Research Article
Floristic Diversity and Life Form Spectrum of Vegetation in Swabi District, Khyber Pakhtunkhwa, Pakistan
Huma Gul1*, Anwar Hussain Khan2, Nasira Bibi3, Rayyan Komal4 and Shabir Ahmad1
1Department of Plant Sciences, Faculty of Biological Sciences, Quaid-i-Azam University, Islamabad, Pakistan; 2Department of Botany, Abdul Wali Khan, University, Mardan, Khyber Pakhtunkhwa, Pakistan; 3Department of Botany, Islamia College University, Peshawar, Khyber Pakhtunkhwa, Pakistan; 4Department of Botany, Women University of Swabi, Khyber Pakhtunkhwa, Pakistan.
Abstract | The current study was conducted to investigate floral structure, life form and leaf size spectrum and habitat status of plants of Swabi District, Pakistan. Regular visits were organized between the years of 2022 to 2023 to collect plant samples of the region and prepare a flora inventory. The life form of the plant and the size of its leaves were determined. Plant species were also classified according to their habitats. In the current study, we collected and identified about 140 species belonging to 102 genera and 53 families. The largest family was Poaceae (15 spp.), followed by Rosaceae (11 spp.) and Solanaceae (7 spp.). Herbaceous vegetation predominates, followed by trees, shrubs and climbing plants. In this study the area was found to be dominated by therophytes with (48 spp., 34%), followed by phanerophytes (39 spp., 28%) and Hemicryptophytes (33 spp., 24%). Examination of leaf shape spectra revealed that Microphyll (43 spp., 31%), followed by Nanophyll (38 spp., 27%), and Mesophyll (34., 24%). In the current study we also classified plants species based on their habitat. The results showed that the largest number of species were found in dry places (31 spp., 22%), followed by moist places (29 spp., 21%), cultivated areas (26 spp., 18%), wasteland areas (23 spp., 16%). This study provides basic information on the flora of Swabi, because the flora of the study area is very diverse therefore further studies will be required to assess the conservation status of the wild flora and obtain quantitative information on the vegetation.
Received | May 08, 2025; Accepted | June 16, 2025; Published | June 26, 2025
*Correspondence | Huma Gul, Department of Plant Sciences, Faculty of Biological Sciences, Quaid-i-Azam University, Islamabad, Pakistan; Email: [email protected]
Citation | Gul, H., A.H. Khan, N. Bibi, R. Komal and S. Ahmad. 2025. Floristic diversity and life form spectrum of vegetation in Swabi District, Khyber Pakhtunkhwa, Pakistan. Pakistan Journal of Weed Science Research, 31(2): 104-116.
DOI | https://dx.doi.org/10.17582/journal.PJWSR/2025/31.2.104.116
Keywords | Ethnobotany, Floristic diversity, Habitat, Life form, Leaf form, Swabi
Copyright: 2025 by the authors. Licensee ResearchersLinks Ltd, England, UK.
This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
Introduction
Vegetation refers to a comprehensive list of plant species found in a given geographic area (Amjad et al., 2017). Understanding vegetation structure provides insight into biodiversity and helps assess current climate conditions (Thakur et al., 2012). It provides an important resource for systematic research on plant life (Khan et al., 2017). Floristic inventory provides a taxonomic perspective on flora, further classifying and analyzing plant species in a given region (Panda et al., 2014). Floristic diversity encompasses both morphological characteristics and ecological interactions across various environments (Catarino et al., 2002). The life form of a plant refers to the shape of its vegetative body which is affected by climate, while the biological spectrum represents the distribution of different classes of life forms (Sharma et al., 2018). Such traits reflect adaptive strategies of plant species to prevailing ecological conditions (Khalid et al., 2017). Life forms and leaf size spectra are important indicators of micro and macro-climatic conditions and of anthropogenic effects in a region (Cain et al., 1959). These studies help to understand local vegetation cover and major climate changes (Oosting, 1948), and provide information about plant physiology and interactions (Rashid et al., 2011). Plant physiognomy traits, such as life form and leaf size spectrum, are often used in vegetation studies (Khalid, 2017), which indicate climate and adaptability to existing climatic conditions. However, biotic factors such as overgrazing and deforestation can alter the distribution of life forms. Although research has been done on the floral spectrum and biology in several regions, these are lacking in the District Swabi, Khyber Pakhtunkhwa, Pakistan. This study aims to address the gap by examining the region’s biological features and flora inventory, as well as by offering the fundamental information required for studies in forestry, taxonomy, ecology, ethnobotany, and conservation.
Materials and Methods
Study area
Swabi District, Khyber, Pakhtunkhwa, Pakistan is located between the Indus and Kabul rivers (Maqsood et al., 2015). It is the fourth largest populated district. Swabi is located between 34.70 °N and 72.280 °E, with a total area of 1,543 km2. Approximately 78% of the district is mountainous, while the remaining 22% comprise flat, and terrain. The district is mainly mountainous (78.0%), while the remaining part (21.0%) is flat, dry land. May and June show significant temperature increases, while July, August and September show almost constant temperatures. June was the month with the highest recorded temperature of 41.5°C. January had the lowest temperature ever recorded, namely 2°C. The woody vegetation includes Quercus sp. Acacia nilotica, Pinus roxburgii, Tamarix aphylla and Acacia modesta. Dominant shrubs include Dodonaea viscosa, Justicia adhatoda. While Saccharum spontaneum, etc. are common (Figure 1).
Materials and Methods
Field visit and data collection
Regular visits were conducted from 2022-2024 to collect and identify the plant specimens and other ecological field data.
Specimen preservation
Collected plants were dried, preserved, and placed on herbarium sheets.
Plant identification
Plant identification was done using the Flora of Pakistan by (Ali et al., 1989-1993).
Floral inventory
A comprehensive floral inventory, alphabetized by plant families, has been compiled.
Classification by leaf size and habitat type
Plant species were classified according to leaf size and habitat type following (Hussain, 1989).
Biological spectrum analysis
Biological spectrum was analyzed using the methodology used by (Raunkiaer, 1934).
Results
Floristic diversity
Floral diversity refers to all plants, both wild and cultivated, present in any geographic area. The floristic composition of each region is influenced by several factors such as prevailing climatic conditions, soil properties, anthropogenic pressures and natural stresses. The total number of plant species present in a given geographical area is called its floral composition. The flora of the Swabi region includes 53 families, 102 genera and 140 species. The largest families were Poaceae (15 spp.), Rosaceae (11 spp.), Dryopteridaceae and Solanaceae (7 spp.), each Polygonaceae (6 spp.), Pteridaceae, Fabaceae, Moraceae and Cucurbitaceae (5 spp.), Euphorbiaceae, Chenopodiaceae, Aspleniaceae, Brassicaceae. and Salicaceae (4 spp.), Fagaceae, Lamiaceae, Cupressaceae and Adiantaceae (3 spp.), Simaroubaceae, Equisetaceae, Amaranthaceae, Urticaceae, Geraniaceae, Verbenaceae and Betulaceae (2 spp.). The remaining families had only one species (Figure 2; Table 1).
Legends: Key to abbreviations: Tables 1 and 2
Habit: T-Tree; S-Shrub; H-Herb; C-Climber. Life form: G-Geophytes; Th-Therophytes; H-Hemicrptophytes; Ch-Chamaephytes; P-phanerophytes; Mic-Microphanerophytes; Mesp-Mesophanerophytes; Megp-Megaphanerophytes. Leaf form: Ap- Aphyllous; L-Leptophyll; N-Nanophyll; Mic-Microphyll; Mes-Mesophyll; Meg-Megaphyll, Mac-Macrophyll. Habitat: A-agricultural fields; D-dry slopes; W-moist places; CU-cultivated; GY-Graveyards; F-forest; M-moist; S-shady places; R-rock crevices; Wp-waste places. Specimen (Herbarium) voucher number: HG-Huma Gul; ISL-Abbreviation of Herbarium of Quaid-i-Azam University Islamabad, Pakistan; QAU-Quaid-i-Azam University, Islamabad, Pakistan.
Herbaceous vegetation was dominant (95 species, 68%), followed by shrubs (13 species, 9%), trees (23 species, 16%) and climbing plants (9 species, 7%) (Figure 3, Table 2). Herbaceous vegetation dominates the study area, followed by trees, shrubs and climbing plants. This predominance of herbaceous vegetation is attributed to the overuse of trees and shrubs by the valley’s inhabitants, which has led to the decline of their population.
Table 1: Ecological characteristics and floristic diversity of the plants of the study area district Swabi.
|
S. No |
Plant Species |
Family |
Habit |
Life form |
Leaf form |
Habitat |
Life cycle |
Voucher numbers |
|
1 |
Adiantum capillus-veneris L. HG-1, ISL, QAU, Pakistan |
Adiantaceae |
Herb |
Hem |
Nan |
Mp |
Perennial |
HG-ISL-110 |
|
2 |
Asiantum venustum D. Don HG-2, ISL, QAU, Pakistan |
Adiantaceae |
Herb |
Hem |
Nan |
Mp |
Perennial |
HG-ISL-111 |
|
3 |
Polystichum wilsonii Christ. HG-3, ISL, QAU, Pakistan |
Dryopteridaceae |
Herb |
Hem |
Nan |
Wap |
Perennial |
HG-ISL-112 |
|
4 |
Cystopteris fragilis (L). Bernh. HG-4, ISL, QAU, Pakistan |
Cystopteridaceae |
Herb |
Geo |
Mic |
Wap |
Perennial |
HG-ISL-113 |
|
5 |
Dryopteris odontoloma (Moore.). HG-5, ISL, QAU, Pakistan |
Dryopteridaceae |
Herb |
Hem |
Lep |
Mp |
Perennial |
HG-ISL-114 |
|
6 |
Asplenium septentrionale (L.) HG-6, ISL, QAU, Pakistan |
Aspleniaceae |
Herb |
Hem |
Lep |
Wap |
Perennial |
HG-ISL-115 |
|
7 |
Polystichum discretum (D. Don) J. Sm HG-7, ISL, QAU, Pakistan |
Dryopteridaceae |
Herb |
Hem |
Nan |
Mp |
Perennial |
HG-ISL-116 |
|
8 |
Hypodematium crenatum (Forssk.) Kuhn. HG-8, ISL, QAU, Pakistan |
Dryopteridaceae |
Herb |
Hem |
Lep |
Mp |
Perennial |
HG-ISL-117 |
|
9 |
Asplenium adiantum-nigrum L. HG-9, ISL, QAU, Pakistan |
Aspleniaceae |
Herb |
Hem |
Nan |
Mp |
Perennial |
HG-ISL-118 |
|
10 |
Dryopteris sieboldii L. HG-10, ISL, QAU, Pakistan |
Dryopteridaceae |
Herb |
Hem |
Lep |
Wap |
Perennial |
HG-ISL-119 |
|
11 |
Dryopteris serrato-dentata (Bedd.) Hayata. HG-11, ISL, QAU, Pakistan |
Dryopteridaceae |
Herb |
Hem |
Lep |
Mp |
Perennial |
HG-ISL-120 |
|
12 |
Adiantum incisum L. HG-12, ISL, QAU, Pakistan |
Adiantaceae |
Herb |
Hem |
Lep |
Mp |
Perennial |
HG-ISL-121 |
|
13 |
Asplenium trichomanes L. HG-13, ISL, QAU, Pakistan |
Aspleniaceae |
Herb |
Hem |
Lep |
Mp |
Perennial |
HG-ISL-122 |
|
14 |
Polystichum lonchitis (L.) Roth. HG-14, ISL, QAU, Pakistan |
Dryopteridaceae |
Herb |
Hem |
Nan |
Mp |
Perennial |
HG-ISL-123 |
|
15 |
Ceterach dalhousiae (Hk.) C. Chr HG-15, ISL, QAU, Pakistan |
Aspleniaceae |
Herb |
Hem |
Nan |
Mp |
Perennial |
HG-ISL-124 |
|
16 |
Equisetum arvense L. HG-16, ISL, QAU, Pakistan |
Equisetaceae |
Herb |
Hem |
Lep |
Wap |
Perennial |
HG-ISL-125 |
|
17 |
Equisetum ramossimum Desf. HG-17, ISL, QAU, Pakistan |
Equisetaceae |
Herb |
Geo |
Aph |
Mp |
Perennial |
HG-ISL-126 |
|
18 |
Pteridium aquilinum (L.) Kuhn. HG-18, ISL, QAU, Pakistan |
Pteridaceae |
Herb |
Geo |
Mic |
Wap |
Perennial |
HG-ISL-127 |
|
19 |
Pteris cretica L. HG-19, ISL, QAU, Pakistan |
Pteridaceae |
Herb |
Hem |
Mic |
Mp |
Perennial |
HG-ISL-128 |
|
20 |
Pteris vitata L. HG-20, ISL, QAU, Pakistan |
Pteridaceae |
Herb |
Hem |
Mic |
Mp |
Perennial |
HG-ISL-129 |
|
21 |
Onychium contiguum Wall ex. Hope HG-21, ISL, QAU, Pakistan |
Pteridaceae |
Herb |
Geo |
Mic |
Wap |
Perennial |
HG-ISL-130 |
|
22 |
Cheilanthes pteridioides (Reichard.) C. Chr. HG-22, ISL, QAU, Pakistan |
Pteridaceae |
Herb |
Hem |
Nan |
Wap |
Perennial |
HG-ISL-131 |
|
23 |
Juniperus communis L. HG-23, ISL, QAU, Pakistan |
Cupressaceae |
Shrub |
Phan |
Lep |
F |
Perennial |
HG-ISL-132 |
|
24 |
Picea simithiana (Wall.) Bioss. HG-24, ISL, QAU, Pakistan |
Pinnaceae |
Tree |
Phan |
Nan |
F |
Perennial |
HG-ISL-133 |
|
25 |
Allium cepa L. HG-25, ISL, QAU, Pakistan |
Alliaceae |
Herb |
Geo |
Mes |
CU |
Annual |
HG-ISL-134 |
|
Table continues on next page............. |
||||||||
|
S. No |
Plant Species |
Family |
Habit |
Life form |
Leaf form |
Habitat |
Life cycle |
Voucher numbers |
|
26 |
Cyperus rotundus L. HG-26, ISL, QAU, Pakistan |
Cyperaceae |
Herb |
Ther |
Nan |
Mp |
Perennial |
HG-ISL-135 |
|
27 |
Oryza sativa L. HG-27, ISL, QAU, Pakistan |
Poaceae |
Herb |
Ther |
Mic |
CU |
Perennial |
HG-ISL-136 |
|
28 |
Hordium vulgare L. HG-28, ISL, QAU, Pakistan |
Poaceae |
Herb |
Hem |
Mic |
Af |
Annual |
HG-ISL-137 |
|
29 |
Dicanthium annulatum (Forssk.) Stapf. HG-29, ISL, QAU, Pakistan |
Poaceae |
Herb |
Hem |
Nan |
Af |
Perennial |
HG-ISL-138 |
|
30 |
Cynodon dactylon L. HG-30, ISL, QAU, Pakistan |
Poaceae |
Herb |
Hem |
Lep |
Drp |
Perennial |
HG-ISL-139 |
|
31 |
Apluda mutica L. HG-31, ISL, QAU, Pakistan |
Poaceae |
Herb |
Hem |
Nan |
Af |
Annual |
HG-ISL-140 |
|
32 |
Avena fatula L. HG-32, ISL, QAU, Pakistan |
Poaceae |
Herb |
Ther |
Mic |
Af |
Annual |
HG-ISL-141 |
|
33 |
Zea maize L. HG-33, ISL, QAU, Pakistan |
Poaceae |
Herb |
Ther |
Mes |
Drp |
Annual |
HG-ISL-142 |
|
34 |
Amanathus spinosus L. HG-34, ISL, QAU, Pakistan |
Amaranthaceae |
Herb |
Ther |
Mic |
Wap |
Annual |
HG-ISL-143 |
|
35 |
Amaranthus viridis L. HG-35, ISL, QAU, Pakistan |
Amaranthaceae |
Herb |
Ther |
Mic |
Drp |
Annual |
HG-ISL-144 |
|
36 |
Nerium oleander L. HG-36, ISL, QAU, Pakistan |
Apocynaceae |
Shrub |
Phan |
Mes |
Mp |
Perennial |
HG-ISL-145 |
|
37 |
Hedra neplensiis K. Koch. HG-37, ISL, QAU, Pakistan |
Araliaceae |
Climber |
Phan |
Mes |
F |
Perennial |
HG-ISL-146 |
|
38 |
Calotropis procera (Willd.) R. Brown HG-38, ISL, QAU, Pakistan |
Asclepediaceae |
Shrub |
Cham |
Mes |
Drp |
Perennial |
HG-ISL-147 |
|
39 |
Berberis Lycium L. HG-39, ISL, QAU, Pakistan |
Berberidaceae |
Shrub |
Phan |
Nan |
Rp |
Annual |
HG-ISL-148 |
|
40 |
Betula utilis D. Don HG-40, ISL, QAU, Pakistan |
Betulaceae |
Tree |
Phan |
Mes |
F |
Perennial |
HG-ISL-149 |
|
41 |
Alnus nitida (spach). Endl. HG-41, ISL, QAU, Pakistan |
Betulaceae |
Tree |
Phan |
Mes |
Wap |
Annual |
HG-ISL-150 |
|
42 |
Raphanus sativus L. HG-42, ISL, QAU, Pakistan |
Brassicaceae |
Herb |
Ther |
Mac |
CU |
Annual |
HG-ISL-151 |
|
43 |
Verbasaccum thapsus L. HG-43, ISL, QAU, Pakistan |
Brassicaceae |
Herb |
Ther |
Meg |
Drp |
Perennial |
HG-ISL-152 |
|
44 |
Thlaspi arvense L. HG-44, ISL, QAU, Pakistan |
Brassicaceae |
Herb |
Ther |
Nan |
Wap |
Annual |
HG-ISL-153 |
|
45 |
Thlaspi griffthianum Boiss HG-45, ISL, QAU, Pakistan |
Brassicaceae |
Herb |
Ther |
Nan |
Wap |
Annual |
HG-ISL-154 |
|
46 |
Cannabis sativa L. HG-46, ISL, QAU, Pakistan |
Cannabaceae |
Herb |
Ther |
Mic |
Wap |
Annual |
HG-ISL-155 |
|
47 |
Chenopodium album L. HG-47, ISL, QAU, Pakistan |
Chenopodiaceae |
Herb |
Ther |
Nan |
Drp |
Annual |
HG-ISL-156 |
|
48 |
Chenopodium botrys L. HG-48, ISL, QAU, Pakistan |
Chenopodiaceae |
Herb |
Ther |
Mic |
Wap |
Annual |
HG-ISL-157 |
|
49 |
Chenopodium foliosum Aschers. HG-49, ISL, QAU, Pakistan |
Chenopodiaceae |
Herb |
Ther |
Nan |
Wap |
Annual |
HG-ISL-158 |
|
50 |
Chenopodium ambrosioides L. HG-50, ISL, QAU, Pakistan |
Chenopodiaceae |
Herb |
Ther |
Mes |
Wap |
Annual |
HG-ISL-159 |
|
Table continues on next page............. |
||||||||
|
S. No |
Plant Species |
Family |
Habit |
Life form |
Leaf form |
Habitat |
Life cycle |
Voucher numbers |
|
51 |
Sedum hispanicum L. HG-51, ISL, QAU, Pakistan |
Crassulaceae |
Climber |
Hem |
Nan |
Mp |
Perennial |
HG-ISL-160 |
|
52 |
Cucumis melo L. HG-52, ISL, QAU, Pakistan |
Cucurbitaceae |
Climber |
Ther |
Mes |
Drp |
Annual |
HG-ISL-161 |
|
53 |
Luffa cylindrica L. HG-53, ISL, QAU, Pakistan |
Cucurbitaceae |
Climber |
Ther |
Mic |
CU |
Annual |
HG-ISL-162 |
|
54 |
Cucumis sativus L. HG-54, ISL, QAU, Pakistan |
Cucurbitaceae |
Climber |
Ther |
Mac |
CU |
Annual |
HG-ISL-163 |
|
55 |
Cucurbita maxima Duch. Ex Lam. HG-55, ISL, QAU, Pakistan |
Cucurbitaceae |
Climber |
Ther |
Meg |
CU |
Annual |
HG-ISL-164 |
|
56 |
Cucurbita Pepo L. HG-56, ISL, QAU, Pakistan |
Cucurbitaceae |
Climber |
Ther |
Meg |
CU |
Annual |
HG-ISL-165 |
|
57 |
Euphorbia helioscopia L. HG-57, ISL, QAU, Pakistan |
Euphorbiaceae |
Herb |
Ther |
Nan |
Drp |
Annual |
HG-ISL-166 |
|
58 |
Euphorbia timctoria L. HG-58, ISL, QAU, Pakistan |
Euphobiaceae |
Herb |
Ther |
Mic |
Drp |
Annual |
HG-ISL-167 |
|
59 |
Euphorbia Peplus L. HG-59, ISL, QAU, Pakistan |
Euphobiaceae |
Herb |
Ther |
Lep |
Af |
Annual |
HG-ISL-168 |
|
60 |
Riccinus communis L. HG-60, ISL, QAU, Pakistan |
Euphobiaceae |
Shrub |
Phan |
Mic |
Drp |
Perennial |
HG-ISL-169 |
|
61 |
Quercus Baloot Griffth. HG-61, ISL, QAU, Pakistan |
Fagaceae |
Tree |
Phan |
Mic |
Drp |
Perennial |
HG-ISL-170 |
|
62 |
Fummaria indica L. HG-62, ISL, QAU, Pakistan |
Fummariaceae |
Herb |
Ther |
Lep |
Drp |
Annual |
HG-ISL-171 |
|
63 |
Erodium cicutarium L. HG-63, ISL, QAU, Pakistan |
Geraniaceae |
Herb |
Ther |
Mes |
Wap |
Annual |
HG-ISL-172 |
|
64 |
Quercus incana Roxb. HG-64, ISL, QAU, Pakistan |
Fagaceae |
Tree |
Phan |
Mic |
Drp |
Perennial |
HG-ISL-173 |
|
65 |
Geranium colinum Sweet. HG-65, ISL, QAU, Pakistan |
Geraniaceae |
Herb |
Hem |
Mic |
F |
Perennial |
HG-ISL-174 |
|
66 |
Swertia cordata (G. Don) Clarke HG-66, ISL, QAU, Pakistan |
Gentianaceae |
Herb |
Ther |
Lep |
Drp |
Annual |
HG-ISL-175 |
|
67 |
Mentha longifolia (L.) Huds. HG-67, ISL, QAU, Pakistan |
Lamiaceae |
Herb |
Hem |
Nan |
Mp |
Perennial |
HG-ISL-176 |
|
68 |
Quercus dilatata Royle. HG-68, ISL, QAU, Pakistan |
Fagaceae |
Tree |
Phan |
Mic |
Drp |
Perennial |
HG-ISL-177 |
|
69 |
Mirabilis jalapa L HG-69, ISL, QAU, Pakistan |
Nyctaginaceae |
Herb |
Ther |
Mes |
Drp |
Perennial |
HG-ISL-178 |
|
70 |
Ajuga bracteosa Wall. ex Benth. HG-70, ISL, QAU, Pakistan |
Lamiaceae |
Herb |
Hem |
Mic |
Drp |
Perennial |
HG-ISL-179 |
|
71 |
Ocimum basilicum L. HG-71, ISL, QAU, Pakistan |
Lamiaceae |
Herb |
Cham |
Nan |
Drp |
Perennial |
HG-ISL-180 |
|
72 |
Morus nigra L. HG-72, ISL, QAU, Pakistan |
Moraceae |
Herb |
Phan |
Mes |
Drp |
Perennial |
HG-ISL-181 |
|
73 |
Juglans regia L. HG-73, ISL, QAU, Pakistan |
Juglandaceae |
Tree |
Phan |
Mic |
Drp |
Perennial |
HG-ISL-182 |
|
74 |
Morus macroura Miq. HG-74, ISL, QAU, Pakistan |
Moraceae |
Herb |
Phan |
Mes |
Drp |
Perennial |
HG-ISL-183 |
|
75 |
Myrtus communis L. HG-75, ISL, QAU, Pakistan |
Myrtaceae |
Shrub |
Phan |
Mic |
Mp |
Perennial |
HG-ISL-184 |
|
Table continues on next page............. |
||||||||
|
S. No |
Plant Species |
Family |
Habit |
Life form |
Leaf form |
Habitat |
Life cycle |
Voucher numbers |
|
76 |
Ficus johanis Boiss. HG-76, ISL, QAU, Pakistan |
Moraceae |
Herb |
Phan |
Mes |
Drp |
Perennial |
HG-ISL-185 |
|
77 |
Morus alba L. HG-77, ISL, QAU, Pakistan |
Moraceae |
Herb |
Phan |
Mes |
Drp |
Perennial |
HG-ISL-186 |
|
78 |
Ficus palmata Forssk. HG-78, ISL, QAU, Pakistan |
Moraceae |
Herb |
Phan |
Mes |
Drp |
Perennial |
HG-ISL-187 |
|
79 |
Jasminum officinale L. HG-79, ISL, QAU, Pakistan |
Oleaceae |
Shrub |
Phan |
Nan |
Drp |
Annual |
HG-ISL-188 |
|
80 |
Oxalis corniculata L. HG-80, ISL, QAU, Pakistan |
Oxalidaceae |
Herb |
Ther |
Nan |
Sp |
Annual |
HG-ISL-189 |
|
81 |
Medicago minima (L.) Grufb. HG-81, ISL, QAU, Pakistan |
Fabaceae |
Herb |
Ther |
Nan |
Af |
Annual |
HG-ISL-190 |
|
82 |
Melilotus officinalis (Linn.) Desr. HG-82, ISL, QAU, Pakistan |
Fabaceae |
Herb |
Ther |
Nan |
Mp |
Annual |
HG-ISL-191 |
|
83 |
Vicia sativa L. HG-83, ISL, QAU, Pakistan |
Fabaceae |
Climber |
Ther |
Nan |
Af |
Annual |
HG-ISL-192 |
|
84 |
Trifolium repens L. HG-84, ISL, QAU, Pakistan |
Fabaceae |
Herb |
Ther |
Nan |
F |
Perennial |
HG-ISL-193 |
|
85 |
Trigonella gracilis Benth. HG-85, ISL, QAU, Pakistan |
Fabaceae |
Herb |
Ther |
Nan |
Mp |
Perennial |
HG-ISL-194 |
|
86 |
Platanus orientalis L. HG-86, ISL, QAU, Pakistan |
Platanaceae |
Tree |
Phan |
Mes |
F |
Perennial |
HG-ISL-195 |
|
87 |
Rumex dentatus L. HG-87, ISL, QAU, Pakistan |
Polygonaceae |
Herb |
Hem |
Mes |
Mp |
Annual |
HG-ISL-196 |
|
88 |
Rumex hastatus D. Don HG-88, ISL, QAU, Pakistan |
Polygonaceae |
Herb |
Cham |
Nan |
Drp |
Perennial |
HG-ISL-197 |
|
89 |
Bistorta amplexicaulis (D. Don) HG-89, ISL, QAU, Pakistan |
Polygonaceae |
Herb |
Hem |
Mes |
F |
Perennial |
HG-ISL-198 |
|
90 |
Polygonum barbatum L. HG-90, ISL, QAU, Pakistan |
Polygonaceae |
Herb |
Ther |
Nan |
Mp |
Perennial |
HG-ISL-199 |
|
91 |
Punica grantaum L. HG-91, ISL, QAU, Pakistan |
Polygonaceae |
Tree |
Phan |
Mic |
Drp |
Perennial |
HG-ISL-200 |
|
92 |
Ranunculus muricatus L. HG-92, ISL, QAU, Pakistan |
Polygonaceae |
Herb |
Geo |
Mic |
Wap |
Annual |
HG-ISL-201 |
|
93 |
Ziziphus mauritiana Lam. HG-93, ISL, QAU, Pakistan |
Rosaceae |
Tree |
Phan |
Nan |
Drp |
Perennial |
HG-ISL-202 |
|
94 |
Potentilla nepalensis Hook. HG-94, ISL, QAU, Pakistan |
Rosaceae |
Herb |
Hem |
Mic |
F |
Perennial |
HG-ISL-203 |
|
95 |
Rosa alba L. HG-95, ISL, QAU, Pakistan |
Rosaceae |
Shrub |
Phan |
Nan |
CU |
Perennial |
HG-ISL-204 |
|
96 |
Rubus ulmifolius Schott HG-96, ISL, QAU, Pakistan |
Rosaceae |
Shrub |
Phan |
Mic |
Mp |
Perennial |
HG-ISL-205 |
|
97 |
Rubus sanctus Schreber HG-97, ISL, QAU, Pakistan |
Rosaceae |
Shrub |
Phan |
Mic |
Mp |
Perennial |
HG-ISL-206 |
|
98 |
Prunus domestica L. HG-98, ISL, QAU, Pakistan |
Rosaceae |
Tree |
Phan |
Mes |
CU |
Perennial |
HG-ISL-207 |
|
99 |
Prunus persica L. Batsch. HG-99, ISL, QAU, Pakistan |
Rosaceae |
Tree |
Phan |
Mes |
CU |
Perennial |
HG-ISL-208 |
|
100 |
Prunus cornuta (Wall. Ex. Royle.) HG-100, ISL, QAU, Pakistan |
Rosaceae |
Tree |
Phan |
Mes |
F |
Perennial |
HG-ISL-209 |
|
Table continues on next page............. |
||||||||
|
S. No |
Plant Species |
Family |
Habit |
Life form |
Leaf form |
Habitat |
Life cycle |
Voucher numbers |
|
101 |
Salix babylonica L. HG-101, ISL, QAU, Pakistan |
Salicaceae |
Tree |
Phan |
Mic |
Wap |
Perennial |
HG-ISL-210 |
|
102 |
Prunus armeniaca L. HG-102, ISL, QAU, Pakistan |
Rosaceae |
Tree |
Phan |
Mes |
CU |
Perennial |
HG-ISL-211 |
|
103 |
Pyrus pashia Ham. Ex. D. Don. HG-103, ISL, QAU, Pakistan |
Rosaceae |
Tree |
Phan |
Mic |
CU |
Annual |
HG-ISL-212 |
|
104 |
Salix tetrasperma Roxb. HG-104, ISL, QAU, Pakistan |
Salicaceae |
Tree |
Phan |
Mes |
Wap |
Perennial |
HG-ISL-213 |
|
105 |
Populus alba Wall. HG-105, ISL, QAU, Pakistan |
Salicaceae |
Tree |
Phan |
Mes |
CU |
Perennial |
HG-ISL-214 |
|
106 |
Populus nigra L. HG-106, ISL, QAU, Pakistan |
Salicaceae |
Tree |
Phan |
Mac |
CU |
Perennial |
HG-ISL-215 |
|
107 |
Pyrus communis L. HG-107, ISL, QAU, Pakistan |
Rosaceae |
Tree |
Phan |
Mic |
CU |
Perennial |
HG-ISL-216 |
|
108 |
Dodonaea viscosa (L.) Jacq. HG-108, ISL, QAU, Pakistan |
Sapindaceae |
Shrub |
Phan |
Mic |
Drp |
Perennial |
HG-ISL-217 |
|
109 |
Veronica polita Fries. HG-109, ISL, QAU, Pakistan |
Scrophulariaceae |
Herb |
Ther |
Nan |
Mp |
Annual |
HG-ISL-218 |
|
110 |
Datura innoxia Mill HG-110, ISL, QAU, Pakistan |
Solanaceae |
Herb |
Ther |
Mes |
Wap |
Annual |
HG-ISL-219 |
|
111 |
Datura stramonium L. HG-111, ISL, QAU, Pakistan |
Solanaceae |
Herb |
Ther |
Mes |
Wap |
Annual |
HG-ISL-220 |
|
112 |
Lycopersicon esculentum Miller HG-112, ISL, QAU, Pakistan |
Solanaceae |
Herb |
Ther |
Mes |
CU |
Annual |
HG-ISL-221 |
|
113 |
Solanum nigrum L. HG-113, ISL, QAU, Pakistan |
Solanaceae |
Herb |
Ther |
Mic |
Drp |
Annual |
HG-ISL-222 |
|
114 |
Solanum pseudo-capsicum L. HG-114, ISL, QAU, Pakistan |
Solanaceae |
Herb |
Ther |
Mic |
G |
Perennial |
HG-ISL-223 |
|
115 |
Solanum tuberosum L. HG-115, ISL, QAU, Pakistan |
Solanaceae |
Herb |
Geo |
Mes |
CU |
Perennial |
HG-ISL-224 |
|
116 |
Urtica dioica L. HG-116, ISL, QAU, Pakistan |
Urticaceae |
Herb |
Ther |
Mic |
Mp |
Perennial |
HG-ISL-225 |
|
117 |
Debregessia salcifolia (D. Don) Rendle. HG-117, ISL, QAU, Pakistan |
Urticaceae |
Shrub |
Phan |
Mic |
Mp |
Perennial |
HG-ISL-226 |
|
118 |
Vitis vinifera L. HG-118, ISL, QAU, Pakistan |
Vitaceae |
Climber |
Phan |
Mes |
CU |
Perennial |
HG-ISL-227 |
|
119 |
Tribulus terrestris L. HG-119, ISL, QAU, Pakistan |
Zygophyllaceae |
Herb |
Hem |
Lep |
Wap |
Annual |
HG-ISL-228 |
|
120 |
Triticum aestivum (L.) HG-120, ISL, QAU, Pakistan |
Poaceae |
Herb |
Ther |
Mic |
CU |
Annual |
HG-ISL-229 |
|
121 |
Avena sativa HG-121, ISL, QAU, Pakistan |
Poaceae |
Herb |
Ther |
Nan |
W |
Annual |
HG-ISL-230 |
|
122 |
Dichanthium annulatum L. HG-122, ISL, QAU, Pakistan |
Poaceae |
Herb |
Hem |
Nan |
W |
Perennial |
HG-ISL-231 |
|
123 |
Physalis minima L. HG-123, ISL, QAU, Pakistan |
Solanaceae |
Herb |
Cham |
Mic |
W |
Annual |
HG-ISL-232 |
|
124 |
Cupressus sempervirens L. HG-124, ISL, QAU, Pakistan |
Cupressaceae |
Tree |
Meg |
Mes |
CU |
Perennial |
HG-ISL-333 |
|
125 |
Verbena officinalis L. HG-125, ISL, QAU, Pakistan |
Verbenaceae |
Herb |
Ther |
Nan |
W |
Perennial |
HG-ISL-334 |
|
Table continues on next page............. |
||||||||
|
S. No |
Plant Species |
Family |
Habit |
Life form |
Leaf form |
Habitat |
Life cycle |
Voucher numbers |
|
126 |
Lantana camara L. HG-126, ISL, QAU, Pakistan |
Verbenaceae |
Shrub |
Ther |
Mic |
W |
Perennial |
HG-ISL-335 |
|
127 |
Datura alba L. HG-127, ISL, QAU, Pakistan |
Simaroubaceae |
Herb |
Cham |
Mes |
W |
Annual |
HG-ISL-336 |
|
128 |
Verbascum thapsus L. HG-128, ISL, QAU, Pakistan |
Simaroubaceae |
Herb |
Nan |
Mic |
W |
Perennial |
HG-ISL-337 |
|
129 |
Arundo donax L. HG-129, ISL, QAU, Pakistan |
Poaceae |
Herb |
Phan |
Mac |
W |
Perennial |
HG-ISL-338 |
|
130 |
Cymbopogan citratus Spreng. HG-130, ISL, QAU, Pakistan |
Poaceae |
Herb |
Hem |
Nan |
CU |
Perennial |
HG-ISL-339 |
|
131 |
Desmostachya bipinnata (L.) Stapf. HG-131, ISL, QAU, Pakistan |
Poaceae |
Herb |
Hem |
Mac |
W |
Perennial |
HG-ISL-340 |
|
132 |
Phalaris minor L. HG-132, ISL, QAU, Pakistan |
Poaceae |
Herb |
Ther |
Mic |
W |
Annual |
HG-ISL-341 |
|
133 |
Sorghum halepense (L.) Pers. HG-133, ISL, QAU, Pakistan |
Poaceae |
Herb |
Geo |
Mic |
W |
Perennial |
HG-ISL-342 |
|
134 |
Colocasia esculentus L. HG-134, ISL, QAU, Pakistan |
Araceae |
Herb |
Geo |
Meg |
CU |
Perennial |
HG-ISL-343 |
|
135 |
Phoenix dactylifera L. HG-2, ISL, QAU, Pakistan |
Arecaceae |
Tree |
Meg |
Mic |
CU |
Perennial |
HG-ISL-344 |
|
136 |
Asparagus officianalis L. HG-136, ISL, QAU, Pakistan |
Asparagaceae |
Herb |
Nan |
Lep |
CU |
Perennial |
HG-ISL-345 |
|
137 |
Narcissus poeticus L HG-137, ISL, QAU, Pakistan |
Amaryllidaceae |
Herb |
Meg |
Mes |
CU |
Perennial |
HG-ISL-346 |
|
138 |
Thuja orientalis L. HG-138, ISL, QAU, Pakistan |
Cupressaceae |
Tree |
Meg |
Nan |
CU |
Perennial |
HG-ISL-347 |
|
139 |
Cynoglossum glochidiatum Wall. Ex HG-139, ISL, QAU, Pakistan |
Boraginaceae |
Herb |
Ther |
Mic |
Drp |
Perennial |
HG-ISL-348 |
|
140 |
Impatiens bicolor Royle. HG-140, ISL, QAU, Pakistan |
Balsaminaceae |
Herb |
Ther |
Mes |
Mp |
Annual |
HG-ISL-349 |
Legends: Key to abbreviations: Tables 1, 2.
Biological spectrum of vegetation
In the present study, a Raunkiaerean classification is applied, study reveals that therophytes are the most abundant life form with (48 spp., 30%), followed by phanerophytes (39 spp., 25%), Hemicryptophytes (33 spp., 21%), Nanophanerophytes (2 spp., 1%), Megaphanerophytes (4 spp., 3%), Geophytes (9 spp., 6%), Mesophanerophytes (18 spp., 11%), and Chamaephytes (5 spp., 3%), were the second most common life forms (Figure 4).
Plant parts used and mode of preparation
Examination of leaf size spectra (Figure 5), Microphyll (43 spp., 31%), followed by Nanophyll (38 spp., 27%), Mesophylls (34 spp., 24%), Leptophyll with (15 spp., 11%), Macrophyll with (5 spp., 3%), Megaphyll with (4 spp., 3%) and Aphyllous has only (1 species) (Figure 5). Plant species are also classified based on their habitat. The results showed that the largest number of species were found in Dry places (31 species., 22%), followed by Moist places (29 species., 21%), Cultivated areas (26 species., 18%), Wasteland areas (23 species., 16%), Wet places (11 spp., 8%), forests places (10 spp., 7%), Agricultural areas (7 spp., 5%). While the rest of all Rocky, Shady and Graveyards places have only (1 spp., 1%) (Figure 6).
Table 2: Summary of ecological characteristics of plants of the study area.
|
S. No |
Characteristics |
Number |
Percentage % |
|
1 |
Vegetation |
||
|
Families |
53 |
-- |
|
|
Genera |
102 |
-- |
|
|
Species |
140 |
-- |
|
|
2 |
Habit |
||
|
Herbs |
95 |
68% |
|
|
Shrubs |
13 |
9% |
|
|
Trees |
23 |
16% |
|
|
Climbers |
9 |
7% |
|
|
3 |
Life form (Spectrum) |
||
|
Therophytes |
48 |
30% |
|
|
Phanerophytes |
39 |
25% |
|
|
Geophytes |
9 |
6% |
|
|
Hemicrptophytes |
33 |
21% |
|
|
Chamaephytes |
5 |
3% |
|
|
Megaphanerophytes |
4 |
3% |
|
|
Nanophanerophytes |
2 |
1% |
|
|
Mesophanerophytes |
18 |
11% |
|
|
4 |
Leaf form |
||
|
Microphyll |
43 |
31% |
|
|
Nanophyll |
38 |
27% |
|
|
Mesophyll |
34 |
24% |
|
|
Leptophyll |
15 |
11% |
|
|
Macrophyll |
5 |
3% |
|
|
Megaphyll |
4 |
3% |
|
|
Aphyllous |
1 |
1% |
|
|
5 |
Habitat |
||
|
Dry places |
31 |
22% |
|
|
Cultivated |
26 |
18% |
|
|
Forest |
10 |
7% |
|
|
Agricultural fields |
7 |
5% |
|
|
Rocky place |
1 |
1% |
|
|
Shady places |
1 |
1% |
|
|
Waste places |
23 |
16% |
|
|
Moist places |
29 |
21% |
|
|
Wet places |
11 |
8% |
|
|
Graveyards |
1 |
1% |
|
|
6 |
Life cycle |
||
|
Annual |
48 |
34% |
|
|
Perennial |
92 |
66% |
|
Discussion
The flora of the Swabi region includes 53 families, 102 genera and 140 species. The largest families were
Poaceae (15 spp.), Rosaceae (11 spp.), Dryopteridaceae and Solanaceae (7 spp.), each Polygonaceae (6 spp.), Pteridaceae, Fabaceae, Moraceae and Cucurbitaceae (5 spp.), Euphorbiaceae, Chenopodiaceae, Aspleniaceae, Brassicaceae. and Salicaceae (4 species), Fagaceae, Lamiaceae, Cupressaceae and Adiantaceae (3 species), Simaroubaceae, Equisetaceae, Amaranthaceae, Urticaceae, Geraniaceae, Verbenaceae and Betulaceae (2 species). The remaining families had only one species. Research in floriculture provides basic information for further investigation of taxonomic and ecological information and for planning sustainable management and conservation of plant resources (Amjad et al., 2017). Many studies, including those by (Durrani et al., 2005) have shown that some families are dominant. The existence of these families was confirmed in the Flora of Pakistan by (Ali et al., 1989-1993) and it was emphasized that they have a wide distribution. Additionally, (Ullah and Badshah, 2017) reported in their study in Lajbouk that the dominant family was Poaceae, followed by Lamiaceae, Asteraceae and Solanaceae. Ullah et al. (2020), described 250 species in 77 families; Asteraceae and Lamiaceae are the main dominant families. These results are in close agreement with those from Jammu and Kashmir (Sharma et al., 2018), in which Asteraceae was identified as the dominant family, followed by Rosaceae, Lamiaceae and Poaceae.
Herbaceous vegetation was dominant (95 spp., 68%), followed by shrubs (13 spp., 9%), trees (23 spp., 16%) and climbing plants (9 spp., 7%). Herbaceous vegetation dominates the study area, followed by trees, shrubs and climbing plants. Similar patterns were observed at different intervals (Khan et al., 2017) in Ranizai, Swat (Ali et al., 2019) in Nowshera region; Swat, (Naveed et al., 2012) Karak, (Anjum et al., 2020) in Baluchistan, (Ullah and Badshah, 2017) in the Jelar Valley; Akhtar in Miandam, Swat (Khalid, 2017) and (Khan et al., 2017) in Darra Adam Khel. The prevalence of herbaceous vegetation and the excessive consumption of trees and shrubs by the inhabitants of the valley lead to a decrease in the decomposition of trees and shrubs. These findings highlighted the urgent need for numerous improvements and conservation efforts. In the present study, therophytes are the most abundant life form therophytes with (48 spp., 34%), followed by phanerophytes (39 spp., 28%), Hemicryptophytes (33 spp., 24%), Nanophanerophytes (2 spp., 1%), Megaphanerophytes (4 spp., 3%), Geophytes (9 spp., 6%), Mesophanerophytes (18 spp., 11%), and Chamaephytes (5 spp., 4%), were the second most common life forms. The physiognomy of flora and vegetation is influenced by life forms and environmental factors. Raunkiær (1934) proposed a classification of life forms based on the placement of permanent structures in adverse conditions that affect the physiognomy of flora and vegetation. Our results are consistent with those of (Cain and Castro, 1959). Similar findings have been documented in studies conducted in Gadoon and Swabi (Sher et al., 2014). The finding of our results is strongly coincides with that of (Haq et al., 2019), who reported the prevalence of therophytes in the region. Similarly, (Kar et al., 2010) obtained similar spectra of life forms during their survey in the grasslands of Odisha, India. Examination of leaf size spectra, Microphyll (43 spp., 31%), followed by Nanophyll (38 spp., 27%), Mesophylls (34 spp., 24%), Leptophyll with (15 spp., 11%), Macrophyll with (5 spp., 3%), Megaphyll with (4 spp., 3%) and Aphyllous has only (1 spp.). Leaf size plays a crucial role in determining various plant functions, such as photosynthesis and transpiration. Understanding the leaf size spectrum of plant species can provide information about their physiological processes and community dynamics (Oosting, 1948). These results are consistent with those reported by (Malik et al., 2007), who showed that similar leaf size classes predominate in Kashmir and Quetta. The results showed that the largest number of species were found in dry places (31 species., 22%), followed by moist places (29 spp., 21%), cultivated areas (26 spp., 18%), wasteland areas (23 spp., 16%), Wet places (11 spp., 8%), forests places (10 spp., 7%), agricultural areas (7 spp., 5%). While the rest of all rocky, shady and Graveyards places have only (1 spp., 1%). The habitat conditions in the region are predominantly dry as the maximum number of species are found in dry habitats, followed by forests. In the present study, we are also classified the Plant species based on their habitat. Various researchers such as (Samreen et al., 2016) have also conducted similar studies. They classified plant species based on their habitat type. Therefore, our findings are relevant in this regard. The biological spectrum (life forms and leaf size spectra) is the most important feature and is widely used in studying vegetation. The life forms of plant species in a region determine the macro and micro climatic conditions of the region (Shimwell, 1971) while determination of leaf size classes is useful for understanding the physiological processes of plant species and their communities (Oosting, 1956). Several works have been published on the floristic lists and ecological characteristics of different Pakistani and foreign locations, such as (Batalha et al., 2002; Kar et al., 2010; Amjad et al., 2012).
Conclusion
This study concludes that the flora of the Swabi region presents a diversity dominated by arid habitats, as evidenced by the maximum number of species found in this area. Although this study provides basic information on the flora of district Swabi, further studies are needed to assess the conservation status of the wild flora and collect quantitative data on the vegetation. Restoration of degraded forests is recommended, prioritizing on-site efforts to facilitate the natural flowering of plants in their natural habitat, rather than resorting to practices elsewhere.
Acknowledgements
The authors highly thankful to anonymous reviewers for their comments to improve the manuscript. We are also thankful to local communities for their help during data collection.
Novelty Statement
This study provides the first comprehensive analysis of the floristic composition and biological spectrum of District Swabi, Khyber Pakhtunkhwa. It highlights unique ecological patterns and adaptive plant strategies in an underexplored region of Pakistan.
Author’s Contribution
Anwar Hussain Khan, Nasira Bibi: Collected and analyzed the data.
Rayyan Komal and Shabir Ahmad: Wrote the text.
Huma Gul: Wrote the final version of the text.
All authors approved the final version of the manuscript.
List of abbreviations
HG, Huma Gul; ISL, Herbarium of Quaid-i-Azam University Islamabad, Pakistan; QAU, Quaid-i-Azam University, Islamabad, Pakistan.
Conflict of interest
The authors have declared no conflict of interest.
References
Ali, S., Shah, S.Z., Khan, M.S., Khan, W.M., Khan, Z., Hassan, N. and Zeb, U., 2019. Floristic list, ecological features and biological spectrum of district Nowshera, Khyber Pakhtunkhwa, Pakistan. Acta Ecol. Sin., 39: 133-141. https://doi.org/10.1016/j.chnaes.2018.08.007
Ali, S.I. and Nasir, Y.J., 1989-1993. Flora of Pakistan-Islamabad, Karachi, pp. 191-204.
Amjad, M.S, Arshad, M., Page, S., Qureshi, R. and Mirza, S.N., 2017. Floristic composition, biological spectrum and phenological pattern of vegetation in the subtropical forest of Kotli District, AJK, Pakistan. Pure Appl. Biol., 2017(2): 426-447. https://doi.org/10.19045/bspab.2017.60043
Amjad, M.S., Hameed, A. and Malik, Z.H., 2012. Life form and leaf spectra reported from sub-tropical to Alpine and Subalpine Zoane of Basu Hills, District Skardu Gilgit Pakistan. Int. J. Emerg. Sci., 2(4): 543-551.
Anjum, S., Hussain, F., Durrani, M.J., Masood, A., Mushtaq, A., Rizwan, S. and Behlil, F., 2020. Floristic Composition, Ecological characteristics and Ethnobotanical profile of protected and open grazing land of Karkhasa, Balochistan. Pak. J. Anim. Pl. Sci., 30(2): 420-430. https://doi.org/10.36899/JAPS.2020.2.0036
Batalha, M.A. and Martins, F.R., 2002. Life-form spectra of Brazilian cerrado sites. Flora-Morphol. Distribut. Funct. Ecol. Plants, 197(6): 452-460. https://doi.org/10.1078/0367-2530-00062
Cain, S.A. and Castro, G.D.O., 1959. Manual of vegetation analysis, pp. 337.
Catarino, L., Martins, E.S. and Diniz, M.A., 2002. Vegetation structure and ecology of the Cufada Lagoon (Guinea-Bissau). Afr. J. Ecol., 40(3): 252-259. https://doi.org/10.1046/j.1365-2028.2002.00367.x
Durrani, M.J. and Hussain, F., 2005. Ecological characteristics of plants of Harboi rangeland, Kalat, Pakistan. J. Trop. Subtrop. Bot., 13(2): 130-138.
Haq, S.M., Malik, A.H., Khuroo, A.A. and Rashid, I., 2019. Floristic composition and biological spectrum of Keran-a remote valley of northwestern Himalaya. Acta Ecol. Sin., 39(5): 372-379. https://doi.org/10.1016/j.chnaes.2018.12.001
Hussain, F., 1989. Field and laboratory manual of plant ecology. National Academy of Higher Education, University Grants Commission, pp. 422.
Kar, P.K., Biswal, A.K. and Barik, K.L., 2010. Floristic composition and biological spectrum of a grassland community of Rangamatia in the district of Mayurbhanj, Odisha. J. Curr. Sci., 15(2): 465-469.
Khalid, S., 2017. Phytosociological and ethnobotanical studies of Mohmand agency Doctoral dissertation, Islamia College Peshawar.
Khan, A., Khan N., Ali, K. and Rahman, I.U., 2017. An assessment of the floristic diversity, life-forms and biological spectrum of vegetation in Swat Ranizai, District Malakand, Khyber Pakhtunkhwa, Pakistan. Sci. Technol. Dev., 36(2): 61-78.
Malik, Z.H., Hussain, F. and Malik, N.Z., 2007. Life form and leaf size spectra of plant communities Harbouring Ganga Chotti and Bedori Hills during 1999-2000. Int. J. Agric. Biol., 9(6): 833-838.
Maqsood, A.M.A., Khan, W.M., Khan, M.S., Waheed, M.W.M. and Ali, S.A., 2015. Taxonomic study of family Papilionaceae of district Swabi, Khyber Pakhtunkhwa, Pakistan, pp. 125-128. https://doi.org/10.19045/bspab.2015.41017
Naveed, S., Hussain, F., Khattak, I. and Badshah, L., 2012. Floristic composition and ecological characteristics of Olea-Acacia forest of Shamshokii District Karak. Glob. J. Incorporat., 12(8): 31-36.
Oosting, H.J., 1956. The study of plant communities, 2nd edition, pp. 69-78.
Oosting, H.J., 1948. The study of plant communities. Soil Sci., 66(2): 163. https://doi.org/10.1097/00010694-194808000-00014
Panda, S.S., Dhal, N.K., Dash, A. and Panda, S.C., 2014. Floristic diversity of Khandapara forest ranges of Nayagarh District Odisha, India. J. Plant Sci., 3(1): 2319-3824.
Rashid, A., Swati, M.F., Sher, H. and Al-Yemeni, M.N., 2011. Phytoecological evaluation with detail floristic appraisal of the vegetation arround Malam Jabba, Swat, Pakistan. Asian Pac. J. Trop. Biomed., 1(6): 461-467. https://doi.org/10.1016/S2221-1691(11)60101-9
Raunkiaer, C., 1934. The life forms of plants and statistical plant geography; being the collected papers of C. Raunkiær.
Samreen, U., Ibrar, M. and Badshah, L., 2016. Floristic composition, ecological characters and biological characters of Darazinda, FRDI Khan, Pakistan. Int. Invent. J. Agric. Soil Sci., 4(1): 9-21.
Sharma, V. and Sharma, N.P., 2018. The phytodiversity and comparative account of biological spectrum of Dehradun and Mussoorie region. Res. J. Life Sci. Bioinf. Pharma. Chem. Sci., 4(5): 250-259.
Sher, Z., Hussain, F. and Badshah, L., 2014. Biodiversity and ecological characterization of the flora of Gadoon Rangeland, District Swabi, Khyber Pakhtunkhwa, Pakistan. Iran. J. Bot., pp. 96-108.
Shimwell, D.W., 1971. The description and classification of vegetation Sedgwick and Jackson 322. London.
Thakur, M., Santvan V.K. and Nigam, A., 2012. Floristic composition and biological spectrum of Darlaghat wild life sanctuary Solan Himachal Pradesh, India. N. Y. Sci. J., 12: 1-14.
Ullah, S. and Badshah, L., 2017. Floristic structure and ecological attributes of Jelar valley flora, district Upper Dir, Pakistan. J. Biodiv. Environ. Sci., 10(5): 89-105.
Ullah, S., Rahman, A., Ullah, I. and Ahmad, I.M., 2020. First floristic inventory and biological spectrum of flora of Lajbouk, Dir Lower, Khyber Pakhtunkhwa, Pakistan. Biosci. Res., 17(3): 1633-1642.