens were col-
lected, tagged, and identified using flora of Pakistan and other
related literature and then deposited in the Herbarium of
Hazara University Mansehra, Pakistan (HUH).
2.1. Environmental data
The Altimeter was used to find elevation of each station,
transect as well as geographical coordinates i.e. latitude and
Plant species and communities assessment in interaction with edaphic and topographic factors 779
longitude. Aspect variation at each quadrat was observed from
sun rise and set using compass and different geographical
techniques.
2.2. Soil collection and analyses
The soil sampling tubes were used to collect the soil samples up
to a depth of 30 cm from each station. The samples were air
dried, grinded for composite sample, sieved through 2 mm
screen to remove the stone pieces and large root particles.
The soil analyses and physiochemical properties were assessed
in the soil science laboratory of Agriculture Research Institute
Tarnab, Peshawar. Soil texture, lime concentration, organic
matter concentration, phosphorous, potassium, sulfate con-
centration and pH were measured. Soil textures were deter-
mined by hydrometer (Koehler et al., 1984), pH was
determined by pH meter (Khan et al., 2012), for lime determi-
nation acid neutralization method was used (Thomas, 1982)
and standardized solution of FeSO4 and K2Cr2O7 were used
for the determination of soil organic matters (Nelson et al.,
1996). AB-DTPA extractable P and K was determined in sam-
ples through method described by (Soltanpour, 1991) and soil
texture was determined by hydrometer method (Koehler et al.,
1984), sulfate was determined using the procedure of (Belyea
and Lancaster, 1999).
2.3. Data analyses
The obtained data of five Transects and 124 quadrates
arranged in MS Excel for further analyses through Cluster
analysis and Two Way Cluster analysis based on presence
and absence value of plant species. The species data was
arranged in row and quadrates in column as per requirement
of PC-ORD version 5 software (Lepsˇ and Sˇ milauer, 2003).
CANOCO software version 4.5 was used to find the influence
of different environmental variables on species compositions
and community formation.
3. Results
A field research conducted in different seasons based on differ-
ent criteria, advance parameters and a statistical approaches is
explained theoretically and diagrammatically as under.
3.1. Species composition with special reference to altitudinal
range of Eelum hills
A total of 124 plant species, belonging to 52 families dis-
tributed over 25 Transects (372 quadrats) were collected from
Eelum hills, including 86 (70%) herbs, 22 (17%) shrubs and 16
(13%) are trees. The topmost leading families were Asteraceae
having 20 species followed by Lamiaceae having 13 Species
and Poaceae with 10 species individually (Table 1).
3.2. Abundant and less abundant species of the area
The abundance of plant species was assessed through Impor-
tance Values Index (IVI) that is explained in the following
sub headings.
3.3. Tree layer
In tree layer Pinus wallichiana, Quercus incana, Quercus baloot,
Cedrus deodara, Ficus palmata and Pyrus pashia were observed
mostly in tree layer of Eelum hills that show highest IVI. The
rare species includes Pistacia integerrima, Acer pentapomicum
and Prunus cornuta having minimum IVI in the region (Fig. 1).
3.4. Shrub layer
In shruby layer the most abundant species with high IVI are
Desmodium elegans, Zizyphus oxyphylla, Berberis lyceum, Sar-
cococca saligna, Datura stramonium and Hedera nepalensis.
Whereas Clematis orientalis, Indigofera heterantha, Justicea
adhatoda, Viburnum grandiflorum and Buddleja crispa was
recorded as rare plant species in region (Fig. 2).
Ficus racemosa
Melia azedarachta
Eucalyptus lanceolata
Pyrus pashia
Ficus palmata
Cedrus deodara
Quercus baloot
Quercus incana
Pinus wallichiana
Figure 1 The top 10 abundant tree species with high important
value index of the Eelum hills.
229.67
188.81
173.57
156.36
151.08
143.12
125.51121.99118.18 117.25
Desmodium elegans Zizyphus oxyphylla
Berberis lycium sarcococca saligna
Datura stramonium Hedera nepalensis
Dodonea viscosa Jasminium officinalis
Calotropis procera Rubus fruticosus
Figure 2 The top 10 most abundant shrubs with high important
value index in the region.
780 M. Khan et al.
3.5. Herb layer
The Sorghum helepense, Solanum xanthocarpum, Stachys
parviflora, Hypericum perforatum, Heliotropium strigosum,
Sedum hisponicum, Stellaria media, Spirea nipponica, Origanum
vulgare and Imperta cylindrical are the abundant herb species
with highest IVI. The rare herb species recorded with low IVI
are Conyza canadensis, Cleoma viscosa, Chrysopogon gryllus,
Calamintha umbrosa and Xanthium strumarium (Fig. 3).
3.6. Plants communities and habitat types
Plant species by origins restricted to specific habitat and be
reached in that particular habitat due to the presence of opti-
mum environmental factors. The five different plant communi-
ties were determined by using Cluster and Two Way Cluster
Analyses through PCORD version 5.
3.7. Result of Cluster analysis
PCORD version 5 clustered five transects (elevation classes)
into 5 communities/groups through Cluster Analyses (Fig. 4).
3.8. Two Way Cluster Analyses
The Two Way Cluster Analyses of 5 transect including 124
quadrates resulted 5 various plant communities. In diagram
the black boxes show presence whereas the white one show
absence of a plant species in the region (Fig. 5).
Indicator species of each plant community were identified
through indicator species analyses (ISA). Among all the envi-
ronmental variables the elevation, organic matter, sand, phos-
phorous and nitrogen played significant role in the
establishment of plant communities of this region. Along with
the environmental gradients the five plant communities are
described as below
1. Pinus-Calotropis-Colchicum community
This community arisen on 35 different stations through
Sorenson measures on the Northern aspect at 1500 m to
3900 m elevation at sea level. The P. wallichiana A.B. Jackson,
Calotropis procera (Willd.) R. Brown and Colchicum luteum
Baker are the characteristics plant species of trees, shrubs
and herbs layer respectively. The other dominated tree species
included Q. baloot and F. palmata. While at the same time the
rare tree species that were recorded are Andrachne cardifolia,
Anaphalis triplinervis and C. deodara. Although the abundant
shrubs layer is dominated by Berberis lycium and S. saligna
whereas the rare species documented are I. heterantha, Justicia
adhatoda and B. crispa in the region. The herbaceous layer is
characterized by Cyperus glomeratus, Polypogon fugax, S. xan-
thocarpum, S. parviflora, Solidago Canadensis, Vicia sativa
however C. umbrosa is the rare herbaceous species of the first
community.
This community is dominated by P. wallichiana, C. procera
and C. luteum have an important value index (IVI) of 27.76,
76.37 and 65.09 respectively. The dominated edaphic factors
show great environmental influences in species composition,
abundance and its distribution pattern of community.
2. Pyrus-Berberis-Hypreicum Community
The community revealed on 28 different stations on the
North-Eastern aspect from 1300 to 3900 m. The topmost indi-
cator species of this community are P. pashia Buch-ham ex D.
Don, B. lycium Royle and H. perforatum Linn. Other indicator
of tree layer is dominated by C. deodara and Q. baloot whereas
F. palmata Litsea deccanensis and A. pentapomicum are rare
tree species of community. The Ziziphus oxyphylla and S. sal-
igna are the dominant while on the other hand C. procera, V.
grandiflorum and Periploca aphylla are the rare shruby species.
The herbaceous layer is characterized by H. strigosum, S. hele-
pensa, Lactuca serriola and Scrophularia sacbiosifolia whereas
rare species included in this layer are Tribulus terrestris, X.
strumarium, Verbascum thapsus and Heracleum spirea in the
region.
The described indicators P. pashia having 11.37, B. lyceum
with 50.03 and Hypricum perforatum with 71.07 IVI were used
for naming the community. The applied statistical analyses of
Canonical Correspondence Analyses (CCA) show the impact
of various environmental variables i.e., elevation and aspects
are the main significant variables in the distribution and com-
position of this plant community.
3. Quercus-Desmodium-Heliotropium Community
Based on Cluster Analysis the 3rd community is established
at 9 different stations after Sorenson measures. It can be
located on the Northern aspect from 1400 to 3700 m at sea
level. The topmost characteristics species are Q. incana Roxb,
226.11
208.99
205.22
191.91
187.57
185.75
164.77
160.69
159.68
157.44
Sorghum helepense Solanum xanthocarpum
Stachys parviflora Hypricum perforatum
Heliotropium strigosum Sedum hisponicum
stellaria media Spirea nipponica
Origanum vulgare Imperta cylindrica
Figure 3 The top ten most dominant herbs with highest IVI of
Eelum hill during different seasons.
Plant species and communities assessment in interaction with edaphic and topographic factors 781
D. elegans DC and H. strigosum Willd one from each tree,
shrub and herb layer respectively. The important value index
(IVI) of Q. incana is 4.43, D. elegans 36.10 and H. strigosum
with 28.88 were recorded in the region. The other dominated
trees are P. wallichiana and Adhatoda vasica. Whereas the rare
tree species recorded are Q. baloot, A. triplinervis and C. deo-
dara with minimum importance values. The dominant shrubs
of the community are D. elegans, Ziziphus oxyphylla and
Rubus fruiticosus. While V. grandiflorum, C. orientalis and Jus-
ticia adhatoda are the rare shrub species in community. The
other characteristics herbaceous species after H. strigosum
includes Amaranthus viridis, Ajuga bracteosa, H. perforatum
and L. serriola. While at the same time C. viscosa, Conyza
bonariensis, H. perforatum, L. serriola, Nepeta laevigata and
Sedum hispanicum are the rare herbaceous species with mini-
mum importance values of the region.
This community is also strongly influenced by Elevation
and Aspects among the measured environmental variables.
4. Cedrus – Dodonea – Sorghum Community
This community comprise of 23 stations at North-southern
aspect at altitudinal range of 1200–3600 m. The characteristic
species include C. deodara (Roxb. Ex Lamb.) G.Don followed
by Q. baloot and Q. incana are the dominated tree species.
The rare tree species included Eucalyptus lanceolata and
Figure 4 The Cluster dendrogram of 124 different station based on Sorenson measure showing 5 plant communities/habitat types. The
grouping of station designated as communities 1, 2, 3, 4 and 5.
782 M. Khan et al.
I. heterantha. The shrub layer has dominated species of Dodo-
nea viscosa followed by Jasminium officinale with Colebrookea
oppositifolia and Justicia adhatoda rare species having mini-
mum IVI in the community. The characteristics herbaceous
layer is dominated by Sorghum helepense, V. thapsus, N. laevi-
gata, S. parviflora and Pennisetum orientale. Besides this the
rare species noted in community are Brachiaria ramosa, H.
spirea, C. Canadensis, V. sativa and Polygonum pusambo.
The important value index (IVI) of indicator species i.e., C.
deodara, Dodonaea viscosa and Sorghum helepense are 10.99,
35.73 and 76.53 respectively.
5. Quercus – Zizyphus – Sedum Community
The community includes 27 different stations on south-west
aspect ranging from 1500 to 3700 m in the study area. The
dominant plants of community in tree, shrub and herb layer
are Q. incana, Ziziphus oxyphylla and S. hispanicum respec-
tively. In which tree layer is dominated by P. wallichiana and
C. deodara abundance and rare species are Melia azedarach,
E. lanceolata and P. pashia. The characteristics shrub Zizyphus
oxyphylla is followed by D. stramonium with rare Shrubs are
Cotinus coggygria and Justicia adhatoda. The herbaceous layer
Figure 5 Different stations of 124 plant species based on Sorenson way of measuring show the Two Way Cluster Analysis through PC-
ORD.
Plant species and communities assessment in interaction with edaphic and topographic factors 783
after S. hisponicum is followed by Carpesium arbotanoides, V.
sativa, Taraxacum officinale and S. xanthocarpum with rare
herbs Arundo donex, Artemisia vulgaris, C. umbrosa, Smilax
glucophylla and Thymus linearis. The characteristics species
Q. incana, Zizyphus oxyphylla and S. hisponicum having an
important value index (IVI) of 18.34, 72.49 and 81.04
respectively.
4. Environmental gradient
Both the species and various environmental gradient variables
data i.e., altitude, aspect, textural class, calcium carbonate,
organic matters concentration, nitrogen, phosphors, potas-
sium, pH, electrical Conductivity, silt and rocky soil were ana-
lyzed through CANOCO software version 4.5. Analyses show
significant effect of all the environmental variables on plant
species composition, distribution pattern and abundance of
the Eelum Hills. In terms of statistical the significance the
value of p (p 6 0.048) shows that the present results are highly
significant (Table 1 and Fig. 6).
5. Discussion
A total of 52 plant families were studied in the Eelum hills Dis-
trict Swat during the summer of 2013. It was found that these
families show similarities with the vegetation communities of
Western Himalayan parts of Malakand, Hazara, Kashmir
and Gilgit Baltistan Regions of Pakistan where they reported
Asteraceae, Lamiaceae, Rosaceae and Poaceae were the top-
most dominant families (Abbas et al., 2016; Abbasi et al.,
2013; Khan et al., 2011a; Shaheen et al., 2011).
Plant species by origins restricted to specific habitat and be
reached in that particular habitat due to the presence of opti-
mum environmental factors (Soil chemistry, biotic and abiotic
factors) which clearly show that plant communities and vege-
tation composition changes along the environmental diversity
from point to point. The five different plant communities were
determined by using Two Way Cluster Analysis and Important
value index. The identified five plant communities were (i)
Community 1 having 35 different stations on North aspect
from 1500 m to 3900 m located on Loamy and Sandy soil,
dominated by P. wallichiana, C. procera and C. luteum while
rare species A. cardifolia, A. triplinervis and C. deodara, I.
heterantha and S. canadensis, containing the lowest quantity
in all of the communities 2.9 also with organic matters 0.416
in the presence of clay, silt and sand 3.6%, 20% and 76.8%
respectively, in Neutral environment with 0.192 electric
conductivity. (ii) Community 2 was formed on 28 different
stations on North-East aspect from 1300 m to 3900 m.
The community is dominated by P. pashia, B. lycium and
H. perforatum while the rare species are F. palmata, C. procera
and X. strumarium. The community is affected by different
environmental variables i.e., CaCO3 2.8, Nitrogen 0.326,
Phosphorus 9.1 and Potassium 80.4 also with clay, silt
and sand in ratio 4.6%, 31.2% and 64.4% respectively.
(iii) Community 3 is composed of 09 stations on North to East
aspect ranging from 1400 m to 3700 m, characterized by dom-
inant vegetation i.e., Q. incana, D. elegans and H. strigosum
while the rare plant species here are Q. baloot, V. grandiflorum
and Nepeta walkers and bear soluble solutes 0.0582%, Electric
conductivity 0.182% and CaCO3 2% etc. Others variables like
soil texture in a ratio of clay 4.6%, silt 26% and sand 84%
with some of basic nutrients nitrogen 0.047%, phosphorus
5.54% and potassium 76.2% with neutral PH are also
Table 1 Analyses of all plants and environmental variables through CANOCO software version 4.5.
Axes 1 2 3 4 Total inertia
Eigen values 0.089 0.064 0.057 0.050 1.193
Species-environment correlations 0.890 0.857 0.886 0.883
Cumulative percentage variance of species data 7.5 12.8 17.6 21.8
Summary of Monte Carlo test (499 permutations under reduced model)
Test of significance of first canonical axis Test of significance of all canonical axes
Eigen value 0.169 Trace 0.979
F-ratio 1.169 F-ratio 1.198
P-value 0.8360 P-value 0.0480
Figure 6 The Canonical Correspondence Analysis (CCA) dia-
gram shows the distribution of 5 plant communities between 5
transects related to various environmental variables.
784 M. Khan et al.
noteworthy. (iv) Community 4 is composed of 23 different
stations on North to southern aspect at 1200 m to 3600 m.
Community 4 is dominated by C. deodara, Dodonea viscosa
and Sorghum helepense while the rare species in this area are
E. lanceolata, C. oppositifolia and C. Canadensis. Soil results
show different ratios of different nutrients i-e CaCO3 3%,
Organic matter 0.0502%, Nitrogen 0.0606%, Phosphorus
4.34% and Potassium 51% in pH 7.48 with texture of clay, silt
and sand in a ratio of 4.12%, 20% and 67.164% respectively.
(v) Community 5 contain 27 stations and located on
South-West aspects from height 1500 m to 3700 m strongly
reflect the environmental variables i.e., clay, silt and sand
0.56%, 23.2% and 13.84% respectively. The dominant plant
species are Q. incana, Zizyphus oxyphylla and S. hisponicum
and the rare are M. azedarach, Justicea adhatoda and
A. vulgaris. The others abiotic factors like nitrogen 0.028%,
phosphorus 9.96%, potassium 71.6%, CaCO3 2.45% and
organic matter 0.58 with pH 7.6. Shaheen et al. (2011), Khan
et al. (2012) (Khan et al., 2012; Shaheen and Shinwari, 2012;
Wana, 2002) also reported various communities of plant
species in relation to environmental variables. The dominant
tree species in the region included P. wallichiana, P. pashia
and Q. incana that were also reported in the Naran Valley of
western Himalayas by Khan et al. (2011b). The Canonical
Correspondence Analysis (CCA) was used to show variation
of 124 plant species in 124 quadrates with different microenvi-
ronments of 5 plant communities (CCA table). After observa-
tion it is analyzed that Elevation, Soil texture (Clay, Silt and
Sand), Calcium carbonate, Organic matter, Nitrogen, Phos-
phorus and Potassium, PH, Electric conductivity (E.C), Total
Soluble Solute (TSS) show significant effect on species distri-
bution and composition with P-value 0.0480. Such impacts
were also being study by numbers of authors in the neighbor-
ing habitats of Pakistan. In addition, any change in environ-
mental variables and altitude cause significant effect in
formation of communities (Chawla et al., 2008; Khan et al.,
2014). This is now the topic of every field scientist to check
and study environmental effect to find the pattern of distribu-
tion of species in different part of the area (Lomolino, 2001).
The present study supplement P. wallichiana has a taxonomic
hierarchy in the region because of the presence in all strands
ranging from 1200 m to 3600 m. Quarcus baloot was reported
from lower ranking 1400 m to 3500 m. C. deodara reached
up to 3800 m clearly indicates its threatening conservation
status. Quarcus species along with some different herbs
(Chenopodium ambrosioides, C. gryllus, Cichorium intybus,
Cleome viscosa, C. luteum, C. bonariensis, C. Canadensis,
Cynanchum arnottianum, C. glomeratus, Delphinium roylei,
Diclliptera roxburghiana, Duchesnea indica, Epilobium hirsu-
tum, Epilobium laxum, Equiestum arvense, Eremostachys
superba, Fragaria nubicola and H. strigosum) indicates the sim-
ilarities of different environmental variables in different part of
the Western Himalayan province in general and more specifi-
cally in Murree, Hazara and Kashmir in altitude from
1100 m to 2900 m (Khan et al., 2013; Takhtajan, 1986). In pre-
sent research work the various statistical techniques were used
i.e., CCA, DCA, PC-ORD and ISA to asses various environ-
mental effects on plant species and communities distribution
which were also used by Khaznadar et al. (2009) and others
very extensively for baseline as well as conservation manage-
ment for future.
Acknowledgments
The authors would like to extend their sincere appreciation to
the Deanship of Scientific Research at King Saud University
for its funding this Research group NO (RG-1435-014). We
are also thankful to the local inhabitants and deputed Pakistan
Army who facilitated us to complete our research project in a
geopolitically tense region, the Eelum Mount Valley.
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Plant species and communities assessment in interaction with edaphic and topographic factors; an ecological study of the mount Eelum District Swat, Pakistan

  • 1. ORIGINAL ARTICLE Plant species and communities assessment in interaction with edaphic and topographic factors; an ecological study of the mount Eelum District Swat, Pakistan Murad Khan a , Shujaul Mulk Khan b,*, Muhammad Ilyas c , Abdulaziz A. Alqarawi d , Zeeshan Ahmad b , Elsayed Fathi Abd_Allah d,e,* a Department of Botany, Hazara University Mansehra, Pakistan b Department of Plant Sciences, Quaid-i-Azam University Islamabad, Pakistan c Department of Botany, Islamabad Model College for Boys G10/4 Islamabad, Pakistan d Department of Plant Production, College of Food & Agricultural Sciences, P.O. Box 2460, Riyadh 11451, Saudi Arabia e Seed Pathology Department, Plant Pathology Research Institute, ARC, Giza 12511, Egypt Received 2 August 2016; revised 29 November 2016; accepted 30 November 2016 Available online 9 December 2016 KEYWORDS Canonical Correspondence Analysis (CCA); Characteristic species; CANOCO; PC-ORD; Eelum; Plant communities; Swat Pakistan Abstract The current analyses of vegetation were aimed to study the different effects of environ- mental variables and plant species and communities interaction to these variables, identified threats to local vegetation and suggestion for remedial measures in the Mount Eelum, Swat, Pakistan. For assessment of environmental variability quantitative ecological techniques were used through quad- rats having sizes of 2 Â 2, 5 Â 5 and 10 Â 10 m2 for herbs, shrubs and trees respectively. Result of the present study revealed 124 plant species in the study area. Canonical Correspondence Analysis (CCA) was used to analyze the ecological gradient of vegetation. The environmental data and spe- cies abundance were used in CANOCO software version 4.5. The presence absence data of plant species were elaborated with Cluster and Two Way Cluster Analysis techniques using PC-ORD ver- sion 5 to show different species composition that resulted in five plant communities. Findings indi- cate that elevation, aspect and soil texture are the strongest variables that have significant effect on * Corresponding authors at: Department of Plant Sciences, Quaid-i-Azam University Islamabad, Pakistan – 45320 (S.M. Khan). Department of Plant Production, College of Food & Agricultural Sciences, P.O. Box 2460, Riyadh 11451, Saudi Arabia (E.F. Abd_Allah). E-mail address: elsayed_22@yahoo.com (E.F. Abd_Allah). Peer review under responsibility of King Saud University. Production and hosting by Elsevier Saudi Journal of Biological Sciences (2017) 24, 778–786 King Saud University Saudi Journal of Biological Sciences www.ksu.edu.sa www.sciencedirect.com http://dx.doi.org/10.1016/j.sjbs.2016.11.018 1319-562X Ó 2016 The Authors. Production and hosting by Elsevier B.V. on behalf of King Saud University. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).
  • 2. species composition and distribution of various communities shown with P value 0.0500. It is rec- ommended to protect and use sensibly whole of the Flora normally and rare species particularly in the region. Ó 2016 The Authors. Production and hosting by Elsevier B.V. on behalf of King Saud University. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). 1. Introduction The study of plant communities is the best way to learn about habit, habitat, niche and vegetation structure (Khan et al., 2016a; Malik, 1986) as well as various interaction among the plants in an ecosystem. Forest ecosystems in the world have a history of fragmentation due to activities of human advance- ment (Chabrerie et al., 2013). The deforestation mask the greenery, created ecological disturbance, drastic change in soil chemistry, physical weathering and denudation of rocks which leading to floods and changed almost the natural structure of vegetation. The important zone of ecological study is to deter- mine the interaction between different biotic and abiotic com- ponents of an ecosystem (Rahman et al., 2016; Tavili and Jafari, 2009). Abiotic variations are well known characteristics both in space and time which effect plant communities and population. The plant communities highlight changes in response to various factors not only related to its zone of ori- gin but also to its ecology (Afzal et al., 2000). The most simply interpretable sign of biological variation is species richness which highlight by different environmental characters (Khan et al., 2016b; Shrestha and Vetaas, 2009). Researchers study several factors (abiotic and biotic) basically which interact in community structure formation. These factors contribute to comprehend distribution, composition and diversity of plant species and communities (Brown, 1984). Variations in plant species composition along altitude and latitude is well estab- lishment phenomenon (Kitayama, 1992; Lieberman et al., 1985; Shaheen et al., 2012) and one of the ultimate effect in restricting plant species and communities types in mountain- ous regions (Khan et al., 2011a). Furthermore soil is an envi- ronmental factor that also determines plant growth which is influenced by organisms, climate, topography, time and parent material (Hoveizeh, 1997). Climate is affected by topography such as slope, elevation and aspect, in addition to affect of evapotranspiration and temperature that as a whole result rich vegetation in the northern aspects as compared to southern ones (Ordon˜ ez et al., 2009). Furthermore, the quantitative analysis has a strong back ground and a lot of different field scientist have contributed to use it (Shaheen and Shinwari, 2012). Quantitative measure updates the feature of vegetation because of its obvious effects on all types of associated life to vegetation communities. Ecologists use multivariate approach for seeking and summarizing ecological set of plants data regarding with environmental variables. The statistical study of these data help in finding actual position of plant species in the field (Curtis and McIntosh, 1950). The multivariate sta- tistical analytical programs assists the ecologists to analyse the effects of environmental variables on whole numbers of species and to know structure in the data set (Anderson et al., 2006). Canonical Correspondence Analysis (CCA) shows the relationship amongst the species as linear combinations of environmental variables graphically (Green, 1979). So this technique interrelates with different types of reciprocal averag- ing with multiple regression techniques together (Ter Braak, 1986, 1987). Canonical Correspondence Analysis (CCA) is a type of direct gradient analyses which show the difference among vegetation patterns under the influence of environmen- tal variables (Al-Qarawi, 2011). The purpose of present study is to attain realistic prototyp- ical form of vegetation and its interaction due to location of Eelum hills – a rich floristic zone, its distant peaks inaccessibil- ity and harsh terrain evaluation. It has been planned to evalu- ate vegetation variability in relation to environmental factors through advanced analytical analyses (CCA, PC-ORD). It is specially intended to quantify the vegetation of the region with various edaphic and physiographic factors to get knowledge about microclimate of each and every plant species. Particu- larly, present research work carried to find out the indicator species of diverse communities through multivariate analyses and the anthropogenic activities as threat to local flora. 2. Materials and methods The Swat has always remained self-sufficient in its natural and agricultural resources (DiPietro et al., 1999). The mount Eelum located on southern watershed of the Murghuzar Valley in famous mountain range with altitude of 9273 feet (Altimeter data). It belts a natural boundary between district Swat and Buner. Agriculture is common practice in the outskirts of Mount Eelum, with typical crops of maize (1069 ton), wheat (3.5 metric ton), rice (2.5 ton), onion and Trifolium, while in fruits, the area is dominated by plum, persimmon and pears. The present study was carried out to find the Indicator species, plant communities, species composition, distribution and abundance with a special relation or interaction to edaphic fac- tors and various threats to flora in the Eelum hills Swat, Pak- istan. The quantitative ecological techniques (Quadrate methods) were carried out for assessment of plant species and environmental variability. The various transects were placed from lower to higher elevations at regular interval of 100 m. Quadrates having sizes of 2 Â 2 m2 for herbs, 5 Â 5 m2 for shrubs and 10 Â 10 m2 for trees were placed ran- domly at systematically established stations. For all quadrates phytosociological attributes i.e., density, frequency, cover, rel- ative density, relative frequency, relative cover and importance values (IVs) were recorded. The plant specimens were col- lected, tagged, and identified using flora of Pakistan and other related literature and then deposited in the Herbarium of Hazara University Mansehra, Pakistan (HUH). 2.1. Environmental data The Altimeter was used to find elevation of each station, transect as well as geographical coordinates i.e. latitude and Plant species and communities assessment in interaction with edaphic and topographic factors 779
  • 3. longitude. Aspect variation at each quadrat was observed from sun rise and set using compass and different geographical techniques. 2.2. Soil collection and analyses The soil sampling tubes were used to collect the soil samples up to a depth of 30 cm from each station. The samples were air dried, grinded for composite sample, sieved through 2 mm screen to remove the stone pieces and large root particles. The soil analyses and physiochemical properties were assessed in the soil science laboratory of Agriculture Research Institute Tarnab, Peshawar. Soil texture, lime concentration, organic matter concentration, phosphorous, potassium, sulfate con- centration and pH were measured. Soil textures were deter- mined by hydrometer (Koehler et al., 1984), pH was determined by pH meter (Khan et al., 2012), for lime determi- nation acid neutralization method was used (Thomas, 1982) and standardized solution of FeSO4 and K2Cr2O7 were used for the determination of soil organic matters (Nelson et al., 1996). AB-DTPA extractable P and K was determined in sam- ples through method described by (Soltanpour, 1991) and soil texture was determined by hydrometer method (Koehler et al., 1984), sulfate was determined using the procedure of (Belyea and Lancaster, 1999). 2.3. Data analyses The obtained data of five Transects and 124 quadrates arranged in MS Excel for further analyses through Cluster analysis and Two Way Cluster analysis based on presence and absence value of plant species. The species data was arranged in row and quadrates in column as per requirement of PC-ORD version 5 software (Lepsˇ and Sˇ milauer, 2003). CANOCO software version 4.5 was used to find the influence of different environmental variables on species compositions and community formation. 3. Results A field research conducted in different seasons based on differ- ent criteria, advance parameters and a statistical approaches is explained theoretically and diagrammatically as under. 3.1. Species composition with special reference to altitudinal range of Eelum hills A total of 124 plant species, belonging to 52 families dis- tributed over 25 Transects (372 quadrats) were collected from Eelum hills, including 86 (70%) herbs, 22 (17%) shrubs and 16 (13%) are trees. The topmost leading families were Asteraceae having 20 species followed by Lamiaceae having 13 Species and Poaceae with 10 species individually (Table 1). 3.2. Abundant and less abundant species of the area The abundance of plant species was assessed through Impor- tance Values Index (IVI) that is explained in the following sub headings. 3.3. Tree layer In tree layer Pinus wallichiana, Quercus incana, Quercus baloot, Cedrus deodara, Ficus palmata and Pyrus pashia were observed mostly in tree layer of Eelum hills that show highest IVI. The rare species includes Pistacia integerrima, Acer pentapomicum and Prunus cornuta having minimum IVI in the region (Fig. 1). 3.4. Shrub layer In shruby layer the most abundant species with high IVI are Desmodium elegans, Zizyphus oxyphylla, Berberis lyceum, Sar- cococca saligna, Datura stramonium and Hedera nepalensis. Whereas Clematis orientalis, Indigofera heterantha, Justicea adhatoda, Viburnum grandiflorum and Buddleja crispa was recorded as rare plant species in region (Fig. 2). Ficus racemosa Melia azedarachta Eucalyptus lanceolata Pyrus pashia Ficus palmata Cedrus deodara Quercus baloot Quercus incana Pinus wallichiana Figure 1 The top 10 abundant tree species with high important value index of the Eelum hills. 229.67 188.81 173.57 156.36 151.08 143.12 125.51121.99118.18 117.25 Desmodium elegans Zizyphus oxyphylla Berberis lycium sarcococca saligna Datura stramonium Hedera nepalensis Dodonea viscosa Jasminium officinalis Calotropis procera Rubus fruticosus Figure 2 The top 10 most abundant shrubs with high important value index in the region. 780 M. Khan et al.
  • 4. 3.5. Herb layer The Sorghum helepense, Solanum xanthocarpum, Stachys parviflora, Hypericum perforatum, Heliotropium strigosum, Sedum hisponicum, Stellaria media, Spirea nipponica, Origanum vulgare and Imperta cylindrical are the abundant herb species with highest IVI. The rare herb species recorded with low IVI are Conyza canadensis, Cleoma viscosa, Chrysopogon gryllus, Calamintha umbrosa and Xanthium strumarium (Fig. 3). 3.6. Plants communities and habitat types Plant species by origins restricted to specific habitat and be reached in that particular habitat due to the presence of opti- mum environmental factors. The five different plant communi- ties were determined by using Cluster and Two Way Cluster Analyses through PCORD version 5. 3.7. Result of Cluster analysis PCORD version 5 clustered five transects (elevation classes) into 5 communities/groups through Cluster Analyses (Fig. 4). 3.8. Two Way Cluster Analyses The Two Way Cluster Analyses of 5 transect including 124 quadrates resulted 5 various plant communities. In diagram the black boxes show presence whereas the white one show absence of a plant species in the region (Fig. 5). Indicator species of each plant community were identified through indicator species analyses (ISA). Among all the envi- ronmental variables the elevation, organic matter, sand, phos- phorous and nitrogen played significant role in the establishment of plant communities of this region. Along with the environmental gradients the five plant communities are described as below 1. Pinus-Calotropis-Colchicum community This community arisen on 35 different stations through Sorenson measures on the Northern aspect at 1500 m to 3900 m elevation at sea level. The P. wallichiana A.B. Jackson, Calotropis procera (Willd.) R. Brown and Colchicum luteum Baker are the characteristics plant species of trees, shrubs and herbs layer respectively. The other dominated tree species included Q. baloot and F. palmata. While at the same time the rare tree species that were recorded are Andrachne cardifolia, Anaphalis triplinervis and C. deodara. Although the abundant shrubs layer is dominated by Berberis lycium and S. saligna whereas the rare species documented are I. heterantha, Justicia adhatoda and B. crispa in the region. The herbaceous layer is characterized by Cyperus glomeratus, Polypogon fugax, S. xan- thocarpum, S. parviflora, Solidago Canadensis, Vicia sativa however C. umbrosa is the rare herbaceous species of the first community. This community is dominated by P. wallichiana, C. procera and C. luteum have an important value index (IVI) of 27.76, 76.37 and 65.09 respectively. The dominated edaphic factors show great environmental influences in species composition, abundance and its distribution pattern of community. 2. Pyrus-Berberis-Hypreicum Community The community revealed on 28 different stations on the North-Eastern aspect from 1300 to 3900 m. The topmost indi- cator species of this community are P. pashia Buch-ham ex D. Don, B. lycium Royle and H. perforatum Linn. Other indicator of tree layer is dominated by C. deodara and Q. baloot whereas F. palmata Litsea deccanensis and A. pentapomicum are rare tree species of community. The Ziziphus oxyphylla and S. sal- igna are the dominant while on the other hand C. procera, V. grandiflorum and Periploca aphylla are the rare shruby species. The herbaceous layer is characterized by H. strigosum, S. hele- pensa, Lactuca serriola and Scrophularia sacbiosifolia whereas rare species included in this layer are Tribulus terrestris, X. strumarium, Verbascum thapsus and Heracleum spirea in the region. The described indicators P. pashia having 11.37, B. lyceum with 50.03 and Hypricum perforatum with 71.07 IVI were used for naming the community. The applied statistical analyses of Canonical Correspondence Analyses (CCA) show the impact of various environmental variables i.e., elevation and aspects are the main significant variables in the distribution and com- position of this plant community. 3. Quercus-Desmodium-Heliotropium Community Based on Cluster Analysis the 3rd community is established at 9 different stations after Sorenson measures. It can be located on the Northern aspect from 1400 to 3700 m at sea level. The topmost characteristics species are Q. incana Roxb, 226.11 208.99 205.22 191.91 187.57 185.75 164.77 160.69 159.68 157.44 Sorghum helepense Solanum xanthocarpum Stachys parviflora Hypricum perforatum Heliotropium strigosum Sedum hisponicum stellaria media Spirea nipponica Origanum vulgare Imperta cylindrica Figure 3 The top ten most dominant herbs with highest IVI of Eelum hill during different seasons. Plant species and communities assessment in interaction with edaphic and topographic factors 781
  • 5. D. elegans DC and H. strigosum Willd one from each tree, shrub and herb layer respectively. The important value index (IVI) of Q. incana is 4.43, D. elegans 36.10 and H. strigosum with 28.88 were recorded in the region. The other dominated trees are P. wallichiana and Adhatoda vasica. Whereas the rare tree species recorded are Q. baloot, A. triplinervis and C. deo- dara with minimum importance values. The dominant shrubs of the community are D. elegans, Ziziphus oxyphylla and Rubus fruiticosus. While V. grandiflorum, C. orientalis and Jus- ticia adhatoda are the rare shrub species in community. The other characteristics herbaceous species after H. strigosum includes Amaranthus viridis, Ajuga bracteosa, H. perforatum and L. serriola. While at the same time C. viscosa, Conyza bonariensis, H. perforatum, L. serriola, Nepeta laevigata and Sedum hispanicum are the rare herbaceous species with mini- mum importance values of the region. This community is also strongly influenced by Elevation and Aspects among the measured environmental variables. 4. Cedrus – Dodonea – Sorghum Community This community comprise of 23 stations at North-southern aspect at altitudinal range of 1200–3600 m. The characteristic species include C. deodara (Roxb. Ex Lamb.) G.Don followed by Q. baloot and Q. incana are the dominated tree species. The rare tree species included Eucalyptus lanceolata and Figure 4 The Cluster dendrogram of 124 different station based on Sorenson measure showing 5 plant communities/habitat types. The grouping of station designated as communities 1, 2, 3, 4 and 5. 782 M. Khan et al.
  • 6. I. heterantha. The shrub layer has dominated species of Dodo- nea viscosa followed by Jasminium officinale with Colebrookea oppositifolia and Justicia adhatoda rare species having mini- mum IVI in the community. The characteristics herbaceous layer is dominated by Sorghum helepense, V. thapsus, N. laevi- gata, S. parviflora and Pennisetum orientale. Besides this the rare species noted in community are Brachiaria ramosa, H. spirea, C. Canadensis, V. sativa and Polygonum pusambo. The important value index (IVI) of indicator species i.e., C. deodara, Dodonaea viscosa and Sorghum helepense are 10.99, 35.73 and 76.53 respectively. 5. Quercus – Zizyphus – Sedum Community The community includes 27 different stations on south-west aspect ranging from 1500 to 3700 m in the study area. The dominant plants of community in tree, shrub and herb layer are Q. incana, Ziziphus oxyphylla and S. hispanicum respec- tively. In which tree layer is dominated by P. wallichiana and C. deodara abundance and rare species are Melia azedarach, E. lanceolata and P. pashia. The characteristics shrub Zizyphus oxyphylla is followed by D. stramonium with rare Shrubs are Cotinus coggygria and Justicia adhatoda. The herbaceous layer Figure 5 Different stations of 124 plant species based on Sorenson way of measuring show the Two Way Cluster Analysis through PC- ORD. Plant species and communities assessment in interaction with edaphic and topographic factors 783
  • 7. after S. hisponicum is followed by Carpesium arbotanoides, V. sativa, Taraxacum officinale and S. xanthocarpum with rare herbs Arundo donex, Artemisia vulgaris, C. umbrosa, Smilax glucophylla and Thymus linearis. The characteristics species Q. incana, Zizyphus oxyphylla and S. hisponicum having an important value index (IVI) of 18.34, 72.49 and 81.04 respectively. 4. Environmental gradient Both the species and various environmental gradient variables data i.e., altitude, aspect, textural class, calcium carbonate, organic matters concentration, nitrogen, phosphors, potas- sium, pH, electrical Conductivity, silt and rocky soil were ana- lyzed through CANOCO software version 4.5. Analyses show significant effect of all the environmental variables on plant species composition, distribution pattern and abundance of the Eelum Hills. In terms of statistical the significance the value of p (p 6 0.048) shows that the present results are highly significant (Table 1 and Fig. 6). 5. Discussion A total of 52 plant families were studied in the Eelum hills Dis- trict Swat during the summer of 2013. It was found that these families show similarities with the vegetation communities of Western Himalayan parts of Malakand, Hazara, Kashmir and Gilgit Baltistan Regions of Pakistan where they reported Asteraceae, Lamiaceae, Rosaceae and Poaceae were the top- most dominant families (Abbas et al., 2016; Abbasi et al., 2013; Khan et al., 2011a; Shaheen et al., 2011). Plant species by origins restricted to specific habitat and be reached in that particular habitat due to the presence of opti- mum environmental factors (Soil chemistry, biotic and abiotic factors) which clearly show that plant communities and vege- tation composition changes along the environmental diversity from point to point. The five different plant communities were determined by using Two Way Cluster Analysis and Important value index. The identified five plant communities were (i) Community 1 having 35 different stations on North aspect from 1500 m to 3900 m located on Loamy and Sandy soil, dominated by P. wallichiana, C. procera and C. luteum while rare species A. cardifolia, A. triplinervis and C. deodara, I. heterantha and S. canadensis, containing the lowest quantity in all of the communities 2.9 also with organic matters 0.416 in the presence of clay, silt and sand 3.6%, 20% and 76.8% respectively, in Neutral environment with 0.192 electric conductivity. (ii) Community 2 was formed on 28 different stations on North-East aspect from 1300 m to 3900 m. The community is dominated by P. pashia, B. lycium and H. perforatum while the rare species are F. palmata, C. procera and X. strumarium. The community is affected by different environmental variables i.e., CaCO3 2.8, Nitrogen 0.326, Phosphorus 9.1 and Potassium 80.4 also with clay, silt and sand in ratio 4.6%, 31.2% and 64.4% respectively. (iii) Community 3 is composed of 09 stations on North to East aspect ranging from 1400 m to 3700 m, characterized by dom- inant vegetation i.e., Q. incana, D. elegans and H. strigosum while the rare plant species here are Q. baloot, V. grandiflorum and Nepeta walkers and bear soluble solutes 0.0582%, Electric conductivity 0.182% and CaCO3 2% etc. Others variables like soil texture in a ratio of clay 4.6%, silt 26% and sand 84% with some of basic nutrients nitrogen 0.047%, phosphorus 5.54% and potassium 76.2% with neutral PH are also Table 1 Analyses of all plants and environmental variables through CANOCO software version 4.5. Axes 1 2 3 4 Total inertia Eigen values 0.089 0.064 0.057 0.050 1.193 Species-environment correlations 0.890 0.857 0.886 0.883 Cumulative percentage variance of species data 7.5 12.8 17.6 21.8 Summary of Monte Carlo test (499 permutations under reduced model) Test of significance of first canonical axis Test of significance of all canonical axes Eigen value 0.169 Trace 0.979 F-ratio 1.169 F-ratio 1.198 P-value 0.8360 P-value 0.0480 Figure 6 The Canonical Correspondence Analysis (CCA) dia- gram shows the distribution of 5 plant communities between 5 transects related to various environmental variables. 784 M. Khan et al.
  • 8. noteworthy. (iv) Community 4 is composed of 23 different stations on North to southern aspect at 1200 m to 3600 m. Community 4 is dominated by C. deodara, Dodonea viscosa and Sorghum helepense while the rare species in this area are E. lanceolata, C. oppositifolia and C. Canadensis. Soil results show different ratios of different nutrients i-e CaCO3 3%, Organic matter 0.0502%, Nitrogen 0.0606%, Phosphorus 4.34% and Potassium 51% in pH 7.48 with texture of clay, silt and sand in a ratio of 4.12%, 20% and 67.164% respectively. (v) Community 5 contain 27 stations and located on South-West aspects from height 1500 m to 3700 m strongly reflect the environmental variables i.e., clay, silt and sand 0.56%, 23.2% and 13.84% respectively. The dominant plant species are Q. incana, Zizyphus oxyphylla and S. hisponicum and the rare are M. azedarach, Justicea adhatoda and A. vulgaris. The others abiotic factors like nitrogen 0.028%, phosphorus 9.96%, potassium 71.6%, CaCO3 2.45% and organic matter 0.58 with pH 7.6. Shaheen et al. (2011), Khan et al. (2012) (Khan et al., 2012; Shaheen and Shinwari, 2012; Wana, 2002) also reported various communities of plant species in relation to environmental variables. The dominant tree species in the region included P. wallichiana, P. pashia and Q. incana that were also reported in the Naran Valley of western Himalayas by Khan et al. (2011b). The Canonical Correspondence Analysis (CCA) was used to show variation of 124 plant species in 124 quadrates with different microenvi- ronments of 5 plant communities (CCA table). After observa- tion it is analyzed that Elevation, Soil texture (Clay, Silt and Sand), Calcium carbonate, Organic matter, Nitrogen, Phos- phorus and Potassium, PH, Electric conductivity (E.C), Total Soluble Solute (TSS) show significant effect on species distri- bution and composition with P-value 0.0480. Such impacts were also being study by numbers of authors in the neighbor- ing habitats of Pakistan. In addition, any change in environ- mental variables and altitude cause significant effect in formation of communities (Chawla et al., 2008; Khan et al., 2014). This is now the topic of every field scientist to check and study environmental effect to find the pattern of distribu- tion of species in different part of the area (Lomolino, 2001). The present study supplement P. wallichiana has a taxonomic hierarchy in the region because of the presence in all strands ranging from 1200 m to 3600 m. Quarcus baloot was reported from lower ranking 1400 m to 3500 m. C. deodara reached up to 3800 m clearly indicates its threatening conservation status. Quarcus species along with some different herbs (Chenopodium ambrosioides, C. gryllus, Cichorium intybus, Cleome viscosa, C. luteum, C. bonariensis, C. Canadensis, Cynanchum arnottianum, C. glomeratus, Delphinium roylei, Diclliptera roxburghiana, Duchesnea indica, Epilobium hirsu- tum, Epilobium laxum, Equiestum arvense, Eremostachys superba, Fragaria nubicola and H. strigosum) indicates the sim- ilarities of different environmental variables in different part of the Western Himalayan province in general and more specifi- cally in Murree, Hazara and Kashmir in altitude from 1100 m to 2900 m (Khan et al., 2013; Takhtajan, 1986). In pre- sent research work the various statistical techniques were used i.e., CCA, DCA, PC-ORD and ISA to asses various environ- mental effects on plant species and communities distribution which were also used by Khaznadar et al. (2009) and others very extensively for baseline as well as conservation manage- ment for future. 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