<<

International Journal of Horticultural Science and Technology Vol. 2, No. 2; December 2015, pp 111-132

Environmental and Anthropogenic Pressures on Geophytes of and the Possible Protection Strategies: A Review

Homayoun Farahmand1* and Farzad Nazari2 1. Department of Horticultural Science, Faculty of Agriculture, Shahid Bahonar University of Kerman, Kerman, Iran. 2. Department of Horticultural Science, College of Agriculture, University of Kurdistan, Sanandaj, Iran. )Received: 12 August 2015, Accepted: 3 October 2015(

Abstract Ornamental geophytes (ornamental ) are international and national heritage considering their contribution to people's life quality around the world. Iranian habitats support about 8000 of flowering (belonging to 167 families and 100 genera) of which almost 1700 are endemic. Iran is a rich country in terms of distribution of bulbous plants. More than 200 species of bulbous species from different families naturally grow in Iran and play an important role in the colorful display of in the plains, mountains, and forests. Unfortunately, some flower bulbs are at the risk of eradication in Iran due to some factors, including inappropriate herboviry and overgrazing, land use change, illegal and flower harvesting, road construction, mining activities, drought, etc. The establishment of protected areas, efficient propagation methods such as micropropagation, gathering the species at the risk of extinction in Botanical Gardens and Research Centers, highlighting the decisive role of Non- governmental organizations (NGOs), and improving tourism are some approaches suggested for better conservation. Meanwhile, under the current situation, national and international protecting rules and regulations should be assigned and fulfilled to save this invaluable natural heritage.

Keywords: Bulbous plants, Iran, genetic erosion, habitat destruction.

Introduction glamorous history as garden plants. Flowers have long been associated with Frescoes and vases decorated with lily each civilization and culture in the world. motifs have been discovered in the relics of Dating as far back as the Neanderthals, ancient Crete, dating from 1800 or 1600 flowers were used to decorate graves and B.C. Records show that the Pharaohs grew celebrate major life events, expressing anemones in their gardens and these emotions in ways that words are deficient. narcissi and lilies were used by the ancient Numerous cultures have incorporated Egyptians in their funeral wreaths flowers in their everyday lives as (Wentzell, 1973). expressions of beauty and art (Anderson, Solomon, the ancient king mentioned in 2006). Bulbous plants have a long and the Old Testament, had a garden containing lilies and Crocus. As early as 380 B.C., the *Corresponding author Email: [email protected] Greeks were using Crocus, lilies, and 112 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015 hyacinths in ceremonial crowns, and the immediate conservation measures are philosopher and botanist Theophrastus, in required to safeguard many of these about 340 B.C., wrote about Allium, species (Sarasan et al., 2006). Worldwide Anemone, Crocus, Cyclamen, Gladiolus, loss of biodiversity is a great global , and Scilla species. Together concern and has increasingly become a with hyacinths and narcissi, lilies had an research focus since the Rio Summit in important place in the gardens of the early 1992 (Lomba et al., 2010). Romans, who valued these flowers for their Conserving biodiversity for its sustainable use in religious ceremonies (Wentzell, 1973). use by the present and future generations is A greater number of bulbous species integral to UNCED’s Agenda 21 and the grow in the and south-eastern International Convention on Biological Europe in comparison to other parts of the Diversity (ICBD) singed by more than 150 world. If a circle be drawn with Istanbul as of the nations which attended the Earth the center and taking in Greece and Summit in 1992. The world is inhabited by Bulgaria, and the , Persia and myriads of life forms, animals and plants. Afghanistan and neighboring countries, it These life forms are of great diversity, living can be seen that many of the most popular in diverse habitats and possessing diverse flowering bulbs are grown within these qualities, which in themselves make very areas (Genders, 1973). This rich vegetation interesting studies. In the present day, many (flora) may reflect the varying climatic species of plants and animals are being conditions in these areas including xeric, destroyed at a rapid rate. Last but not least, it mesic and alpine climates. Variation is the is an undeniable fact that the human race has law of nature. It occurs everywhere and taken upon itself an arrogant role, as though every moment. The variety and variability Homo sapiens is the only species and other of organisms and ecosystems is referred to species do not matter (Kumar and Sharma, as biological diversity or biodiversity. 2001). Biodiversity is recognized to be of global importance, yet species and habitats Ornamental geophytes in Iran continue to be under increasing pressure Iran is the sixteenth largest country in the from human-induced influences, whether in world (FAO, 2005) and after ranks urban, rural or wilderness settings (Hill et the richest country of plant diversity in the al., 2006). Middle East (Yavari and Shahgolzar, The World Conservation Union’s 2010). Iran is located in the Middle East (IUCN’s) Red List of Threatened Plants and surrounded by Armenia, Azerbaijan, suggests that 34000 plant species are the Caspian Sea, and Turkmenistan on the threatened globally, equivalent to some north, Afghanistan and Pakistan on the 12.5% of the estimated world flora. The East, Oman Sea and Persian Gulf on the world’s biodiversity is declining at an South and and Turkey on the west. unprecedented rate. During the period The population of Iran is about 70 million 1996-2004, a total of 8321 plant species with a growth rate estimated as 1.7% and were added to the International Union for has 30 provinces (Heshmati, 2007). Iran’s the Conservation of Nature and Natural important mountains are the Alborz and Resources (IUCN, 2004). The main Zagros ranges. These mountains play an purpose of IUCN Red List is to catalogue important role in determining the non- and highlight those taxa that are facing a uniform spatial and temporal distribution higher risk of global extinction. During this of precipitation in the whole country. The period, there was an increase of over 60% area within the mentioned mountain ranges in the number of plants recorded as is a high plateau with its own secondary critically endangered. This is alarming and ranges and gradually slopes down to Environmental and Anthropogenic Pressures on Geophytes of … 113 become desert which continues into is less than 100 mm in the central region southern parts of Afghanistan and near the (Amiraslani and Dragovich, 2013). The Pakistan border. The Damavand peak in rich flora and fauna and the unique the Alborz reaches 5670 m above the mean landscapes of this land, as well as its sea level while the Caspian coastal area is ancient civilization, have attracted many below sea level (-28 m) (Heshmati, 2007). biologists and orientalists (Yavari and The country's climate is mainly arid and Shahgolzar, 2010). semi-arid, except the northern coastal and Iranian habitats support about 8000 parts of western Iran. The climate is species of flowering plants (belonging to extremely continental with hot and dry 167 families and 100 genera) of which summers and very cold winters particularly almost 1700 are endemic (Eftekhari and in inland areas. The average annual rainfall Ramezani, 2004). These plant species grow of the country is about 240mm with on four Ecological Zones (Fig. 1) namely, maximum amounts in the Caspian Sea Hyrcanian, Zagros, Iran-o-Touranian and plains, Alborz and Zagros slopes with more Khalij-o-Omanian which have different than 1800 and 480mm, respectively ecological and climatic conditions (Heshmati, 2007). Minimum precipitation (Heshmati, 2007).

Fig. 1. Distribution of the four ecological zones of Iran (Heshmati, 2007)

More than 200 species of bulbous plants spp. (Polyphyllaceae) Geranium tuberosum from the major families including (Geraniaceae) have not been included in , Iridaceae and Amaryllidaceae Wendelbo's (1977) contribution. are grown in Iran and play an important The introduction of new species and role in the colorful display of flowers to be records of flower bulbous plants from Iran found in the plains, mountains and forests such as Oxalis articulata (Ghahremaninejad (Wendelbo, 1977). It should be noted that and Gholamian, 2006), Tulipa faribae some species from including Arum (Ghahreman et al., 2007), Muscari kurdicum spp. L. and spp. Schott Maroofi (Maroofi, 2007), Eminium jaegeri (Mozaffarian, 2003) and from Orchidaceae (Bogner and Boyce, 2008), Gagea calcicola [Orchis spp., Gymnadenia spp., (Zarrei et al., 2010), Gagea alexii (Ajani et Dactylorhiza spp., Steveniella spp. al., 2010), Allium (Razyfard et al., 2011) and (Mozaffarian, 2003), Epipactis rechingeri Leopoldia tijtijensis (Jafari, 2012) indicates Renz, Ophrys kurdistanica Renz and the richness of geophytic species in Iran. The Ophrys turcomanica Renz (Renz, 1978)], flower bulbs of Iran have high potentials for Corydalis spp. (Fumariaceae), Leontice the horticulture and floriculture industry and

114 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015 could be used as cut flowers, pot flowering Grazing pressure has a simultaneous effect plants, and garden and landscape plants on both soil and range vegetation cover (Nazari et al., 2007; Nazari et al., 2011; (Mohseni Saravi et al., 2005). Soil physical Farahmand and Nazari, 2014; Nazari et al., properties play an important role in the 2014). establishment and growth of rangeland plants. Soil bulk density, mechanical Factors affecting habitat resistance, porosity, and infiltration rate are destruction and genetic erosion of all affected by soil texture and rangeland flower bulbs in Iran management practices (Chaichi et al., 2005). Inappropriate herbivory and Trampling by livestock results in compaction overgrazing of the soil surface and this affects soil Climatic conditions and grazing history are infiltration. The destructive effects of high two important factors affecting species intensity grazing on the physical properties composition and biodiversity in rangeland in of soil have been reported by many semi-arid ecosystems (Hassani et al., 2008). researches (Chaichi et al., 2005). Overgrazing by livestock has been The alpine zone in Iran has been less considered as a major degrading factor for affected by humans compared to other plant cover, soil and microclimate in lowland ecosystems. The harsh conditions woodlands in southwestern Australia (Yates and physical barriers limit human et al., 2000). Overgrazing changes vegetation settlement and intensive agricultural structure and composition. Ultimately, some activities. However, in recent years, the species increase in abundance and others strong impact of grazing is increasingly decrease (Hassani et al., 2008). Domestic threatening the fragile subalpine and alpine livestock has grazed Mediterranean ecosystems in Iran even in legally rangelands for thousands of years, in protected arenas (Akhani, 1998, 2004). The particular regions that are found in West Asia mountain meadows, steppes and xerophytic and North Africa (WANA) (Louhaichi et al., plant communities represent sufficient food 2009). Under long-term intensive grazing, potential for cattle. Overgrazing leads to the shift in species composition frequently the destruction of vegetation, loss of involves the replacement of palatable with biological diversity, and erosion of soil. unpalatable plant species particularly woody The dominance of thorn-cushion formation perennials that provide low to no forage is obviously one of the consequences of value (Louhaichi et al., 2009). Overgrazing long-term overgrazing and land use in the has often been perceived as a major factor in Iranian plateau. The severe overgrazing in the degradation of Mediterranean landscapes most parts of high altitudes in recent years (Noy-Meir and Oron, 2001). Sheep and goat has resulted in a spread of poisonous production was historically an important species (e.g. Euphorbia) observed in occupation for rural populations located Alborz, Binalud and Sahand Mountains within WANA countries (Noor Ahmad, (Noroozi et al., 2008). 2006; Louhaichi et al., 2009). Livestock and Although it has been claimed that plants interact constantly within rangeland geophytes usually respond positively to ecosystems. Overgrazing pressure that grazing in the Mediterranean vegetation accompanies an increase in the human and (Noy-Meir and Stenberg, 2001), the livestock populations causes a significant response of geophytes to herbivory varies reduction in plant growth vigor and considering morphological, physiological, reproduction ability and poor establishment geographical and some other influencing of valuable plants, which leads in turn to a conditions. For instance, Noy-Meir et al. changed botanical composition and soil (1989) categorized geophytes to cattle moisture properties (Amiri et al., 2008). grazing as positive, negative, or neutral. Environmental and Anthropogenic Pressures on Geophytes of … 115

Meanwhile, as mentioned by Noy-Meir destruction, not overgrazing that is mentioned and Stenberg (2001), the reaction of some for some palatable geophytes. Thus, the geophytes to grazing was not consistent. It physical damage to plants from one side and seems that some dicot geophytes such as the soil compaction from another side, , Ranunculus asiaticus adversely affect plant growth and and Cyclamen persicum respond to development in this case. Animal trafficking grazing in a negative manner (Noy-Meri directly damages blooming plants (Fig. 2 A) and Oron, 2001) and some members of and prevents and seed formation (Fig. 2 Liliaceae give a positive response to B), as well. As this time of the year coincides grazing (Noy-Meir and Orong, 2001). It is with spring rainfalls, the soil is wet and the reported that grazing has positive effects rate of damage is severe. Some people pick on Anemone coronaria L. (Perevolotsky et the flowering stems just for their fleeting al., 2011). However, the response to beauty and take them to their homes. herbivory (grazing) is also dependent on Interestingly, because of the bad smell plant species, the time of grazing, and the released by this plant particularly after traffic magnitude of animals. harvest, it cannot be kept at home and should In the case of some geophytes in Iran be placed outside. Therfore, this kind of trampling by animals is an adverse factor. For harvesting not only has no benefit for the instance, although imperialis is gatherer, but also adversely affects plant unpalatable to animals while green, due to growth cycle, because the photosynthetic chemical compounds such as alkaloids, which are the main sources of glycosides, calcium oxalates, etc., it suffers photosynthesis process are harvested. In greatly from animal trafficking and trampling addition, after harvest, not only are seeds not during spring. The breakage of the flower formed but also carbohydrate supply for stem caused by animals not only prevents bulblet formation and mother bulb growth is fruit and seed formation, but also weakens disturbed. Therefore, the sexual and asexual the underground bulbs because the leaves that reproductive means are impaired. This should provide the bulbs with carbohydrate species is awfully eye-catching during its reserves for bulblet formation and subsequent flowering time in spring and the mountains growth and flowering are destroyed in this and plains covered with this fabulous flower way. Thus, in the case of the Fritillaria bulb attract many nature lovers and and similar ones, inappropriate grazing and enthusiasts particularly in provinces located animal trafficking are responsible for habitat in the western parts of the country.

Fig. 2. A and B. Fritillaria imperialis: physical damage of animals during growth and flowering season, as shown in the pictures, is a challenge for this species in many parts of the country (A) Derak Mountain in Shiraz province and (B) Manesht Mountain in Ilam province).

116 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015

Grazing pressure has a simultaneous locality. Tulipa spp. (Fig.3 E and F) suffers effect on both soil and range vegetation greatly from inappropriate and heavy cover (Mohseni Saravi et al., 2005). grazing in many parts of Iran. The genus Trampling by livestock results in Tulipa has 12-18 species in Iran, amongst compaction of the soil surface and this which four species, namely, T. ulophyla, T. affects soil infiltration. The destructive harazensis, T. montana and T. urumiensis effects of high intensity grazing on the are endemic (Farahmand and Nazari, physical properties of soil have been 2014). Unlike Fritillaria spp. and some reported by many researches (Chaichi et other bulbous plants which are unpalatable, al., 2005; Azarnivand et al., 2011). tulips are highly palatable. Consequently, Livestock and plants interact constantly inappropriate grazing and overgrazing within rangeland ecosystems. The directly and indirectly threaten them. As overgrazing pressure that accompanies an tulips are palatable, the leaves are eaten by increase in the human and livestock animals and this defoliation gradually populations causes a significant reduction weakens the bulbs. Animals that feed on in plant growth vigor and reproduction seeds, bulbs, or other reproductive parts ability and poor establishment of valuable directly reduce the plant’s reproduction and plants, which leads in turn to a changed may kill the plant (Crawley, 1983; Lubbers botanical composition and soil moisture and Lechowicz, 1989; Anderson, 1994). properties (Amiri et al., 2008). The Unfortunately, the flowering season of interaction effects of different management some bulbous plants coincides with late and environmental factors on rangeland winter and early spring throughout the vegetation are so complicated that it is country and this time of the year is suitable difficult to distinguish their effects from for the regular migration of Nomads (the so each other. Many scientists believe that called Ashayer in Persian) from subtropical vegetation destruction in rangeland is and tropical regions to temperate ones. because of the increment of the grazing This phenomenon is obviously a challenge pressure and soil deterioration at the same for palatable species such as tulips and time (Mohseni Saravi et al., 2005). even unpalatable plant species (Fritillaria Another endangered species is Fritillaria spp.). Due to favorable conditions, this gibbosa Boiss. (Gol-e-Sarnegoun-e- time of the year is suitable for the growth Ghouzi) which is an elegant one and development (fruit and seed formation) particularly for pot plant production and of most spring flowering bulbs, but the especially for rock garden design. This plants are eaten by animals or trampled as species is under increasing pressure in the a consequence of heavy animal trafficking. northern parts of Fars province mainly due Animal trafficking damage and particularly to inappropriate and heavy grazing during overgrazing gradually weaken the plants the growth and flowering season. The same and may eradicate them if practiced for conditions described for Fritillaria spp. successive years. Some bulbous species could be mentioned for two Iris species in such as Eremurus spp. are not palatable Fars province viz. Iris lycotis Woron. when green in the spring, but heavy and (Zanbagh-e-Gol Dorosht) and Iris lineolata inappropriate grazing trample them, and (Trautv.) Mathew (Zanbagh-e-Parvane'i) consequently, flower stems are damaged (Fig. 3A, B and C). The habitats of some and seeds are not formed in heavily grazed Iris species are under pressure in some areas. Grazing may have different impacts other parts of the country such as on plant species due to herbivore Khorasan-Shomali province as shown in preference or plant resistance Fig. 3D. Therefore, this phenomenon is not (Perevolotsky et al., 2011). restricted to just one province or one Environmental and Anthropogenic Pressures on Geophytes of … 117

A B

C D

E F

Fig. 3. A) Iris lycotis Woron. (Zanbagh-e-Gol Dorosht), B) Iris lineolata (Trautv.) Mathew (Zanbagh-e-Parvane'i), C) Land use change and road construction are threatening factors for their habitat destruction in the northern parts of Fars province (Dehbid), and D) Animal grazing in a meadow in Khorasan-Shomali province. Iris species are not palatable while green but the physical damage is considered a threat in these cases. E and F) Tulipa spp. are palatable and overgrazing by animals or rodents is the real threat for them particularly during blooming from late winter to early spring (Fars province, Dehbid).

Sternbergia spp. is another exquisite species is now scarcely found in Fars ornamental bulb in some regions of Iran. In province, where it was once seen abundantly some parts of Fars, Ilam and Kohgiluyeh and in mountains and plains. The most important Boyer-Ahmad provinces, these spectacular factor responsible for this depletion is flower bulbs are locally called “Gole Bi assumed to be inappropriate herbivory and Mennate Baroon” meaning the plants that do overgrazing in the habitats during its growth not need rainfall to flower in autumn [this and development. This species is also bulbous plant produces flowers before sporadically grown in Kohgiluyeh and production in autumn, the state called Boyer-Ahmad, Ilam and Kurdistan provinces hysteranthous by De Hertogh and Le Nard where the mountainous and inaccessible (1993)]. This species is slow-to-propagate nature of the habitats and less animal traffic because a few bulblets are annually formed help to preserve it singly or in scattered on the mother bulb; unfortunately, this populations (Fig. 4 A and B). Illegal 118 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015 collection for cut flower industry, fast Persian name Susan-e-Chelcheragh or development of the tourist industry, urban Susan-e-Chehelchergh (Fig. 4 C and D), is a expansion, and building of roads have been perennial endangered rare species endemic to mentioned as the factors which threaten Iran mostly found in Gilan province. This Sternbergia lutea in Turkey (Gurbuz et al., plant grows at altitudes between 1750-2100 2009). Even in the case of grape hyacinth m in Euxino-Hyrcanian province and it is (Muscari spp.), which is easily propagated under the surveillance of Iranian Regional by seed and bublet formation and so Environmental Protection Agency (Jalili and considered weed in some cases, trampling Jamzad, 1999). This statement of Wendelbo and land use change is a critical problem. (1977) is surprising about this rare species: It might be claimed that all geophyte “Indeed, if the Department of the species have developed underground Environment had not placed guards in specialized organs such as bulb, tuber, Rudbar locality (Gilan province) and corm, , etc. to cope with abiotic declared it a National Nature Monument, this and biotic stresses. Although these beautiful species might well have been on its evolutionary developed organs play an way to extinction by now.” Fortunately, important role in bypassing environmental governmental protection of habitats of this stresses, they greatly suffer from stressful native, endangered, and spectacular bulbous factors during their active growth and species in Gilan province (Damash village), development which, unfortunately, occur which was put into effect about five decades predominantly in developing countries. ago, is continuing. ledebourii (Baker) Boiss. with the

A B

C D

Fig. 4. Sternbergia sp. grows singly or in scattered populations in mountainous areas in some provinces such as Ilam (A) and Kohgiluyeh and Boyer-Ahmad (B). C and D) Lilium ledebourii (Baker) Boiss. a critically endangered species endemic to the north of Iran. Environmental and Anthropogenic Pressures on Geophytes of … 119

Climatic change (Drought and bulbous species which are in part difficult to temperature) propagate. Iran is now experiencing a decade th Recent climatic models predict that the 21 of severe drought and this phenomenon has century will be characterized by increasing resulted in drastic damage to the country's temperature, changing precipitation vegetation particularly in drought-prone patterns and more frequent severe events regions. Although geophytes have developed such as heat waves and droughts specialized organs to bear adverse (Pourbabaei et al., 2014). Climate change environmental conditions, under severe is one of the most important ecological periods of drought they may be damaged, problems of our times (Eppich et al., because optimal climatic conditions and, 2009). There are many literature references most importantly, rainfall is required for from recent years indicating that increasing them to make reserves via the photosynthesis temperature could force alpine plants to process for the dormant (rest) period. migrate upwards until they reach the Therefore, the lesser the rainfall, the shorter highest elevations. Therefore, many the growth and development period and the mountain ranges which host a large lower the carbohydrate reserves, number of endemic plants are very likely to consequently. The amount of snow has suffer critical losses (Grabherr et al., 1994; dramatically decreased during the past Korner, 1999; Theurillat and Guisan, 2001; decades in the country and this phenomenon Pauli et al., 2007). is alarming for those flower bulbs native to West Asia and North Africa (WANA) are mountainous and alpine zones. characterized by low rainfall and high fluctuation of the precipitation. During the Land use change (farming and last century, this region experienced many mechanization, agricultural and episodes of drought whose frequency has horticultural activities, road increased during the last decades (McNeely, construction, mining activities, etc.) 2003). This climatic phenomenon has Semi-arid and arid rangelands form nearly negatively affected agricultural and livestock 30% of the world’s land surface (Stafford production and led to natural resource Smith, 1996; Sivakumar et al., 2005). Land degradation. These problems have been degradation is a serious matter in the upper associated with high population growth, and catchment of the semi-arid regions of Iran. In hence they have been aggravated by the use these areas the main causes of land of non-adapted management of natural degradation are conversion of rangelands to resources (McNeely, 2003). agricultural areas, improper plowing and Iran's climate is mainly arid and semi- irrigation, overgrazing, poor vegetation cover arid, except the northern coastal and parts of and extensive livestock, which all lead to western Iran. The climate is extremely sudden changes in biological diversity continental with hot and dry summers and (Heshmati et al., 2013). Ecological problems very cold winters, particularly in inland and the increasing deterioration of natural areas. The average annual rainfall of Iran is resources are due to unsustainable and about 240 mm with maximum amounts in improper land use (Heshmati et al., 2013). the Caspian Sea plains, Alborz and Zagros Environmental degradation caused by slopes with more than 1800 mm and 480 inappropriate land use is a worldwide mm, respectively (Heshmati, 2007). problem that has attracted the attention of According to Dore (2005), variance is found sustainable agriculture production systems in the case of precipitation everywhere and (Ayoubi et al., 2011). dry areas may become drier in the future. Agriculture land conversion (ALC) has Thus, global warming will adversely affect been introduced as one of the most important the vegetation of Iran and in particular, the factors affecting ecosystems (Barati et al., 120 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015

2015). Transformation or destruction of challenges, sustainable management of semi- habitats due to unsustainable land use is one arid systems requires profound knowledge of of the major threats to biodiversity. Land-use the system dynamics (Tietjen and Jeltsch, change is perceived as a key driver of future 2007). The rate of legal and illegal land use biodiversity loss (Bosing et al., 2014). change in Iran has been alarming during the Transportation infrastructure that enhances past decades and should be managed so that connectivity among human settlements often it will not impair vegetation cover and results in decreased connectivity among biodiversity any further. The establishment remaining natural habitats and wildlife of protected areas is a primary strategy to populations (Makki et al., 2013). Habitat conserve biodiversity, although reserves fragmentation and the creation of barriers by alone cannot guarantee that biodiversity will transportation infrastructures reduce be maintained (Noor Ahmed, 2006). landscape connectivity, and this is suspected Some populations of the genus Narcissus to be one of the most important factors tazetta L. grow naturally in the southern and causing wildlife population decline (Makki northern parts of Iran particularly in southern et al., 2013). An important type of land use is provinces, including Fars and Khuzestan. the production of livestock. Livestock From the perspective of ecotourism, the management also strongly influences current natural habitats of Narcissus L. in vegetation dynamics. World-wide plant Iran particularly the southern ones, are species composition has changed because of considered a potential. Many natural habitats land utilization by domestic livestock as an of Narcissus have been destroyed mainly due increase in grazing pressure can lead to a to mechanization through the use of heavy reduction of palatable grasses and herbs and field machines including tractors and also woody plants. This shift in plant species illegal and uncontrollable harvest, changing composition has been shown to be the habitats and pastures for agricultural accompanied by reduction in primary purposes (Fig. 5. A and B). (Farahmand, productivity. Because of these probable 2007; Farahmand et al., 2007).

A B

Fig. 5. A and B) Narcissus tazetta cv. Meskin at the risk of extinction due to mechanization and changing its habitat to wheat farms in the southern regions of Iran.

Fortunately, some protected areas have country (Farahmand, 2007). Dating back been established in southern provinces just to some decades ago and before the particularly in Fars province, to conserve emergence of mechanization, narcissus the remnant populations of Narcissus plants were naturally found as narrow tazetta L. in the southern parts of the bands between fields especially in the Environmental and Anthropogenic Pressures on Geophytes of … 121 southern provinces of Iran such as Fars, loss of vegetation and fauna, soil Khuzestan and Bushehr. But nowadays degradation, altered hydrology, and only sporadic populations of this plant landform (Drake at al., 2010). As mining species are found in remote mountainous exploitations greatly affect ecosystems and sites, plains at high elevations (in Fars particularly disturb vegetation cover, in the province), or as protected areas just modern world, sustainable mining is being mentioned above. Factors threatening practiced in developed counties to restore Narcissus tazetta populations are similar to natural landscapes during mining the other bulbous species grown in operations or as a post-mining strategy hillsides and plains suitable for agricultural (Farahmand et al., 2014). and horticultural purposes. Many hectares of these types of lands have recently been Medicinal use, illegal and allocated to farming purposes and this uncontrollable harvesting habitat destruction and fragmentation has The growing popularity of traditional resulted in the genetic erosion of plant medicine and the unrestricted collection of species particularly bulbous plants in many medicinal plants from the wild have put parts of Iran. It is noteworthy to seriously many of the slow growing bulbous plant contemplate the statement presented by species at the risk of over-exploitation and Wendelbo about 40 years ago: "Although extinction in South Africa. Medicinal Iran boasts a rich and diverse flower plants are used by billions of people in species, there is no simple illustrated guide most developing countries because of the to the flowering plants. Sheep, goats, and frequently inadequate provision of modern tractors in particular, have combined to medicine, their low cost, effectiveness, as despoil and eradicate the natural plant well as cultural beliefs and preferences cover over vast stretches of Iran (Sheldon et al., 1997; Shanley and Luz, (Wendelbo, 1977)". Changes in land use, 2003). In South Africa, bulbs are one group abandonment of grazing and some of plants that are highly valued and traditional land management practices have extensively used in the traditional medicine been mentioned as the important factors for systems. Bulbs are used in the treatment of reducing biodiversity in Nracissus species various ailments (Katerere and Eloff, 2008) in Central Spain (Rios et al., 2010). and considerable research resources have Road construction (Fig.3 C) for many been directed towards screening for purposes and also mining activities are two biologically active compounds. Bulbs are other factors with drastic effects on plant ranked as one of the most popular plant species habitats and niches. An important groups sold at most of the traditional threat to the alpine ecosystems of Iran in medicinal markets in South Africa recent years is road construction in many (Mander, 1997). Their use in herbal mountainous areas (Heshmati, 2007). Not medicine involves destructive uprooting of only do such roads destroy large parts of the whole plant. Harvesting of the whole the area, but they also ease access to the plant, roots and bulbs account for high altitudes both for mass climbers and approximately 50% of the more than 500 grazing animals. Mining operations have species and 48% of the volume of plants an important role in environmental changes sold in the traditional modern market in (Alavi et al., 2011). The damage to soil and Johannesburg (Williams, 2003). The non- vegetation caused by mining is usually suitable harvesting threatens the survival of extreme, because the original ecosystems valuable medicinal plant species; sadly, are drastically disturbed or buried by the however, people's livelihood depends on mining process (Martinez-Ruiz et al., them (Ncube et al, 2011). 2007). Mining practices can result in the

122 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015

Tanzania is a wild orchid biodiversity 6A) in some parts of Iran (case study, hotspot and has a high prevalence of personal observation in Kerman province), HIV/AIDS. Every year, between 2.2 to 4.1 and may be in some other parts of the million orchid plants consumed in Zambia country, due to people’s lack of expertise originate from Tanzania. In addition, more and absence of protective rules. than two million orchid tubers find their Surprisingly, the bulbs of this species are way illegally to the markets of Zambia sold in winter (the newly-emerged plants annually. The harvesting of some orchid are picked and sold) and due to lack of species by HIV/AIDS gatherers and non- branching root system; the plants are HIV/AIDS gatherers was studied by Challe withered and finally die after some time. and Price (2009). The results of this study Ornithogalum spectabilis is also used as a indicated the decline of some orchid medicinal and nutritive plant in some parts species in Tanzania. Unfortunately, the of Iran including Kurdistan province (Fig. income of some people depends on this 6 B). Orchis spp. is also used for making type of business and the harvesting and in ice cream and in confectionary, as well. some cases smuggling of orchids, which The dried flowers of genus Orchis is also inevitably have negative effects on the used for making a kind of tea. The survival and diversity of orchid species in are also used for medicinal this country. purposes. The leaves of Biarum spp. (Fig. Some medicinal bulbous plants in Iran 6 C) with an endemic species in Iran face challenges similar to those reported (B.straussii) are used for making a kind of for South Africa. For instance, a kind of meal called “Ashe Cardeh” (in Persian) in jam is made of the rhizome of some parts of Iran, particularly the northern Polygonatum orientale (Liliaceae) parts of Fars province (e.g., Eghlid). Since rhizomatous plants mostly grown in the the underground specialized structure of northern parts of Iran. This jam is called this plant is a tuberous-like organ, this “Morabbay-e-Shaghaghol” in Persian, and unsustainable harvesting of the leaves is a sold in local markets. As the rhizomes are threat for this species because the used for making this jam, the plants are photosynthetic leaves provide the tubers destroyed to get the rhizome and this way with carbohydrates ensuring growth and of unsustainable (destructive) harvesting is development. Eremurus spp. (Fig. 6 D) a risky method threatening this valuable tuberous roots are also used for preparing a bulbous plant species restricted to the kind of glue called “Serish”. The flowers northern parts of Iran. A kind of powder is are also used with egg in Kerman province produced from the bulbs of F. imperialis as a meal. Since this species also suffers (liliaceae) in Iran. This slow-to-propagate from inappropriate herbivory and popular bulbous plant is also under some overgrazing as it was mentioned earlier, other pressures previously discussed. some protection must come into effect for Unfortunately, for making this special this multipurpose bulbous plant. In powder, the bulbs should be harvested and general, in the case of almost all bulbous the species is at the risk of extinction in plants, either bulbs or leaves are used for some regions of Iran. medicinal purposes, and both types of Urginea maritima (Liliaceae) is another harvesting are threatening if not handled bulbous plant which is illegally and sustainably. mistakenly sold as Iris hollandica (Fig.

Environmental and Anthropogenic Pressures on Geophytes of … 123

A B

C D s

Fig. 6. Urginea maritima which is mistakenly sold as Iris hollandica in the city of Kerman, B) Ornithogalum sp. Leaves ready for sale at a local market of the city of Sanandaj called “Gilakhe” in the Kurdish language, C and D) Biarum and Eremurus spectabilis sold as spring vegetables in an Iranian local market, respectively.

Population growth rate and been heightened due to poor management development practices and the arid or semi-arid climate The increase in human population has regime characteristics of this area increased the expectations of life standards (Louhaichi et al., 2009). and exacerbated the scarcity of natural The vast region covering the arid and resources (Gholami et al., 2013). Sheep semi-arid lands of North Africa, the Middle and goat production was historically an East, and East and Central Asia -the important occupation for rural populations Palaearctic Desert- is the cradle of the Old located within WANA countries World civilization. While they have given (Louhaichi et al., 2009). Currently WANA us most of our domestic animals and some rangelands support high human population of our most important crops, those arid densities that apply significant pressures on lands have been devastated by wars, these resources through elevated livestock overgrazing, and the vagaries of climate for grazing practices. These impacts have led thousands of years. Today, as population to increased rates of desertification, a increase and modern technology become problem that will continue to worsen, more pervasive, many of the rural people unless proper management measures are living in this region face the ancient developed and implemented that reduce scourges of hunger, pestilence, and conflict these grazing impacts. Over time, impacts (McNeely, 2003). One of the tragedies of associated with livestock grazing have this situation is that the biological

124 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015 resources which could help make these people of the detrimental effects of lands productive are often abused rather overgrazing is very useful. Indigenous than nurtured. Thus, the major challenge in ecological knowledge (IEK) has played a the implementation of the Convention of key role in the economy and cultural Biological Diversity (CBD) in arid lands development of human beings for lies not so much in the biology of the millennia (Ghorbani et al., 2013). Some species but rather in the social, economic, projects (in state and private sector) should and political reasons within which people be assigned and implemented similar to operate (McNeely, 2003). those performed for pasture and forest The population of Iran is about 70 million restoration in the country during the past and the growth rate estimated as 1.7% (FAO, decades. So, the growing areas (habitats) of 2005). Iran has the sixteenth largest geophytes are expanded from the present population in the world (Malekafzali, 2004). ones to new ones in other parts of the This growth rate is very high and the country. In tow mountainous regions in population is young. To meet the Kerman province, the bulbs of Fritillaria requirements of this population, some types imperialis were planted for the first time of agricultural and horticultural activities are and their growth and blooming were encouraged which have been and are harmful successful and promising. These activities for biodiversity in short and long term could guarantee conservation purposes in periods. Vegetation cover in Afghanistan has the same situations elsewhere in Iran. been modified significantly through millennia Meanwhile, the establishment of some of human occupation. In a country where stations for bulbous plants particularly in over 80 percent of the population relies western and northern regions are proposed. directly on the natural resource base to meet their daily needs, widespread environmental War and terrorism degradation poses an immense threat to As covering the negative effects of war and future livelihoods (UNEP, 2003). terrorism is beyond the scope of this Social issues such as low income, review, these factors are briefly presented poverty and low levels of welfare and here. War and terrorism have left an education result in land degradation extensive imprint on landscapes throughout through improper land use activities the world (Mannion, 2003). The vast (Heshmati et al., 2013). Meat is a major region covering the arid and semi-arid part of people’s diet in Iran. Thus, a part of lands of North Africa, the Middle East, and income in rural areas is obtained from East and Central Asia -the Palearctic animal husbandry such as sheep, goat, cow Desert- is the cradle of the Old World and even camel. On the other hand, the civilization. While they have given us most main income source for Nomads (Ashayer) of our domestic animals and some of our is animal husbandry. Consequently, most important crops, those arid lands have grazing fields, pastures, and forests is been devastated by wars, overgrazing, and inevitable for those involved in animal the vagaries of climate for thousands of husbandry. Meanwhile, our country is not years (McNeely, 2003). well industrialized at the present and these Conflicts and geopolitical forces are types of income support the country to be important drivers of land use and land less dependent on oil industry. cover change (Gibson, 2012). The many Accordingly, we should seek approaches to environmental impacts of hostility include fulfill the balance between the income the infrastructure necessary for the from animal husbandry and our limited preparation of war, including training natural resources such as pastures, forests, grounds, camps, barracks, weapon testing, meadows, etc. Furthermore, informing etc. However, the immediate impact of war Environmental and Anthropogenic Pressures on Geophytes of … 125 and terrorism are usually sudden and parts of the world. If a circle be drawn with dramatic and can be direct or indirect. Istanbul as the center and taking in Greece Direct impacts include bomb and blast and Bulgaria, Syria and the Lebanon, Persia damage to settlements. Defoliation and and Afghanistan and neighboring countries, ecosystem destruction, the dumping of the it can be seen that many of the most popular machinery of war, and the destruction of flowering bulbs are grown within these areas resources also occur (Mannion, 2003). The (Genders, 1973). Thus, there remains no immediate impacts of war and terrorism doubt that war and terrorism are potential are obvious. The effects on landscape can risks for bulbous species throughout the be as devastating as earthquakes or world and particularly for the area just volcanic eruptions as buildings collapse mentioned above. Ultimately, some new and craters develop (Mannion, 2003). The approaches and solutions should be adopted war between Iraq and Iran which lasted for and implemented to settle these devastating about 8 years also had some drastic effects clashes for a more peaceful world and, on both countries' vegetation and consequently, a more biologically diverse inevitably on bulbous plants, as well. Since planet. the main center of this war was restricted to southern, western and south-western Insects and diseases, rodents, birds, parts of Iran which are the cradle for many and small animals bulbous plants, some habitat degradation These biotic agents are also partly involved occurred in these areas. For instance, it is in the scenario of bulbous plants’ genetic believed that mourning iris (Iris susiana) is resource erosion. Some insects feed on the a bullous species which has taken its name seeds of some species and the sexual from Shoosh which is now a city in propagation of these species is disturbed. As Khuzestan province. It should be noted that the seed is a bridge between generations and the nomenclature is somehow controversial increases variation and diversity, the lack of as reported by Saad and Khuri (2003). seed formation is a threat for the host Currently some new waves of battles, species. Fungi, bacteria, and viruses are the conflicts, and clashes triggered by extremists main diseases found in ornamental flower and terrorist groups in the region particularly bulbs. The other less studied threatening Syria and Iraq (and to some extent group of biotic stresses is nematodes. Afghanistan) and the newly emerged terrorist Rodents are also important in this regard and group called Daesh are all potential risks for should be taken seriously especially for the vegetation cover and may affect the palatable organs under severe drought vegetation cover of Iran in border lines with conditions. Some insects feed on the these countries. Many decades of conflict capsules and seeds of Iris species in Iran. have been mentioned as one of the main Mice and even some kinds of birds such as reasons for deforestation and widespread loss chukar partridge or chukar (Alectoris chukar) of vegetation cover in Afghanistan (UNEP, are interested in tulip bulbs as a source of 2003). During over two decades of conflict, food. Deer and insects have been reported as Afghanistan’s natural resource base has been two factors responsible for reducing the heavily damaged by military activities, population of Turkey's cap lily (Lilium refugee movements, over-exploitation, and a superbum) which is a rare lily species in lack of management and institutional Turkey. In addition to the threatening factors capacity. The past three to four years of mentioned earlier, F. imperialis are at risk drought have worsened this damage (UNEP, during and after blooming. Some rodents dig 2003). A greater number of bulbous and up the bulbs of this species for the hidden cormous species grow in the Middle East and food source reserved in the bulbs (Fig. 7. A south-eastern Europe in comparison to other and B).

126 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015

A B

Fig. 7. Bulb (A) and flowering plants (B) of Fritillaria imperialis damaged by rodents in Manesht Mountain of Ilam province

The devastating factors mentioned in national and international levels. The this contribution are the most important identification of the ploidy level of these ones threatening the bulbous plant species is proposed using modern techniques vegetation of Iran. Now that we have just including flow cytometry and ploidy passed 2010 as “The International Year of analyzer. The data available now date back Biodiversity”, it seems that we shoulder a to some years ago gathered by some great responsibility for biodiversity botanists and are most probably incomplete. conservation around the world. Thus, the Little information is available about the following approaches are proposed for the natural breeding, mutation breeding, and the fulfillment of this purpose in Iran: relationship among the species of some 1. Increasing the protected areas in Iran genera including Tulipa spp., Iris spp. and to conserve the existing species as Fritillaria spp., which are rich in this regard. efficiently as possible. The establishment Thus, some state-sponsored comprehensive of protected areas is a primary strategy to researches should be conducted in order to conserve biodiversity. obtain reliable data for many application 2. Gathering the species at the risk of fields including horticultural, extinction in Botanical Gardens and pharmaceutical, aesthetical, breeding, etc. Research Centers for better conservation. 7. Following and implementing the rules 3. Providing people with scientific assigned by the associated institutes such knowledge through propagating information as IUCN, CBD, etc. in public media and encouraging them to 8. The measures proposed by UNEP contribute more in this regard. should be put into effect. 4. Highlighting the decisive role of 9. More attempts should be made to NGOs and increasing the number of these restore the degraded ecosystems and Non- Governmental Organizations in Iran. fragmented habitats. 5. Conducting researches on the various 10. GIS and modeling findings should aspects of growth and development of be applied efficiently. these species including ecology, 11. Tissue culture and biotechnology phenology, physiology, propagation, etc. to application is vital and viable. have a database for precise decisions. 12. Improving tourism as a clean 6. It is highly recommended that the industry is of considerable importance. bulbous species of Iran be studied based on 13. Indigenous Ecological Knowledge is morphological and particularly molecular very important for involving people in the markers in order to attain a deep knowledge assigned programs. about them for upcoming researches at Environmental and Anthropogenic Pressures on Geophytes of … 127

Covering all of these suggestions is extensive collection (Vedat Ulug et al., beyond the scope of this review article, so 2010). It should be noted that the bulbs of only the 11th and 12th suggestions are this species, which is difficult and slow to presented in some details here. propagate, is exported to the Netherlands, Germany, England, the US, Japan, and Tissue culture and biotechnology Denmark. We believe that biodiversity loss is a global It is already reported that Fritillaria concern not restricted to any single part of species are at the risk of extinction in Iran the world. Although this phenomenon (Ebrahimi et al., 2006). Indirect somatic occurs more seriously in developing embryogenesis from petal explants was countries, the people of the entire world used for micropropagation of F. imperialis, derive benefits from this biodiversity and an endangered bulbous plant in Iran should, therefore, be responsible. Thus, (Mohammadi-Dehcheshmeh et al., 2008). some promising reports from Iran and Indirect organogenesis of F. imperialis has other countries experiencing the same been reported by Rahimi et al. (2013). A scenario are briefly presented here protocol for the micropropagation of indicating the efforts of scientific media to “Susan-e-Chelcheragh”, Lilium ledebourii somehow solve the problem. (Baker) Boiss has been developed There are many techniques available for developed while studying the effects of the conservation of the plant genetic growth regulators, sucrose concentration, resources of rare and endangered species. harvesting season, and cold treatment These include micropropagation, seed (Azadi and Khosh-Khui., 2007). A Somatic germination and regeneration from callus, embryogenesis protocol has also been embryo rescue, and cryopreservation. established for the regeneration of this Micropropagation in bulbous plants, as an species by using new vegetative alternative to the conventional methods for microscales and the transverse thin cell vegetative propagation, attracts much layer (tTCL) of young bulblet roots as the attention due to its advantages including explant source (Bakhshaie et al., 2010). fast multiplication (Chang et al., 2000). This species is critically endangered as Banciu et al. (2010) investigated the in mentioned earlier. Farahmand (2007), vitro propagation of the critically Farahmand et al. (2007) and Farahmand endangered species of Scilla autumnalis L. and Khosh- Khui (2009) investigated twin- The plant is protected in the National Red scaling, chipping and micropropagation of List of higher plants in Romania. In vitro two Narcissus tazetta L. populations propagation was optimized by Al-Gabbiesh locally known as Narges-e-Shahla and et al. (2006) for the two endangered Narges-e-Meskin. They developed asexual species of Iris namely, I. petrana and I. propagation methods and optimized a atrofusca. A tissue culture protocol was protocol for in vitro propagation of these also developed for the mass propagation of two populations of Narcissus tazetta. Lilium speciosum Thunb. var. gloriosoides which are fortunately under governmental Baker, a native and rare perennial bulbous protection in some provinces such as Fars plant only known at altitudes of 150-660 m and Khuzestan. Biotechnology could also in northern Taiwan (Chang et al., 2000). be used as an efficient tool for germplasm Several propagation techniques were conservation particularly for endangered used to find a practical and fast method of species (Paunescu, 2009). propagation for Fritillaria persica in Turkey. This comprehensive research was Improving the tourist industry done after some scientists warned that the Tourism has long been considered a ‘clean species should be protected against industry’, without any considerable negative

128 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015 effects on the environment (Van der Duim among them makes this group of plants and Caalders, 2002). However, this image is spectacular, particularly during spring, now outdated. Most parties are aware of the autumn, and winter when the mountains possible negative impacts and see the need and plains in Iran are covered with them for action (UNEP, 2000). At the same time, and become scenic. Thus, conserving this tourism is able to contribute to a growing biodiversity is a prerequisite for a viable awareness of the value of nature (Urry, and dynamic tourist industry. 1992), and hence, to public support for the protection of biodiversity (Van der Duim and Conclusion Caalders, 2002). Biodiversity is vital for In conclusion, inappropriate herboviry and tourism. Coasts, mountains, rivers, and overgrazing during the growth and forests are major attractions for tourists flowering season, mechanization, land use around the world. Wildlife and landscapes in change, drought, road construction, mining mountainous areas are important attractions activities, urban expansion, plant material for tourists (WTO, 2010). The development overexploitation, habitat fragmentation and of tourism can also be a way to make nature ecosystem degradation, conversion of reserves economically viable and to provide habitats for agricultural and horticultural employment and income for the local purposes, lack of protection rules, illegal population (UNEP, 2000). In this manner, it and uncontrollable bulb and cut flower can provide a viable alternative to other more harvesting as a source of income for native damaging activities such as slash and burn poor people, changing the pastures to dry agriculture, cattle farming, hunting, wood farmlands, pest and disease attacks, and, to collection, mining and the like (Collins, a lesser extent, war and terrorism are the 1998., Ross and Wall, 1999). main factors threatening flower bulbs of Iran holds myriads of attractions from Iran as national and international heritage. the point of view of ecotourism. One of the As the natural multiplication rate of many most outstanding features of Iran is its ornamental bulbs are low, and, at the same unique nature boasting thousands of plant time, the rate of extinction and eradication and animal species, some of which are rare is high, some steps should be taken and endemic. Ornamental bulbous plants of according to the suggestions presented here Iran have particular tourism appeals for at local, national, and international levels nature enthusiasts from all around the to conserve these invaluable natural world. The presence of winter, summer, resources for current and future spring and autumn-flowering species generations. References Ajani, Y., J. Noroozi and I.G. Levichev. 2010. in Choghart Iron Mine Desert Region (Used Gagea alexii (Liliaceae), a New Record from method: Fuzzy AHP). Austral. J. Basic and Subnival Zone of Southern Iran with Key and Appl. Sci. 5: 1075-1078. Notes on Sect. Incrustatae. Pak. J. Bot. 42:67–77. Al-Gabbiesh, A., D.S. Hassawi, and F.U. Afifi. Akhani, H. (Ed.). 1998. Plant biodiversity of 2006. In Vitro Propagation of Endangered Iris Golestan National Park. Stapfia 53, Species. J. Biol. Sci. 6:1035-1040. Biologiezentrum des O.Ö. Landesmuseums, 411 p. Amiraslani, F., and D. Dragovich. 2013. Combating Akhani, H. 2004. A New Spiny, Cushion-like Desertification in Iran Over the Last 50 Years: an Euphorbia (Ephorbiaceae) from South of West Overview. J. Environ. Mgt. 92:1-13. Iran With Special Reference to the Amiri, F., A. Arianpour, and S. Fadai. 2008. Phytogeographic Importance of Local Endemic Effects of Livestock Grazing on Vegetation Species. Bot. J. Linn. Soc. 146:107-121. Composition and soil Moisture Properties in Alavi, A., H. Alinejad-Rokny, and M. Sadegh- Grazed and Non-Grazed Range Site. J. Biol. Sci. Zadeh. 2011. Prioritizing Crescive Plant Species 8: 1289-1297. Environmental and Anthropogenic Pressures on Geophytes of … 129

Anderson, N.O. 2006. Flower Breeding and Context of HIV/AIDS in the Southern Highlands Genetics: Issues, Challenges and Opportunities for of Tanzania. J. Ethnobiol. Ethnomed. 5:41. the 21st Century, Springer, Netherlands, 822p. Chang, C., C.T. Chen, Y.C. Tsai, and W.C. Anderson, R.C. 1994. Height of white-flowered Chang. 2000. A Tissue Culture Protocol for trillium (Trillium grandiflorum) as an index of Propagation of a Rare Plant, Lilium speciosum deer browsing intensity. Ecol. Applications 4: Thunb. var. glorisoides Baker. Bot. Bull. Acad. 104-109. Sin. 41:139-142. Ayoubi, A., F. Khormali, K.L. Sahrawat, and A.C. Collins, A. 1998. Tourism Development and Rodrigues de Lima. 2011. Assessing Impact of Natural Capital. Ann. Tourism Res. 26:98-109. Land Use Change on Soil Quality Indicators in a Crawley, M.J. (Ed.). 1983. Herbivory: The Leossial Soil in Golestan Province, Iran. J. Agr. Dynamics of Animal-Plant Interactions. Sci. Tech. 13:727-742. University of California Press, Berkley, 447 p. Azadi, P., and M. Khosh-Khui. 2007. De Hertogh, A., and M. Le Nard (Ed.). 1993. Micropropagation of Lilium ledebourii (Baker) The Physiology of Flower Bulbs. Elsevier Boiss. As Affected by Plant Growth Regulators, Science Publishing. The Netherlands, 811 p. Sucrose Concentration, Harvesting Time and Cold Treatments. Electron. J. Biotechnol. 4:582-589. Dore, M.H.I. 2005. Climate Change and Changes in Global Precipitation Patterns: What Azarnivand, H., A. Farajollahi, E. Bandak, and Do We Know? Environ. Intel. 31:1167-1181. H. Poozesh. 2011. Assessment of the Effects of Overgrazing on the Soil Physical Characteristics Drake, J.A., R.S.B. Greene, B.C.T. Macdonald, and Vegetation Cover Changes in Rangelands of J.B. Field, and G.L. Pearson. 2010. A Review of Hosainabad in Kurdistan Province, Iran. J. Landscape Rehabilitation in Ecosystem Rangeland Sci. 1:95-102. Engineering for Mine Closure. In: Proceedings of International Conference on Mine Closure. (Eds. Bakhshaie, M., M. Babalar, M. Mirmasoumi, Fourie, A., Tibett, M., and J. Wiertz.). Perth, WA, and A. Khalighi. 2010. Somatic Embryogenesis Australian Center for Geomechanics 241-249. and Plant Regeneration of Lilium ledebourii (Baker) Boiss., an Endangered Species. Plant Ebrahimi, E., M, Mohammdi-Delcheshmeh, and cell Tissue Organ Cult. 102:229-235. M. Sardari. 2006. Fritillaria Species are at the Risk of Extinction in Iran: Study on Effective Banciu, C., M. Mitoi, F. Helepciuc, and F. Factors and Necessity of International Attention. Aldea. 2010. In Vitro Propagation of Critically HortScience 41:1002. Endangered Species Scilla autumnalis L. Biochemical Analysis of the Regenerants. Tom. Eftekhari, T., and M. Ramezani. 2004. XVII. 2: 318-323. Introduction to Plant Biodiversity in Iran. In: Biodiversity and Medicinal Plant Wealth of Barati, A.A., A. Asadi, K. Kalantari, H. Azadi, South Asian Countries (Eds. Pushpangadan, P., and F. Witlox. 2015. Agriculture Land K.N. Nair, and M.R. Ahmad). National Conversion in Northwest Iran. Intl. J. Environ. Botanical Research Institute, Lucknow-226001, Res. 9:281-290. India, 39-40. Bogner, J., and P. Boyce. 2008. Eminium Eppich, B., L. Dede, A. ferenczy, A. jaegeri, a New Species from Northwester Iran. Garamvogyi, L. Horvatch, I. Isepy, S.Z. Pristzer, Willdenowia 38:149. and L. Hungary. 2009. Climatic Effects on the Bosing, B.M., D. H. Haarmeyer, J. Dengler, and Phenology of Geophytes. Appl. Ecol. Environ. J.U. Ganzhorn. 2014. Effects of Livestock Res. 7: 253-266. Grazing and Habitat Characteristics on Small FAO, 2005. Food and Agricultural Commodities Mammal Communities in the Knersvlakte in Production. South Afr. J. Arid Environ. 104:124-131. http://faostat.fao.org/site/339/default.aspx. Chaichi, M.R., M. Mohseni Saravi, and A. Farahmand, H. 2007. Micropropagation of Fars Malekian. 2005. Effects of Livestock Trampling Endemic Narcissus L. Populations. Shiraz Univ. on Soil Physical Properties and Vegetation Shiraz, Ph.D. Diss. 134p. Cover (Case study: Lar Rangeland, Iran). Intel. J. Agr. Biol.7:904-908. Farahmand, H., and F. Nazari. 2014. Horticultural and Ornamental Values of Iran’s Challe, J.F.X., and L.L. Price. 2009. Engangerd Bulbous Plants. 1st Natl. Ornamental Plants Edible Orchids and Vulnerable Gatheres in the Congr. October 21-22, 2014. P-27.

130 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015

Farahmand, H., and M. Khosh- Khui. 2009. The Grabherr, G., M. Gottfried, and H. Pauli. 1994. Effects of BA, IBA and NAA on Proliferation of Climate Effects on Mountain Plants. Nature Narcissus Shahla and Meskin in Fars 369: 448. Province. Proc. of the 6th Iranian Horticultural Gurbuz, B., K.M. Khawar, N. Arslan, A. Ipek, Science Congr. July 13-14, 2009. P: 84-85. E.O. Sarıhan, S. Ozcan, I. Parmaksız, and S. Farahmand, H., M. Khosh-Khui and A. Mirici. 2009. Adaptation of Endemic Shekafandeh. 2007. The Effects of Activated Mediterranean Sternbergia candida Mathew Et Charcoal (AC) and Light Regime on Bulblet T. Baytop in the continental climate of Central Induction and Growth of Two Narcissus tazetta Anatolia. Scientia Hort. 123: 99–103. L. Populations in Fars Province. Proc. of the 5th Hassani, N., H.R. Asghari, A.S. Frid, and M. Iranian Horticultural Science Congr. Sept. 3-6, Nurberdief. 2008. Impact of Overgrazing in 2007. P-292. Long Term Traditional Grazing Ecosystem on Farahmand, H., M. Khosh-Khui, and A.R. Vegetation Aroun Watering Points in A Semi- Khosravi. 2007. Classification of Narcissus tazetta Arid Rangeland of North-Eastern Iran. Pak. J. L. Populations in Southern Parts of Iran Based on Biol. Sci. 11:1733-1737. Vegetative and Reproductive Characteristics. Proc. Heshmati, G.A. 2007. Vegetation Characteristics of the 5th Iranian Horticultural Science Congr. Sept. of Four Ecological Zones of Iran. Intel. J. 3-6, 2007. P-114. Plant Prod. 1: 215-224. Farahmand, H., M. Sarchesmeh Pour, H. Heshmati, M., A. Abdu, N.M. Majid, and J. Mohamadi, H. Daei Parizi, and H. Fallah. 2014. Shamshuddin. 2013. Land Degradation and Sustainable Mining with Emphasis on Degraded Preventive Measures from the Perspective of the Ecosystems. 1st National Congr. on Sustainable Stakeholders. Amer. J. Appl. Sci. 10:1061-1076. Management of Soil and Environmental Resources. Sept. 10-11, 2014. P: 1-12. Hill, D., M. Fasham, G. Tucker, M. Shewry, and P. Shaw (eds.). 2006 Handbook of Biodiversity Farahmand. H., and M. Khosh-Khui. 2006. Methods. Cambridge University Presss. The Effect of Growth Regulators on Propagation of Edinburgh Building, Cambridge. U.K. 486 p. Two Narcissus L. Populations Through Twin- Scaling and Chipping. Iran. J. Hort. Sci. IUCN. 2004. The International Union for Technol. 7: 169-180. Conservation of Nature and Natural Resources Red List of Threatened Species. A Global Genders, R. (Ed.). 1973. Bulbs, A Complete Species Assessment. Handbook of Bulbs, Corms and Tubers (Robert http://www.iucnredlist.org/. Hale and Company, London, U.K. 662p. Jafari, A. 2012. A New Species of Leopoldia Ghahreman, A., F. Attar, and F. (Asparagaceae) From Iran. Phytotaxa 43:61-64. Ghahremaninejad. 2007. A New Species of Tulipa (Liliaceae) From Western Iran. Novon: J. Jalili, A., and Z. Jamzad (Eds.). 1999. Red Data Bot. Nomenclature17: 437-439. Book of Iran Research Institute of Forests and Rangelands. Iran. 748 p. Ghahremaninejad, F., and F. Gholamian. 2006. A New Record (Oxalis articulata) From Iran. Katerere, D.R., and Eloff, J.N. 2008. Anti- Irn. J. Bot. 12: 55-56. bacterial Activity of Hypoxis hemerocallidea (Hypoxidaceae): Can Leaves be Substituted for Gholami, A., B. Rezaei, E. Panahpour, and A. Corms as a Conservation Strategy? J. Delavari. 2013. The Appraisal of land Use Change Enthopharmacol. 74:613-616. and its Influence on Soil Quality Indexes in Gambue Region Western of Khouzestan Province. Korner, C. (Ed.). 1999. Alpine Plant Life: Intel. J. Farming Allied Sci. 2: 999-1002. Functional Plant Ecology of High Mountain Ecosystems. Springer-Verlag, Berlin, Heidelberg. Ghorbani, M. H., Azarnivand, A.A. Mehrabi, M. 359p. Jafari, H. Nayebi, and K. Seeland. 2013. The Role of Indigenous Ecological Knowledge in Kumar, V., and A. K. Sharma (Eds.). 2001. Managing Rangelands Sustainably in Northern Plant Biotechnology and Biodiversity. Agrobios, Iran. Ecol. Soc. 18: 1-15. Jodhpur, India. 374p. Gibson, G.R. 2012. War and Agriculture: Three Lomba, A., L. Pellissier, C. Randin, J. Vicente, Decades of Agriculture Land Use and Land F. Moreira, J. Honardo, and A. Guisan. 2010. Cover Change in Iraq. State Univ. Ph.D. Diss. Overcoming the Rare Species Modeling 145p. Paradox: A Novel Hierarchical Framework Environmental and Anthropogenic Pressures on Geophytes of … 131

Applied on an Iberian Endemic Plant. Biol. Nazari, F., H. Farahmand, and M. Ghasemi Conserv. 143:2647-2657. Ghehsareh. 2014. The Effects of different Amounts of Natural Zeolite on Vegetative and Louhaichi, M., A.K. Salkini, and S.L. Petersen. Reproductive Characteristics of Narcissus 2009. Effect of Small Ruminant Grazing on the tazetta L. cv. Shahla. J. Plant Prod. 2:39-48. Plant Community Characteristics of Semi-Arid Mediterranean Ecosystems. Intl. J. Agr. Biol. Nazari, F., H. Farahmand, M. Khosh-Khui, and 11:681-689. H. Salehi. 2007. Effects of Two Planting Methods on Vegetative and Reproductive Lubbers, A., and M. Lechowicz. 1989. Effects of Characteristics of Tuberose (Polianthes Leaf Removal on Reproduction vs. Belowground tuberosa L.). Adv. Natural Appl. Sci. 1:26-29. Storage in Trillium grandiflorum. Ecol. 70:85- 96. Nazari, F., H. Farahmand, M. Khosh-Khui, and Makki, T., S. Fakheran, H. Moradi, M. Iravani, H. Salehi. 2011. Effects of Different Pot and J. Senn. 2013. Landscape-Scale Impacts of Mixtures on Vegetative, Reproductive and Transportation Infrastructure on Spatial Physiological Characteristics of Iranian Dynamics of Two Vulnerable Ungulate Species Hyacinth (Hyacinthus orientalis L. cv. Sonbol- in Ghamishloo Wildlife Refuge, Iran. Ecol. e-Irani). Intl. J. Agr. Food Sci. 1:34-38. Indicators 31:6-14. Ncube, B., J.F. Finnie, and J. Van Staden. 2011. Malekafzali, H. 2004. Population Control and Seasonal Variation in Antimicrobial and Reproductive Health in the Islamic Republic of Photochemical Properties of Frequent Used Iran. Arch. Iran. Med. 7: 247-250. Medicinal Bulbous Plants From South Africa. Mander, M. 1997. The Marketing of Indigenous South Afr. J. Bot. 77:387-396. Medicinal Plant in South Africa a Case Study in Noor Alhamad, M. 2006. Ecological and KwaZulu-Natal. Investigation Report No. 164, Species Diversity of Arid Mediterranean Institute of Natural Resources, Univ. of Natal Grazing Land Vegetation. J. Arid Environ. 66: Pietermaritzburg. 698-715. Mannion, A.M. 2003. The Environmental Noroozi, J., H. Akhani, and S.W. Breckle. 2008. Impact of War and Terrorism. Geographical Biodiversity and Phytogeography of Alpine the Paper 169. 22p. Alpine Flora of Iran. Biodiversity Conserv. Maroofi, M. 2007. A New Species of the Genus 17:493-521. Muscari (Liliaceae) From Iran. Iran. J. Bot. 13: Noy-Meir, I., and T. Oron. 2001. Effects of 75-77. Grazing on Geophytes in Mediterranean Martinez-Ruiz, C., B. Fernandez- Santos, P.D. Vegetation. J. Vegetation Sci. 12:749-760. Putwain, and M.J. Fernansez-Gomez. 2007. Noy-Meir, I., M. Gutman, and M. Kaplan. 1989. Natural and Man-Induced Vegetation on Mining Response of Mediterranean Grassland Plants to Wastes: Changing in the Floristic Composition Grazing and Protection. J. Ecol. 77:290-310. During Early Succession. Ecol. Eng. 30:286-294. Pauli, H., M. Gottfried, and T. Dribock. 2007. McNeely, J.A. 2003. Biodiversity in Arid Signal of Range Expansions and Contributions Regions: Values and Perceptions J. Arid of Vascular Plants in the High Alp: Environ. 54:61-70. Observations (1994-2004) at the GLORIA Mohammadi-Dehcheshmeh, M., A. Khalighi, A. Master Site Schrankogel, Tyrol, Austria. Global Naderi, M. Sardari, and E. Ebrahimie. 2008. Change Biol. 13:147-156. Petal: a Reliable Explant for Direct Bulblet Paunescu, N. 2009. Biotechnology for Endangered Regeneration of Endangered Wild Populations Plant Conservation: A Critical Overview. of Fritillaria imperialis L. Acta Physiol. Plant. Romanian Biotechnol. Lett. 14:4095-14103. 30: 395–399 Perevolotsky, A., R. Schwarts-Tazchor, R. Mohseni Saravi, M., M.R. Chaichi, and B. Yonathan, and G. Neeman. 2011. Geophytes- Attaeian. 2005. Effects of Soil Compaction by Herbivore Interactions: Reproduction and Animal Trampling on Growth Characteristics of Population Dynamics of Anemone coronaria L. Agropyrum repens (case study: Lar rangeland, Plant Ecol. 212:563-571. Iran). Intl. J. Agr. Biol. 7: 909-914. Pourbabaei, H., V. Rahimi, and M.N. Adel. Mozaffarian, V. (Ed.). 2003. A Dictionary of 2014. Effects of Drought on Plant Species Iranian Plants Names. Farhang-e-Moaser, Diversity and Productivity in the Oak Forests of Tehran, Iran. (In Farsi). 671 p. Western Iran. Ecol. Balkanica 6:61-67.

132 Int. J. Hort. Sci. Technol; Vol. 2, No. 2; December 2015

Rahimi, A., M. Aghaalinejad, and N. Arslan. European Alps: a Review. Climatic Change 2012. Geophytes of Sulduz Region, West 50:77-109. Azerbayjan Province, Iran and Their Tietjen, B., and F. Jeltsch. 2007. Semi-arid Characteristics. Pure Appl. Bio.1:18-21. Grazing Systems and Climate Change: a Survey Rahimi, M., M.H. Daneshvar, M.Heydari, and of Present Modeling Potential Ad Future Needs. F. Yari. 2013. In Vitro Micropropagation of J. Appl. Ecol. 44: 425-434. Fritillaria imperialis L. Through Induction of UNEP (United Nations Environment Programme). Indirect Organogenesis. Intl. J. Agron. Plant 2003. Afghanistan Post-conflict Environmental Prod. 4:418-424. Assessment. 180 p. http://www.unep.org/. Razyfard, H., S. Zaree, R.M. Fritsch, and H. UNEP. 2000. Report of the Fifth Meeting of the Maroofi. 2011. Four New Species of Allium Conference of the Parties to the Convention on (Alliaceae) From Iran. Ann. Bot. Fennici 48:352- Biological Diversity. Nairobi, May 15-26. 360. Urry, J. 1992. The “Tourist Gaze” and the Renz. J. 1978. Orchidaceae, In: Flora Iranica Environment. Theory, Culture and Society 9:1-26. (ed. Rechinger, K. H.). Austria.125p. Van der Duim, R., and J.Caalders. 2002. Rios, S., J. Juan, V. Martinez-Frances, E. Biodiversity and Tourism Impacts and Laguna, D. Rivera, F. Alcaraz, A. Verde, J. Interventions. Ann. Tourism Res. 29: 743-761. Fajardo, J.L. Casas, and J.E. Ramirez. 2010. Endemic Species of Narcissus in Central Spain: Vedat Ulug, B., A.B. Korkut, E.E. Sisman, and Biodiversity and Conservation under Grazing Muratozyavuz. 2010. Research on Propagation Pressure by Wild and Domestic Herbivorous. Methods of Persian Lily Bulbs (Fritillaria Options Mediterraneennes 92: 79-83. persica L.) with Various Vegetative Techniques. Pak. J. Bot. 42: 2785-2792. Ross, S. and G. Wall. 1999. Ecotourism: Towards Congruence between Theory and Wendelbo. P. 1977. Tulips and Irises of Iran and Practice. Tourism Mgt. 20: 123-132. Their Relatives. Botanical Institute of Iran. M.A. Fardin, Tehran, Iran. 83p. Saad, L., and S. Khuri. 2003. Hanging in There by a Fall- the Oncocyclus Irises of Lebanon. Wentzell G.K 1973 How to Grow Bulbs. British Iris Society. 3p. Lane Magazine and Company, California, U.S.A. 80p. Sarasan, V., R. Gripps, M.M. Ramsay, C. Atherton, M. McMichean, G. Prendergast, and Williams, V.L. 2003. Hawkers of Health: an J.K. Rowntree. 2006. Conservation In Vitro of investigation of the Faraday Street Traditional Threatened Plants-Progress in the Past Decade. Medicine market in Johannesburg, Gauteng. In Vitro Cell. Dev. Biol. Plant 42:206-214. Report to Gauteng Directorate of Nature Conservation, DACEL. Plant Ecology and Shanley, P., and Luz, L. 2003. The Impacts of Conservation Series. Vol.15 Univ. of the Forest Degradation on Medicinal Plant Use and Witwatersrand, Johannesburg. Implication Purpose for Health Care in Eastern Amazonia. Bioresource 53:573-584. WTO. 2010. World Tourism Organization. Tourism and Biodiversity Achieving Common Sheldon, J.W., M.J. Balick, and S.A. Laird. 1997. Goals towards Sustainability. Madrid, Spain. 73p. Medicinal Plants: Can Utilization and Conservation Coexist? Adv. Econ Bot. 12:1-104. Yates, C.G., D.A. Norton, and R.J. Hobbs. 2000. Grazing Effect on Plant Cover, Soil and Sivakumar, M.V.K., H.P. Das, and O. Brunini. Microclimate in Fragmented Woodlands in 2005. Impacts of Present and Future Climate South-Western Australia: Implication for Variability and Change on Agriculture and Restoration. Austral. Ecol. 25: 36-47. Forestry in the Arid and Semi-Arid Tropics. Climatic Change 70: 31-72. Yavari, A., and S. M. Shahgolzar. 2010. Floristic Study of Khan-Gormaz Protected Area Stafford Smith, D.M. 1996. Management of in Hamadan Province, Iran. Intel J. Agr. Biol. Rangelands: Paradigms and Their Limits. In: 12:271-275. The Ecology and Management of Grazing Systems (eds. Hodgson, J., and A. W.Illis). Zarrei, M., P. Wilkin, M. Ingrouille, and CAB, Wallingford, UK. 325-375. M.W. Chase. 2010. Gagea calcicola (Liliaceae), a New Species from Southwestern Iran. Kew Theurillat, J.P., and A. Guisan, 2001. Potential Bulletin 65: 89-96. Impacts of Climate Change on Vegetation in the