Floristic Diversity of Jabal Al-Ward, Southwest Tabuk Region, Kingdom of Saudi Arabia
by
, , , and
Ahmed Elkordy
1,*
,
Iman H. Nour
2
,
Faten Y. Ellmouni
3,
Najla A. Al Shaye
4,
Dhafer A. Al-Bakre
5 and
Ahmed EL-Banhawy
6
1
Botany and Microbiology Department, Faculty of Science, Sohag University, Sohag 82524, Egypt
2
Botany and Microbiology Department, Faculty of Science, Alexandria University, Alexandria 21511, Egypt
3
Botany Department, Faculty of Science, Fayoum University, Fayoum 63514, Egypt
4
Department of Biology, College of Science, Princess Nourah bint Abdulrahman University, Riyadh 11564, Saudi Arabia
5
Biology Department, College of Science, University of Tabuk, Tabuk 47512, Saudi Arabia
6
Botany and Microbiology Department, Faculty of Science, Suez Canal University, Ismailia 41522, Egypt
*
Author to whom correspondence should be addressed.
Agronomy 2022, 12(11), 2626; https://doi.org/10.3390/agronomy12112626
Submission received: 7 October 2022
/
Revised: 21 October 2022
/
Accepted: 21 October 2022
/
Published: 25 October 2022
(This article belongs to the Special Issue Recent Progress in Plant Taxonomy and Floristic Studies)
Abstract
:Jabal Al-Ward is one of the Hijazi mountains situated between Al-Ulā and Al-Wajh, southwest Tabuk Province, Saudi Arabia’s northwesterly border region. It is considered the highest mountain in this area and is enriched in wildlife. For the first time, the present research aimed to investigate the floristic composition, phytogeographical distribution, and plant diversity in Jabal Al-Ward. One hundred ninety-eight species representing 47 plant families have been identified. The Asteraceae, Poaceae, and Fabaceae represented more than a third of the region’s floristic composition. The perennial species (53.5%) were dominant over the annuals (46.46%). This is a prominent feature in Jabal Al-Ward, where the perennial species may be more tolerant of climatic changeability than the annuals. Seven life form categories were found; therophytes (46.46%) showed to be the most common life form. In addition, there were four main phytogeographical groups: Mono-regional, Bi-regional, Pluri-regional, and Worldwide. The Mono-regional and Bi-regional categories had the highest participation, with 38.5% and 37.4%, respectively. Thirty-six species (18.2%) were found to be native to the Saharo-Arabian region. The Saharo-Arabian region was combined with eight more regions, including Saharo-Arabian/Sudano-Zambesian (12.6%), Irano-Turanian/Saharo-Arabian (9.1%), Mediterranean/Saharo-Arabian (5.6%), Irano-Turanian/Mediterranean/Saharo-Arabian (4.5%), Irano-Turanian/Saharo-Arabian/Sudano-Zambesian (2%), Euro-Siberian/Irano-Turanian/Mediterranean/Saharo-Arabian and Saharo-Arabian/Sudanian (1% each), Mediterranean/Saharo-Arabian/Sudano-Zambesian, and Irano-Turanian/Mediterranean/Saharo-Arabian/Saharo-Zambesian (0.5% each). The current study demonstrated the highest species richness compared to earlier research on various locations in Tabuk Province. In future work, the species and endemic richness along elevation gradients should be studied in Jabal Al-Ward. As well as the IUCN status of each taxon, the DNA barcoding of endangered species will be of great significance if applied in the surveyed area.
1. Introduction
The Kingdom of Saudi Arabia’s total area is around 2,250,000 km2. This vast area holds diverse heterogenic landscapes. It is considered an arid or semi-arid region, where the xerophytic plants represent the highest proportion of Saudi Arabian flora [1]. The country’s topography reflects the diversified flora explored by Collenette [2] and Chaudhary [3,4,5]. The flora of Saudi Arabia is one of the wealthiest biodiversity areas in the Arabian Peninsula, with substantial crops and medicinal plants [6]. Saudi Arabia contained 2223 species and 816 genera assigned to 129 families, with about 147 endemic species [5]. The flora’s taxa are of combined origin; North African, East African, Mediterranean, and Irano-Turanian plants [7,8].
The Tabuk region occupies approximately 146,072 km2 and is situated in the northwestern part of Saudi Arabia, with diverse ecosystems and habitats [9,10]. One of the most important agricultural areas in Saudi Arabia is the Tabuk region, which produces about a quarter of the country’s olive and dates. A floristic survey was conducted in eight discrete regions of Tabuk by Rajasab [11] to reveal 198 plant species belonging to 52 families. Eighty-two species representing 30 families were recognized by Moawed and Ansari [12] in the coastal areas of the Red Sea (from Ras Hemaid to Umluj road across Al Wajh and Dhiba regions) in Tabuk province. Al-Mutairi et al. [13] recorded ninety-six species exemplifying thirty-eight families at four localities in Tabuk (Sharma, Alqan, Al-Lwaz Mountains, and Alzetah). A total of 102 species belonging to 34 families were recorded in the Alaqan region by Moawed [14]. At the Harrat ArRahah, a volcanic field in South Tabuk, 135 species represent 34 families by Fakhry and Al-Kenany [15]. In addition, Alghanem et al. [16] identified 30 perennial species (15 families) at Al-Wadi Al-akhder. At the same time, 69 weed species representing 20 families were detected in farms of the Tabuk region [17]. Al Mutairi [9] reported one hundred and sixty-three species assigned to forty-one families at five sites (Aldesah, Alzetah, Alawz, Harra and Sharma). Ansari et al. [18] have estimated the identified species cited in the different studies of Tabuk and mentioned two hundred twenty-seven species in their comprehensive review. These species belonged to 157 genera and 45 angiosperms’ families, including 12 endangered species. However, Astragalus collenettiae Hedge & Podlech was the only endemic species recorded by Fakhry & Kenany [15] in the Harrat ArRahah.
Achillea fragrantissima (Forssk.) Sch.Bip., Artemisia judaica L., Ochradenus baccatus Delile and Rhazya stricta Decne. Were mentioned to have potent anti-microbial activity against nosocomial pathogens [19]. Al-Mutairi et al. [13] and Moawed [14] reported that the dominant plant families were: Asteraceae, Brassicaceae, Chenopodiaceae, Fabaceae, Lamiaceae, Poaceae, Resedaceae, and Zygophyllaceae. Moreover, the plant life form categories, phytogeographical affinities, and the economic importance of the vegetation in this area have been studied [9,13,14,20].
Al-Mutairi et al. [13] highlighted the importance of exploring floristic compositions for analyzing socioeconomic and vegetation in this unique area. Moreover, Al-Mutairi et al. [9,13] stated that Tabuk is a biodiversity hot spot region and should be subjected to a conservation program to protect its natural resources. Assessing the floristic composition in a particular area provides insights into species, habitats, or ecosystem diversity. Thus, suitable conservation strategies should be implemented to save the threatened taxa and their habitats [21]. In addition, studies on regional floras are crucial to perform cross-biome comparisons. These studies also serve as the basis for further analyses of the plant communities’ function, structure, and evolution in order to better understand the delimitation and mapping of biomes [22,23].
Jabal Al-Ward is one of the Hijazi mountains located between Al-Ulā and Al-Wajh, southwest Tabuk province, where this region is about 900 and 1600 m asl. However, Jabal Al-Ward is regarded as the highest mountain in this region, with up to 2096 m asl [24]. Generally, Jabal Al-Ward is enriched in wildlife, including flora, amphibians, and reptiles [25,26]. This region mainly consists of some valleys that cut across the mountains and act as large natural drainages [24].
Despite the previous trials to describe the floristic composition of the Tabuk region [9,11,12,13,14,15,16,17,19,20], Jabal Al-Ward has remained unsatisfactorily studied. Therefore, the present study contributed to investigating and evaluating the floristic composition, phytogeographical distribution, and plant diversity of the wild plant taxa growing in the Jabal Al-Ward region, southwest Tabuk, Saudi Arabia, for the first time.
2. Materials and Methods
2.1. Study Area
This study was performed in the Jabal Al-Ward region (Figure 1) during most plant species’ active growing seasons.
The excursions were conducted during the growing seasons of 2019 and 2020. The eremic vegetation was surveyed in 25 localities, in the mountain ridges, distributed to cover the study area, and their elevations ranged from 1435 m to 1807 m asl. The geographical coordinates were recorded for each locality (Table 1). Each locality was visited at least three times to ensure that the required field data was entirely recorded. Sampling surveys using quadrats of 50 m × 50 m is recommended for arid habitats [27,28]; however, the quadrate size 10 m × 10 m was suitable for the current study, as the species number was constant in the latter quadrate size.
The quadrate was randomly distributed at each site to record the vegetation of the studied area. Species included in the quadrate’s border were counted in the sampling. The plants with their vegetative branches spreading over the quadrate’s sides were also considered, even though their roots were anchored outside the borders.
The study area lies within the eremic subtropical dry zone, characterized by hot summers and warm winters [29]. The Tabuk region had 33.5 mm of annual precipitation on average from 1978 to 2013, which is less than the 250 mm worldwide average for arid regions [30]. Data concerning monthly climatology of min-, mean- and max-temperature, and precipitation during the period of 1991–2020 at Tabuk, Saudi Arabia, were obtained from the Climate Change Knowledge Portal [31]. The average annual rainfall from 1991 to 2020 was 5.725 mm, and the minimum was detected in August and September (0.42 and 0.4 mm, respectively), while the maximum was in November (14.95 mm). The average monthly minimum temperature was 6.9 °C in January, whereas the average maximum was 37.81 °C in August (Figure 2).
2.2. Plant Collection and Species Identification
Identification of the collected taxa followed Collenette [2], Cope [32], Mighaid [33], and Chaudhary [3,4,5]. Nomenclature was revised for accepted names through the Plants of the World Online (POWO) [34] and Taxonomic Name Resolution Service (TNRS) [35]. Voucher specimens were deposited in the herbarium of the Biology Department, College of Sciences, Taibah University Al-Ulā branch. Life form categories were recognized after Govaerts et al. [36], who updated Raunkiaer’s [37] classification. Phytogeographical categories were distinguished based on Wickens [38], Zohary [39], and White and Léonard [40]. The generic coefficient (GC) was calculated according to Jaccard [41], which is the ratio of the total number of genera to the total number of species. The statistical analysis was performed using Microsoft Excel to create the charts and histograms.
3. Results
Floristic Composition
This study identified 198 vascular plant species in Jabal Al-Ward, and no gymnosperms were listed. The recorded taxa belonged to 152 genera in 47 plant families. The Dicotyledonous families accounted for 83%, while the Monocotyledonous represented 17% (Figure 3). The Monocotyledonous families are Asparagaceae, Asphodelaceae, Colchicaceae, Cyperaceae, Iridaceae, Liliaceae, and Poaceae. Perennial species constituted 53.54% (106 species); meanwhile, the annuals recorded 46.46% (92 species).
The floristic analysis of the Jabal Al-Ward region revealed the presence of the following families: Asteraceae (29 species), Poaceae (25 species), Fabaceae (23 species), and Brassicaceae (14 species); they account for (14.57%, 12.56%, 11.55%, and 7.53%) of the total flora of the study area respectively. Amaranthaceae, Lamiaceae, Solanaceae, and Zygophyllaceae were represented by 9–7 species, accounting for 8% of the entire flora. Apocynaceae, Boraginaceae, and Euphorbiaceae were represented by 6–5 species. Caryophyllaceae, Geraniaceae, Plantaginaceae, and Resedaceae were represented by four species. Two to three species represented ten plant families, while twenty-two plant families were represented by at least one plant species (Table 2, Figure 4). The species richness in Jabal Al-Ward accounted for 8.9%, genera 18.6%, and families 36.43% of the total flora of Saudi Arabia. The generic coefficient (%) is 76.8% in the study area, while Saudi Arabia accounted for 36.7%. Anthemis scrobicularis Yavin was the only endemic species recognized in the study area.
Seven life form categories were observed in the current study. The most frequent group was the therophytes, with 92 species, followed by chamaephytes, which were identified as 55 different species. There were 22 species of hemicryptophytes. Thirteen species were cryptophytes and twelve species were identified as phanerophytes. Three species were helophytes and one parasitic species was recorded in the Jabal Al-Ward area. Percentages of each life form relevant to the total number of species are illustrated in Figure 5.
The chorological analysis of Jabal Al-Ward vegetation showed that the Mono-regional group was represented by the highest number of taxa 76 (38.5%). It comprised seven chorotypes; Saharo-Arabian (18.2%) with 36 species accounted for the highest representation. The Saharo-Arabian region was combined with eight more regions, including Saharo-Arabian/Sudano-Zambesian (12.6%), Irano-Turanian/Saharo-Arabian (9.1%), Mediterranean/Saharo-Sindian (5.6%), Irano-Turanian/Mediterranean/Saharo-Arabian (4.5%), Irano-Turanian/Saharo-Arabian/Sudano-Zambesian (2%), Euro-Siberian/Irano-Turanian/Mediterranean/Saharo-Arabian, and Saharo-Arabian/Sudanian (1% each), Mediterranean/Saharo-Arabian/Sudano-Zambesian, and Irano-Turanian/Mediterranean/Saharo-Arabian/Sudano-Zambesian (0.5% each).
Followed by Irano-Turanian (7.10%), the latter chorotype was recorded by 14 species (7.10%). Additionally, it was found in eight different arrangements with other floristic regions, such as: Irano-Turanian/Saharo-Arabian (9.1%), Irano-Turanian/Mediterranean (8.10%), Irano-Turanian/Mediterranean/Saharo-Arabian (4.5%), Euro-Siberian/Irano-Turanian/Mediterranean (3%), Irano-Turanian/Saharo-Arabian/Sudano-Zambesian (2%), Euro-Siberian/Irano-Turanian and Euro-Siberian/Irano-Turanian/Mediterranean/Saharo-Arabian (1% each), and Irano-Turanian/Mediterranean/Saharo-Arabian/Sudano-Zambesian (0.5%). Fifteen species were documented to belong to the Mediterranean region and achieved 5.60% as a Mono-regional element. Furthermore, seven mixed regions were indicated, such as Irano-Turanian/Mediterranean (8.1%), Mediterranean/Saharo-Arabian (5.6%), Irano-Turanian/Mediterranean/Saharo-Arabian (4.5%), Euro-Siberian/Irano-Turanian/Mediterranean (3%), Euro-Siberian/Irano-Turanian/Mediterranean/Saharo-Arabian (1% each) and Mediterranean/Saharo-Arabian/Sudano-Zambesian and, Irano-Turanian/Mediterranean/Saharo-Arabian/Sudano-Zambesian (0.5% each). The Sudano-Zambesian chorotype has ten species representing 5.1% and it is found with four other mixed regions Finally, Cenchrus echinatus L. is an alien species representing the American type with 0.5%.
Afterward, the Bi-regional elements have six main chorotypes with 74 taxa (37.40%). The highest element was Saharo-Arabian/Sudano-Zambesian with 25 species representing 12.6%, followed by Irano-Turanian/Saharo-Arabian with 18 species (9.1%), Irano-Turanian/Mediterranean with 16 species (8.10%), then Mediterranean/Saharo-Arabian with 11 species (5.6%). Conversely, only 1% of the total number of species belonged to the Euro-Siberian/Irano-Turanian (Centaurea sinaica DC. and Malva neglecta Wallr.) and Saharo-Arabian/Sudanian (Heliotropium bacciferum Forssk. and Nanorrhinum hastatum (R.Br. ex Benth.) Ghebr.).
Subsequently, the Worldwide assemblage contained 25 species and occupied 12.60% of the recorded taxa. The Cosmopolitan types scored 5.60% for 11 species. The lowest scores were recorded for Paleotropical, Pantropical, and Neotropical at 3.50%, 3.0%, and 0.50%, respectively.
Finally, the Pluri-regional attained six chorotypes, accounting for 11.50% with 23 species. The Irano-Turanian/Mediterranean/Saharo-Arabian, Euro-Siberian/Irano-Turanian/Mediterranean, Euro-Siberian/Irano-Turanian/Mediterranean, and Irano-Turanian/Saharo-Arabian/Sudano-Zambesian exhibited 3.5%, 3%, and 2%, respectively. While one species was categorized for each of the following chorotypes: Mediterranean/Saharo-Arabian/Sudano-Zambesian (Rumex vesicarius L.) and Irano-Turanian/Mediterranean/Saharo-Arabian/Sudano-Zambesian (Citrullus colocynthis (L.) Schrad.) (Figure 6, Table 3).
4. Discussion
Tabuk province is characterized by diverse habitats, including coastal plains, valleys, dunes, wadis, salt pans (sabkhas), and mountain ridges [42]. These habitats represent biogeographic units that guarantee a perfect distribution of this region’s flora and fauna life regime [10]. Mountains are of great floristic and ecological importance in the Middle East. They provide a shelter for many species, which qualifies them as centers of species richness [43].
The Tabuk region has a high diversity of plants [9,20]. However, the present study demonstrates that the highest number of species (198 species representing 47 families) were recorded in one region, compared with the former studies performed in discrete areas of Tabuk [9,11,12,13,14,15,16,17].
The most dominant families are the Asteraceae, Poaceae, and Fabaceae. They represented more than a third of Jabal Al-Ward’s floristic composition. The dominance of these families over the others is attributed to their ability to seed dispersal efficiency of their taxa, leading to a high diversity and wide distribution [44]. Al-Mutairi [13] mentioned that the Asteraceae is dominant in a different area of the Tabuk region. Additionally, our findings concur with several floristic studies conducted at different Saudi Arabian localities [45,46,47]. However, fourteen percent of the total number of families were represented by only one species: Aizoaceae, Asparagaceae, Asphodelaceae, Cistaceae, Convolvulaceae, Crassulaceae, Cyperaceae, Ephedraceae, Iridaceae, Molluginaceae, Moraceae, Nitrariaceae, Nyctaginaceae, Orobanchaceae, Papaveraceae, Portulacaceae, Primulaceae, Rhamnaceae, Rubiaceae, Scrophulariaceae, Tamaricaceae, and Typhaceae. The three genera with the highest species richness are Astragalus (Fabaceae), Euphorbia (Euphorbiaceae), and Fagonia (Zygophyllaceae); four species have been reported for each genus. The generic coefficient is 76.8% in Jabal Al-Ward, which is more than twice that of Saudi Arabia. Based on the high percentage of generic coefficient, it can be concluded that there are more intergeneric competitions in the area [48]. Furthermore, Al-Nafie [49] mentioned that the existence of a certain number of species corresponding to different taxa is a salient characteristic of this region, showing high plant diversity. Members of the recognized families are also well known for their higher economic and medicinal potentiality [50,51,52,53,54,55,56,57,58]. Anthemis scrobicularis was the only endemic species recorded in the surveyed area [59]. Many studies also reported limited endemism in the various regions of the country [15,49,60,61,62].
In the current study, the perennial species were dominant over the annuals (53.54% to 46.46%). The perennial/annual ratio is affected by abiotic factors such as the aridity of the area and the amount of precipitation [62,63]. This is a notable characteristic of Jabal Al-Ward because perennial plants may be more tolerant of climatic changeability than annual plants [64]. The predominant life forms among the others are the therophytes (46.46%), followed by chamaephytes (27.78%) and phanerophytes (6.06%). These findings are in line with some research on desert ecosystems [13,14,15,44,45,46,47,60,65,66,67]. Thakur [48], Das, et al. [68] and Fadl et al. [60] reported that the dominance of the therophytic pattern and phanerophytes are associated with lower altitudes, warm-dry arid climate, and habitat disturbances. On the other hand, at higher altitudes, hemicryptophytes and cryptophytes overwhelm cold conditions. The relatively high occurrence of chamaephytes (27.78%) is also associated with the desert habitat, topography, and biotic factors [69]. However, floristic research documented the predominance of other life forms over therophytes in Jabal Fayfa, Mecca, and Taif [61,62,70]. Lower frequency was observed for the helophytes (1.52%) in the current study, as they are indicators of the wetlands [71,72]. Cistanche tubulosa (Schenk) Wight was the only parasitic species documented in Jabal Al-Ward, where it grows mainly on the root of the Calotropis procera (Aiton) Dryand. Tree, which is commonly distributed in some arid areas [73].
The identified species were classified into four major phytogeographical groups: Mono-regional, Bi-regional, Pluri-regional, and Worldwide. It was remarkable that the Mono-regional and Bi-regional groups achieved the highest representation at 38.5% and 37.4%, respectively. The presence of interzonal habitats contributes to the higher prevalence of Bi-regional elements [39]. The abundance of Pluri-regional and global taxa is another feature of the Saudi Arabian flora [49]. The existence of species growing in many regions of the world, or the widely distributed plants indicates the relationship between the Arabian Peninsula and these regions (Euro-Siberian, Irano-Turanian, Mediterranean, Sudanian, and Sudano-Zambesian). The dispersal of these species in the Arabian Peninsula is influenced by climate change and the long-distance migration of people, animals, and birds [70].
Saudi Arabia’s vegetation belongs to Saharo-Arabian region [39]. Thirty-six species belonged to the Saharo-Arabian region, with the best representation accounting for 18.2%. According to Zohary [74], Saharo-Sindian is corresponding to Saharo-Arabian. Abdel Khalik et al. [62] point out that the Saharo-Arabian and Sudano-Zambezian species are good indicators of desert habitats. This explains the present study’s relatively high contribution of Saharo-Arabian/Sudano-Zambesian. The Saharo-Arabian taxa in Saudi Arabia were developed gradually and discontinuously from some adjoining regions under the aridity’s effect, such as the Sudanian, Mediterranean, and Irano-Turanian regions [39]. Therefore, our findings are consistent with most studies carried out in the various Saudi Arabian provinces, especially Tabuk [12,13,14,45,65].
The Irano-Turanian chorotype was recorded by fourteen species (7.10%) and it was found in eight different arrangements with other floristic regions. The Irano-Turanian region is one of the world’s largest and most diverse floristic regions and serves as a source forthe halophytes (such as Halocnemum strobilaceum (Pall.) M.Bieb., Haloxylon salicornicum (Moq.) Bunge ex Boiss., Caroxylon imbricatum (Forssk.) Moq., Heliotropium bacciferum Forssk., H. crispum Desf., H. europaeum L., Tamarix aphylla (L.) H.Karst.), and xerophytes (representing the rest of the studied taxa) for adjacent countries [75,76]. The region is also characterized by relatively low precipitation and a long dry season. The maximum temperature was measured in the summer, similar to the hottest spots in the Sahara, while the minimum winter temperatures were lower than those recorded in the Mediterranean region [77]. These characters make this region a transition between the Saharo-Arabian and the Mediterranean.
Fifteen species were documented to belong to the Mediterranean region and achieved 5.60% as a Mono-regional element. According to Abdel Khalik et al. [62], the survival of Mediterranean species in the study area indicates a more mesic environment.
Recent studies conducted in the Arabian Peninsula have relied on DNA barcode markers to assess genetic variation among taxa in various geographical regions [78,79]. Projects are ongoing worldwide to create DNA barcode libraries for vascular plant flora and make these data accessible to conserve and utilize biodiversity [80]. DNA barcodes are used to enhance our understanding of how species evolve and interact and how we can delay their extinction [81,82].
5. Conclusions
The current study demonstrated the highest species richness compared to former studies performed in separate locations in Tabuk Province. One hundred ninety-eight plant species belonging to forty-seven plant families were identified in Jabal Al-Ward. The Asteraceae, Poaceae, and Fabaceae represented more than a third of Jabal Al-Ward’s floristic composition. Annual species (46.46% of the total) were subordinate to perennial species (53.54%). Perennial species may be more tolerant of climatic changeability than annuals. This is a prominent feature in Jabal Al-Ward. Therophytes (46.46%) exemplify the most predominant life forms over the others, as they are associated with lower altitudes, warm-dry arid climate, and habitat disturbances. The recorded plant species were classified into four phytogeographical categories, with the highest representations being for the Mono-regional and Bi-regional groups. The phytogeographical distribution of the species revealed that thirty-six species (18.2%) belonged to the Saharo-Arabian region. The Saharo-Arabian and Sudano-Zambezian species are reliable indicators of desert habitats, which explained the highest contribution of Saharo-Arabian Sudano-Zambesian in the present study. In Saudi Arabia, the Saharo-Arabian taxa were developed gradually and discontinuously from some adjoining regions such as the Sudanian, Mediterranean, and Irano-Turanian regions.
Author Contributions
Conceptualization, A.E. and A.E.-B.; methodology, A.E., A.E.-B., N.A.A.S. and D.A.A.-B.; Software, F.Y.E. and A.E.-B.; data curation, A.E., F.Y.E., A.E.-B. and I.H.N.; investigation, A.E., F.Y.E., A.E.-B. and I.H.N.; resources, A.E., A.E.-B., N.A.A.S. and D.A.A.-B.; Formal analysis, A.E., F.Y.E., A.E.-B. and I.H.N.; writing—original draft preparation, I.H.N., A.E., F.Y.E. and A.E.-B.; writing—review and editing, I.H.N., F.Y.E., A.E.-B., A.E., N.A.A.S. and D.A.A.-B.; funding acquisition, A.E., I.H.N., F.Y.E., N.A.A.S., D.A.A.-B. and A.E.-B. All authors have read and agreed to the published version of the manuscript.
Funding
This research received no external funding.
Data Availability Statement
The data presented in this study are available in this article.
Conflicts of Interest
The authors declare no conflict of interest.
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Figure 1.
Map of the Kingdom of Saudi Arabia showing the study area’s location. The red rectangle refers to Jabal Al-Ward region.
Figure 1.
Map of the Kingdom of Saudi Arabia showing the study area’s location. The red rectangle refers to Jabal Al-Ward region.
Figure 2.
Climatic diagram showing min-, mean- and max-temperature, and precipitation during (1991–2020) in Tabuk, Saudi Arabia. The chart is based on the Climate Change Knowledge Portal data (CCKP 2021).
Figure 2.
Climatic diagram showing min-, mean- and max-temperature, and precipitation during (1991–2020) in Tabuk, Saudi Arabia. The chart is based on the Climate Change Knowledge Portal data (CCKP 2021).
Figure 3.
Histogram of the family, genera, and species number based on class Dicotyledonous and Monocotyledonous in Jabal Al-Ward.
Figure 3.
Histogram of the family, genera, and species number based on class Dicotyledonous and Monocotyledonous in Jabal Al-Ward.
Figure 4.
The proportional contribution of plant families in Jabal Al-Ward.
Figure 5.
Life form spectrum of the recorded species in Jabal Al-Ward region. TH = Therophytes, CH = Chamaephytes, HEM = Hemicryptophytes, PH = Phanerophytes, GE = Geophytes, CR = Cryptophytes, HEL = Helophytes, PA = Parasites.
Figure 5.
Life form spectrum of the recorded species in Jabal Al-Ward region. TH = Therophytes, CH = Chamaephytes, HEM = Hemicryptophytes, PH = Phanerophytes, GE = Geophytes, CR = Cryptophytes, HEL = Helophytes, PA = Parasites.
Figure 6.
Floristic regions and chorotypes from the recorded taxa in Jabal Al-Ward. Note: American (AM), Cosmopolitan (COSM), Euro-Siberian (ES), Irano-Turanian (IT), Mediterranean (ME), Neotropical (NEO), Paleotropical (PAL), Pantropical (PAN), Saharo-Arabian (SA), Sudano-Zambesian (SZ), and Sudanian (SUD).
Figure 6.
Floristic regions and chorotypes from the recorded taxa in Jabal Al-Ward. Note: American (AM), Cosmopolitan (COSM), Euro-Siberian (ES), Irano-Turanian (IT), Mediterranean (ME), Neotropical (NEO), Paleotropical (PAL), Pantropical (PAN), Saharo-Arabian (SA), Sudano-Zambesian (SZ), and Sudanian (SUD).
Table 1.
Coordinates of 25 sampling sites in Jabal Al-Ward.
| Locations | Coordinates | |
|---|---|---|
| Latitude (N) | Longitude (E) | |
| 1 | 26°26′52.7″ | 37°15′51.9″ |
| 2 | 26°26′53.7″ | 37°15′52.7″ |
| 3 | 26°26′54.5″ | 37°15′53.3″ |
| 4 | 26°26′54.9″ | 37°15′54.2″ |
| 5 | 26°26′55.1″ | 37°15′55.1″ |
| 6 | 26°26′55.5″ | 37°15′56.1″ |
| 7 | 26°26′56.4″ | 37°15′56.5″ |
| 8 | 26°26′57.3″ | 37°15′57.2″ |
| 9 | 26°26′57.2″ | 37°15′58.2″ |
| 10 | 26°26′56.9″ | 37°15′59.4″ |
| 11 | 26°26′56.4″ | 37°16′00.8″ |
| 12 | 26°26′56.0″ | 37°16′02.4″ |
| 13 | 26°26′55.6″ | 37°16′03.5″ |
| 14 | 26°26′55.7″ | 37°16′04.7″ |
| 15 | 26°26′56.4″ | 37°16′05.2″ |
| 16 | 26°26′57.3″ | 37°16′05.3″ |
| 17 | 26°26′58.2″ | 37°16′05.6″ |
| 18 | 26°26′58.9″ | 37°16′06.1″ |
| 19 | 26°26′58.6″ | 37°16′07.1″ |
| 20 | 26°26′57.9″ | 37°16′07.9″ |
| 21 | 26°26′57.4″ | 37°16′08.5″ |
| 22 | 26°26′56.6″ | 37°16′09.1″ |
| 23 | 26°26′56.0″ | 37°16′09.8″ |
| 24 | 26°26′55.5″ | 37°16′10.7″ |
| 25 | 26°26′55.2″ | 37°16′11.8″ |
Table 2.
List of plant taxa recorded in Jabal Al-Ward. Life span: Annual (ANN), Perennial (PER). Life form: Chamaephytes (CH), Cryptophytes (CR), Helophytes (HEL), Hemicryptophytes (HEM), Parasites (PA), Phanerophytes (PH), Therophytes (TH). Chorotypes: American (AM), Cosmopolitan (COSM), Euro-Siberian (ES), Irano-Turanian (IT), Mediterranean (ME), Neotropical (NEO), Paleotropical (PAL), Pantropical (PAN), Saharo-Arabian (SA), Sudano-Zambesian (SZ), and Sudanian (SUD).
Table 2.
List of plant taxa recorded in Jabal Al-Ward. Life span: Annual (ANN), Perennial (PER). Life form: Chamaephytes (CH), Cryptophytes (CR), Helophytes (HEL), Hemicryptophytes (HEM), Parasites (PA), Phanerophytes (PH), Therophytes (TH). Chorotypes: American (AM), Cosmopolitan (COSM), Euro-Siberian (ES), Irano-Turanian (IT), Mediterranean (ME), Neotropical (NEO), Paleotropical (PAL), Pantropical (PAN), Saharo-Arabian (SA), Sudano-Zambesian (SZ), and Sudanian (SUD).
| Plant Family | Taxa | Life Form | Chorology | Life Span |
|---|---|---|---|---|
| Acanthaceae | Blepharis edulis (Forssk.) Pers. | CH | IT + SA + SZ | PER |
| Hygrophila auriculata (Schumach.) Heine | TH | PAN | ANN | |
| Aizoaceae | Aizoon canariense L. | TH | SZ | ANN |
| Amaranthaceae | Aerva javanica (Burm.f.) Juss. ex Schult. | CH | PAL | PER |
| Alternanthera pungens Kunth | TH | NEO | ANN | |
| Amaranthus hybridus L. | TH | PAN | ANN | |
| Bassia muricata (L.) Asch. | TH | IT + SA | ANN | |
| Bassia eriophora (Schrad.) Asch. | CH | IT + SA | PER | |
| Chenopodium murale L. | TH | COSM | ANN | |
| Halocnemum strobilaceum (Pall.) M.Bieb. | CH | IT + ME + SA | PER | |
| Haloxylon salicornicum (Moq.) Bunge ex Boiss. | CH | SA | PER | |
| Caroxylon imbricatum (Forssk.) Moq. Syn. Salsola imbricata Forssk. | PH | SZ | PER | |
| Apiaceae | Deverra tortuosa (Desf.) DC. | CH | SA | PER |
| Ferula sinaica Boiss. | HEM | IT | PER | |
| Apocynaceae | Calotropis procera (Aiton) Dryand. | PH | SA + SZ | PER |
| Apteranthes europaea (Guss.) Murb. Syn. Caralluma europaea (Guss.) N.E.Br. | CH | ME + SA | PER | |
| Leptadenia pyrotechnica (Forssk.) Decne. | PH | SA | PER | |
| Marsdenia tenacissima (Roxb.) Moon Syn. Pergularia tomentosa L. | CH | SA + SZ | PER | |
| Rhazya stricta Decne. | CH | SA + SZ | PER | |
| Solenostemma oleifolium (Nectoux) Bullock & E.A.Bruce ex Maire Syn. Solenostemma argel (Delile) Hayne | CH | SA | PER | |
| Asparagaceae | Bellevalia flexuosa Boiss. | CR | ME | PER |
| Asphodelaceae | Asphodelus tenuifolius Cav. | CR | SA + SZ | PER |
| Asteraceae | Achillea fragrantissima (Forssk.) Sch.Bip. | CH | IT + SA | PER |
| Achillea falcata L. | CH | IT | PER | |
| Anthemis scrobicularis Yavin | TH | IT + ME + SA | ANN | |
| Anthemis melampodina (Boiss.) Eig subsp. deserti | TH | ME + SA | ANN | |
| Artemisia herba-alba Asso | CH | SA | PER | |
| Artemisia judaica L. | CH | SA | PER | |
| Atractylis carduus (Forssk.) C. Chr. | TH | ME | ANN | |
| Calendula tripterocarpa Rupr. | TH | PAN | ANN | |
| Centaurea procurrens Sieber ex Spreng. | CH | ME | PER | |
| Centaurea sinaica DC. | TH | ES + IT | ANN | |
| Echinops glaberrimus DC. | HEM | SA | PER | |
| Echinops spinosissimus Turra | CH | IT + SA | PER | |
| Filago desertorum Pomel | TH | IT + SA | ANN | |
| Helichrysum stoechas (Ten.) Nyman subsp. barrelieri | HEM | ME | PER | |
| Ifloga spicata (Forssk.) Sch.Bip. | TH | SA | ANN | |
| Ifloga spicata (Forssk.) Sch. Bip. subsp. albescens Chrtek | TH | ME + SA | ANN | |
| Lactuca serriola L. | TH | IT | ANN | |
| Pseudognaphalium luteoalbum (L.) Hilliard & B.L.Burtt Syn. Laphangium luteoalbum (L.) Tzvelev | HEL | IT + ME + SA | PER | |
| Launaea procumbens (Roxb.) Ramayya & Rajagopal | TH | SA | ANN | |
| Launaea spinosa (Forsk.) Sch.Bip. ex Kuntze | CH | SA | PER | |
| Onopordum boissierianum Raab-Straube & Greuter Syn. Onopordum sibthorpianum Boiss. & Heldr. | HEM | ME + SA | PER | |
| Picris cyanocarpa Boiss. | TH | SA | ANN | |
| Pulicaria incisa (Lam.) DC. | CH | SA + SZ | PER | |
| Pulicaria undulata (L.) C.A.Mey. | CH | SA + SZ | PER | |
| Ramaliella tortuosissima (Boiss.) Zaika, Sukhor. & N.Kilian Syn. Scorzonera tortuosissima Boiss. | CH | IT + SA | PER | |
| Senecio glaucus L. | TH | IT + SA | ANN | |
| Sonchus oleraceus (L.) L. | TH | COSM | ANN | |
| Tanacetum sinaicum (Fresen.) Delile ex K.Bremer & Humphries | CH | IT | PER | |
| Urospermum picroides (L.) Scop. ex F.W.Schmidt | TH | IT + ME | ANN | |
| Boraginaceae | Alkanna orientalis (L.) Boiss. | CH | IT + ME | PER |
| Arnebia hispidissima (Lehm.) A.DC. | TH | SA + SZ | ANN | |
| Echium horridum Batt. | TH | ME + SA | ANN | |
| Gastrocotyle hispida (Forssk.) Bunge | TH | IT + SA | ANN | |
| Trichodesma africanum (L.) Sm. | TH | SA + SZ | ANN | |
| Heliotropiaceae | Heliotropium bacciferum Forssk. | CH | SA + SUD | PER |
| Heliotropium crispum Desf. | HEM | IT + SA | PER | |
| Heliotropium europaeum L. | TH | ES + IT + ME | ANN | |
| Brassicaceae | Coincya tournefortii (Gouan) Alcaraz, T.E.Díaz, Rivas Mart. & Sánchez-Gómez Syn. Brassica tournefortii Gouan | TH | ME + SA | ANN |
| Diplotaxis harra (Forssk.) Boiss. | TH | IT + SA | ANN | |
| Diplotaxis acris (Forssk.) Boiss. | TH | IT + ME | ANN | |
| Enarthrocarpus strangulatus Boiss. | TH | SA | ANN | |
| Eremobium aegyptiacum (Spreng.) Asch. ex Boiss. | HEM | SA | PER | |
| Eremobium aegyptiacum var. lineare (Delile) Zohary | HEM | SA | PER | |
| Farsetia aegyptia Turra | CH | SA + SZ | PER | |
| Lepidium didymum L. | TH | SA | ANN | |
| Matthiola arabica Boiss. | TH | SA | ANN | |
| Morettia canescens Boiss. | CH | ME | PER | |
| Morettia parviflora Boiss. | TH | SZ | ANN | |
| Rhamphospermum arvense (L.) Andrz. ex Besser Syn. Sinapis arvensis L. | TH | ME | ANN | |
| Sisymbrium irio L. | TH | ES + IT + ME + SA | ANN | |
| Zilla spinosa (L.) Prantl subsp. spinosa | CH | ES + IT + ME + SA | PER | |
| Caryophyllaceae | Gymnocarpos decandrus Forssk. | CH | SA | PER |
| Gypsophila viscosa Murray | TH | IT | ANN | |
| Polycarpaea robbairea (Kuntze) Greuter & Burdet | CH | SA + SZ | PER | |
| Silene villosa Forssk. | TH | SA | ANN | |
| Cistaceae | Helianthemum lippii (L.) Dum.Cours. | CH | SA + SZ | PER |
| Cleomaceae | Cleome amblyocarpa Barratte & Murb. | TH | SA + SZ | ANN |
| Cleome arabica L. | CH | SUD | PER | |
| Colchicaceae | Colchicum ritchii R.Br. | CR | SA | PER |
| Colchicum tunicatum Feinbrun | CR | IT | PER | |
| Convolvulaceae | Convolvulus arvensis L. | CR | PAL | PER |
| Crassulaceae | Umbilicus intermedius Boiss. | CR | IT + ME | PER |
| Cucurbitaceae | Citrullus colocynthis (L.) Schrad. | HEM | IT + ME + SA + SZ | PER |
| Cucumis prophetarum L. | HEM | SA | PER | |
| Cyperaceae | Cyperus rotundus L. | CR | COSM | PER |
| Ephedraceae | Ephedra aphylla Forssk. | PH | SA | PER |
| Euphorbiaceae | Chrozophora oblongifolia (Delile) A.Juss. ex Spreng. | CH | SZ | PER |
| Euphorbia granulata Forssk. | TH | SZ | ANN | |
| Euphorbia peplus L. | TH | COSM | ANN | |
| Euphorbia prostrata Aiton | TH | COSM | ANN | |
| Euphorbia retusa Forssk. | TH | COSM | ANN | |
| Fabaceae | Vachellia tortilis (Forssk.) Galasso & Banfi Syn. Acacia tortilis (Forssk.) Hayne | PH | SZ | PER |
| Alhagi graecorum Boiss. | CH | IT + ME | PER | |
| Astragalus eremophilus Boiss. | TH | IT + ME + SA | ANN | |
| Astragalus palaestinus Eig | TH | ME | ANN | |
| Astragalus spinosus (Forssk.) Muschl. | CH | IT + SA | PER | |
| Astragalus tribuloides Delile | TH | IT + SA | ANN | |
| Crotalaria aegyptiaca Benth. | HE | SZ | PER | |
| Hippocrepis cyclocarpa Murb. | TH | ME | ANN | |
| Hippocrepis unisiliquosa L. | TH | IT + SA | ANN | |
| Lotus corniculatus L. | HEM | COSM | PER | |
| Lotus glinoides Delile | TH | SZ | ANN | |
| Lotus lanuginosus Vent. | HEM | SA | PER | |
| Medicago laciniata (L.) Mill. | TH | SA | ANN | |
| Medicago polymorpha L. | TH | COSM | ANN | |
| Melilotus indicus(L.) All. | TH | PAL | ANN | |
| Onobrychis ptolemaica (Delile) DC. | HEM | IT | PER | |
| Ononis natrix L. | CH | ME | PER | |
| Retama raetam (Forssk.) Webb | PH | SA | PER | |
| Senna italica Mill. | CH | SZ | PER | |
| Tephrosia purpurea (L.) Pers. | CH | SA + SZ | PER | |
| Trigonella anguina Delile | TH | SA | ANN | |
| Trigonella glabra Thunb. subsp. glabra Syn. Trigonella hamosa Del. ex Smith | TH | ME + SA | ANN | |
| Trigonella stellata Forssk. | TH | IT + SA | ANN | |
| Geraniaceae | Erodium laciniatum (Cav.) Willd. | TH | SA | ANN |
| Erodium oxyrhinchum M.Bieb. | TH | SA + SZ | ANN | |
| Erodium oxyrhinchum (Boiss.) Schönb.-Tem.subsp. bryoniifolium | TH | IT | ANN | |
| Monsonia nivea (Decne.) Webb | CR | SA + SZ | PER | |
| Iridaceae | Moraea sisyrinchium (L.) Ker Gawl. | CR | IT + ME | PER |
| Lamiaceae | Pseudodictamnus undulatus (Benth.) Salmaki & Siadati Syn. Ballota undulata (Sieber ex Fresen.) Benth. | CH | ME | PER |
| Lavandula coronopifolia Poir. | CH | SA + SZ | PER | |
| Lavandula pubescens Decne. | CH | SA + SZ | PER | |
| Mentha longifolia (L.) Huds. | CH | PAL | PER | |
| Mentha longifolia (Briq.) Harley subsp. typhoides | HEM | PAL | PER | |
| Otostegia fruticosa (Forssk.) Schweinf. ex Penzig | CH | SA | PER | |
| Stachys aegyptiaca Pers. | CH | ME + SA | PER | |
| Teucrium polium L. | CH | IT + ME | PER | |
| Liliaceae | Gagea commutata K. Koch | CR | IT | PER |
| Gagea reticulata (Pall.) Schult. & Schult.f. | CR | IT | PER | |
| Malvaceae | Malva neglecta Wallr. | TH | ES + IT | ANN |
| Malva parviflora L. | TH | IT + ME | ANN | |
| Molluginaceae | Glinus lotoides L. | TH | PAL | ANN |
| Moraceae | Ficus palmata Forssk. | PH | SUD | PER |
| Nitrariaceae | Peganum harmala L. | HEM | IT + ME + SA | PER |
| Nyctaginaceae | Boerhavia repens L. | CH | PAL | PER |
| Orobanchaceae | Cistanche tubulosa (Schenk) Wight | PA | IT + SA + SZ | PER |
| Papaveraceae | Fumaria parviflora Lam. | TH | COSM | ANN |
| Plantaginaceae | Kickxia floribunda (Boiss.) Täckh. & Boulos | CH | SA | PER |
| Nanorrhinum hastatum (R.Br. ex Benth.) Ghebr. | CH | SA + SUD | PER | |
| Plantago ciliata Desf. | TH | IT + ME + SA | ANN | |
| Plantago lanceolata L. | TH | IT + ME + SA | ANN | |
| Poaceae | Avena barbata Pott ex Link | TH | ME | ANN |
| Bromus scoparius L. | TH | IT + ME + SA | ANN | |
| Bromus danthoniae Trin. | TH | IT | ANN | |
| Bromus madritensis L. | HEM | IT + ME | PER | |
| Cenchrus echinatus L. | TH | AM | ANN | |
| Centropodia fragilis (Guinet & Sauvage) Cope | TH | ME + SA | ANN | |
| Cutandia memphitica (Spreng.) Benth. | TH | IT + ME | ANN | |
| Cynodon dactylon (L.) Pers. | CR | PAN | PER | |
| Enneapogon desvauxii P.Beauv. | HEM | IT + SA | PER | |
| Eragrostis aegyptiaca (Willd.) Delile | TH | SZ | ANN | |
| Eremopyrum bonaepartis (Spreng.) Nevski | TH | IT | ANN | |
| Lamarckia aurea (L.) Moench | TH | IT + ME | ANN | |
| Lolium perenne L. | HEM | COSM | PER | |
| Panicum turgidum Forssk. | CR | SA + SZ | PER | |
| Parapholis incurva (L.) C.E.Hubb. | TH | IT + ME | ANN | |
| Phalaris minor Retz. | TH | IT + ME | ANN | |
| Phalaris paradoxa L. | TH | IT + ME | ANN | |
| Poa annua L. | TH | ES + IT + ME | ANN | |
| Polypogon monspeliensis (L.) Desf. | TH | IT + ME + SA | ANN | |
| Rostraria pumila (Desf.) Tzvelev | TH | ME + SA | ANN | |
| Schismus barbatus (L.) Thell. | TH | IT + SA | ANN | |
| Stipellula capensis (Thunb.) Röser &Hamasha Syn. Stipa capensis Thunb. | TH | IT + SA | ANN | |
| Stipa lagascae Roem. & Schult. | HEM | IT + ME | PER | |
| Stipa obtusa (Nees & Meyen) Hitchc. | HEM | SA + SZ | PER | |
| Stipagrostis ciliata (Desf.) De Winter | HEM | IT + SA + SZ | PER | |
| Polygonaceae | Rumex spinosus L. Syn. Emex spinosa (L.) Campd. | TH | PAN | ANN |
| Rumex vesicarius L. | TH | ME + SA + SZ | ANN | |
| Portulacaceae | Portulaca oleracea L. | TH | ME + SA | ANN |
| Primulaceae | Anagallis arvensis L. | TH | ES + IT + ME | ANN |
| Rhamnaceae | Ziziphus spina-christi (L.) Desf. | PH | SA + SZ | PER |
| Resedaceae | Caylusea hexagyna (Forssk.) M.L.Green | TH | SA + SZ | ANN |
| Ochradenus baccatus Delile | PH | SA | PER | |
| Reseda muricata C. Presl | CH | SA | PER | |
| Reseda sphenocleoides Deflers | CH | SA + SZ | PER | |
| Rubiaceae | Galium spurium L. | TH | ES + IT + ME | ANN |
| Scrophulariaceae | Verbascum sinaiticum Benth. | HEM | IT + SA | PER |
| Solanaceae | Datura innoxia Mill. | TH | COSM | ANN |
| Hyoscyamus desertorum (Asch. ex Boiss.) Täckh. | TH | SA | ANN | |
| Hyoscyamus pusillus L. | TH | IT | ANN | |
| Lycium depressum Stocks | PH | IT | PER | |
| Lycium shawii Roem. & Schult. | PH | SA + SZ | PER | |
| Solanum incanum L. | CH | SUD | PER | |
| Solanum americanum Mill. | HEM | ES + IT + ME | PER | |
| Withania somnifera (L.) Dunal | CH | IT + ME | PER | |
| Tamaricaceae | Tamarix aphylla (L.) H.Karst. | PH | IT + SA + SZ | PER |
| Typhaceae | Typha domingensis Pers. | HEL | PAN | PER |
| Urticaceae | Forsskaolea tenacissima L. | CH | SA + SZ | PER |
| Parietaria alsinifolia Delile | TH | SA | ANN | |
| Zygophyllaceae | Fagonia arabica L. | CH | SA | PER |
| Fagonia bruguieri DC. | CH | SA | PER | |
| Fagonia glutinosa Delile | CH | SA | PER | |
| Fagonia mollis Delile | CH | SA | PER | |
| Seetzenia lanata (Willd.) Bullock | TH | SUD | ANN | |
| Tetraena simplex (L.) Beier & Thulin | TH | SA + SZ | ANN | |
| Tribulus terrestris L. | TH | ES + IT + ME | ANN |
Table 3.
The number of the recorded taxa belonging to the main floristic categories and their relevant percentages (%) in Jabal Al-Ward. American (AM), Cosmopolitan (COSM), Euro-Siberian (ES), Irano-Turanian (IT), Mediterranean (ME), Neotropical (NEO), Paleotropical (PAL), Pantropical (PAN), Saharo-Arabian (SA), Sudano-Zambesian (SZ), and Sudanian (SUD).
Table 3.
The number of the recorded taxa belonging to the main floristic categories and their relevant percentages (%) in Jabal Al-Ward. American (AM), Cosmopolitan (COSM), Euro-Siberian (ES), Irano-Turanian (IT), Mediterranean (ME), Neotropical (NEO), Paleotropical (PAL), Pantropical (PAN), Saharo-Arabian (SA), Sudano-Zambesian (SZ), and Sudanian (SUD).
| Chorotype | Number of Species | Percentage (%) |
|---|---|---|
| Mono-Regional | ||
| AM | 1 | 0.50% |
| IT | 14 | 7.10% |
| ME | 11 | 5.60% |
| SA | 36 | 18.20% |
| SUD | 4 | 2.00% |
| SZ | 10 | 5.10% |
| Subtotal | 76 | 38.50% |
| Bi-regional | ||
| ES + IT | 2 | 1.00% |
| IT + ME | 16 | 8.10% |
| IT + SA | 18 | 9.10% |
| ME + SA | 11 | 5.60% |
| SA + SZ | 25 | 12.60% |
| SA + SUD | 2 | 1.00% |
| Subtotal | 74 | 37.40% |
| Pluri-regional | ||
| ES + IT + ME | 6 | 3.00% |
| IT + ME + SA | 9 | 4.50% |
| IT + SA + SZ | 4 | 2.00% |
| ME + SA + SZ | 1 | 0.50% |
| ES + IT + ME + SA | 2 | 1.00% |
| IT + ME + SA + SZ | 1 | 0.50% |
| Subtotal | 23 | 11.50% |
| Worldwide | ||
| COSM | 11 | 5.60% |
| NEO | 1 | 0.50% |
| PAL | 7 | 3.50% |
| PAN | 6 | 3.00% |
| Subtotal | 25 | 12.60% |
| Total | 198 | 100% |
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Elkordy, A.; Nour, I.H.; Ellmouni, F.Y.; Al Shaye, N.A.; Al-Bakre, D.A.; EL-Banhawy, A. Floristic Diversity of Jabal Al-Ward, Southwest Tabuk Region, Kingdom of Saudi Arabia. Agronomy 2022, 12, 2626. https://doi.org/10.3390/agronomy12112626
AMA Style
Elkordy A, Nour IH, Ellmouni FY, Al Shaye NA, Al-Bakre DA, EL-Banhawy A. Floristic Diversity of Jabal Al-Ward, Southwest Tabuk Region, Kingdom of Saudi Arabia. Agronomy. 2022; 12(11):2626. https://doi.org/10.3390/agronomy12112626
Chicago/Turabian StyleElkordy, Ahmed, Iman H. Nour, Faten Y. Ellmouni, Najla A. Al Shaye, Dhafer A. Al-Bakre, and Ahmed EL-Banhawy. 2022. "Floristic Diversity of Jabal Al-Ward, Southwest Tabuk Region, Kingdom of Saudi Arabia" Agronomy 12, no. 11: 2626. https://doi.org/10.3390/agronomy12112626
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