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‫سبلان، نماد تنوع زیستی و قله¬های بلند قفقاز جنوبی-ایران Sabalan a symbol of Biodiversity, high rangelands and peaks of South Caucasus-Iran

Authors:
  • Research center of agriculture and natural resource of Ardabil province-Iran.

Abstract

Abstract The study of ecological characteristics of Festuca sulcata Beck. was carried out with the aim of identifying and obtaining useful information for use in rangeland improvement programs. In the first, using vegetation map and field visit, based on the size and distribution of the species, five Sites were selected for sampling. In each site, three transects were 100 meters and along the transects, 10 plots of 1×1 were randomly selected. The factors related to canopy cover, bush height, species frequency forage and seed production were measured by transect and plat (systematic-randomized ) method. Also some qualitative characteristics such as root system, phenology, seed quality, regeneration, preference value and chemical composition of the plant were studied. The results showed that this species in the study area is found between 2200 to 3800 m a.s.l on soils clay- loam texture with an acidic to alkaline. From the beginning of May to the end of June, the time of growth and the July to mid-August is the time of ripened and seed dissemination. Its palatability was as high as grade I in early flowering, but the best grazing time is in seed ripened stage. In the post-seeding stage (at the stage of harden the plant) is less livestock's tendency to graze. forage production yield was 528.58 kg dry matter per hectare and seed production 95.33 kg per hectare. Due to the resistance of this species to cold and frost, this species is suitable for restoration and improvement of rangelands with more than 350 mm rainfall.
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DOI: 10.22092/irn.2019.120092
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


sharifnia.j@gmail.com
*Assistant Prof., Forests and Rangelands Research Division, Agriculture and Natural ResourcesRe-
search Center of Ardabil Province, Agricultural Research, Education and Extension Organization,
AREEO, Ardabil, Iran E-mail: sharifnia.j@gmail.com
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           
 
Sabalan: a symbol of biodiversity and high peaks of
South Caucasus-Iran
J. Sharifi*
Abstract
Sabalan is the third highest peak in Iran and one of the high mountain ranges of the South Caucasus in Iran.
The Sabalan Mountain has three famous peaks, whose great peak is called the Savalan Sultan, located at
an altitude of 4811 meters above sea level. The other two peaks are the Heram and Kasra located on the
northern and southern sides of the main peak. The Sabalan peak is in the list of natural national treasures
of the country with the registration number 12 /19496. This ecosystem is rich in plant and animal species
due to its biodiversity, valleys and slopes. The presence of alpine, subalpine, and some endemic species
is a feature of the Sabalan ecosystem. High peaks over 4,000 meters above sea level with glaciers has
provided the grounds for the formation of meadows, unique landscapes and consequently, good conditions
for the range management, beekeeping, tourism and mountaineering. The nomadic community of Elsuvan
(Shahsuvan) is the only population in the area exploiting rangelands. Regarding the damages caused in
Sabalan due to overgrazing, climate change, exploitation of medicinal plants in natural habitats, development
of the road system in these mountains and tourism programs, the necessity of reviewing the environmental
management of the area and paying attention to the sustainable exploitation of the Sabalan ecosystem is
very important and a matter of necessity and urgency.
Keywords: Sabalan, biodiversity, subalpine rangelands, ELsuvan nomads
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











 
  
        


   





Erigeron caucasicus   
Tripleurospermum caucasicum
Potentilla gelida Festuca rubra
Ranunculus trichophyllus, Saxifraga sibirica,
Draba siliquosaDidymophysa aucheri










Sherman et al.,) 
(2007













 

.(Michelle et al., 2013) 



       

         
      
          
         
 . (Sharifi et al., 2014)    
(Colchicum raddeanum Regel. K. Perss.) 
(Colchicum caucasicum (M.Bieb.) Spreng)
   (Iris reticulata M. B) 
  (Ornithogalum montanum Boiss.)
 (Puschkinia hyacinthoides Baker.)
 (Muscari racemosum (L.) Lam. & DC.)
(Fritillaria zagrica Stapf)
(Veronica triphyllos L.)
 Gagea reticulata Schult.f

.(Sharifi et al., 2014 


           
  
       

(Carum caucasicum (M.Bieb.) Boiss.) 
(Asparagus verticillatus L.)
(Dianthus pachypetalus Stapf)
(Dictamnus albus L.)
(Echinops robustus Bunge) 
(Equisetum palustre L.)
(Glycyrrhiza glabra L.)
(Hypericum scabrum L.)
(Heliotropium suaveolens M. B.)
(Lotus corniculatus L.)
(Lamium album L. subsp. album) 
(Verbascum thapsus)
(Mentha aquatica L.)
(Nasturtium officinale R.Br) 
(Nepeta heliotropifolia Lam.)
(Pimpinella tragium Vill.)
(Prangos uloptera DC.)
(Stachys lavandulifolia Vahl.)
(Thymus kotschyanus Boiss. & Hohen)
(Nepeta menthoides Boiss. & Buhse) 

Rechinger, 2005
4/6
9/2
79/3
6/9
        Th
       Ge
            He
Ch

irannature.areeo.ac.ir 


 

Phlomis olivieri L
Phlomis tuberosa L

Thymus kotschyanus Boiss. & Hohen.

Salvia aethiopis L.

Nasturtium officinale R.Br

Achillea wilhelmsii C. Koch.

Hypericum perforatum L

Urtica dioica L

Achillea millefolium L.
 
irannature.areeo.ac.ir 


        
     
    
       
      
         
        

       





Festuca sulcata - Alopecurus textilis - Carex sp.
      







Astragalus rostratus C.A.Mey.
Astragalus savellanicus Podlech
Alopecurus aucheri L.
Alopecurus textilis Boiss.
Astragalus carduchorum Boiss. & Hausskn. ex Boiss.
Campanula gilliatii Milne-Redhead.
Didymophysa aucheri Boiss.
Erysimum caespitosum DC.
Koeleria eriostachya Panc.
Oxytropis aucheri Boiss.
Potentilla hololeuca Boiss.
Trifolium montanum L.

 

















       



  



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   
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Article
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Aims The eastern Himalayan region of Southwest China represents the world’s most biodiverse temperate region as well as a cultural hotspot undergoing rapid cultural and ecological change. This area represents the center of origin for many plant groups including horticulturally valuable species of Pedicularis, Rhododendron and Primula. Alpine meadows here also provide summer pastures for Tibetan yak herders and the source for important medicinal plants. Stocking levels for livestock here have quadrupled over the last five decades and shrubs are encroaching into many historical rangelands. Yak herders voice concerns over both shrub encroachment and shrinking grasslands. In this study, we sought to determine: (i) Are alpine rangelands in Deqin County overgrazed and degraded? (ii) What are the local impacts of grazing on plant diversity and community composition? And (iii) which environmental variables covary with these differences in species composition across the grazing gradient? Methods To examine the ecological impacts of grazing in Deqin County, northwest Yunnan and assess its long-term sustainability, we used county records to determine historical population and livestock numbers, confirmed the results of interviews by Haynes (2011) and surveyed plant species richness and cover along a grazing gradient extending away from herder huts. Along these transects, we sampled 1 m² quadrats at 5 m intervals, noting species present and percent cover for vascular plants, grasses, sedges, rushes, moss, lichen, exposed rock, bare ground and feces. We also measured the average and maximum plant height within each quadrat. We then computed species richness for each of the 38 transects, calculating alpha and beta diversities. We used one-way ANOVAs to compare mean species richness values and average and maximum plant height across grazing intensities. To chart changes in composition along the 100m gradient, we also plotted the percent cover of graminoid, forb, shrub and bare ground versus distance from the hut. We applied NMS ordination to relate community patterns to environmental variables and grazing intensity using distances to determine species groupings. Important Findings Livestock impacts are clearly evident with proportions of grass and bare ground decreasing, shrubs increasing and forbs maintaining even cover with increasing distance from the huts. In comparison with earlier surveys of sites farther from huts, we found reduced plant cover and diversity. Plant species richness almost doubles with increasing distance from herder huts from 9.9 to 19.3 species per 1 m² quadrat. An ordination of species and environmental variables demonstrates that grazing strongly affects plant community com position across these plots with strong impacts on palatable plants. If herd sizes remain large and suitable areas for grazing continue to decline, the cumulative impacts of grazing appear likely to degrade the rich diversity of the region and reduce rangeland quality, threatening its ability to sustain current grazing levels.
Article
Full-text available
Implementing conservation actions on-the-ground is not a straightforward process, especially when faced with high scientific uncertainty due to limited available information. This is especially acute in regions of the world that harbor many unique species that have not been well studied, such as the alpine zone of the Hengduan Mountains of Northwest Yunnan (NWY), a global biodiversity hotspot and site of The Nature Conservancy’s Yunnan Great Rivers Project. We conducted a quantitative, but rapid regional-level assessment of the alpine flora across NWY to provide a broad-based understanding of local and regional patterns of the alpine flora, the first large-scale analysis of alpine biodiversity patterns in this region. Multivariate analyses were used to classify the major plant community types and link community patterns to habitat variables. Our analysis indicated that most species had small distributions and/or small population sizes. Strong patterns emerged with higher diversity in the more northern mountains, but beta diversity was high, averaging only 10% among sites. The ordinations indicated that elevation and geographic location were the dominant environ-mental gradients underlying the differences in the species composition among communities. The high beta diversity across the alpine of these mountains implies that conservation strategies ultimately will require the protection of large numbers of species over a large geographical area. However, prioritization should be given to areas where potential payoffs are greatest. Sites with high species richness also have a greater number of endemic species, and, by focusing efforts on these sites, conservation investments would be maximized by protecting the greatest number of unique species.
Alpine wetland flora, species life forms and chorology of the Sabalan Mountain-Iran
  • J Sharifi
  • A Jalili
  • G Shaker
  • E Zandi Esfahani
Sharifi, J., Jalili, A., Shaker, G. and Zandi Esfahani, E., 2014. Alpine wetland flora, species life forms and chorology of the Sabalan Mountain-Iran. Journal of Bio diversity and Envirronmental Sciences, 5(2): 173-180.