Volume 6, Issue 3, June Issue - 2018, Pages:572-581
|Authors: Ahmed Alghamdi, Khalil Mseddi, Mohanad Abdelgadir, Sherif Sharawy|
|Abstract: A reservoir in the current study describes where endemic plants are most likely to thrive and provide natural gene bank for native seed species. Twelve sites representing different altitudinal zones of Jabal Salma in Ha’il region, Saudi Arabia were regularly visited for two consecutive years. From each site 2–5 locations were investigated for floristic composition and types of vegetation. During the study, the presence of total 150 species representing 39 families was recorded. Among the reported species, the highest number of species (25 species) were belong to the family Asteraceae which was followed by the family Brassicaceae, (17 species), Fabaceae (14 species), Boraginaceae (11 species), Caryophyllaceae (10 species) and finally Poaceae (9 species). However, 15 other families including Acanthaceae, Convolvulaceae, Moraceae, Nyctaginaceae and Primulaceae, were monospecific which represented by only a single species. In addition, the effect of elevation on plant species distribution along altitudinal gradient of Jabal Salma has been noticed clearly in this study. According to the current findings, Jabal Salma can be strongly considered as a reservoir for native seed species as it provides refuge for 21 endangered species, 43 medicinal species, 45 ornamental species, 48 forage species and 13 edible species. However, despite accessibility difficulties, Jabal Salma “unfortunately” is not well protected against invasive species where 27 exotic species where recorded.|
|Full Text: 1 Introduction Worldwide, natural rangelands and grasslands have been severely degraded in the last few decades (Conant et al., 2017). Overgrazing and growth of human population (83% growth between 1990–2015) which exacerbate the issue of climatic change, have been reported as the main factors causing the loss of biological diversity of natural grasslands (Aukema et al., 2017). Rangelands of Saudi Arabia suffer strongly from harsh climate where long periods of drought and high temperatures take place along with intensive grazing (Baig et al., 2017). The Saudi Ministry of Environment, Water and Agriculture has previously declared many rangelands in Ha’il region, north of Saudi Arabia, as severely degraded zones in terms of plant biodiversity (Alghamdi, 2017). It has also raised an alarm about the invasion by external and dangerous exotic species. In addition, Mseddi et al., (2017) reported that many invasive plant species have been introduced to Ha’l’s natural landscapes from neighboring wheat and alfalfa fields of the surrounding regions. Recently, the Saudi Ministry of Environment and Water and Agriculture have set new ambitious plans in order to fight desertification and save the country’s natural landscapes including rangelands, grasslands, forests and wild areas. The aforementioned ministry has launched a restoration program for natural landscapes by planting four million trees by the end of year 2020. This program is designed to revive the Saudi flora by re-planting native species including trees and shrubs (Heneidy et al., 2017). Therefore, the Saudi government needs to look carefully for original resources of local seed species that can be planted in millions by 2020. Such native seed species can be collected from natural enclosure habitats that are difficult to be accessed by humans and grazing animals. Mseddi et al. (2016) reported that enclosure rangelands for a period of 15 years can restore a large part of local seed species. We argued that native seed species can be exploited in restoration programs and to afford species with economic value (such as; forage, ornamental and medicinal species) which currently are completely disappeared in the natural regions. Collecting native seed species in Saudi Arabia particularly in Ha’il region has been proved by Alghamdi (2017) who has successfully collected 40 species from protected rangeland zone compared to neighboring open area where only 15 species were collected. We also argued that plant biodiversity measures such as species diversity and richness should provide important indicators of the assessment of human impacts on the ecosystems, and therefore such measures can serve as a basis for conservation and restoration programs. Therefore, the objective of the current work was to assess the floristic composition and plant species diversity in Jabal Salma at the east of Ha’il region. Jabal Salma was chosen because it is a special topographic area consisting of a chain of mountains which is difficult to be accessed by humans and their livestock. To the best of our knowledge the current study will be the first of its kind. Hoping that these difficulty accessed mountains will provide unique source of information about native seeds of a diverse species to be reported in this paper. 2 Materials and methods 2.1 The study area Jabal Salma is a chain of mountains located about 60 km far from the city of Ha’il and extends from the north-east to the south-west about 13 km (Figure 1). Ha’il region located in northern central of Saudi Arabia and extends between 25° 29'N and 38° 42'E. The altitude varies from 992 (plateau) to 1300 meters (the highest peak). Belonging to Saudi Arabia, Jabal Salma in Hail region, has a desert climate characterized by elevated heat during the day and a drop in night temperatures, with a very low annual precipitations. Due to the influence of the sub-tropical high pressure system, there is a significant difference in humidity and temperature. Such as in other parts of Saudi Arabia, the sun-rays are intense and rarely diffused by clouds. Minimum temperature can reached about 5°C in January while in summer temperature raised up to 50 ° C during August, with a daytime variation of 25°C. Precipitation is erratic and irregular with an average of 150 mm/year. The main source of precipitation comes from the winter cyclones of the Mediterranean Sea and the Eastern Atlantic Ocean. Jabal Salma is far from the sea, but it rains in the rainy season. The driest months extend from September to mid-October (Schultz & Whitney 1986). The relative humidity recorded in summer was very low and not exceed 15% in July, whereas, it was about 53 % in January with an annual average of 31% 2.2 Floristic composition and plant species diversity Flora investigation in Jabal Salma was conducted in 12 site locations in which numerous quadrats of 5 X 5 m were randomly allocated. Number of plants was counted and their frequencies were obtained following Pielou, (1959). Randomly placed quadrats have been aligned to cover 3 altitudinal zones of Jabal Salma from down to the top (Valley, Foothill and Top). The potentiality of the economic value of plant species was assessed according to the literature and information collected from local inhabitants. Plant specimens were studied and identified using a Leica stereoscope. The taxonomic classification of the species was identified following Collenette (1999) and Chaudhary (2001). 3 Results and Discussion The floristic composition and vegetation features in Jabal Salma were studied during two consecutive years (2015-2016). The study showed very high plant diversity with richness index of 150 species belonging to 39 families (Table 1).This number of species in Jabal Salma represent 6.9% of the total plant species recorded in Saudi Arabia (2172 species reported by AlZubaide et al., 2017). Low biological diversity percentage of Jabal Salma in comparison to Saudi Arabia’s diversity could be attributed to the harsh environment conditions particularly low rainfall and high temperature which resemble the Sahara climate that covers most of the country (El-Ghanim et al., 2010). The floristic analysis in Jabal Salma showed that the Asteraceae was the most abundant family with the highest number of species (25 species). Previously the Asteracea family has been reported as the dominant family in Hail area (El-Ghanim et al., 2010). The second largest family in the study area is the Brassicacea which is represented by 17 species followed by Fabacea (14 species), Boraginaceae (11 species), Caryophyllaceae (10 species) and finally Poaceae (9 species) (Figure 2). These families were reported as the most dominant flora in Jabal Salma. These families were followed by 15 families represented by 2-6 species and 19 families represented only by single species. The floristic analysis showed that annuals plants were the most abundant plants whereas trees are represented only by three spaced trees. In addition, the current study found that about 21 plants in Jabal Salma were considered to be threatened species or have already become extinct according to Al-Turki & Al-Olayan (2003) including: Anthemis sheilaea, Arabidopsis erysimoides, Astragalus collenettiae, Trisetaria chaudharyana, Aerva javanica, Alyssum homalocarpum, Anchusa aegyptiaca, Anvillea garcini, Calendula micrantha and Cenchrus ciliaris. These species were also considered as threatened or have already become extinct according to Alghamdi, (2017) who compared the floristic composition of other protected and accessible areas in Hail. Also, a number of species from the current study area have been identified in a previous study to be endemic only in Jabal Salma and have been classified as endemic-endangered, such as Anthemis sheilaea, Arabidopsis erysimoides, Astragalus collenettiae and Trisetaria chaudharyana. Meanwhile other species which were encountered rarely in the current survey, such as; Echinops glaberrimus, Ochradenus arabicus and Zygophyllum propinquum were classified as endemic to Jabal Salma and all over Saudi Arabia (Al-Turki & Al-Olayan, 2003). According to the results of present study, Jabal Salma is holding many species of economic values where 43 of them classified as medicinal, 45 ornamental and 13 edibles species can be used for human consumption. The most frequent medicinal species include; Salvia deserti, Salvia spinoza, Savignya parviflora, Polygonumbellardii, Pteranthus dichotomus, Pulicariaori entalis, Periploca aphylla, Teucrium polium and Trigonella stellate. Also these mountains were considered as a safe refuge for many ornamental species such as Cenchrus ciliaris, Centaurea scoparia, Centaurea sinaica, Trichodesma africanum, Trigonella stellate, Salvia spinosa, Savignya parviflora, Scabios aolivieri, Gypsophila capillaris and Hibiscus micranthus. These results would confirm the biological diversity of mountains as special habitats in Saudi Arabia. In accordance with Zhang et al (2016) elevation along the altitudinal gradient plays major role in plant distribution in mountains due to many variables including; slope degree and position, soil pH, organic matter, total nitrogen and available nitrogen. In agreement with this statement, the current study clearly showed that the plants were distributed in different patterns according to altitudinal gradient. Some species like Asphodelus fistulosus, Euphorbia retusa, Haloxylonsali cornicum, Acacia tortilis, Plantago ovate, Aizon canariense, Anastatica hierochuntica, Schismus barbatus and Trigonella stellate were dominated the non-pastoral zones on the low and flat areas surrounding the mountains. Further, in the foothill several pastoral species have been reported including; Cenchrus ciliaris, Cynodon dactylon, Lolium rigidum, Schismus barbatus, Stipa capensis, Stipagrostis Plumosa, Plantago amplexicaulis, Plantago cylindrica, Plantago ovate, Medicago laciniataand Astragalus corrugatus. The availability of such number of pastoral species could be easily attributed to topographic difficulties which prevent grazing animal including camels, sheep and goats from reaching Jabal Salma foothill. At high altitudes (top of Jabal Salma) and within its ridges and small valleys there were many medicinal and aromatic plants which have been considered as threatened to extinct species in other open habitats. Such species include Ballota undulata, Lavandula stricta, Salvia deserti, Salvia spinosa, Teucrium polium, Asphodelus fistulosus, Calendula micrantha and Tribulus terrestris. The invasion of exotic species is considered to be the main destructor of diversity and ecological equilibrium in natural landscapes (Dogra et al., 2010). In this study and despite accessibility difficulties of Jabal Salma, 27 species were identified as weeds for example, Sisymbrium irio, Spergula fallax, Rumex vesicarius, Medicago laciniata, Lolium rigidum, Lactuca serriola, Cynodon dactylon and Conyza discoridis. These species were also reported previously as weeds in Ha’il by (Mseddi et al., 2017). Historically, Hail region was considered as an excellent area for forage and pasture throughout the year (Al-Rowaily et al., 2016). However, due to human disturbances which took place in the last few decades such as; intensive grazing, over cutting and urban sprawl, many rangelands of Ha’il were degraded into a less productive pasture with a few shrubs and trees (mainly Acacias) which in turn seek refuge in wadis and foothills. However, we believe that Ha’il region's mountains still hold a number of economic, endemic and rare species, some of which are endemic only in Jabal Salma the current study area. In the current study, the floristic composition analysis showed that the family Asteraceae followed by Brassicacea, Fabacea, Boraginaceae, Caryophyllaceae, and Poaceae were the most dominant families. The dominance of Asteraceae, Brassicaceae and Poaceae families has been also reported by Al-Turki & Al-Olayan (2003) and El-Ghanim et al. (2010) who worked on some accessible areas in Hail region. They found the most common genera was Astragalis (Asteraceae) which was represented by 8 species, followed by Arnebia (Boraginaceae) and Fagonia (Zygophyllaceae) with three species for each family (El-Ghanim et al., 2010) reported that Euphorbia (Euphorbia), Heliotropium (Boraginaceae) and Plantago (Plantaginaceae) were the most common genera. Each of these genera was represented by three species. In addition, Al-Turki & Al-Olayan (2003) found that Plantago and Astragalus were the most common genera in the whole region of Hail. According to the current findings, Jabal Salma holds many species of economic values those where classified as medicinal, ornamental and edibles species used for human consumption. These results would confirm the biological diversity of mountains as a special habitat in Saudi Arabia. In accordance with this a similar recent study was conducted by AlZubaide et al. (2017) to assess the floristic composition of Shada Mountain in the south of Saudi Arabia and found there many species of economic value including; medicinal, grazing, fuel and edible. As reported by Dogra et al. (2010), the invasion by exotic species was considered to be the main disturbing factor of wild ecosystems. The presence of some noxious and invasive weeds such as Lolium rigidum and Lactuca serriola have been reported in the current study and this should raise the alarm to the local authority to take rapid action in order to prevent these noxious species from destructing the natural vegetation of Jabal Salma. This warning must be taking seriously as it is well documented now that invasive alien species is the second greatest threat to biodiversity after habitat loss (Thapa & Maharajan, 2014). Conclusion Although there is a huge loss of plant biodiversity in Saudi Arabia, the outcomes of the current study provide strong evidence that inaccessible zones such as Jabal Salma still hold a number of endemic and rare species of economic value. Therefore, Jabal Salma could be described as a reservoir for native seed species which could be exploited by the Saudi government in order to provide native plants to fight desertification and to stop the loss of biodiversity. Acknowledgement Part of the current study was carried out in the Staff Research Laboratory, Biology Department, College of Science, University of Ha’il, Saudi Arabia. Authors are grateful to many colleagues for their support. Also, authors extend their appreciation to the Deanship of Scientific Research at the University of Ha’il (Saudi Arabia) for funding this work (Project no. 0150437). Conflict of Interest Statement There is no conflict of interest|
Al-Rowaily S, Assaeed A, Al-Khateeb S, Al-Qarawi A, Al Arifi F (2016) Vegetation and condition of arid rangeland ecosystem in Central Saudi Arabia. Saudi Journal of Biological Sciences. In press, corrected proof, Available online 24 December 2016
Al-Turki T, Al-Olayan H (2003) Contribution to the flora of Saudi Arabia: Hail region. Saudi Journal of Biological Sciences 10:190-222.
Alghamdi AA (2017) Quantifying the level of degradation in two adjacent rangeland areas in Ha’il district. International Journal of Applied Research 3:107-110.
AlZubaidem M, AlZahrani H, AlToukhy A (2017) Floristic Composition and Life Forms for Wild Plants of Shada Highest Mountain and Wadi Sagamah at Al BahaArea, Saudi Arabia. Middle-East Journal of Scientific Research 25 : 1342-1348.
Aukema JE, Pricope NG, Husak GJ, Lopez-Carr D (2017) Biodiversity Areas under Threat: Overlap of Climate Change and Population Pressures on the World’s Biodiversity Priorities. PloS one 12:e0170615.
Baig MB, Straquadine GS, Aldosari FO (2017) Revisiting extension systems in saudi arabia: emerging reasons and realities. Journal of Experimental Biology and Agricultural Sciences 5:s160-s164.
Chaudhary SA (2001) Flora of the Kingdom of Saudi Arabia. Ministry of Agriculture and Water, Riyadh.
Collenette IS (1999) Wildflowers of Saudi Arabia. 799 pp. National Corrunission for Wildlife Conservation, Riyadh.
Conant RT, Cerri CE, Osborne BB, Paustian K (2017) Grassland management impacts on soil carbon stocks: a new synthesis. Ecological Applications 27:662-668.
Dogra SD, Sood SK, Dobhal PK, Sharma S (2010) Alien plant invasion and their impact on indigenous species diversity at global scale: A review. Journal of Ecology and the Natural Environment 2 : 175-186.
El-Ghanim WM, Hassan LM, Galal TM, Badr A (2010) Floristic composition and vegetation analysis in Hail region north of central Saudi Arabia. Saudi journal of Biological Sciences 17:119-128.
Heneidy SZ, Halmy MWA, Bidak LM (2017) The ethnobotanical importance and conservation value of native plants in eastern Arabian Peninsula. Feddes Repertorium 128:105-128.
Mseddi K, Al-Shammari A, Sharif H, Chaieb M (2016) Plant diversity and relationships with environmental factors after rangeland exclosure in arid Tunisia. Turkish Journal of Botany 40:287-297.
Mseddi K, Alghamdi A, Sharawy S, Ibrahim N (2017) Screening of weeds and their effect on alfalfa (Medicago sativa). Indian Journal of Agricultural Sciences 87:1565-1571.
Schultz E, Whitney JW (1986) Upper Pleistocene and Holocene lakes in the An Nafud, Saudi Arabia. Hydrobiologia 143:175–90.
Pielou EC (1959) The use of point-to-plant distances in the study of the pattern of plant populations. The Journal of Ecology 47: 607-613.
Thapa N, Mahrajan M (2014) Invasive Alien Species: Threats and Challenges for Biodiversity ConservationA Case Study of Annapurna Conservation Area, Nepal. Proceedings of the
Zhang C, Li X, Chen L, Xie G, Liu C, Pei S (2016) Effects of Topographical and Edaphic Factors on Tree Community Structure and Diversity of Subtropical Mountain Forests in the Lower Lancang River Basin. Forests 7 : 1-17.