Academia.eduAcademia.edu
Kurdistan Region – Iraq Ministry of Higher Education and Scientific Research Salahaddin University – Erbil Plant Composition and Adaptation of Crested Wheatgrass (Agropyron cristatum L.) in Some Locations of Erbil Governorate A Thesis Submitted to the Council of the College of Agriculture - Salahaddin University - Erbil in Partial Fulfillment of the Requirements for the Degree of Master in Forestry Science – Range Management By Mohanad Eyoob Mustafa B.Sc. Plant Production - College of Agriculture-Salahaddin University - 2007 Supervised by Asst. Prof. Salim S. Maroof February. 2015 A.D. Jamady Al-Ula 1436 Al-H. Rashame 2714 K. ‫ك ْاَْ ْعلَى ۞ الَ ِ‬ ‫س َوى ۞ َوالَ ِذي قَ َد َر فَ َه َدى‬ ‫ف‬ ‫ق‬ ‫ل‬ ‫خ‬ ‫ي‬ ‫ذ‬ ‫َ‬ ‫َ‬ ‫اس َم َربِّ َ‬ ‫َ‬ ‫َ‬ ‫) َسبِّ ِح ْ‬ ‫َ‬ ‫۞‬ ‫ِ‬ ‫َح َوى ۞(‬ ‫َوالَذي أَ ْخ َر َج ال َْم ْر َعى ۞ فَ َج َعلَهُ غُثَاء أ ْ‬ ‫(س ورة اْعلى‪:‬‬ ‫ايه ‪)5-1‬‬ SUPERVISOR CERTIFICATION I certify that this thesis was prepared under my supervision at the Department of Forestry and Horticulture, College of Agriculture, University of Salahaddin-Erbil, as a partial fulfillment of the requirements for the Degree of M.Sc. in Forestry (Range Management). Signature: Supervisor: Asst. Prof. Mr. Salim Sabir Maroof Date: 24 / 11 / 2014 -------------------------------------------------------------------------------------Head of the Department of Forestry and Horticulture In view of the available recommendations, I forward this thesis for debate by the Examining Committee. Signature: Name: Asst. Prof. Mr. Nashat Maulood Abdulrahman Head of the Forestry and Horticulture Department Date: 24 / 11 / 2014 I II Acknowledgements By the name of Allah, First of all, I want to express my gratitude and thanks to Almighty and Merciful allah for providing me with the capability to compelete successfully this work, with blessing and pease upon Prophet Mohammad. I would like to express my sincere gratitude to the my supervisor Asst. Prof.Salim Sabir Maroof for the supervision, guidance, assistance, encouragement throught complilation of this thesis. Thanks to the Dean of the Agriculture College (Prof. Dr. Sardar Yaseen Sardari) and Head of the Forestry and Horticulture Department (Assist Prof. Mr. Nashat Maulood) for facilities and support that they offered to me. I would like to express my thanks to every member, espasially to Prof. Dr. Akram O. Esmail, Prof. Dr. Jawher S. Fatah, Dr. Sami M. Amin, Mr. Ali Hussen, Mr. Dler A. Othman, Mr.Mohammed A. Anter, Mr.Soran S. Aziz, Mrs. Narin S. Ali, Mr. Hawar A. Sidik, Mr. Beston H. Ahmad, Mr. Hardy. K. Awla and Mr. Arshad Yasin. I am very gratiful to Dr. Abdullah S. Sardar (college of education) and Mr. Ali M. Galaley for helping me during the identification and classification of plant species. Finally, I am forever indebted to my amazing parents for their encouregment when it was most reqiured. Further, the permanent support of my wife and family members can never be thanked by words, I would also like to express my gratitude and thanks to the peaple who were behind my success in both social and acadimic life. Mohanad.. III My Dedication to:  Our beloved country.  Honest soul of my father and mother.  My dear and so respectable wife.  My lovely triple childrens(Meryam,Marwa,Mina).  My big brother, his wife and child(Aya).  My well beloved brothers with best regards.  Finally, those who tought me. IV Summary SUMMARY The study of plant composition was carried out during April and May (2014) to estimate plant distribution in identified points especially grasses which they were laying in the north east of Erbil between Harir to Haji Omeran. The areas was divided to eleven points with an interval spaced approximately (7-8) km. List quadrate method (m2) was used randomly to estimate the individual species of the areas. The data enable the complication of cover percentage, plant frequency and density within their relative and forage value. The results can be summarizing as: 1- The identified species of the area were belong to (30) families, (93) genus and (174) species. Legume cover (14) genus and (30) species. While grasses cover (12) genus and (39) species. 2- The average vegetation coverage in all locations was (71%). But bare soil, litter and rock cover was (8.93%), (11.136) and (9.20%) respectively. 3- The average of high, intermediated and low forage value was (50.11%), (39.39%) and (10.50%) respectively. 4- The average percentage of Fabaceae, Poaceae and other families in the studied area was (18.77), (21.74) and (59.49) respectively. Highest value of Fabaceae was (29.17)% in Choman and Poaceae was (33.33)% in Similan. 5- Hordeum murinum ssp. Glaucum and Hordeum bulbosum L. were the indicated the highest relative density (5.02%) and (4.16%) of total species, on the other hand, Alcea kurdica Alef, Linaria vulgaris and Colchicum autumnale L. showed the lowest relative density (0.02%) overall species. 6- Hordeum bulbosum L. showed the highest relative frequency (2.42%) and then followed by Notobasis syriaca (2.08%) and Lactuca serriola (1.73%). Whereas, Erodium trichomanifolium, Galium murale, and Anemon coronaria were showed the lowest percentage (0.0035%) overall species. Whereas the study adaptation of crested wheatgrass (Agropyron cristatum L.) was carried out in Choman and Soran locations in two seasons fall and spring which they are located in forest zone of Iraq. The experiment started in November until May 2014. Shoot and root characters and chemical analysis of the species were conducted. Random V Summary complete block design (RCBD) was used for eight plots for each location four replication for fall season and other for spring season. The study was covered germination percentage, weed ratio and growth parameters such as shoot and root weight (fresh and dry), shoot and root length with their ratio, and chemical analysis such as dry matter, crude protein, crude fiber, crude lipid and nitrogen free extract (NFE). The results can be summarized as mentioned bellow: 1- Soran location was recorded the highest germination percentage (62.23%), while growth parameters were recorded high value in Choman and there were no significantly effect on the length of shoots and roots. 2- Spring season of seeding showed the highest germination percentage (71.30%), whereas, fall season was recorded the highest value in other growth characters and there were no effect on length of plant. 3- The interaction between locations and seasons indicated that Soran's spring season showed the highest value in germination percentage, while the highest value were recorded in fresh and dry weight of shoots and roots, while, and the length of shoots and roots were not affected in Choman's fall season. 4- The chemical analysis of crested wheatgrass was significantly difference in both locations and seasons. The highest value of dry matter was recorded in Choman's fall season (22.52%), and the highest ash value was recorded in Soran's spring season (24.74%). Nonetheless, the highest protein value was observed in soran's and Choman's fall season (16.28%) and (15.97%). Crud fiber was recorded the highest value in spring season of Choman and Soran location (17.68%) and (16.77%). On the other hand, crud lipid recorded the highest value in Soran's fall season but NFT recorded high value in spring season of Soran and Choman location (35.47%) and (35.50%)respectively. VI Contents Section Title Supervisor Certification Examination Committee Certification Acknowledgements Dedication Summery Contents List of tables List of figures List of appendix Page I II III IV V VII IX X X CHAPTER ONE 1. 1-2 INTRODUCTION CHAPTER TWO 2. 2.1. 2.2. 2.2.1. 2.2.2. 2.2.3. 2.2.4. 2.2.5. LITERATURE REVIEW Plant Composition Adaptation of Crested Wheatgrass Botanical Description Usage of species Adaptation of species Season of Seeding Chemical Analysis of species 3-19 3 11 11 13 15 16 18 CHAPTER THREE 3. 3.1. 3.1.1. 3.1.2. 3.1.3. 3.1.4. 3.1.5. 3.2. 3.2.1. 3.2.2. 3.2.2.1. MATERIALS AND METHODS Plant Composition Field work Coverage Percentage: Forage value Density and Relative Density Frequency and Relative Frequncy Adaptation of Crested Wheatgrass 3.2.2.2. Soran Selected specie Locations: Choman 20-34 20 23 23 23 24 25 26 26 26 26 26 VII 3.2.3. Seasons: 26 3.2.3.1. Fall Season Seeding 26 3.2.3.2. Spring Season Seeding 26 3.2.4. 3.2.5. 3.2.6. 3.2.6.1. 3.2.6.2. 3.2.6.3. 3.2.6.4. 3.2.6.5. 3.2.6.6. 3.2.6.7. 3.2.6.8. 3.2.6.9. 3.2.6. 3.2.6.1. 3.2.6.2. 3.2.6.3. 3.2.6.4. 3.2.6.5. 3.2.6.6. Soil Analysis Experiment Design Measurements: Germination Percentage 27 28 31 31 31 31 31 31 31 31 32 32 32 32 33 33 33 34 34 Shoot and Root Fresh Weight Shoot and Root Dry Weight Shoot Length Root Length Shoot Root Ratio Germination Speed Shoot Elongation Speed Root Elongation Speed Chemical Analysis: Dry Matter Crud Protein Crud Lipid Crud Fiber Ash Content Nitrogen Free- Extract CHAPTER FOUR 4. 4.1. 4.1.1. 4.1.2. 4.1.3. 4.1.4. 4.1.5. 4.2. 4.2.1. 4.2.1.1. 4.2.1.2. 4.2.1.3. 4.2.2. RESULTS AND DISCUSSIONS Plant Composition Cover Percentage Forage Value Plant structure Density and Relative Density Frequency and Relative Frequency Adaptation of Crested Wheatgrass Measurements: Effect of Location Effect of Season Interaction Effect Chemical Analysis: VIII 35-54 35 36 38 39 40 41 46 46 46 48 50 52 4.2.2.1. 4.2.2.2. 4.2.2.3. Effect of Location 52 52 53 Effect of Season Interaction Effect CHAPTER FIVE 5. 5.1. 5.2. CONCLUSION AND RECOMMENDATION CONCLUSION RECOMMENDATION REFERENCES APPENDIX ARABIC SUMMARY KURDISH SUMMARY 55-56 55 56 57 65-76 ‫ب‬-‫أ‬ A-B List of Tables No. 1 2 3 4 5 6 7 8 9 10 11 12 13 Titles Location, Elevation, Coordination and Average Raining of the studied area. Metrological data at Choman and Soran locations during the period (2013/2014). Soil analysis of studied area. List of weeds germinated at plots of Choman and Soran locations. Coverage percentage overall studied area. Forage value of species overall loc ations. Percentage of Fabaceae, Poaceae and Other Families in studied area. Relative Frequency and Density of plant species. Interaction Effect of locations and seasons on germination percentage and other growth characters on Crested Wheatgrass. Germination and length elongation speed. Effect of location on chemical analysis (%) of Crested Wheatgrass. Effect of season on chemical analysis (%) of Crested Wheatgrass. Interaction Effects of location and season on Chemical analysis (%) of Crested Wheatgrass. IX Page 21 27 27 30 36 38 40 41 51 51 52 53 54 List of Figures No. Titles Page 1 2 3 4 Map of Iraq/Erbil, locations of studied area. Field Design of Crested Wheatgrass. Effect of Location on germination percentage. Effect of Locations on Shoot and Root weight at Fresh and Dry Conditions. Effect of locations on shoot and root length. Effect of seasons on germination percentage. Effect of seasons on shoot and root length. Effect of seasons on shoot and root weights in fresh and dry condition. 22 25 47 5 6 7 8 47 47 49 49 49 Appendices No. 1 2 3 4 5 6 7 8 9 10 Titles All plant species of studied area with their Life cycle, Plant density and Forage value. Parts of Crested Wheatgrass (Agropyron cristatum L.) General Agro-Ecological Zones (AEZ) of Iraq. Plant distribution of studied area. Seeding of Crested Wheatgrass in Soran. Growth of Crested Wheatgrass in Choman. Spring season germination of Crested Wheatgrass in Soran. Growing of Crested Wheatgrass in fall season. Samples of Crested Wheatgrass. Chemical analysis of Crested Wheatgrass. X Page 65 71 71 73 74 74 75 75 76 76 Chapter One Introduction 1. INTRODUCTION Rangeland defined as a „‟uncultivated land that will provide the necessities of life for grazing and browsing animals and the herders families that depend on them‟‟. Therefore it includes deserts, forests, natural grassland and shrublands. Rangeland has a key role as grazing lands in pastoral use, as wildlife habitat and as biosphere reserves. Appropriates management is essential for all this uses if we are too prevent degradation of the resources that provides the base for all the activities that occur now on rangelands or may occur in the futures (Squires, 2009). Currently, in the rangeland management science and determination of range capacity, accurate and true information about range production is crucial. In fact, range production is considered as a basis for range management (Pourbabaei et al., 2012). Importance of forest and natural Pasture are protection, biodiversity conservation and impact on livestock development as a first source which supports animals feed. Rangeland Provides a large possibilities to increase the number of animals and animal products such as meat, wool and skins. Grasses could distinguish from other crops by which they are not harvested by hand but returned by churning of the animal(Williams et al., 1968). Four vegetation zones are recognized in Iraq: the desert, the steppe, the mountain forest, and the Alpine regions (Omer, 2011). Natural pasture in Iraq consists 46% of country‟s total areas (Rathwan and Fahri, 1975). Generally natural pasture in the Kurdistan distributed in different region including lowland, scrubland and higher mountain. Rangeland of Kurdistan region was estimated to be (4,762,609 dunam) in 2013 and is approximately (140,399 dunam) in Erbil (Ministry of Agriculture and Water Resource, 2013). 1 Chapter One Introduction Kurdistan is a rich region with rangeland if it is exploited scientifically and it is also significant economically in livestock development and animal production which play fundamental role in increasing national economy, much of the cropland is losing its inherent productivity due to poor agricultural practices and over exploitation(Omer, 2011). In last two decades, rangeland misused and exposed to degradation and damage due to several factors including internal and external. These are involved natural and others human entered factors. Natural factors including drought which lead to land deterioration, level of groundwater and vegetation coverage. The humans entered factors such as fire, overgrazing and continuous indiscriminate cutting trees and shrubs for fuel, exploiting grazing areas to Agricultural/Horticulture purposes (Gebril and Saeid, 2012). To improve and maintain the degraded rangeland new forage species must interred to country such as crested wheatgrass which have been interred to various region of the world because it a perennial monocot grass that belong to Poaceae family, the plant can be grown in the cool season, drought tolerant, can stand extreme condition and high forage value (Kirk et al., 1934) Because of above problems the following studies have been studied: 1. Plant composition from areas between Harir to Haji Omeran The overall aim of this part is to identify the distribution of natural vegetation and all other basic information about rangeland resources in the area. Particularly, botanical composition and productivity of natural rangeland are also studied. 2. Adaptation of an exported species crested wheatgrass (Agropyron cristatum (L).Gaertn) The purpose of this part is to find out the potentiality of adapting the crested wheatgrass in two different environments of the Erbil governorate (Choman and Soran) and under two different seasons (Fall andSpring). 2 Chapter Two Literature Review 2. LITERATURE REVIEW 2.1. Plant Composition The study of plant composition is conducted on natural range, it is desirable to determine herbage species, their frequency and forage quality. Such information furnishes a basic research for many studies on palatability, stoking rate, utilization and duration of grazing, improvement or degeneration of range, effect on climate and watershed management (Maroof, 1978). Several survey studies have been conducted in Iraq, involving evaluation and estimation of the rangeland productivity and nutrient value of some important species, while other studies focused on factors affecting nutrient value and productivity of range (Besefky, 2011). The extensive works of Gillett (1948), Springfield (1954), Guest and AlRawi (1966) constitute valuable contribution to the vegetation survey, in these complete descriptions of grass species found in Iraq which are the most important studies in the 20th century. Buringh (1960) mentioned that as a consequence of the arid and semiarid climate, vegetation is scarce in large parts of Iraq. Forest vegetation mostly occurs in the Kurdish mountains due to geographical position. The flora of Iraq is of a heterogeneous phyto-geographical character and according to Zohary (1950) three principal plant geographical regions are represented in this country which are; Mediterranean region, Irano-Turanian region and Saharo-Sindian region. Holm et al., (2002) identified general Agro-Ecological Zones (AEZ) of Iraq in to three regions and each with a characteristic farming system (Appendix, 3) 3 Chapter Two Literature Review 1. Lowland AEZ: in the southern part of the region. Annual rainfall is between 250-600mm and topography is relatively flat between 300-600 m above sea level. 2. Upland AEZ: in the inter-mountain areas of the central part of the region, where annual rainfall varies between 500 and 900 mm. 3. Hill and Mountain AEZ: in the northern border areas with Turkey and Iran that characterized by steep landscapes and an annual rainfall between 800 and 1200 mm. Gillett (1948) has mentioned that oak forest of Kurdistan Mountains is a big source of valuable. Pasturage comprising of Avena sterilis, Poa bulbosa, Hordeum sp., Lolium rigidum, Bromus macrostachys and Phalaris paradoxa. Schwan (1954) during travelling to the Mountains of the Kurdistan region noted that the region had good vegetation in the spring season but it is often misleading in determining the value of vegetation. Springfield (1954) has cited that the forest zone of the Kurdistan region is rich with grazing species which is most of them belong to Poacea, Fabacea, Brassicaceae, Apiaceae, Asteraceae and others famillies. Such as; Poa bulbosa, Chysopogon gryllus, Phalaris paradoxa, Hordeum bulbosum, Lolium rigidum, Vicia sativa, Trifolium procumbens, Vicia tenufolia, Vicia narbonensis, Rigidula medicago, Lathyrus cicera, Brassica arvensis, those species indicate to a certain extent of zone for grazing. Guest (1966) revealed that forest zone of Irano-Anatolian sub-region had extra ordinarily richness in endemics, more active from other region in the formation and germination of variety species. Townsend and guest (1968) have recorded habited and introduced grasses in Iraq which was found in mountain region with useful fodder comprising of Lolium perenne, Dactylis glomerata, Poa bulbosa. Al-Tikriti and Abdullah (1969) mentioned that the forest zone contain suitable forages like Agropyron elongatum, Avena clauda, Hordume bulbosa. 4 Chapter Two Literature Review Yousif (1971) have concluded that protecting from grazing for 3 years led to improve speacies and appear some high forage plants as Stipa barbata. FAO (1975) classified existing grass species into three groups according to their forage values:(I)-High forage value includes Lolium rigidum, Bromus arvensis. (II)-Intermediate forage value includes Daucus carota Gallium aparine, Ranunculus asiaticus and Senecio vulgaris. (III)-Low forage value includes Echinops ritro and Colchicum autumnale. Maroof (1978) studied forage value of grasses in the Dohuk governorate and recorded (17) families, (43) genus and (49) species in which the grasses compressing most of them as; Agropyron panormitanum, phalaris paradoxa, Hordeum marinum, Lolium loliaceum, Lathyrus gorgoni, Trifoluim campestre, Trigonella stellata, Anthemis hyaline and Centaurea solstitialis. Al-Kittany et al., (1978) have investigated the effect of fires on oak forest and vegetation covers of Zawita. As a result the fires have negative effect on grass family rather than legume family. Salihi (1980) studied vascular plants in Pira Macron mountain, as a result (543) species which are related to (68) families were found and most of them were grasses. Qassim (1981) made a study in the Kurdistan region in the Atrush region (33) families, (95) genus (107) species, but in the Zawita region (28) families, (77) genus and (86) species. While in the Sinjar region (24) families, (53) genus and (60) species from grasses and herbs have been found. Toma (1983) has adverted on the plants of Maklub Mountain as a result forage crop type of the Maklup mountain is favorable than the Gali bandaw mountain, that‟s because of environment difference especially in temperature and precipitation. Aani and Hadad (1986) have cited the ecology of plant biodiversity in Tikrit, (58) species have found and the vegetation of this region exposed to 5 Chapter Two Literature Review cruel environmental con ditions including turbidity and human interred factors. Ali (1988) studied vegetation composition in the Namrud and east and west region of Mosul boundary. The Namrud region recorded few families (25), (95) genus and (142) species. While east region of the Mosul boundary recorded high families (29), (108) genus and (164) species but in Western region of the Mosul boundary recorded high genus and species (28) families, (120) genus and (184) species. Tilman et al., (1996) prepared an experiment on the biodiversity effect on productivity and sustainability of grassland ecosystem. The result showed that ecosystem productivity increased significantly with increasing plant biodiversity. In nearby native grassland, plant productivity and soil nitrogen utilization increased with increasing plant species richness. Aziz (1999) inscribed on structure of plant biodiversity in the north east of Erbil governorate at Hanara area and verified (29) genus. In addition, some rare distributed plants in Iraq have been recorded. Such as Typha minima, Equisetum romossisimum and Agilopis columnaris. Bishay (2003) point out that Natural Forestry of Iraq reported to the Near East Forestry Commission in 1998, according to the report natural forests composed mainly with Quercus aegylops, Quercus infectoria and Quercus libani with some Acer sp., Ulmus sp., Juglans sp., Prunus sp., Crataegus azarolus, Pistacia vera, Juniperus sp., Pinus sp., and Populus sp. and riverine forests with Populus euphratica and Salix sp. Iraq wetlands are important region for many birds that migrated from northern and eastern Europe. Saeed (2003) studied flowering plants in the Kurdistan mountains in the Revanduz region and found that the region was rich with flowering plant especially herbs. (43) Families, (140) genus and (175) species has been recorded. 6 Chapter Two Literature Review Al-Obadee (2004) has concluded on four rangeland locations that ecologically different. The investigation was carried out to evaluate range plants qualitatively and quantitatively and preparing maps for rangeland of the Ninevah province by using satellite images and aerial photographs. The result indicated that the best month to delineation range sites in Badyet Al-jazeera and Sinjar Mountain were in April and May. Such speices are Avena sp., Hordium sp., Cynodon dactylon, Polypogon monspeliensis, Lolium rigidum, Poa sp., Filago spathulata, Lathyrus sp., Medicago sp., Onobrychis crist-gali, Trifolium sp., Vicia sp., Brassica arrvensis, Centaurea sp., Malva sp., Pisum sativa, Ranunculus asliaticus, Trigonella sp., and plantago sp. Al Pierson (2006) has concluded that major grasses present at upland and mountain are Agropyron sp., and Poa sp. Forbs observed include dandelion, thistles, and composites. Undoubtedly many other species appear as the spring green up occurs and new growth becomes more apparent. Most upland areas are extremely rocky and many areas are covered 40% or more by rocks. Gintzburger et al., (2006) have stated that the dominant vegetation of the rangelands of West Asia and the Near East are Poaceae are mainly represented by Bromus, Poa, Stipa, Agropyron, Aegylops, Hordeum, Avena, Lolium, Orysopsis, Hyparrehnia. Compositae with the common Artemisia herba-alba cover very large tracts of the Near Eastern steppe from Iraq, Iran and further East towards Middle Asia. Artemisia sp. is an essential summerautumn feed throughout the region. Other taxonomically complex genera Achillea, Cousinia, Echinops, Anthemis, Centaurea, Carthamus, Helichrisum, Inula, Senecio, Scorozonera, Gymnarhena, Gundelia, Koelpinia. Those are well represented on post-cultural areas. Fabaceae are mostly Mediterranean (Trifolium, 120 sp.; Trigonella, Annual Medicago, Vicia, Lotus, Lathyrus, Onobrychis, Hedysarum, Cicer, Lens). They are largely exploited and selected for feed and food production in Mediterranean agricultural systems and crop rotations. Some Astragalus sp. has been identified in the region. The 7 Chapter Two Literature Review richness of this genus may be related to its poor palatability and toxic record. Cruciferae are known mostly as annuals and common weeds but make little contribution to the forage calendar. Mahmoud (2007) studied the area from Erbil to Harir, the result showed that (22) families, (61) genus and (28) species has founded, Poaceae was the most founded families among others by (15) genus and (28) species like Aegilops triuncialis, Agropyron cristatum, Echinaria capitata, Lolium loliaceum, Lotus corniculatus, Alyssum meniocoides, Galium setaceum, Medicago rigidula, Pisum sativum, Centuarea solstitialis, Malva rotundifolia Galium setaceum, Bromus lancelatus. This guides that the region is rich with vegetation although there were more overgrazing and deterioration appeared in the area and it could be improved and developed. Ganjo (2008) has noted on land section of Deraluk region in the Dohuk governorate. Typha sp. and Salix alba shrubs with grass lands are features of this landscape which forms a distinct bioregion. Rural and cattle grazing are the predominant settlement land uses there. No industrial, mining and commercial activities detected there and the stratification of plant community structure on the area which composed by grasses (55%), herbs (20%), shrubs (15%) and trees (10%). Such as Prunus amygdalis, Lolium sp., Avena sp., Bromus sp., Aegilops sp., Vicia sp., Lathyrus sp., Trifolium sp., Madicago sp. and Phalaris sp. Ates and Tekeli (2011) have mentioned that aspect, slop and altitude are three basic topographic factors that control the distribution and botanic composition of rangelands and other vegetation‟s types. Lahony et al., (2013) stated on the Hawraman lowest zone and found that the area shows unique since it characterizes the Irano-Tranian and Alpine zone extension reaching the Iraqi territories with rather rich fauna and flora. Such as Papaver rhoeas, Iris sp., Vicia villosa, Vicia variabillis, Trifolium 8 Chapter Two Literature Review purpurcum, Trifolium fragiferum, Geranim tuberosum, Alcea kurdic, Hordeum sp., Vulpia sp., and Bromus sp. Saeed (2013) made a survey for the species of Centaurium Hill (Gentianaceae) in the Kurdistan region to identify the samples preserved in some Iraqi herbaria and to add a small part to the Flora of Iraq. The study dealt with the ecology and geographical distribution of the species. As a result two species Centaurium erythraea subsp. turcicum and Centaurium pulchellum were found. Saeed (2013) made a systematic study of gross morphology of plants – which collected during field trips and dry ones for most specimen preserved with Iraqi herbaria which is the genus Ferulago Koch belong to the Umbelliferae family. The genus in Kurdistan region of Iraq was specified in two species Ferulago angulata and Ferulago stellate. Characteristics of a taxonomic value, ecology and soil quality that the genus grows were specified. Abdulhasan et al., (2009) citied on vegetation survey in some region of Kurdistan as: 1- In the Bahrka which located on the Greater Zab River, approximately 33 km to the northwest of Erbil city. The area is composed of steppes and highlands. The land is mostly used for agriculture. During the surveys (55) plant species was recorded such plants Portulaca oleracea, Datura stramonium (herbs) and Phragmites australis (grass) and the nonvegetated cover was about 40-50%. 2- In the Haji Omran on northeast of Erbil city about 2 km from the Iranian border. The area is characterized by hills, streams and meadows. This site contains about (160) plant species. The dominant plants were Astragalus spp, Geranium tuberosum, Rumex hastatula. 3- In the Sakran mountain northeast of Erbil city near the Choman town. The mountain peaks are covered with snow. This region includes high number 9 Chapter Two Literature Review of plant species about (146). Pistacia eurycarpa, Crataegus azorolus, Pyrus syriaca, Prunus microcarpa, Anagyris foetida, Galium sp., Populus alba and Salix sp. in Mountain Forest zone and Cousinia sp., Prangos pabularia, Rumex ribes, Daphne mucronata, Alkanna kotschyana, Ferulago angulata and Biebersteinia multifida in sub alpine area .This area has been locally proposed for consideration as a National Park. 4- In Sari Hassan Bag that located in northeast of the Soran town. (20) species were identified in this area. One waypoint was surveyed in the area which is characterized by Astragalus sp., Acantholimon sp. and Hyoscyamus reticulatus. Ferulago angulata is also characteristic of this habitat type. 5- In the Halgurd Mountain which located in North West of Haji Omran town. The surveys identified (50) plant species Astragalus helgurdensis, Ferulago angulate, Cousinia sp., Rumex hastatula, and Smyrnium cordifolium in Mountain Forest Vegetation zone and Arabis caucasica and Ornithogalum lushanii in Alpine Vegetation zone. 6- In the Doli Smaquli & Ashab that located in northeast of the city of Erbil near Shaqlawa District. This site includes a high number of plant species about (120). Such as Aegilops spp., Poa bulbosa, Lolium temulentum, Scabiosa palaestina, Cousinia sp., Salvia palaestina, Astragalus sp. The site is located in the Zagros mountain range. The non-vegetated area covered about (5%). Livestock production/grazing, tourism and changes to degradation land as a result of agricultural expansion and housing construction remain high threats. High vegetation cover and many important plant species make this region one of the most important plant areas in the Kurdistan region. 10 Chapter Two Literature Review 2.2. Adaptation of crested wheatgrass Selection of a certain grass for planting in a specific area is one of the major considerations in re-seeding rangeland artificially (Maroof, 1978). 2.2.1. Botanical Description Wolfe and Kipps (1953) have concluded that crested wheatgrass is hardy perennial bunch grasses that produces abundance of both basal and stem leaves and has a wide-spreading, deep root system. The stems are fine and develop dense tufts. The dense spikes are 2 to 3 inches long; the spikelets are closely crowded and tend to form comb like crescents. Crested wheatgrass thought to be one of the largest genuses in the tribe Triticeae Dumortier, they are more than 100 species (Dewey, 1983). Regnum – Plantae Divisio - Tracheophyta Subdivisio - Spermatophytina Class - Magnoliopsida Superordo - Lilianae Ordo - Poales Familia - Poaceae Tribus - Triticeae Dumort. Genus - Agropyron Gaertn. Species - Agropyron cristatum (L.) Gaertn. Johnson (1986) has mentioned that crested wheatgrass is composed of several cool-seasons, taxonomically identified as Agropyron cristatum. It was successfully introduced into North America in 1906 from Eurasia. 11 Chapter Two Literature Review Crested wheatgrass is a deep-rooted bunch grass which is tolerant of the moisture stress and the low winter temperatures common in the brown and dark brown soil zone. It adapted to the most soil textures, the standard type is more tolerant of drought, but the Fairway type is better adapted to moist conditions. Crested wheatgrass is not well adapted to saline soils and spring flooding. Seed yields are more consistent in regions receiving 350-500 mm of annual precipitation. Under dry conditions, seed head formation may be inadequate to justify harvest of the seed (Kruger and Council,1998). USDA (2004) repored that Crested wheatgrass is a perennial bunchgrass, without rhizomes, resistant to fire, drought, cold temperatures, and heavy grazing, growing to a height of 45.72 to 76.2 centimeter. It's a dense spikelet, with a conspicuously flattened head, 3.81 to 7.62 centimeter long, tapering toward the tip; spikelet numerous, overlapping and placed flat-wise on the rachis, contain 4 to 8 florets per spikelet; glumes about half the length of the spikelet; both the glumes and lemmas usually taper to a point or into a short awn. Leaf blades flat, vary in fineness with the vigor of the plant, usually glabrous; sheaths glabrous or pubescent on lower leaves; leaves rolled in the bud; ligules short and membranous; auricles short, pointed and clasping the stem. Due to commonly being planted in monocultures (single species) stands in the past, some feel crested wheatgrasses are not ecologically appropriate. It is important to consider multiple species mixes to avoid this conception (Appendix, 2). 12 Chapter Two Literature Review 2.2.2. Usage of species Wolfe and Kipps (1953) have stated that crested wheatgrass is used both as pasture and hay. Its forage is very palatable and of good quality, it should be cut for hay soon after it comes into head and before it blooms. Early-cut hay is higher in protein and more palatable than late-cut hay it produces good seed crops, except during the drought period. Crested wheatgrass is highly palatable and a nutritious spring forage. It can be especially useful to ranchers, where spring forage shortages are common (Johnson, 1986). Crested wheatgrass tends to become fibrous at maturity, and therefore palatability and nutritional quality of the plant decline after June (Mayland et al., 1992). Crested wheatgrass provides little summer grazing, in some habitat types with sufficient soil moisture; it can continue to grow in fall after summer dormancy (Bakker et al., 1997). Sheet and Page (2001) have noted that crested wheat grass is commonly recommended for forage production. It is palatable to all classes for livestock and wildlife and it is desirable feed in spring and fall if it re-grows enough. It can withstand very heavy grazing pressure (65%) use and greater (Cook et al., 1958) (Caldwell et al., 1981). The best forage types in order are Hycrest. Crested wheat grasses are beneficial for soil stabilization. They have potential to compete with other aggressive introduced grasses. Although, they are not compatible, while, it mixes with native species. Moreover, for reducing competition by using only livestock may be insufficient to permit establishment of desirable seeded species. In general, high levels of utilization by livestock during the growing season reduces the vigor of crested wheatgrass and may leads to mortality of some, but not all 13 Chapter Two Literature Review plants (Wilson and Pärtel, 2003). Early summer grazing may be detrimental to crested wheat grass due to lower carbohydrate (Pellant et al., 2005). Conner (2008) has mentioned that scientist have carried out an agricultural experiment on the crested wheat grass. They realized the plant was useful for grazing and particular valuable because it could grows in drought conditions with little or no care and would continue to produce high quality feed even after several years of heavy use. USDA (2012) has cited that crested wheatgrass provides some of the earliest spring grazing, starting its growth in early April. It is used quite extensively as a drought-tolerant in the early-season of grass pasture. Crested wheat grass is usually seeded alone to provide early spring and late fall grazing. It is used widely in drier climates which can be used for hay production and will make nutritious feed, but is more suited to pasture use. Light, infrequent applications of nitrogen (4.6 kg/ha) and appropriate irrigation will increase total biomass production and lengthen the green period. Grant-Hoffman et al., (2012) has concluded that areas planted with crested wheatgrass can be less favorable for native plants. While crested wheatgrass does not spread as readily as some other expansive species. One reason for the continued use of crested wheat grass in the western U.S. is the ability of crested wheatgrass to compete with other more detrimental invasive plants, most notably Bromus tectorum. In addition, there have been reports of early success with planting native species into areas with crested wheatgrass present, a process known as „assisted succession‟. 14 Chapter Two Literature Review 2.2.3. Adaptation of species Wolf and Kipps (1950) have revealed that crested wheatgrass was introduced into the United States in 1898 from Russian Turkistan and Second introduction was made from the same place in 1906. It‟s a good grass-more valuable perhaps than all other range-forage species. Al-Rawi (1964) has revealed that crested wheatgrass arises at the forest zone of Kurdistan mountains exactly in Rawanduz district. Guest (1966) as mentioned in flora of Iraq that crested wheatgrass is occurs in Iraq over the frontier and should be looked in the mountains; in another place on stony slopes, often on calcareous soil. Turkey, Caucasus, Iran etc. Introduced in to North America (Canada, USA) and other part of Europa like; Britain, Spain. Dewey and Asay (1975) have reported that crested wheatgrass is indigenous to central Asia, including parts of the USSR, China, Afghanistan, Turkey and Iran. These grasses have come into wide usage arid rangland in the United States and Canada. Most crested wheatgrass introduction have come from the USSR (Union of Soviet Socialist Republics). USDA plant inventory recorded from 1898 to 1971 showed 175 introductions from the USSR, 50 from China and Manchuria, 29 from turkey and 17 from Iran virtually all plants breeding has been centered on USSR-derived collection. Latitudes where crested wheatgrass grows in Iran, 35 to 40 are equivalent to northern Arizona and come from latitudes north of 40, and crested wheatgrass has found its greatest adaptation in North American. Gokkus et al., (1997) has carried out a study on the effect of climate on the morphological, agronomical and chemical properties of crested 15 Chapter Two Literature Review wheatgrass, and has reported that crested wheatgrass is one of the most adaptive forage crops in eastern Anatolian region and it has an excessive ability to re-form the degraded land. USAD (2004) stated that crested wheatgrass is adapted to areas where annual precipitation averages 10 inches and where the frost free period is generally less than 140 days, It does well up to 9,000 feet elevation. Crested wheatgrass grows on shallow to deep, moderately course to fine textured, moderately well to well drained and weakly acidic to moderately alkaline soils. Under saline conditions, vigor and production are reduced. It is not well adapted to salty soils. All crested wheatgrasses are cold tolerant, can withstand moderate periodic flooding in the spring, and are very tolerant of fire. They will not tolerate long periods of inundation, poorly drained soils or excessive irrigation. USDA (2008) reported that Crested wheatgrass is well adapted to stabilization of disturbed soils. Their drought tolerance, fibrous root systems, and good seedling vigor make these species ideal for reclamation in areas receiving 8 to 16 inches annual precipitation. 2.2.4. Season of seeding Crested wheatgrass usually starts growth in the early spring. It stops growing during long, hot, dry period of summer, but it again makes growth when the weather becomes moist and cools (Wolfe and Kipps, 1953). Currie and Peterson (1966) have declared that forage available for use by livestock varies with the season in which ranges are used. Rainfall in April determined forage yields of ranges grazed in the spring; May and July rainfall 16 Chapter Two Literature Review determined forage yields for fall-grazed ranges. Expected forage yields and stocking rates can therefore be predicted from precipitation measurements. Holl et al., (1988) cited that crested wheatgrass is an important dry land grass. It germinates under a wide range of conditions, has strong seedling vigor and successfully establishes under challenging conditions. It is best adapted to heavier soils of good fertility, with early growth in spring ahead of most other native or introduced grasses. It becomes dormant during hot and dry summer months, but growth resumes when moisture is sufficient. It is completely winter hardy across the plains and is long-lived, persistent and easily endures adverse management and heavy grazing pressure. The ability to germinate and grow rapidly during the early spring season is critical if a seedling is to successfully compete with annual weeds. Crested Wheatgrass is a highly competitive species and where it is well adapted, may become the dominant species of the re-vegetated area. Sheet and Page (2001) have reported that crested wheatgrass start to growth in early spring and flower in late spring. It reproduces from seeds and tillers. It may regrow in the fall if moisture is sufficient. Crested wheat grass germinates earlier and grows more rapidly at colder temperatures. This is an important competitive advantage when dealing with winter annual species such as cheatgrass. The best seeding results are obtained from seeding in very early spring on heavy to medium textured soils and in late fall on medium to light textured soils. Late summer (August to mid-September) seeding is not recommended unless irrigation is available. It is not very tolerant of spring flooding. 17 Chapter Two Literature Review 2.2.5. Chemical Analysis of species Cook (1959) has studied on the effect of site on the palatability and nutritive content of seeded wheatgrasses (Crested wheatgrass, Intermediate wheatgrass and Tall wheatgrass). It has been reported that all wheatgrass suffered about the same loss on unfavorable site and the palatability of all wheatgrass was significantly greater on all unfavorable sites when compared to favorable sites. Buman et al., (1988) investigated a study on seedling competition between mountain rye, crested wheatgrass, and downy brome. Soil moisture depletion was monitored gravimetrically. Dry root and shoot weight, shoot area and root length of mountain rye was greater than that of both Downy Brome and Hycrest crested wheatgrass at every sampling period over the 6week. The results indicated that mountain rye provide vigorous competition as seedling. Gökkuş and Ali (1996) investigate the effect of seasonal (fall and spring) of nitrogen application on the growth of crested wheatgrass. Nitrogen application in both fall and spring increased shoot and root weight but decreased the root/shoot ratio. The fall application of nitrogen did not affect stem and leaf rates but the spring application decreased the stem rate and increased the leaf rate. Taghizadeh et al., (2009) carried out a study on investigation of genetic diversity in crested wheatgrass. Random Amplified Polymorphic DNA (RAPD) markers have been used to characterize the genetic diversity of 10 Iranian populations of crested wheatgrass (Agropyron cristatum). RAPD marker data proved to be a good method of assessing genetic variation among populations of crested wheatgrass. 18 Chapter Two Literature Review USDA (2012) has reported that the quality and quantity of the crested wheatgrass forage is usually increased when planted with a legume, such as alfalfa. Forage quality is very good in early growing season with crude protein levels approximately 18 percent age. Crude protein levels fall to around 4 percentages during the summer when plants are dormant. It provides excellent feed for cattle, sheep, and horses in the spring. Elk, deer, and antelope utilize the forage early and late in the growing season. The seed is used by birds and rodents, and stands provide nesting cover for upland birds. 19 Chapter Three Materials and Methods 3. MATERIALS AND METHODS 3.1. Plant Composition The study of plant composition was carried out during spring 2014 from 15th April to 7th May between Harir and Haji Omeran areas figure (1) with approximately distance of 100 km which located among 11 sites (table, 1) to identify and count the type of species in the area. The study area was mountainous natural rangeland and contains forests which are rich with many species. Random sampling methods were used for vegetation analysis (Rathwan and fahri, 1975) (Sorrells and Glenn, 1991). General visual survey method was used for identification the quantitative characters of vegetation sample that depends on individual‟s theoretical estimation (Sankri, 1996). The climate of area related to Sub-humid upland and mountain region which have an average annual rainfall (400mm -1100 mm) and the temperatures are slightly milder in summer and lower in winter than in Erbil (Omer, 2011). 20 Chapter Three Materials and Methods Table (1): Location, Elevation, Coordination and Average Rainfall of the studied area (Razvanchy, 2014). No Location Distance from Erbil Elevation (m) Coordination Latitude (N) Longitude (E) (km) Average Rainfall (mm) 1 Harir 75 700 36°33' 9.61" N 44°22'45.96"E 600 2 Spilk 84 843 36°36'58.18"N 44°19'18.47"E 610 3 Kalakin 93 846 36°36'59.86"N 44°20'27.83"E 628 4 Zargaly 99 839 36°23'55.29"N 44°58'20.81"E 650 5 Soran 115 680 36°39'16.96"N 44°32'15.87"E <650 6 Smilan 125 731 36°31'26.99"N 43°53'51.29"E 700 7 Omerawa 134 877 36°35'24.26"N 44°48'3.60"E < 700 8 Choman 150.5 1110 36°38'15.87"N 44°53'21.12"E 778 9 Derband 159 1340 36°41'12.23"N 44°55'28.68"E 823 10 Azadi 166 1693 36°44'32.82"N 44°28'9.68"E 930 175 1988 36°40'30.15"N 45° 2'43.25"E <1000 Haji11 Omeran 21 Chapter Three Materials and Methods Figure (1): Map of Iraq/ Erbil, locations of studied area. 22 Chapter Three 3.1. Materials and Methods Field work A quadrate which is comprised from (m2) is thrown randomly in each location according to FAO (1975). Data of the variables were recorded. 3.1.1. Coverage Percentage: A. Vegetation Coverage: total species were estimated in the sample. B. Bare Soil. C. Rock: when the rock percentage of a unit area ≥ (15 %) it means the area is suffering from degradation (Fahri, 2009). D. Litter: is the area of ground covered by the vertical projection of the outermost perimeter of the natural spread of plant foliage (Sheley et al., 2008). Plant samples were collected manually by sickle. Each sample wrapped by a paper and placed between wood panels in order to maintain the quality of samples. Afterwards, the samples placed on a paper board in the laboratory for: 1- Segregate each species of the sample according to their units 2- Notation individuals of each species for calculating total individual. 3- Specimens of species were made for identification the species according to their families, genus and species in biological herbaceous of Education College/ Salahaddin University. In addition to help of other experience lecturers in this field. 3.1.2. Forage Value Forage value is the classification of plants depending on their grazing intensity and palatability (Al-Obade, 2004). The plants were classified as follows: I- High forage value: it includes the species that all parts can be grazed in all seasons such as Trifollum sp., Medicago sp., Bromus sp. 23 Chapter Three II- Materials and Methods Intermediate forage value: this includes the species which is partially grazed in a season. Such as Notobasis syriaca, Brassica nigra, Plantago lanceolata. III- Low forage value: includes the species which is not used by animals in any season. Such as Euphorbia cheiradenia, Marrubium vulgare and Papaver hybridum. 3.1.3. Density and Relative Density Total density is the number of individuals per unit area (m2). All species and their individuals were recorded in order to calculate the density of each species in the area (Besefky, 2011). . Number of individuals of specific species in all samples Species density = Total number of samples Relative density = density of specific species / sum of all species' density X100. According to (FAO, 1975) plant density degree arranged as follows: Plant individuals per (m2) 1 Density degree Very Rare Symbols VR 2-4 Rare R 5-14 Infrequent I 15-29 Frequent F 30-99 Abundant A More than 100 Very Abundant VA 24 Chapter Three 3.1.4. Materials and Methods Frequency and Relative Frequency Number of sample containing specific species divided by total number of samples observed (Besefky, 2011). 25 Chapter Three Materials and Methods 3.2. Adaptation of Crested Wheatgrass 3.2.1. Selected species A certified seed crested wheatgrass (Agropyron critatum (L.) Gaert) imported from USA during fall 2013. 3.2.2. Locations: 3.2.2.1. Choman It is located in the northeast of Erbil governorate about (160) km figure (1). The majority of lands is severe ruggedness mountain and bordered to the north east by Hasaarost Mountain. It‟s geographical coordinate (36°39'33") north and (44°42'11") east. Its elevation is (1110m) above sea level with average precipitations in last ten years is (512 mm), and the temperatures (4.570C). 3.2.2.2. Soran It is located in the northeast of Erbil governorate about (115 km) with latitude (36°36'23.18"N) and longitude (44°39'2.56"E), and its elevation is (680 m) above sea level. The other name of Soran is Diana. Average precipitations is (476mm) and temperatures is (7.320C) in last ten years. 3.2.3. Seasons: 3.2.3.1. Fall Season Seeding The study season was started in 16th November, 2013 by depending on first raining at fall season. 3.2.3.1. Spring Season Seeding The study season was started in 21st March, 2014. 26 Chapter Three Materials and Methods Table (2): Metrological data at Soran and Choman locations during the period 2013/2014 (Agro Meteorological Center, 2014). Soran Choman Months Raining Snow Average Raining Snow Average volume volume temperature volume volume temperature (mm) (cm) (0C) (mm) (cm) (0C) November 73.9 0 14.4 117.1 0 6.1 December 106.9 0 5.3 116.4 0 0.4 January 105.8 15 4.2 92.7 27 -3.5 February 13.3 0 8.2 12.5 0 -1.5 March 135.8 0 11.3 182.4 0 4.5 April 25.1 0 16.7 43.1 0 10.5 May 13.9 0 21.5 17 0 15.5 TOTAL 474.7 15 581.2 27 * Humidity data was necessary for experiment but it was not available. 3.2.4. Soil analysis Soil sample of both locations were taken randomly from (30cm) depth to analyse some mechanical and chemical characteristics of soil. Analyses have been done according to Rowell (1996), in Agriculture Research Center/Ministry of Agriculture –Erbil (table, 7). Table (3): Soil analysis of studied area. EC PH N P K ds/m 1:1 % ppm ppm Soran 0.3 7.85 0.1 3.4 Choman 0.1 7.8 0.04 3 Location SOIL TEXTURE USDA SOIL TEXTURE clay silt Sand 120 36.7 38.8 24.5 Clay Loam 80 39.2 48.3 12.5 Silty Clay Lom 27 Chapter Three Materials and Methods 3.2.5. Experiment design The study was designed as Randomized Complete Block Design (RCBD) and each location were consists of 8 plots (4 plots for fall and 4 plots for spring season). The size of plot was 2m long and 1.5m wide with a guard stripe of 0.25m between the plots. Every plot were contains seven rows, each of 2m length with 0.25m spacing between the consecutive rows(Figure, 2). The data were submitted to analyse of variance, means were compared by Duncan multiple range test (1955) at probability level of 0.05 for field and 0.01 for chemical analyse by using (SAS, 2005). The soil was ploughed precisely and leveled by plough tractor, after the design finished (7g) (El-Tekriti and Mohammad, 1982) of seeds were sown for each row then covered with fine soil. During the growth period of study, weeds were controlled by hand to provide more valuable condition for preserving soil‟s nutrient and moisture (table, 4). The seeding emergence was recorded after germination. In addition, other characters value were recorded for the plant such as fresh and dry weight of shoot and root and length of shoot and root within shoot root ratio. 28 Chapter Three Materials and Methods Figure (2): Field design of Crested Wheatgrass. 29 Chapter Three Materials and Methods Table (4): List of weeds which germinated at plots of Choman and Soran location. Weed Species Season Family Life Cycle Cyperus sp. Fall&Spring Cyperaceae Perennial Cynodon dactylon L. Fall Poaceae Perennial Hordeum bolbosum L. Spring Poaceae Perennial Convolvus arvensis L. Fall&Spring Convolvulaceae Perennial Bromus sp. Fall&Spring Poaceae Perennial Linum sp. Fall Linaceae. Perennial Pecris sp. Spring Zygophyllaceae Annual Tribulus terrestris L. Spring Zygophyllaceae Annual Heliotropium europiran L. Spring Boraginaceae Annual Xanthium strumarium L. Spring Asteraceae Annual Polygonum aviculare L. Fall&Spring Polygonaceae Annual Cardaria draba L. Spring Brassicaceae Annual Amaranthus deflexus L. Spring Amaranthaceae Annual Atriplex sp. Spring Amaranthaceae Annual Lactuca serriola L. Fall Asteraceae Biennial Portulaca oleracea L. Spring Portulacaceae Annual Plantago lanceolata L. Fall Plantaginaceae Annual Senecio sp. Fall Asteraceae Annual Brassica nigra L. Fall Brassicaceae Annual Echinops sp. Fall Asteraceae Annual 30 Chapter Three 3.2.6. Materials and Methods Measurements: 3.2.6.1. Germination percentage (%) The germination percentage was estimated in field according to (Ismail and Kardoush, 2011) as follows: 3.2.6.2. Shoot and Root fresh weight (g) The shoot and root fresh weight was measured by sensitive balance. 3.2.6.3. Shoot and Root dry weight (g) Shoot and root system was dried by oven until reach the constant weight at 70˚C (Baninasab and Mobli, 2008). 3.2.6.4. Shoot length (cm) Shoot length was measured from the contact point between the stem and the soil surface to the tip of the main stem (Shekhany, 2014). 3.2.6.5. Root Length(cm) Root length was measured from the contact point between the stem to the growing tip of the root (Shekhany, 2014). 3.2.6.6. Shoot Root Ratio Shoot Root Ratio was measured by dividing total shoot dry weight on Total root dry weight (Sadeghipour and Aghaei, 2013). 3.2.6.7. Germination speed (seeding/day) The germination speed was estimated according to (Ismail and Kardoush, 2011). Germination speed umber of germinated umber of germinated seeds at the first count seeds at the second count umber of days for the umber of days for the second count first count umber of germinated umber of germinated seeds at the third count seeds at the fourth count umber of days for the umber of days for the third count fourth count 31 Chapter Three Materials and Methods 3.2.6.8. Root elongation speed (cm/day) Root elongation speed was calculated as follows (Shekhany, 2014): 3.2.6.9. Shoot elongation speed (cm/day) Shoot elongation speed was calculated as follows (Shekhany, 2014): 3.2.7. Chemical Analysis Four means replicates samples have been taken from each plot of Choman and Soran in fall and spring season. Samples dried in oven with 700C until reach the constant weight. Then it digested by Rotel digesters and well mixed for making chemical analysis on it (A.O.A.C, 2000). 3.2.7.1. Dry Matter That part of feed, which is not water. Percent DM = 100% moisture%. Feed values and nutrient requirements for ruminants are expressed on a dry matter or moisture-free basis to compensate for the large variation in moisture content of feeds commonly fed to cattle. Calculation: Dry Matter % =100 (C-A)/ (B-A) Where: A = weight of clean, dry scale pan (g) B = weight of scale pan + wet sample (g) C = weight of scale pan + dry sample (g) 32 Chapter Three Materials and Methods 3.2.7.2. Crude Protein Because of its cost, protein is the most important dietary nutrient in a commercial operation .Analysis is done by Kjeldahl's method, which evaluates the total nitrogen content of the sample after it has been digested in sulphuric acid with a mercury or selenium catalyst. Crude protein (%) = nitrogen in sample × 6.25 3.2.7.3. Crude Lipid (Ether extract) The crude lipid is content of a feedstuff. Fat is an energy source with 2.25 times the energy density of carbohydrates. In this method, the fats are extracted from the sample with diethyl ether and evaluated as a percentage of the weight before the solvent is evaporated. Calculations Crud lipid % = 100 B-A/C Where: A = weight of clean dry flask (g) B = weight of flask with fat (g) C = weight of sample (g) 3.2.7.4. Crude Fiber Crude fiber is a traditional measure of fiber content in feeds. This method gives the crude fiber content of the sample after it has been digested in sulphuric acid and sodium hydroxide solutions. The difference in weight after burning indicates the quantity of fiber present. Calculations Crud fiber % = 100 B-A/C Where: 33 Chapter Three Materials and Methods A = weight of crucible with dry residue (g) B = weight of crucible with ash (g) C = weight of sample (g) 3.2.7.5. Ash Content Is the measure of the total amount of minerals present within food. This method is used to determine ash content in feedstuffs by burning. Ash is considered as the total mineral or inorganic content of the sample. Calculations Ash content % = 100 B-(A-C)/C Where: A = weight of crucible with sample (g) B = weight of crucible with ash (g) C = weight of sample (g) 3.2.7.6. Nitrogen-Free Extract (NFE) The result is obtained by subtracting the percentages calculated for each nutrient from 100 based on dry matter, any errors in evaluation will be reflected in the final calculation. Calculations based on dry matter: Nitrogen-free extract (%) = 100 - (A + B + C + D) Where: A = ash content (%) B = crud protein content (%) C = crude lipid content (%) D = crude fiber content (%) 34 Chapter Four Results and Discussions 4. RESULTS AND DISCUSSIONS 4.1. Plant Composition Appendix (1) shows all plants of studied area (Harir to Haji Omeran). During the survey period (30) families, (93) genus and (174) species were recorded. Recorded legumes had the highest value of genus (14) then followed by grasses (12) genus which approximately equal to (15.05%) and (12.90%) of total plant percentage. However, grasses were recorded the highest value in species which were (39), while the legume record (30) species which equıvalent to (22.28%) and (17.14%) of total species. The results indicated that the area is rich with natural vegetation resource and has a high potentiality to produce numerous plant species. This was due to favorable climatic conditions prevalent in the forest zone such as annual precipitation and suitable temperature which enhance the growth of plants during the growing season Guest (1966). North east of Kurdistan region is not only rich with a high number of genus and species but it is also one of the most active areas in the formation of species(Omer, 2011). The most dominant species in the studied area are Centaurea Solstitialis, Lactuca serriola, Notobasis syriaca, Onobrychis crista-galli, and Hordeum bulbosum. The result is corresponded to Besefky (2011) that there is more grazing pressure and low amount of moisture in lowest elevation causing removal of grasses and exciting herbs as compared to slight grazing in mid and higher altitudes. 35 Chapter Four 4.1.1. Results and Discussions Cover Percentage: This could be considered as a criterion to measure the changes in vegetation (Table, 5). Table (5): Coverage percentage overall studied area. Location Vegetation Bare Soil Litter Rock Harir 72 8.25 7 12.75 Spilk 75 5 8.25 11.75 Kalakin 70 12.5 12 5.5 Zargaly 45 11.8 10.7 32.5 Soran 75 7.25 10.75 7 Smilan 61 10.5 18.5 10 Omerawa 64 12 20.75 3.25 Choman 73 9.5 10.25 7.25 Derband 79 6.5 13 1.5 Azadi 80 7.25 8.25 4.5 Haji-Omeran 85 6.5 3 5.5 70.45 8.82 11.13 9.59 Average A. Vegetation Coverage The average of plant covering in the studied area was (70.45%). It varied in Zargaly and Haji Omeran places which were (45%) and (85%) respectively (table, 5). The reason of occurring low vegetation percentage in Zargaly area is due to the present of mountains and high amount of rock 36 Chapter Four Results and Discussions percentage with the comparison to other studied areas because topography is the principle limiting factors in vegetation growth(Jin et al., 2008). B. Bare Soil Average bar soil percentage over all locations was (8.82%), the highest value was shown in Kalakin (12.5%) and the lowest value was in Spilk (5%). This is because of land being sloppy and heavy precipitation in Kalakin which leads to soil erosion and/or water runoff (table, 5). C. Litter Average litter percentage in all locations was (11.13%). Highest value of litter recorded at Omerawa (20.75%) and lowest value observed at Haji Omeran (3%). This is due to more water runoff in Omerawa (table, 5). D. Rock Average rock percentage in studied areas was (9.59%), it was (32.5%) in Zargaly and (3.25%) in Omerawa (table, 5). Generally the results corresponded to Aziz (1999) and Mahmoud (2007) in which the vegetation coverage percentage increases as the plant biodiversity distribution directed toward mountainous region and higher elevation as compared to lowland area which is exploded unwell and due to poor management and inadequate planning and allocation of trained human resources; agricultural extension services and agricultural vocational education, in particular, are in need of major improvements(Jaradat, 2003). 37 Chapter Four 4.1.2. Results and Discussions Forage Value While the purpose of classification is to understand rangeland condition and palatability usage, the forage value has more importance than soil protection and erosion (table, 6). Table (6): Forage value of species overall locations. Forage Value Location I II III Harir 38.71% 58.06% 3.23% Spilk 60.00% 20 % 20% Kalakin 38.46% 53.85% 7.69% Zargaly 55.56% 38.89% 5.56% Soran 68.42% 26.32% 5.26% Smilan 64.29% 28.57% 7.14% Omerawa 36.84% 42.11% 21.05% Choman 62.96% 29.63% 7.41% Derband 41.67% 33.33% 25% Azadi 39.39% 51.52% 9.09% Haji-Omeran 44.90% 51.02% 4.08% 50.11% 39.39% 10.50% Average The results of classification recorded that the average high forage value was (50.11%), which vary between Soran (68.42%) and Omeran (36.84%). However, the average of intermediate forage value was (39.39%) which was fluctuated between 58.06% (Harir) and 20% (Spilk). On the other hand, the average of low forage value was (10.5%) changing from (25%) in Darbend to (3.23%) in Harir. High forage value is dominant, followed by intermediate forage value then low forage value. Both high and intermediated forage value comprised (89.5%) of total forage value of the studied area because of the 38 Chapter Four Results and Discussions appropriate climate during growth and spring season and/or difference of grazing intensity in some areas. The result was corresponded to Maroof (1978) concluded that plants of high forage value increase and low forage value decrease whenever the direction of grazing point toward the forest and forest zone. In addition to Gillett (1948) stated that Kurdistan forest is substantially rich for fodder and natural pasture. 4.1.3. Plant Structure Generally, species of studied area mostly consist of Fabaceae, Poaceae and some other families (table, 7). Average percentage of Fabaceae was (18.77) % while Poaceae was (21.74) % and of other 28 families were (59.49) %. Fabaceae recorded its highest value in Choman (29.17) % while the lowest value recorded in Omerawa (5.88) %. Maximum percentage of Poaceae recorded in Smilan (33.33) % however, least density was recorded in Choman (4.17) %. Other families including Asteraceae, Brasicaceae, Malvaceae, Liliaceae and other families (Appendix, 1) are comprised the remaining percentage. These families recorded their highest value in Darband (73.91) % while the lowest value was recorded in Smilan (41.67) %. As it is seen in table (4) the plant density increased generally from Harir to Haji Omeran. This may possibly due to increase elevation and climatic condition that subjected to higher precipitation and suitable temperature during spring season as compared to the other lowlands locations (Omer, 2011). 39 Chapter Four Results and Discussions Table (7): Percentage of Fabaceae, Poaceae and Other Families in studied area. Location Harir Spilk Kalakin Zargaly Soran Smilan Omerawa Choman Derband Azadi Haji-Omeran Average Fabaceae % Poaceae % Other Families % 11.55 20 15.38 23.25 26.08 25 5.88 29.17 17.39 25 18.43 15.38 20 30.78 30.77 21.73 33.33 29.42 4.17 8.7 18.75 13.15 73.07 60 53.84 45.98 52.19 41.67 64.70 66.66 73.91 56.25 68.42 18.77 21.74 59.49 4.1.4. Density and Relative Density Density could measure as numbers of individual per unit area. Table (8) shows that the highest species density in the studied area was Hordeum murinum ssp. Glaucum (280) individuals and Hordeum bulbosum (232) individuals with a relative density (5.02%) and (4.16%) respectively, while Alcea kurdica Alef, Linaria vulgaris, Colchicum autumnale were recorded the lowest relative density (0.02%) among overall species. The result corresponded to Mahmoud (2007) that the area is rare grazed or ungrazed because of inability of liverstook to reach or existence of snow in some area during grazing which cover the vegetation and lead to presence of species under snow in larger density. Whereas in some other area soil fertility of region may also lead to excess high plant density as a result of residual of plants and animals . 40 Chapter Four Results and Discussions 4.1.5. Frequency and Relative Frequency Frequency is the percent of the number of samples containing a given species to the total number of the samples observed. This method is equivalent to principle this study and to assess of biodiversity compassion and distributions. It also can regard as a distributions degree for species in specific plant ecology. Table (8) shows the most relative frequency species among all other plants overall area was from Poaceae Hordeum Bulbosum which has a density (15.9%) and relative frequency (0.0025) then followed by Notobasis syriaca (13.6%) and relative frequency (0.021) while the lowest frequency (0.0035) were recorded in Erodium trichomanifolium, Galium murale, Anemon coronaria. This may despite to habit of the area which the species are growing (Jaradat, 2003) that concluded the grasses are an interesting genetic resource in Iraq. Table (8): Relative Frequency and Density of studied Plant Species. Family Apiaceae Asteraceae F % RF D % RD % Ainsworthia trachycarpa Boiss. 4.55 0.007 0.98 0.77 Daucus carota L. 6.82 0.011 0.59 0.47 Lagoicia cuminnoides L. 2.27 0.004 1.39 1.1 Scandix pecten-veneris L. 6.82 0.011 0.36 0.29 Torilis arvensis L. 2.27 0.004 1.27 1.01 Achillea tomentosa L. 2.27 0.004 0.57 0.45 Achillea millefolium L. 6.82 0.011 0.86 0.68 Anthemis arvensis L. 6.82 0.011 0.45 0.36 Anthemis austriaca Jacq. 4.55 0.007 0.84 0.67 Anthemis punctata Vahl. 4.55 0.007 0.41 0.32 Carduus pycnocephalus L. 11.4 0.018 2.2 1.74 Centaurea Solstitialis L. Barnaby's Thistle 9.09 0.014 1.64 1.3 4.55 0.007 0.25 0.2 6.82 0.011 0.5 0.4 Species Centaurea iberica Trevir. ex Spreng. Chardinia orientalis (L) KUNTZE 41 Chapter Four Results and Discussions Asteraceae Cichorium intybus L. Cirsium acarna (L.) Moench Cirsium tuberosum (L.) All. Conyza bonariensis (L.) Cronquist Crepis capillaris (L.) Wallr. Crupina crupinastrum (Moris) Vis. Filago arvensis L. Lactuca serriola L. Notobasis syriaca (L.) Cass. Rhagadiolus stellatus (L.) Gaertn. Senecio sp. Senecio gallicus Vill. Senecio vulgaris L. Sonchus oleraceus (L.) L. Tragopogon sp. Tragopogon pratensis L. Tragopogon pterocarpus DC. Boraginaceae Anchusa azurea L. Anchusa sp. Echium italica L. Alyssum dasycarpum Stephan ex Willd. Biscutella didyma L. Brassica elongata Ehrh. Brassica juncea (L.) Czern. Brassica nigra (L.) K.Koch Capsella bursa-pastoris (L.) Medik. Cardaria draba (L.) Desv. Coluteocarpus vesicaria (L.) Holmboe Cyperus asper (Liebm.) O'Neill Isatis glauca Aucher ex Boiss. Lepidium draba L. Lobularia maritima (L.) Desv. Thlaspi perfoliatum L. Cactaceae Echinops ritro L. Caprifoliaceae Cephalaria syriacum L. Caryophyllaceae Vaccaria pyramidata Medik. Cistaceae Helianthemum salicifolium (L.) Mill. Colchicaceae Colchicum sp. Colchicum autumnale L. Convolvulaceae Convolvulus arvensis L. Convolvulus stachydifolius Choisy Cyperaceae Cyperus rotundus L. Dipsacaceae Scabiosa arvensis L. 42 2.27 2.27 2.27 2.27 2.27 9.09 2.27 11.4 13.6 2.27 2.27 4.55 2.27 6.82 2.27 4.55 2.27 2.27 2.27 2.27 4.55 2.27 2.27 2.27 11.4 2.27 4.55 2.27 2.27 2.27 4.55 4.55 2.27 2.27 4.55 6.82 2.27 2.27 2.27 9.09 2.27 2.27 4.55 0.004 0.004 0.004 0.004 0.004 0.014 0.004 0.018 0.021 0.004 0.004 0.007 0.004 0.011 0.004 0.007 0.004 0.004 0.004 0.004 0.007 0.004 0.004 0.004 0.018 0.004 0.007 0.004 0.004 0.004 0.007 0.007 0.004 0.004 0.007 0.011 0.004 0.004 0.004 0.014 0.004 0.004 0.007 0.95 0.11 0.11 0.11 0.23 1.05 0.61 1.18 2.16 0.89 0.41 0.05 1.14 1.68 0.02 0.05 0.07 0.43 0.02 0.02 0.64 0.77 1.05 0.82 4.34 0.25 0.59 0.55 0.05 0.23 1.02 0.09 0.02 0.02 1.52 0.93 0.34 0.11 0.02 0.91 0.05 0.45 0.27 0.76 0.09 0.09 0.09 0.18 0.83 0.49 0.94 1.71 0.7 0.32 0.04 0.9 1.33 0.02 0.04 0.05 0.34 0.02 0.02 0.5 0.61 0.83 0.65 3.44 0.2 0.47 0.43 0.04 0.18 0.81 0.07 0.02 0.02 1.21 0.74 0.27 0.09 0.02 0.72 0.04 0.36 0.22 Chapter Four Dipsacaceae Euphorbiaceae Fabaceae Results and Discussions Scabiosa palaestina L. Euphorbia cheiradenia Boiss. & Hohen. Euphorbia cuspidata Bertol. Euphorbia helioscopia L. Euphorbia microsphaera Boiss. Euphorbia peplus L. Astragalus sp. Coronilla scorpioides L. Hymenocarpos circinnatus (L.) Savi. Lathyrus ochrus (L.) DC. Lathyrus sativa L. Lotus corniculatus L. Marrubium vulgare L. Medicago minima (L.) L. Medicago orbicularis (L.) Bartal. Medicago polymorpha L. Medicago sativa L. Medicago truncatula Gaertn. Mellilotus indica L. Mellilotus officinalis L. Onobrychis crista-galli (L.) Lam. Onobrychis aequidentata (Sm.) d'Urv. Scorpiurus muricatus L. Trifolium campestre Schreb. Trifolium pratense L. Trifolium sp. Trifolium alexandrium L. Trifolium angustifolium L. Trifolium dubium Sibth. Trifolium fragiferum L. Trifolium pilulare Boiss. Trifolium repens L. Trifolium stellatum L. Trifollium purpureum L. Triticum dicoccum L. Triticum sp. Vicia narbonensis L. Vicia sp. Vicia villosa L. Vicia articulata Hornem. Vicia hybrida L. Vicia michauxii Spreng. Vicia sativa L. 43 4.55 4.55 2.27 2.27 2.27 2.27 2.27 2.27 2.27 2.27 2.27 2.27 4.55 2.27 2.27 4.55 2.27 4.55 2.27 2.27 9.09 2.27 2.27 6.82 2.27 2.27 2.27 6.82 2.27 2.27 2.27 6.82 4.55 2.27 2.27 4.55 2.27 2.27 2.27 4.55 4.55 4.55 2.27 0.007 0.007 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.007 0.004 0.004 0.007 0.004 0.007 0.004 0.004 0.014 0.004 0.004 0.011 0.004 0.004 0.004 0.011 0.004 0.004 0.004 0.011 0.007 0.004 0.004 0.007 0.004 0.004 0.004 0.007 0.007 0.007 0.004 0.82 0.82 0.05 0.43 0.48 0.14 0.23 0.25 0.11 0.14 0.52 0.23 0.45 1 1.39 0.5 0.09 0.27 0.98 0.84 2.93 0.77 0.98 1.59 0.25 0.07 0.07 1.39 0.23 0.34 0.3 1.02 0.82 1.34 0.77 0.59 0.61 0.34 0.73 0.36 0.57 0.75 0.23 0.65 0.65 0.04 0.34 0.38 0.11 0.18 0.2 0.09 0.11 0.41 0.18 0.36 0.79 1.1 0.4 0.07 0.22 0.77 0.67 2.32 0.61 0.77 1.26 0.2 0.05 0.05 1.1 0.18 0.27 0.23 0.81 0.65 1.06 0.61 0.47 0.49 0.27 0.58 0.29 0.45 0.59 0.18 Chapter Four Geraniaceae Iridaceae Ixioliriaceae Lamiaceae Liliaceae Malvaceae Onagraceae Papaveraceae Plantaginaceae Poaceae Results and Discussions Erodium cicutarium (L)l'her Erodium trichomanifolium L. Geranium rotandifolum L. Gladiolus atropurpureus L. Gladiolus italicus L. Ixiolirion tataricu L. Mentha sp. Mentha longifolia (L.) L. Phlomis kurdica RECH. FIL. Stachys annua (L.) L. Muscari neglectum Guss. ex Ten. Alcea sp. Alcea kurdica Alef. Malva nicaeensis All. Malva parviflora L. Epilobium sp. Papaver glaucum L. Papaver rhoes L. Papaver argemone L. Papaver hybridum L. Linaria vulgaris L. Plantago bellardii All. Plantago lanceolata L. Veronica spicata L. Aegilops crasa L. Aegilops triuncialis L. Aleuropas sp. Avena ludoviciana L. Avena sterrilis L. Avena fatua L. Bromus arvensis(L) Bromus scoparius L. Bromus sterilis L. Bromus tectorum L. Bromus danthoniae Trin. Bromus erectus Huds. Bromus repens Borbás ex Nyman Dactylis glomerata L. Echinaria capitata L. Hordeum glaucum L. Hordeum murinum ssp. Glaucum. Hordeum bulbosum L. Hordeum marinum Huds. 44 2.27 2.27 4.55 2.27 2.27 4.55 2.27 9.09 2.27 2.27 2.27 2.27 2.27 2.27 4.55 2.27 2.27 2.27 2.27 4.55 2.27 2.27 6.82 2.27 2.27 11.4 2.27 2.27 4.55 4.55 2.27 2.27 2.27 4.55 2.27 6.82 6.82 4.55 2.27 2.27 11.4 15.9 2.27 0.004 0.004 0.007 0.004 0.004 0.007 0.004 0.014 0.004 0.004 0.004 0.004 0.004 0.004 0.007 0.004 0.004 0.004 0.004 0.007 0.004 0.004 0.011 0.004 0.004 0.018 0.004 0.004 0.007 0.007 0.004 0.004 0.004 0.007 0.004 0.011 0.011 0.007 0.004 0.004 0.018 0.025 0.004 1.18 0.11 0.25 0.34 2.27 0.05 1.11 1.57 0.07 0.25 0.32 0.02 0.02 0.89 0.59 0.14 0.05 0.07 0.05 0.05 0.02 0.68 2.7 0.52 1.3 3.27 1.02 0.64 0.95 1.39 0.39 0.5 0.32 1.59 0.5 1.64 1.11 0.82 1.45 2.27 6.36 5.27 0.45 0.94 0.09 0.2 0.27 1.8 0.04 0.88 1.24 0.05 0.2 0.25 0.02 0.02 0.7 0.47 0.11 0.04 0.05 0.04 0.04 0.02 0.54 2.14 0.41 1.03 2.59 0.81 0.5 0.76 1.1 0.31 0.4 0.25 1.26 0.4 1.3 0.88 0.65 1.15 1.8 5.04 4.17 0.36 Chapter Four Poacea Polygonaceae Primulaceae Ranunculaceae Rosaceae Rubiaceae Verbenaceae Results and Discussions Hordeum spontaneum K.Koch Hordeum sp. Lolium Perenne L. Lolium temulentum L. Lolium rigidum Gaudin. Phalaris aquatica L. Phalaris minor Retz. Poa bulbillifera L. Chrtek& Hadac Poa bulbosa L. Chrtek& Hadac Setaria glauca (L.) P.Beauv. vulpia myuros L. Polygonum aviculare L. Polygonum maritimum L. Anagallis arvensis L. Androsace maxiama L. Anemon coronaria L. Ranunculus kochii L. Ranunculus arvensis L. Ranunculus asiaticus L. Ranunculus aucheri Boiss. Ranunculus lanuginosus L. Ranunculus millefolius Banks & Sol. Poterium sanguisorba L. Galium aparine L. Galium murale (L.) All. Galium tricornutum Dandy Sherardia arvensis L. Verbena officinalis L. *F=Frequency, RF=Relative Frequency, D=Density, RD=Relative Density. 45 2.27 2.27 4.55 2.27 2.27 2.27 4.55 2.27 2.27 2.27 2.27 6.82 2.27 4.55 2.27 2.27 2.27 4.55 2.27 2.27 2.27 2.27 4.55 4.55 2.27 2.27 2.27 2.27 0.004 0.004 0.007 0.004 0.004 0.004 0.007 0.004 0.004 0.004 0.004 0.011 0.004 0.007 0.004 0.004 0.004 0.007 0.004 0.004 0.004 0.004 0.007 0.007 0.004 0.004 0.004 0.004 1.23 0.11 1 0.43 0.3 0.7 1.14 0.45 0.05 0.14 0.75 0.59 1.16 0.82 0.34 0.5 0.11 1 0.23 0.14 0.11 0.3 1.07 0.48 0.09 0.7 0.55 0.27 0.97 0.09 0.79 0.34 0.23 0.56 0.9 0.36 0.04 0.11 0.59 0.47 0.92 0.65 0.27 0.4 0.09 0.79 0.18 0.11 0.09 0.23 0.85 0.38 0.07 0.56 0.43 0.22 Chapter Four Results and Discussions 4.2. Adaptation of crested wheatgrass 4.2.1. Measurements: 4.2.1.1. Effect of Location The results were showed that locations have effected on the germination percentage and other growth characters of crested wheatgrass. Figure (3, 4 and 5) referred to differences between locations. Choman‟s location has affected all studied characters of crested wheatgrass in compare with Soran‟s location except in germination percentage. The result showed that there is no significant effect in root weight (fresh, dry) and in length of shoot and root figure (5). Although, location has affected in germination percentage, fresh shoot weight and dry shoot weight. In addition, the highest mean value of germination percentage was recorded (62.225%) in Soran while the lowest mean value (46.050%) was recorded in Choman. It may refer to differences in environmental condition (Ates and Tekeli, 2011) has mentioned that topography is the principal controlling factor in vegetation growth and the amount of rainfall and the type of soil play secondary roles. Shoot weight in both conditions (fresh and dry) has also affected by location which has recorded its high mean value (0.754 g) and (0.4 g) in Choman location while the lowest value was recorded (0.318 g) and (0.188 g) in Soran location. These results may refer to difference of soil and site limitation (Vallentine, 2000) (figure, 4). 46 Chapter Four Results and Discussions 70 a 60 b Percentage 50 40 Choman 30 Soran 20 10 0 Germination Percentage * Means with the same letter are not significantly different at probability level. 0.05 Figure (3): Effect of location on germination percentage. a 0.8 0.7 0.6 Weight(g) a 0.5 a 0.4 Choman b Soran 0.3 b b a 0.2 b 0.1 0 Fresh Shoot Weight Dry Shoot Weight Fresh Root Weight Dry Root Weight * Means with the same letter are not significantly different at probability level. 0.05 Figure (4): Effect of locations on shoot and root weight at fresh and dry conditions. 20 a a Length(cm) 15 a 10 Choman a Soran 5 a a 0 Shoot Length Root Length Shoot Root Ratio * Means with the same letter are not significantly different at probability level. 0.05 Figure (5): Effect of locations on shoot and root length. 47 Chapter Four Results and Discussions 4.2.1.2. Effect of Season The effect of season has observed on the germination percentage and other growth characters of crested wheatgrass except shoot and root length and shoot root ratio. Figure (6, 7 and 8) indicates that there is significant difference at germination percentage, fresh shoot weight, dry shoot weight, fresh root weight and dry root weight. Fall seeding were more significant performance in all characters than sprig, it may refer to higher precipitation ratio in fall season than in spring season. Germination percentage recorded higher mean value in spring (71.3%) while it recorded lower mean value (36.9%) in fall season (figure, 6). Thus; spring seems to be more favorable for grass germination as it had ability to germinate in early spring season (Holl et al., 1988). Season had significant effect in fresh shoot weight ,dry shoot weight, fresh root weight and dry root weight with a high mean value (0.921, 0.600, 0.525 and 0.255 g) in fall season while it recorded low mean value (0.151, 0.069, 0.073 and 0.056 g) in spring season respectively. It may refer to environmental factors such as temperature and precipitation (figure, 7). 48 Chapter Four Results and Discussions 80 a 70 Percentage 60 50 b 40 Fall Spring 30 20 10 0 Germination Percentage * Means with the same letter are not significantly different at probability level. 0.05 Figure (6): Effect of seasons on germination percentage. 1 a 0.9 0.8 weight (g) 0.7 a 0.6 a Fall 0.5 0.4 Spring a 0.3 b 0.2 b b 0.1 b 0 Fresh Shoot Weight Fresh Root Weight Dry Shoot Weight Dry Root Weight * Means with the same letter are not significantly different at probability level. 0.05 Figure (7): Effect of seasons on shoot and root weights in fresh and dry condition. 20 a Length (cm) a 15 a Fall 10 a 5 Spring a a 0 Shoot Length Root Length Shoot Root Ratio * Means with the same letter are not significantly different at probability level. 0.05 Figure (8): Effect of seasons on shoot and root length. 49 Chapter Four Results and Discussions 4.2.1.3. Interaction Effect Table (9) showed that there are significant effects on germination percentage, fresh and dry shoot and root weight at interaction of locations and seasons without effect on length of root and shoot and their ratio. Germination percentage recorded its high mean value at spring season in Soran and Choman (80.95%) (61.65%) while it recorded low mean value (30.45%) at fall season in Choman. It may refer to climatic condition of Choman‟s fall which is not enough suitable as in Soran‟s spring. Fall season of Choman recorded the highest mean value in shoot fresh weight, root fresh weight, shoot dry weight and root dry weight (1.27, 0.875, 0.72 and 0.29 g) whereas the lowest mean value was recorded in Soran‟s spring season (0.065, 0.030, 0.0480 and 0.043 g) respectively. These results showed that Choman‟s fall season has favorable effect on all growth characters except germination percentage because it recorded the lowest value during seeding in Choman‟s fall season. it is agreement with (Svejcar, 1990) stated that the more roots the better shoot growth. 50 Chapter Four Results and Discussions Table (9): Interaction Effect of locations and seasons on germination percentage and other growth characters on Crested Wheatgrass . Locations Seasons Germination Fresh percentage % Fall Choman Sprıng Fall Soran Sprıng shoot Fresh Dry Dry Shoot Root root shoot root length length root weight weight weight weight (cm) Shoot (cm) ratio (g) (g) (g) (g) 30.45 1.270 0.875 0.720 0.29 19.530 12.53 2.813 d a a a a a a a 61.65 0.238 0.108 0.098 0.070 15.853 6.828 1.46 b bc b bc b a a a 43.5 0.573 0.342 0.330 0.220 18.138 8.315 2.295 c b ab b ab a a a 80.95 0.065 0.03 0.048 0.043 15.605 5.855 1.425 a c b c b a a a * Means with the same letter are not significantly different at probability level. 0.05 Table (10): Germination and length elongation speed. Location Season Germination Germination Shoot percentage speed (%) Shoot Root length elongation length elongation (cm) speed (cm) (cm) Choman Fall Soran Root speed (cm) 30.45 0.17 19.53 0.12 8.32 0.1 Spring 61.65 1.02 15.85 0.2 6.83 0.09 Fall 43.5 0.24 18.13 0.23 12.53 0.16 Spring 80.95 1.34 15.6 0.2 5.86 0.07 Table (10) shows that germination speed of spring season of Soran is higher among others because the highest mean value of seed germination is recorded. But elongation speed of (shoot and root) length is higher in Soran‟s fall seasons because they are recorded the highest value in length elongation speed. 51 Chapter Four Results and Discussions 4.2.2. Chemical Analysis: 4.2.2.1. Location Locations were significantly effected on chemical analyses of crested wheatgrass. Soran location table (11) was showed significant effect for dry matter, ash, crud protein, crud lipid and NFE with a higher percentage value (20.585, 15.750, 16.005, 7.978, and 52.816) in Soran location while Choman location recorded lower percentage value (11.395, 8.661, 14.375, 6.755 and 45.966%) respectively. These differences may refer to the differences in altitude of locations as in table (7) (Botani, 2014) has concluded that forage value generally affected by altitude. While there were no significant differences in crude fiber. Table (11): Effect of location on chemical analysis (%) of Crested Wheatgrass. Location Dry Ash Matter Soran Choman Crud Crud Crud Protein Fiber Lipid NFE 20.585 15.750 16.005 14.920 7.978 52.816 a a a a a a 11.395 8.661 14.375 14.808 6.755 45.966 b b b a b b * Means with the same letter are not significantly different at probability level. 0.01 4.2.2.2. Effect of Season The effect of seasons was significantly observed on chemical analysis of crested wheatgrass as in (table, 12). Spring season was more effective than fall season because the dry matter of created wheatgrass is related to rate of growth, which is dependent upon soil and climate parameters (Mayland, 1986). 52 Chapter Four Results and Discussions Table (12): Effect of season on chemical analysis (%) of Crested Wheatgrass. Season Dry Ash Matter Spring 18.395 a Fall 13.585 b 13.686 a 10.725 b Crud Crud Crud Protein Fiber Lipid NFE 15.850 17.227 7.620 51.433 a a a a 14.530 12.500 7.113 47.350 b b b b * Means with the same letter are not significantly different at probability level. 0.01 4.2.2.3. Interaction Effect The interactions of locations and seasons were also affected the chemical analysis of crested wheatgrass. The results (table,13) were showed that fall season of Choman and Soran provided the highest means value of dry matter (22.52%) and (18.65%) as compared to spring season of Choman and Soran, while there were observed lowest means value (14.27%) and (8.5%) respectively. That is because winds and high temperatures during the growing season result in high evaporation rates which reduce the moisture available and increase dry matter on plants. (Willard and Schuster, 1973). Spring season of Soran recorded higher mean value in ash percentage (18.1%) than that recorded in Choman‟s fall and spring season (9.273%) and (8.05%) since highest ash contents occurred just before new growth began in the spring and Ash content was reduced with advanced stage of maturity (Teka et al., 2012). Fall season of Soran and Choman's spring season were recorded the highest means value in protein (16.28%) and (15.97%) while the lowest means value (12.78%) were recorded only in spring season of Soran because the environmental conditions caused considerable accrual of plant size, which 53 Chapter Four Results and Discussions causing reduction of crude protein content by uncommonly low reserve of soil nitrogen before planting (Bártová et al., 2009). Spring season of Choman recorded the highest mean value of crud fiber (17.68%) while the lowest means value was recorded in fall season of Choman (11.93%) because increasing in altitude lead to decrease in crud fiber (McCreary, 1927). Soran‟s fall season recorded high mean value in crud lipid (8.68%) whereas, the lowest mean value (6.56%) among others interaction have recorded in Soran‟s spring season. There were no significant difference in spring season of Choman and Soran. Spring season of Soran showed highest mean value in NFE (54.210%) due to increasing in altitude which leads to increase in NFE (McCreary, 1927) while lowest mean value in fall season of Choman was (44.205%). Table (13): Interaction Effects of Locations and Seasons on Chemical analysis (%) of Crested Wheatgrass. Season Location Dry Ash Crud Crud Crude NFE Protein Fiber Lipid 9.273 15.73 11.93 7.275 44.205 a c a b b c 18.65 13.4 16.28 13.07 8.68 51.430 b b a b a ab 14.27 18.1 12.78 16.77 6.56 54.210 c a b a c a 8.05 15.97 17.68 6.95 48.633 c a a bc b Matter Choman 22.52 Fall Soran Soran Spring Choman 8.5 d * Means with the same letter are not significantly different at probability level. 0.01 54 Chapter Five Conclusion and Recommendation CONCLUSION AND RECOMMENDATION 5.1. Conclusion Results conclude that mountainous region of the Kurdistan is rich with natural rangeland it may refers to climatic condition and topography of the region but the areas misused and not managed well. 1- Presence of more variance species in the area that have differ forage value. Half of individuals were from high forage value. 2- Presence of high plant density in the studied areas. 3- Poaceae and Fabaceae have predominant the area and they can be regarded as a most current families which adapted in the area. 4- The studied area has favorable humidity and temperature for plant distribution which have positive effect on presentation of being high plant density. 5- Crested wheatgrass has ability to resist hard climate conditions and environments including low temperature, heavy precipitation and weed competitions. 6- Soran was the best adapted location for germination of crested wheatgrass but growth character was less favorable than Choman location. Spring was the best season for germinating seeds, while fall season seeding was more favorable for growth characters. 7- It appeared that chemical analysis of crested wheatgrass was more significant in Soran location than Choman location and spring season showed better result than fall season. 8- Soil moisture is one of the most necessary requirements during seeding of crested wheatgrass. 55 Chapter Five Conclusion and Recommendation 5.2. Recommendation 1- Using modern survey methods such as remote sensing because it was not available for current study. 2- Collecting of seeds in dense areas with plants and replanting pastures in damage areas, taking into the environmental conditions of region. 3- Establishing of terraces to pasture areas to maintain and protect from soil erosion especially at slope area. 4- Establishing of stone dams to reduce the effects of erosion. 5- Cleaning of mountains from mines boom as it is dangerous. 6- Implementing of Artificial projects for the owners of cattle and sheep by alfalfa crop cultivation and multiple sizes for avoiding overgrazing during growing seasons of species. 7- More studies are required about the other species. 8- Conducting further studies on other uses of crested wheatgrass including grazing system. 9- Carrying out more research for chemical analyzing of seeds of crested wheatgrass. 10- Undertaking investigations on other growth stages of crested wheatgrass including; flowering, fruit and seed stages. 56 Refrence REFERENCES Abdulhasan, N. A., Salim, M. A., Al-Obaidi, G. S., Ali, H. J., Al-Saffar, M. A., Abd, I. M. and Shaish, A. K. (2009). Habitat Mapping and Monitoring Project Classification and Description of Southern Iraqi Marshlands (National Park Area). Nature. Agro Meteorological Center, (2014). Kurdistan Region of Iraq, General directorate of agriculture. Ministry of Agriculture and Water source, Erbil. A.O.A.C., (2000). Official Methods of Analysis, Benjamin Eran Kliostation, Washington.1: chapter 4, Pp 20-21. Aani, H. A. and Hadad, Y. S. (1986). Study Environment of Natural Vegetation in Some Dunes region – Near beige, J. of Agricultural Research and Water Source (plant production) 5(2): 281-265. Al-Rawi, A. (1964). Wild plants of Iraq with Their Distribution. Third Edition, Baghdad. Government Press. Al Pierson, (2006) Assessment of Rangelands in Iraq Preliminary Report, USAID. Pp 5-6. Al.Tikriti, M. A. and Abdullah, K. M. (1969). Range and Its Management in Iraq. Iraq Agricultural Magazine 24:59-83.Canada. Ali, T. T. (1988). Qualitative, Quantitative and Taxonomical Study of Vegetation in Namroud, East and West Mosul Dam, Thesis, college of Agriculture and Forestry. Mosul univ.(in Arabic). Al-Kittany M. M., Hassan S. M., Al-Marrof I. M. and Al-Raho H. A. (1978). Effect of Fire on Pine Forest and Natural Vegetation in Zawita. J. AlRaffidain Agricultur, 15(2), 1980, college of Agriculture and Forestry. Mosul univ. Al-Obadee, A. J. (2004). Delineation and Evaluation of Range Land In Ninevah Province By Using Remote Sensing Ph.D. Thesis, Univ. of Musul, Ninevah.(in Arabic). 57 Refrence Ates, E. and Tekeli, A. S. (2011). Change of Some Morphological and Forage Quality Properties Depends on Different Pasture Aspects in, Romanian. J. of Grasslands and Forage Crops 31(3). Aziz, F. H. (1999). Study Vegetation and Some Environment Effect on Plant Distribution at Hanara/ Erbil region. J. of Education College, univ. of Salahaddin: 133-151. Bakker, J. D., Christian, J., Wilson, S. D. and Waddington, J. (1997). Seeding Blue Grama in Old Crested Wheatgrass Fields in Southwestern Saskatchewan. J. of Range Management: 156-159. Baninasab, B. and Mobli, M. (2008). Morphological Attributes of Root System and Seedling Growth in Three Species of Pistacia. Silva Lusitana, EFN, Lisboa. Portugal 16(2): 175-181. Bártová, V., Bárta, J., Diviš, J., Švajner, J., and Peterka, J. (2009). Crude Protein Content in Tubers of Starch Processing Potato Cultivars in Dependence on Different Agro-Ecological Conditions, J. of Central European Agriculture, 10(1): 57-65. Bishay, F. K. (2003). Towards Sustainable Agricultural Development in Iraq. Rome: Food and Agriculture Organization of the United Nations (FAO). Besefky, K. I. S. (2011). Effect of Elevation and Aspect on Natural Vegetation Characteristics of Some Locations in Duhok Governorate, Iraqi Kurdistan Region. Botani, K. A. (2014) Effect of Aspect and Elevation on Qualitative Characteristics of Vegetation developing in Ishawa region at North of Iraq. J. of mesopotamial Agriculture, 42(3). Buman, R. A., Monsen, S. B. and Abernethy, R. H. (1988). Seedling Competition Between Mountain Rye,'Hycrest'crested Wheatgrass, and Downy Brome. J. of Range Management: 30-34. Buringh, P. (1960) Soils and Soil Conditions in Iraq, Ministry of Agriculture Baghdad. Caldwell, M. M., Richards, J. H., Johnson, D. A., Nowak, R. S. and Dzurec, R. S. (1981). Coping with Herbivory: Photosynthetic Capacity and Resource 58 Refrence Allocation in two Semi-arid Agropyron bunchgrasses. Oecologia, 50(1): 14-24. Conner, L. (2008). Growing Wild Crested Wheatgrass and the Landscape of Belonging, ProQuest. Cook, C. W., Stoddart, L. A. and Kinsinger, F. E. (1958) Responses of Crested Wheatgrass to Various Clipping Treatments. Ecological Monographs, 237272. Cook, C. W. (1959). The Effect of Site on the Palatability and Nutritive Content of Seeded Wheatgrasses. J. of Range Management Archives. 12(6): 289-292. Currie, P. O. and Peterson, G. (1966). Using Growing-eason Precipitation to Predict Crested Wheatgrass Yields. J. of Range Management: 284-288. Dewey, D. and Asay, K. (1975). The Crested Wheatgrasses of Iran. Crop Science 15(6): 844-849. Dewey, D. R., (1983). Historical and Current Taxonomic Perspectives of Agropyron, Elymus and related genera. Crop Sci., 23: 637-642. Duncan, D. B. (1955). Multiple Ranges and Multiple (f) test Biometric II, Pp1-2. El-Tekriti, R. A. and Mohammad, R. M. (1982). Rangeland Management . Fahri, F. A. (2009). Proposed System of Land Pasture Classification in Iraq, journal of Al-Taqani, 22(1):111-120. F.A.O. (1975). Range Management in northern Iraq. Technical Report No. 3. Food and Agriculture organization. Rome. Ganjo, D. G. A. (2008). Deraluk Hydropower Project Dohuk/Kurdistan Region Governorate (KGR)-Iraq. Gebril, A. O. and Saeid, A. G. (2012). Importance of Pastoral Human Factor Overloading in Land Desertification: Case Studies in Northeastern Libya. Proceedings of World Academy of Science, Engineering and Technology, World Academy of Science, Engineering and Technology. Gillett, J. B. (1948). Pasture and wild fodder plants of Iraq. Ministry of Agriculture, Baghdad. 59 Refrence Gintzburger, G., Le Houérou, H. N. and Saïdi, S., (2006). Near East-West Asia Arid and Semi-arid Rangelands. Science et changements planétaires/Sécheresse, 17(1): 152-168. GlobalSecurity.org, http://www.globalsecurity.org/jhtml/jframe.html#http://www.globalsecurity .org/military/world/iraq/images/iraq-map-province1.gif. Gökkuş, A. and Ali, K. (1996). Canopy and Root Development of Crested Wheatgrass in Relation to the Quantity and Time of Nitrogen Application. Turkish J. of Agriculture and Forestry, 20(4): 289-293. Gökkuş, A. and Ali, K. O. Ç. (1997). Changes in Morphological and Agronomical and Chemical properties of Crested Wheatgrass (Agropyron critatum Geartn L.) in Relation to Time, Plant Height and above Ground Biomass. Central Research institute For Field Crops, 6(2):36. (In Turkish). Grant-Hoffman, M. N., Clements, A., Lincoln, A. and Dollerschell, J. (2012). Crested wheatgrass (Agropyron cristatum) Seeding in Western Colorado: What can we learn? Management, 3(2): 89-96. Guest, E. R. (1966). Flora of Iraq. Vol. 1. Baghdad: Ministry of Agriculture of the republic of Iraq. Guest, E. R. (1966). Flora of Iraq. Vol. 9. Baghdad: Ministry of Agriculture of the Republic of Iraq. Holl, F., Chanway, C., Turkington, R. and Radley, R. (1988). Response of Crested Wheatgrass (Agropyron cristatum L.), Perennial Ryegrass (Lolium perenne) and White Clover (Trifolium repens) to Inoculation with Bacillus Polymyxa. Soil Biology and Biochemistry, 20(1): 19-24. Holm, A., Salih, H., Ibrahim, B., Ali, N. and Ezat, B. (2002). Grazing systems and livestock production in the three northern Governorates of Iraq. A report of results of surveys by the FAO range program. Ismail, O. M. and Kardoush, M. (2011). The Impact of Some Nutrient Substances on Germination and Growth seedling of Pistacia vera L. Australian J. Basic and Applied Sci., 5(5): 115-120. 60 Refrence Jaradat, A., 2003. Agriculture in Iraq: Resources, Potentials, Constraints, Research Needs and Priorities. Food, Agriculture and Environment, 1(2): 160-166. Jin, X., Zhang, Y., Schaepman, M., Clevers, J. and Su, Z., (2008). Impact of elevation and aspect on the spatial distribution of vegetation in the Qilian mountain area with remote sending data. The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, 37(7): 1385-1390. Johnson, K. L. (1986). Crested wheatgrass; its values, problems and myths; symposium proceedings, Utah State Univ., Logan, USA. Kapur, P. and S. R. Govil (2000). Experimental Plant Ecology. CBS Publishers and distributors, Dariyaganji, New Delhi, India. Kirk, L., Stevenson, T. and Clarke, S. (1934) Crested Wheat grass. Kruger, G. and Council, S. F. (1998) Crested Wheatgrass Seed Production. saskatchewan forage, Canada agriculture. Lahony, S. R. A., Mohammad, M. K., Ali, H. H., Al-Moussawi, A. A. and AlRasul, M. S. A. (2013). Hawraman Lowest Zone, Kurdistan province North East of Iraq. Bull. Iraq Nat. Hist. Mus., 12(4): 7-34. McCreary, W. (1927). Wyoming Forage Plants and Their Chemical Composition, Studies 8, Wyoming Exp. Sta. Bull, 157: 91. Mahmoud, A. H. (2007). The Study of Vegetation and Adaptation of some Varieties of (Lathyrus sativa L.) in Erbil Governorate. Thesis. Univ. of Salahaddin, Erbil (in Arabic). Maroof, S. S. (1978). Some Studies of Distribution and Adaptation of Grasses in Northern Iraq. M.Sc. Thesis. Mosul Univ. Mayland, H. F. (1986). Factors affecting yield and nutritional quality of crested wheatgrass. Mayland, H. F., Asay, K. H. and Clark, D. H. (1992) Seasonal trends in Herbage Yield and Quality of Agropyron. J. of Range Management, 45(4): 369-374. Ministry of Agriculture and Water Source. Krg, (2013). General Directory, department of Rangeland, personal interview. Erbil. www.moawr-krg.org. 61 Refrence Omer, T. M. A. (2011). Country Pasture/Forage Resource Profiles. FAO, available on: http://www.fao.org/ag/AGP/AGPC/doc/Counprof/PDF% 20files/iraq.pdf. Pellant, M., Lysne, C. R., Shaw, N. and Pellant, M. (2005). Strategies to enhance plant structure and diversity in crested wheatgrass seeding. Proceedings of the USDA Forest Service. RMRS-P-38. Fort Collins, CO: Rocky Mountain Research Station: 64-70. Pourbabaei, H., Farajollahi, A., Parvane, E., and Gholinejad, B. (2012). Assessment and Comparison of Different Methods for Estimating Forage Production (Case Study: Rangeland of Kurdistan Province). J. of Rangeland Science. Qassim, Y. M. (1981). Selection of wild ungulate according to the pasture plant in Atrosh,zaweta and Sinjar enclosures. Thesis, College of Agriculture and Forestry. Mosul univ. (in Arabic). Rathwan, M. S. and Fahri, A. k. (1975). Forage Crops and Range vol. 1-2 College of agriculture, univ. of Mosul.(in Arabic) Razvanchy, H.A.S., (2014).Modelling some of the soil properties in the iraqi kurdistan region using landsat datasets and spectroradiometer. Salahaddin University, Thesis (Ms.c), Kurdistan Region, Iraq. Rowell, D. R. (1996). Soil Science: Methods and Applications. Longman, Harlow. Sadeghipour, O. and P. Aghaei (2013). Improving the growth of cowpea (Vigna unguiculata L. Walp) by magnetized water. J. Bio. and unv. Sci. 3(1):37-43. Saeed, J. F. (2003) Study survey of flowering plants in Gali Ali Bag Strait. J. of univ. of Sallahadin, Arbil, 1(15):5-15. Saeed, J. F. (2013). Morphological Study of the Centaurium pulchelum and C.erythraea (Gentianaceae) in Kurdistan region of Iraq. J. of university of anbar for pure science, 7(1). Saeed, J. F., and Wadi, K. D. (2013). A Systematic Study about the Genus Ferulago Boiss.(Umbelliferae) Growing in Kurdistan Region of Iraq. Advances in Bioresearch, 4(2). 62 Refrence Salihi, Y. S. (1980). Vascular Plants of Bira Macron Mountain. Thesis, college of science/Sallahadin Univ. Sankari, M. N. (1996). Method of measuring density and vegetation structure. Arab Organization for Developing Range Agriculture and Development. Forage. Modern University of Methods Arabic for country, hartum.Pp117-151. (in Arabic) SAS, (2005). Statistical Analysis System Institute, cary NC, USA. Schwan, H. E. (1954). A Management Program for the Livestock Ranges in Iraq. Ministry of Agriculture, Baghdad. Sheet, P. F. and G. C. Page (2001). “Plant Fact Sheet.” USA. Sheley, R. L., Mangold, J., Goodwin, K. and Marks, J. (2008). Revegetation Guidelines for the Great Basin: Considering Invasive Weeds. US Department of Agriculture. Agricultural Research Service. Shekhany, H. K. (2014). Influence of Magnetized Water on the Ability of Nutrient uptake, the Growth of two Cultivars of Pistachio(Pistacia vera L.) seedling. Thesis, Salahaddin univ., Erbil. Sorrells, L. and Glenn, S. (1991). Review of Sampling Techniques Used in studies of Grassland Plant Communities. Proceedings of the Oklahoma Academy of Sciences. Springfield, H. W. (1954). Forage in Iraq. Ministry of Agriculture, Baghdad Pp16. (c.f Maroof, 1978) Squires, V. R. (2009). Range and Animal Sciences and Resources Managements. Vol-1- Australia Pp 2. Svejcar, T. (1990). Root length, Leaf area, and Biomass of Crested wheatgrass and Cheatgrass Seedlings. J. of Range Management: 446-448 Taghizadeh, R., Jafari, A., Choukan, R. and Asghari, A. (2009). Investigation of Genetic Diversity in Crested Wheatgrass (Agropyron cristatum (L.) Garetn.) populations using RAPD molecular markers. J. of Plant Science Research. 63 Refrence Teka, H., Madakadze, I. C., Angassa, A., and Hassen, A. (2012). Effect of Seasonal Variation on the Nutritional Quality of Key Herbaceous Species in Semiarid Areas of Borana, Ethiopia. Indian J. of Animal Nutrition 29, 324-332. Tilman, D; Wedin, D. and Knops J. (1996). Productivity and Sustainability Influenced by Biodiversity in Grassland Ecosystem. Nature 379,718-720. Highlighted in Nature News and Views 379, 673-674 by P. Kareiva. Toma, S. M. (1983). Surveying and Evaluating of Pasture Plants in Some Location in the North of Iraq as base of rangeland for wild ungulate. Thesis, College of Agriculture and Forestry/Univ.of Mosul. Towensend, C. C. and E. Guest (1968). Flora of Iraq, Vol. (1-9) Ministry of Agriculture. Baghdad. Iraq. USDA, (2004). The Plants Database, Version 3.5 [Online]. National Plant Data Center, Baton Rouge, LA. Available at http://plants.usda.gov/cgi_bin/plant_profile.cgi?symbol=AGCR (verified 12 July 2004). USDA, (2008). The Plants Database. National Plant Data Center, Baton Rouge, LA, USA. USDA, (2012). USDA Natural Resources Conservation Service, Plant Materials Center, Bismarck, ND 58504 . Available at http://plants.usda.gov. Vajari, M., Razvi, S. M., and Jalali, A. M. (2013). A Survey on Effects of Enclosure on Vegetation Dynamic of Rangelands of Guilan Province. Vallentine, J. F. (2000).Grazing management. Elsevier. Willard, E.E. and Schuster, J.L., (1973). Chemical Composition of Six Southern Great Plains Grasses as Related to Season and Precipitation. J. of Range Management Archives, 26(1): 37-38. Williams, R. E., Allred, B., Denio, R. M. and Paulsen, J. H. A. (1968). Conservation, Development, and use of the World's Rangelands. J. of Range Management: 355-360. Wilson, S. D. and Pärtel, M. (2003). Extirpation or coexistence? Management of a Persistent Introduced Grass in a Prairie Restoration. Restoration Ecology 11(4): 410-416. 64 Refrence Wolfe, T. K. and. Kipps M. S. (1953). Production of Field Crops. J. Soil Science 76(4): 319. Yousif, S. (1971) Natural Pasture. Shafiq printing, Vol. 1, Baghdad, page 448. Zohary, M. (1950). The Flora of Iraq and Its Phytogeographical Subdivision. Iraq Dep. Agri.Bull.No.3:141-142. 65 Appendix Appendix (1): All species of studied area with their Life Cycle, Plant Density and Forage Value. Family Poaceae Genus Aegilops L. P. F. C D V Aegilops crasa L. A A III Aegilops triuncialis L. P F III Species Aleuropas Aleuropas sp. Avena Avena ludoviciana L. A I I Avena sterrilis L. A F I Avena fatua L. A F I Bromus arvensis (L). P F I Bromus scoparius L. A F I Bromus sterilis L. A A I Bromus tectorum L. A A I Bromus danthoniae Trin. P F I Bromus erectus Huds. A A I Bromus repens Borbás ex Nyman A F I Dactylis Dactylis glomerata L. P A I Echinaria Echinaria capitata L. A VR II Hordeum Hordeum glaucum L. A VR II Hordeum murinum A VA II Hordeum bulbosum L. A F II Hordeum marinum Huds. A F II Hordeum spontaneum K.Koch. A A II Hordeum sp. A I II Lolium Perenne L. A F I Lolium temulentum L. P F I Lolium rigidum Gaudin. A A I Phalaris aquatica L. A I II Phalaris minor Retz. A F II Poa bulbillifera L.Chrtek& Hadac A F II A R II Bromus VR I ssp.Glaucum. Lolium Phalaris Poa Poa bulbosa L. Chrtek& Hadac. 65 Appendix Poaceae Fabaceae Vulpia Vulpia myuros L. A VR II Setaria Setaria glauca (L.) P.Beauv. A I III Astragalus Astragalus sp. Coronilla Coronilla scorpioides L. A I I Hymenocarpos Hymenocarpos circinnatus (L.) A I I Lathyrus ochrus (L.) DC. A I I Lathyrus sativas L. A F I Lotus Lotus corniculatus L. P I I Medicago Medicago orbicularis L. A A I Medicago minima (L.) L. P A I Medicago orbicularis (L.) Bartal. P A I Medicago polymorpha L. A A I Medicago sativa L. A R I Medicago truncatula Gaertn. A I I Mellilotus indica L. A A I Mellilotus officinalis L. A A I Onobrychis crista-galli (L.) Lam. P A I Onobrychis aequidentata B R I I II Savi. Lathyrus Mellilotus Onobrychis (Sm.) d'Urv. Scorpiurus Scorpiurus muricatus L. A A I Trifolium Trifolium campestre Schreb. P F I Trifolium pratense L. A A I R I Trifolium alexandrium L. A R I Trifolium angustifolium L. P I I Trifolium dubium Sibth. A I I Trifolium fragiferum L. P F I Trifolium pilulare Boiss. A I I Trifolium repens L. A F I Trifolium stellatum L. P I I Trifollium purpureum L. A A I Trifolium sp. 66 Appendix Fabaceae A A I F I Vicia narbonensis L. A F I Vicia sp. A F I Vicia villosa L. A A I Vicia articulata Hornem. A I I Vicia hybrida L. A I I Vicia michauxii Spreng. A I I Vicia sativa L. A I I Achillea tomentosa L. A F I Achillea millefolium L. P VR II Anthemis arvensis. A R I Anthemis austriaca Jacq. A F II Anthemis punctata Vahl. P F II Carduus Carduus pycnocephalus L. A A II Centaurea Centaurea Solstitialis L. A F II P VR II Triticum Triticum dicoccum L. Triticum sp. Vicia Asteraceae Achillea Anthemis Barnaby's Thistle Centaurea iberica Trevir.ex Spreng. Chardinia Chardinia orientalis (L.) Kuntze. A R I Cichorium Cichorium intybus L. A A I Cirsium Cirsium acarna (L.) Moench. P I II Cirsium tuberosum (L.) All. P I II Conyza bonariensis (L.) A I III Conyza Cronquist. Crepis Crepis capillaris (L.) Wallr. A I II Crupina Crupina crupinastrum (Moris) A R II Vis. Filago Filago arvensis L. P F I Lactuca Lactuca serriola L. A VR I Notobasis Notobasis syriaca (L.) Cass. B I II Rhagadiolus Rhagadiolus stellatus (L.) Gaertn. A A I Senecio Senecio sp. 67 F II Appendix Asteraceae Brassicaceae Senecio gallicus Vill. B VR II Senecio vulgaris L. P A II Sonchus Sonchus oleraceus (L.) L. P A I Tragopogon Tragopogon pratensis L. A VR I Tragopogon Tragopogon pterocarpus DC. A R I Echium Echium italica L. A VR I Alyssum Alyssum dasycarpum Stephan ex P F II Senecio Willd. Biscutella Biscutella didyma L. A A I Brassica Brassica elongata Ehrh. P A I Brassica nigra (L.) K.Koch. P A II Capsella bursa-pastoris (L.) A I I Capsella Medik. Cardaria Cardaria draba (L.) Desv. A F II Coluteocarpus Coluteocarpus vesicaria (L.) P F II Holmboe. Apiaceae Boraginaceae Isatis Isatis glauca Aucher ex Boiss. A I I Lepidium Lepidium draba L. P I II Lobularia Lobularia maritime (L.) Desv. B R II Thlaspi Thlaspi perfoliatum L. P VR II Cyperus Cyperus asper (Liebm.) O'Neill. A R II Ainsworthia Ainsworthia trachycarpa Boiss. A F II Daucus Daucus carota L. A F II Lagoicia Lagoicia cuminnoides L. A A II Scandix Scandix pecten-veneris L. A VR I Torilis Torilis arvensis L. A A I Anchusa Anchusa azurea L. P F II Anchusa sp. P VR II Cactaceae Echinops Echinops ritro L. A VR III Caprifoliaceae Cephalaria Cephalaria syriacum L. P A I Caryophyllaceae Vaccaria Vaccaria pyramidata Medik. A VR II Cistaceae Helianthemum Helianthemum salicifolium A F II (L.)Mill. 68 Appendix Colchicaceae Convolvulacea Colchicum Convolvulus Colchicum autumnale L. P VR III Colchicum sp P I III Convolvulus arvensis L. P I I Convolvulus stachydifolius Choisy. A R II Cyperaceae Cyperus Cyperus rotundus L. A F II Dipsacaceae Scabiosa Scabiosa arvensis L. P I I Scabiosa palaestina L. A F I Euphorbia cheiradenia A F III Euphorbia cuspidata Bertol. A R III Euphorbia helioscopia L. P F III Euphorbia microsphaera Boiss. P I III Euphorbia peplus L. P I III Marrubium Marrubium vulgare L. B I III Mentha Mentha sp. P A II Mentha longifolia (L.) L. A F II Phlomis Phlomis kurdica RECH. FIL. P R I Stachys Stachys annua (L.) L. A I III Teucrium Teucrium polium L. A R I Liliaceae Muscari Muscari neglectum Guss. A I III Malvaceae Alcea Alcea sp. Euphorbiaceae Euphorbia Boiss.& Hohen. Lamiaceae Malva VR II Alcea kurdica Alef. A VR II Malva nicaeensis All. A A I Malva parviflora L. A A I Onagraceae Epilobium Epilobium sp. P I II Papaveraceae Papaver Papaver glaucum L. A VR III Papaver rhoes L. A VR III Papaver argemone L. A R III Papaver hybridum L. A VR III Plantago bellardii All. A A II Plantago lanceolata L. P F II Veronica Veronica spicata L. A I II Linaria Linaria vulgaris L. A VR II Plantaginaceae Plantago 69 Appendix Polygonaceae Primulaceae Ranunculaceae Polygonum aviculare L. P I I Polygonum maritimum L. A A II Anagallis Anagallis arvensis L. P I I Androsace Androsace maxiama L. A F I Anemon Anemon coronaria L. P F I Ranunculus Ranunculus kochii L. B I II Ranunculus arvensis L. A F I Ranunculus asiaticus L. A I II Ranunculus aucheri Boiss. B I II Ranunculus lanuginosus L. P I II Ranunculus millefolius Banks & Sol. P I II Polygonum Rosaceae Poterium Poterium sanguisorba L. A A I Rubiaceae Galium Galium aparine L. A F II Galium murale (L.) All. A R II Galium tricornutum Dandy. P F II Sherardia Sherardia arvensis L. A F I Verbenaceae Verbena Verbena officinalis L. P F I Geraniaceae Geranium Geranium rotandifolum L. A R III Erodium Erodium trichomanifolium L. P I II Erodium cicutarium (L.)l'her. P A II Eladiolus atropurpureus L. P F III Gladiolus italicus L. P VA III Ixiolirion tataricum L. A VR III Iridaceae Ixioliriaceae Gladiolus Ixiolirion * NOTE: P.D=Plant density, F.V= Forage Value, L.C=Life Cycle, A=Annual, B=Biannual, P=Perennial. 70 Appendix Appendix (2): Parts of Crested Wheatgrass Appendix (3): General Agro-Ecological Zones (AEZ) of Iraq (Holm et al., 2002). 1. Lowland AEZ: in the southern part of the region. Annual rainfall is between 250-600mm and topography is relatively flat between 300-600 m above sea level. The region supports a mixed dry-land farming system. There are strong interactions with pastoral systems. Livestock graze the stubble of the harvested crops and may graze the growing crops of barley in dry years. Barley grain is fed as a supplement and straw is collected and stored for feeding during winter. Otherwise, animals graze, nearly treeless areas of natural pastures (range), based mainly on annual legumes, grasses and some perennial grasses. 71 Appendix 2. Upland AEZ: in the inter-mountain areas of the central part of the region, where annual rainfall varies between 500 and 900 mm. Mixed farming systems occupy wide upland valleys. Cropping patterns are similar to the lowland system. Sheep, goats and cattle are an important component of this mixed farming system. Livestock normally graze natural pasture and waste areas within the farm during winter and then graze crop residues during summer. Animals are fed barley grain when feed resources are limited. Natural grazing land consists of mostly treeless areas on slopes with southern aspects and degraded forest coppice or forest understory on slopes with northern aspects. 3. Hill and Mountain AEZ: in the northern border areas with Turkey and Iran that characterized by steep landscapes and an annual rainfall between 800 and 1200 mm. The farming system is described as an „upland pastoral farming system‟. Two sub-systems exist, sedentary pastoral system and the nomadic pastoral system. The nomadic pastoral system is based on travel herders who seasonally move their livestock between lowland and higher mountain areas. Natural grazing land consists of restricted treeless alpine pastures 2000 m above sea level and forest understory in lower altitudes. The steeper slopes are often inaccessible to all livestock except goat. Perennial grasses are common. Some leguminous herbs are presented. Quercus sp. dominates the wooded areas. These and less dominant tree species for example Pistacia sp. and Prunus sp. provide feed for livestock during winter through ancient practices of sheaving (cutting branches for fodder). 72 Appendix Appendix (4): Plant distribution of studied area 73 Appendix Appendix (5): Seeding of Crested Wheatgrass in Soran. Appendix (6): Growth of Crested Wheatgrass in Choman. 74 Appendix Appendix (7): Spring season germination of Crested Wheatgrass in Soran. Appendix (8): Growing of Crested Wheatgrass in fall season. 75 Appendix Appendix (9): Samples of Crested Wheatgrass. Appendix (10): Chemical analysis of Crested Wheatgrass. 76 ‫ا‪ ēĥĒĉ‬ك‪ğ‬ردست‪À‬ن – العرا‪ć‬‬ ‫‪ğ‬زارة التع‪ ēĥĒ‬الع‪À‬ل‪ğ Ĥ‬البحث الع‪Ē‬م‪Ĥ‬‬ ‫ج‪À‬مع‪ Æ‬صاح الد‪ĥ‬ن – ارب‪ĥ‬ل‬ ‫الترك‪ Áĥ‬النب‪À‬ت‪ğ Ĥ‬تك‪ĥĥ‬ف نب‪ ÇÀ‬حش‪ĥ‬ش‪ Æ‬كر‪ĥ‬ستد‬ ‫)‪(Agropyron cristatum L.‬‬ ‫ف‪ Ĥ‬بعض من‪À‬ط‪ Ĉ‬مح‪À‬فظ‪ Æ‬أرب‪ĥ‬ل‬ ‫رس‪À‬ل‪Æ‬‬ ‫م‪Ċ‬دم‪ Æ‬ال‪ Ģ‬مج‪Ē‬س ك‪ ÆĥĒ‬الزراع‪ – Æ‬ج‪À‬مع‪ Æ‬صاح الد‪ĥ‬ن – ارب‪ĥ‬ل ‪ğ‬ه‪ Ĥ‬جزء من متط‪Ē‬ب‪ ÇÀ‬درج‪Æ‬‬ ‫م‪À‬جست‪ĥ‬ر ع‪ ēğĒ‬زراع‪ - Æĥ‬الغ‪À‬ب‪ -ÇÀ‬أدارة المراع‪Ĥ‬‬ ‫م‪Ğ‬ند ا‪ Áğĥ‬مصط‪ĢĆ‬‬ ‫من ‪ĉ‬بل‬ ‫بك‪À‬ل‪ğ‬ر‪ğĥ‬س – اانت‪À‬ج النب‪À‬ت‪ – Ĥ‬ك‪ ÆĥĒ‬الزراع‪ -Æ‬ج‪À‬مع‪ Æ‬صاح الد‪ĥ‬ن‪0222 -‬‬ ‫ب‪À‬شراف‬ ‫أ‪ .ē .‬س‪À‬ل‪ ē‬ص‪À‬بر معر‪ğ‬ف‬ ‫‪ 0223‬ك‪ğ‬ردى‬ ‫جم‪À‬د‪ ģ‬اا‪ğ‬ل‪ 2341 Ģ‬هجر‪ģ‬‬ ‫شب‪À‬ط ‪ 0225‬م‪ĥ‬اد‪ģ‬‬ ‫الخاص‪Æ‬‬ ‫الخاصة‬ ‫اجر‪ Çĥ‬الدراس‪ Æ‬الترك‪ Áĥ‬النب‪À‬ت‪ Ĥ‬خال ن‪ĥ‬س‪À‬ن‪ -‬ا‪Àĥ‬ر‪ 0223/‬لمعرف‪ Æ‬ت‪ğ‬ز‪ĥ‬ع النب‪À‬ت‪ ÇÀ‬ف‪ Ĥ‬الم‪ğ‬ا‪ĉ‬ع المخت‪À‬رة خ‪À‬ص‪Æ‬‬ ‫الحش‪À‬ئش ف‪ Ĥ‬شم‪À‬ل شر‪ ć‬ارب‪ĥ‬ل ب‪ĥ‬ن منط‪ ÆĊ‬حر‪ĥ‬ر‪-‬ح‪À‬ج‪ Ĥ‬عمران‪ .‬ت‪ ē‬تحد‪ĥ‬د )‪ (22‬م‪ĉğ‬ع‪ً À‬بمس‪À‬ف‪ Æ‬ب‪ĥ‬ن‪ Æĥ‬م‪Ċ‬داره‪À‬‬ ‫ح‪ğ‬ال(‪ 3-2‬ك‪ .)ē‬استعم‪ ÇĒ‬طر‪ )List Quadrate( ÆĊĥ‬ذا‪ Ç‬مس‪À‬ح‪ 0ē Æ‬بص‪ğ‬ة عش‪ğ‬ائ‪ Æĥ‬لتحد‪ĥ‬د اان‪ğ‬اع ف‪Ĥ‬‬ ‫الم‪ğ‬ا‪ĉ‬ع‪ğ .‬تتضمن الب‪Àĥ‬ن‪ ÇÀ‬نسب‪ Æ‬التغط‪ ğ Æĥ‬التكرار النب‪À‬ت‪ğ ÇÀ‬الكث‪À‬ف‪ Æ‬مع ال‪ĥĊ‬م‪ Æ‬الع‪. ÆĥĆĒ‬‬ ‫‪ĥğ‬مكن ت‪Ē‬خ‪ĥ‬ص اه‪ ē‬النت‪À‬ئج كم‪-: ĤĒĥ À‬‬ ‫‪ .‬تتبع النب‪À‬ت‪ ÇÀ‬الت‪ğ Ĥ‬جد‪ Ç‬ف‪ Ĥ‬المنط‪ ÆĊ‬المدر‪ğ‬س‪ Æ‬ال‪ )42( Ģ‬ع‪À‬ئ‪ )44(ğ ÆĒ‬جنس ‪ )223(ğ‬ن‪ğ‬ع‪ .‬تضمن الب‪ğĊ‬ل‪ÇÀĥ‬‬ ‫(‪)23‬جنس‪ )42(ğ ً À‬ن‪ğ‬ع‪ ,َÀ‬ب‪ĥ‬نم‪ À‬تتبع الحش‪À‬ئش (‪ )20‬جنس‪ )44(ğ ً À‬ن‪ğ‬ع‪.َÀ‬‬ ‫‪ .‬تب‪Ē‬غ معدل نسب‪ Æĥ‬تغط‪ Æĥ‬النب‪À‬ت‪ ÇÀ‬اارض (‪ )%22.35‬ف‪ Ĥ‬المنط‪ ÆĊ‬كم‪ À‬تب‪Ē‬غ هذة النسب‪ Æ‬ل‪Ē‬ترب‪ Æ‬الع‪À‬ر‪ğ Æĥ‬النث‪À‬ر‬ ‫‪ğ‬الصخ‪ğ‬ر (‪ )%4.54( ğ )%22.24( ğ )%3.30‬ع‪ ĢĒ‬الت‪ğ‬ال‪.Ĥ‬‬ ‫‪ .‬ك‪À‬ن‪ Ç‬نسب‪ Æ‬النب‪À‬ت‪ ÇÀ‬ذا‪ Ç‬ال‪ĥĊ‬م‪ Æ‬الع‪ ÆĥĆĒ‬الع‪À‬ل‪ğ Æĥ‬المت‪ğ‬سط‪ğ Æ‬ال‪ğ‬اطئ‪ )%22.52(ğ )%44.44(ğ )%52.22( Æ‬ع‪ĢĒ‬‬ ‫الت‪ğ‬ال‪.Ĥ‬‬ ‫‪ .‬ب‪Ē‬غ‪ Ç‬معدل الع‪À‬ئ‪ ÆĒ‬الب‪ğĊ‬ل‪ğ Æĥ‬النج‪ğ ÆĥĒĥ‬ب‪ ÆĥĊ‬الع‪ğ‬ائل كم‪ .)%54.34( ğ )%02.23( ğ )%23.22 ( ĤĒĥ À‬اع‪ĢĒ‬‬ ‫النسب‪ Æ‬ك‪À‬ن‪ Ç‬ل‪Ē‬ع‪À‬ئ‪ ÆĒ‬ب‪ğĊ‬ل‪ )% 04.22( Æĥ‬ف‪ Ĥ‬ج‪ğ‬م‪À‬ن ‪ğ‬الع‪À‬ئ‪ ÆĒ‬نج‪ )% 44.44( ÆĥĒĥ‬ف‪ Ĥ‬سم‪ĥ‬ان‪.‬‬ ‫‪ .‬ك‪À‬ن‪ Ç‬الكث‪À‬ف‪ Æ‬النسب‪ Æĥ‬اع‪ )%5.02( ĢĒ‬ف‪ Ĥ‬نب‪ )%3(ğ Hordeum murinum spp.Gloucum ÇÀ‬ف‪Ĥ‬‬ ‫‪ğ Hordeum bulbosum‬ك‪À‬ن‪ Ç‬ا‪ĉ‬ل ‪ĥĉ‬مت‪ )%2.20( ÀĞ‬ف‪Linaria vulgaris, Alceae kurdica Ĥ‬‬ ‫‪ .‬ب‪Ē‬غ‪ Ç‬اع‪ ĢĒ‬نسب‪ Æ‬التكرار (‪ )%25.4‬ف‪ Ĥ‬نب‪ Hordeum bulbosum. ÇÀ‬ث‪ĥĒĥ ē‬ه نب‪Notobasis syrica ÇÀ‬‬ ‫‪Erodium trichomanifolium,‬‬ ‫(‪ )%24.1‬ب‪ĥ‬نم‪ À‬ك‪À‬ن‪ Ç‬ا‪ĉ‬ل نسب‪ Æ‬التكرار (‪ )%2.2245‬ف‪ Ĥ‬النب‪ÇÀ‬‬ ‫‪.Galium murale, Anemon coronaria.‬‬ ‫ام‪ À‬بنسب‪ Æ‬لدراس‪ Æ‬تك‪ĥĥ‬ف نب‪ ÇÀ‬حش‪ĥ‬ش‪ Æ‬كر‪ĥ‬ستد ف‪Ċ‬د اجر‪ Çĥ‬هذه الدراس‪ Æ‬ف‪ Ĥ‬ج‪ğ‬م‪À‬ن ‪ ğ‬س‪ğ‬ران ال‪ğ‬ا‪ĉ‬عت‪À‬ن ف‪Ĥ‬‬ ‫منط‪ ÆĊ‬الغ‪À‬ب‪ğ ÇÀ‬ف‪ Ĥ‬م‪ğ‬سم‪ĥ‬ن الخر‪ĥ‬ف ‪ğ‬الرب‪ĥ‬ع‪ .‬تم‪ Ç‬دراس‪ Æ‬ف‪ Ĥ‬تشر‪ĥ‬ن الث‪À‬ن‪ Ĥ‬حت‪ Ģ‬ا‪Àĥ‬ر ‪ 0223‬ع‪ ĢĒ‬بعض ص‪ÇÀĆ‬‬ ‫الجزء الخضر‪ğ ģ‬الجذر‪ ģ‬ل‪Ē‬نب‪ ÇÀ‬كذل‪ ċ‬بعض التح‪ĥĒ‬ا‪ Ç‬ك‪ĥ‬م‪Àĥ‬ئ‪ Æĥ‬له‪ .‬طب‪ Ĉ‬تصم‪ ēĥ‬ال‪Ċ‬ط‪À‬ع‪ ÇÀ‬العش‪ğ‬ائ‪ Æĥ‬الك‪À‬م‪ÆĒ‬‬ ‫)‪ (RCBD‬ف‪ Ĥ‬ثم‪À‬ن‪ Æĥ‬ل‪ğ‬ح‪ Æ‬لكل م‪ĉğ‬ع ب‪À‬ربع مكررا‪ .Ç‬ضمن‪ Ç‬الدراس‪ Æ‬نسب‪ Æ‬اانب‪ ğ ÇÀ‬اادغ‪À‬ل ‪ğ‬بعض ص‪ ÇÀĆ‬النم‪ğ‬‬ ‫مثل ‪ğ‬زن الخضر‪ğ ģ‬الجذر‪( ģ‬الطر‪ğ ģ‬الج‪À‬ف) ‪ğ‬ط‪ğ‬ل الخضر‪ ģ‬الجذر‪ğ ģ‬نسبت‪.ÀĞ‬كذل‪ ċ‬غط‪ Ç‬الدراس‪ Æ‬التح‪ĥĒ‬ل‬ ‫الك‪ĥ‬م‪ ģğÀĥ‬كت‪Ċ‬د‪ĥ‬ر م‪À‬دة الج‪À‬ف‪ğ Æ‬نسب‪ Æ‬اال‪Àĥ‬ف ‪ ğ‬بر‪ğ‬ت‪ĥ‬ن ‪ ğ‬مستخ‪Ē‬ص الده‪ğ‬ن ‪ ğ‬الن‪ĥÀ‬تر‪ğ‬ج‪ĥ‬ن حرة‪.‬‬ ‫‪ğ‬ادن‪À‬ه م‪Ē‬ح‪ Ĉ‬أه‪ ē‬النت‪À‬ئج‪-:‬‬ ‫ سج‪ ÇĒ‬م‪ĉğ‬ع س‪ğ‬ران اع‪ ĢĒ‬نسب‪ Æ‬اانب‪ ,)%10.04(ÇÀ‬ب‪ĥ‬نم‪ À‬ك‪À‬ن‪ĥĉ Ç‬م‪ Æ‬ص‪ ÇÀĆ‬النم‪ ğ‬اع‪ ĢĒ‬ف‪ Ĥ‬م‪ĉğ‬ع ج‪ğ‬م‪À‬ن ‪ğ‬ل‪ē‬‬‫تسجل فر‪ ÇÀĉğ‬معن‪ Æĥğ‬ف‪ Ĥ‬ط‪ğ‬ل الخضر‪ ğ ģ‬الجذر‪.ģ‬‬ ‫ ب‪Ē‬غ‪ Ç‬اع‪ ĢĒ‬نسب‪ Æ‬اانب‪ ÇÀ‬ف‪ Ĥ‬الزراع‪ Æ‬الرب‪ĥ‬ع‪ )%22.42( Æĥ‬ب‪ĥ‬نم‪ À‬اد‪ Ç‬الزراع‪ Æ‬الخر‪ ÆĥĆĥ‬ال‪ Ģ‬تسج‪ĥ‬ل اع‪ ĢĒ‬نسب‪Æ‬‬‫الص‪ ÇÀĆ‬الن‪À‬م‪ğ Æĥ‬ل‪ĥ ē‬ظ‪Ğ‬ر هذا الت‪À‬ث‪ĥ‬ر ف‪ Ĥ‬ط‪ğ‬ل النب‪.ÇÀ‬‬ ‫ ‪ĥ‬ب‪ĥ‬ن مع‪À‬م‪ ÆĒ‬التداخل ب‪ĥ‬ن الم‪ĉğ‬ع ‪ğ‬الم‪ğ‬س‪ ē‬ب‪À‬ن الزراع‪ Æ‬الرب‪ĥ‬ع‪ Æĥ‬ف‪ Ĥ‬م‪ĉğ‬ع س‪ğ‬ران ل‪ ÀĞ‬اع‪ ĢĒ‬نسب‪Æ‬‬‫اانب‪ )% 32.45(ÇÀ‬ب‪ĥ‬نم‪ À‬اد‪ Ç‬الزراع‪ Æ‬الخر‪ ÆĥĆĥ‬ال‪ Ģ‬اع‪ĥĉ ĢĒ‬م‪ Æ‬ف‪ Ĥ‬ال‪ğ‬زن الطر‪ ğ ģ‬الج‪À‬ف ل‪Ē‬جزء الخضر‪ğ ģ‬‬ ‫الجذر‪ğ ģ‬ل‪ ē‬تظ‪Ğ‬ر ال‪Ć‬ر‪ ÇÀĉğ‬المعن‪ Æĥğ‬ف‪ Ĥ‬ط‪ğ‬ل الخضر‪ ģ‬الجذر‪ģ‬‬ ‫أ‬ ‫الخاص‪Æ‬‬ ‫ اظ‪Ğ‬ر التح‪ĥĒ‬ل الكم‪ ģğÀĥ‬اختافأ معن‪ĥğ‬أ ف‪ Ĥ‬الم‪ĉğ‬ع‪ĥ‬ن ‪ ğ‬الم‪ğ‬سم‪ĥ‬ن‪.‬‬‫ سج‪ ÇĒ‬م‪À‬دة الج‪À‬ف‪ Æ‬ف‪ Ĥ‬النب‪ ÇÀ‬الحش‪ĥ‬ش‪ Æ‬الحنط‪ Æ‬اع‪ĥĉ ĢĒ‬م‪ Æ‬ف‪ Ĥ‬الزراع‪ Æ‬الخر‪ ÆĥĆĥ‬ف‪ Ĥ‬ج‪ğ‬م‪À‬ن (‪ ,)%00.50‬ب‪ĥ‬نم‪À‬‬‫ف‪ Ĥ‬الزراع‪ Æ‬الرب‪ĥ‬ع‪ Æĥ‬ف‪ Ĥ‬س‪ğ‬ران سج‪ ÇĒ‬اع‪ ĢĒ‬نسب‪ Æ‬الرم‪À‬د (‪.)%23.2‬اع‪ĥĉ ĢĒ‬م‪ Æ‬ل‪Ē‬بر‪ğ‬ت‪ĥ‬ن ك‪À‬ن‪ Ç‬ف‪ Ĥ‬الزراع‪Æ‬‬ ‫الخر‪ ÆĥĆĥ‬ف‪ Ĥ‬س‪ğ‬ران (‪ ğ )%21.03‬ج‪ğ‬م‪À‬ن (‪ .)%25.42‬ب‪ĥ‬نم‪ À‬سج‪ ÇÀ‬اال‪Àĥ‬ف الخ‪À‬م‪ Æ‬اع‪ ĢĒ‬ال‪ĥĊ‬م‪ Æ‬ف‪ Ĥ‬الزراع‪Æ‬‬ ‫الرب‪ĥ‬ع‪ Æĥ‬ف‪ Ĥ‬س‪ğ‬ران ‪ ğ‬ج‪ğ‬م‪À‬ن (‪ )%21.22(ğ)%22.13‬ح‪ĥ‬ثم‪ À‬سج‪ ÇĒ‬مستخ‪Ē‬ص اا‪ĥ‬ثر اع‪ĥĉ ĢĒ‬مت‪ ÀĞ‬ف‪ Ĥ‬الزراع‪Æ‬‬ ‫الخر‪ ÆĥĆĥ‬ف‪ Ĥ‬س‪ğ‬ران ف‪Ċ‬ط ‪ğ‬اع‪ĥĉ ĢĒ‬م‪ Æ‬ل‪Ē‬ن‪À‬تر‪ğ‬ج‪ĥ‬ن الحرة سجل ف‪ Ĥ‬الزراع‪ Æ‬الرب‪ĥ‬ع‪ğ Æĥ‬الخر‪ ÆĥĆĥ‬لم‪ĉğ‬ع س‪ğ‬ران‬ ‫(‪.)%52.34( ğ )%53.02‬‬ ‫‪Á‬‬ (Agropyron cristatum L.) ĢĆ‫ مصط‬Áğĥ‫ند ا‬Ğ‫م‬ ‫سالم صابر معروف‬ List Quadrate . . . Hordeum murinum spp.Gloucum Linaria vulgaris, Alceae Kurdica Hordeum bulbosum Erodium Notobasis syrica trichomanifolium,Galium Murale, Anemom Coronaria RCBD A B