種群的 的英文怎麼說

中文拼音 [zhǒngqúnde]
種群的 英文
clinal
  • : 種名詞(姓氏) a surname
  • : Ⅰ名詞(聚在一起的人或物) crowd; group Ⅱ量詞(用於成群的人或物) group; herd; flock
  • : 4次方是 The fourth power of 2 is direction
  1. In the present study, aflp ( amplified fragment length polymorphism ) markers was used to examine population of abies yuanbaoshanensis in order to understand the level of population genetic variation and genetic structure. the result would help to evaluate its evolutionary potentiality and the degree of being endangered and could provide scientific basis for making right protection strategy. high - quality dna was extracted using ctab method from those tender leaves of forty - three fully - developed trees in population abies yuanbaoshanensis

    本研究選用一高效檢測遺傳變異分子標記? ? aflp技術來分析元寶山冷杉種群的遺傳多樣性,旨在了解該在分佈區內遺傳變異水平和遺傳結構情況;研究結果將有助於更清楚地認識這一瀕危類生存潛力和瀕危程度,而且可以為制定何挽救和保護措施提供科學依據。
  2. The results showed that the mean proportion of polymorphic loci ( ppb ) of anabasis aphylla, which comprised 3 subpopulations ( 58 individuals sampled ), generated by 16 primers was 94. 56 %, the value of ppb of ceratocarpus arenarius, which had 4 subpopulations ( 80 individuals sampled ), using 16 primers was 98. 00 %. the paper had proved that the higher genetic diversity and the genetic differentiation existed in the populations of boih anabasis aphylla and ceratocarpus arenarius, while the latter had much more genetic diversity than the former. moreover, the study discussed the shannon information index and nei ' s gene diversity index of the two species natural populations, which indicated that there were more genetic variations within the subpopu

    另外,通過rapd資料聚類分析及相關性分析研究,發現無葉假木賊和角果藜自然種群的遺傳結構與綠洲沙漠過渡帶微生境生態因子(主要是土壤因子)相關,其中無葉假木賊亞遺傳多樣性水平不僅與土壤含水量( w ) 、鉀鈉離子濃度( k + na )和氯離子濃度( cl )呈顯著正相關( p 0 . 05 ) ,還與土壤中有機質( som ) 、全氮( nt )和全磷( pt )含量呈顯著負相關;同時,角果藜種群的遺傳多樣性水平與土壤中有機質( som )和全氮( nt )含量呈顯著正相關,而與co _ 3 ~ ( 2 - )濃度呈顯著負相關;除此之外,其它土壤生態因子與兩物遺傳多樣性水平相關性均不顯著(卜0 . 05 ) 。
  3. Form. taxus chinensis var. mairei is protecting plant in the first class, which is a precious and endangering plant in china in this paper, the quantitative characterics of form. taxus chinensis vsr. mairei population including age structure, spatial distribution pattern, growth dynamics of tree basal area, niche characterics, fractal dimension and competition between specises were studied using methods of mathematics ecology from the angle of population ecology of form. taxus chinensis var. mairei, then the prent state and the endangering causes were analysed. this research offers gist to protecting and enlarging the crude resourse of form. taxus chinensis vsr. mairei population, afforesting plantation and sustainable utilize for us

    本文從南方紅豆杉生態學角度、主要應用數學生態學方法探討南方紅豆杉種群的數量特徵,包括南方紅豆杉年齡結構、空間格局(探討分佈格局動態規律與生境相互關系) 、不同立地條件下優勢度增長趨勢、生態位寬度、生態位相似比例、生態位重疊、空間占據能力及間競爭等,分析其目前現狀及瀕危原因,期望為南方紅豆杉野生資源保護和擴大、營造人工林及可持續利用提供理論基礎,也為瀕危植物生態學研究提供參考。
  4. The growth dynamics of tree basal area of form. taxus chinensis var. mairei population in different altitude were discussed using the liu - logistic model, and the results showed that the altutide of 790 meters is more suitable to the survive of form. toms chinensis var. mairei population than 990 meters. plot sampling was selected and dynamic analysis was used to study the height structure of taxus chinensis var. mairei population, and the quadrate picture of height structure and the curve of survival rate were drew

    運用改進模型對南方紅豆杉在不同海拔梯度優勢度增長進行了探討,表明海拔790m處南方紅豆杉具有較大環境容納量,但增長速度不快,海拔990m處南方紅豆杉環境容納量不高,但具有較大增長速度,這可能與發育階段不同有關,兩地海拔均為南方紅豆杉適宜生長海拔高度,相比而言,海拔790m珍稀瀕危植物南方紅豆杉數量特徵研究高度更宜於南方紅豆杉種群的生長。
  5. The method of modified simplex was applied to optimize the models, and the fitting results show that liu - logistic model was more suitable than logistic model to the actual growth trend of form. taxus chinensis var. mairei population, and the highest growth rate of basal area was the tenth age class, namely the phase when breast diameter was 68 ~ 76 cm

    以胸高斷面積代替生物量,分別採用logistic常規模型及劉金福提出logistic改進模型對南方紅豆杉種群的增長動態進行研究,運用改進單純形法對模型進行優化,擬合結果表明改進模型比logistic常規模型更符合南方紅豆杉種群的增長趨勢,南方紅豆杉種群的最大增長速度出現在第10齡級,即胸徑為68 76cm時期。
  6. The competition among those species like s. tsinyunensis, dryopteris erythrosora and veronicastrum stenostachyum etc., is intense in the communities, which may be one of the reasons why s. tsinyunensis is going to be endangered and with a very restricted distribution. the distribution patterns of the seven populations of s. tsinyunensis are clumped among the eight populations we studied, except population v of random distribution. the spatial pattern of 6 populations of s. tsinyunensis have high consistency with the negative binominal distribution, while another 2 populations, i. e., i and iii are poisson distributions

    6 )縉雲黃芩各空間分佈格局基本呈聚集分佈,其中7個種群的分佈格局類型是聚集分佈,其聚集強度較高,另有一個為隨機分佈;其種群的離散分佈擬合結果也嚴格符合一定數學模式,其中負二項分佈、 poisson分佈分別是該物空間分佈理論分佈模式,其中6個擬合出結果是負二項分佈,i和m擬合出結果是poisson分佈。
  7. Control effect of biological agents on the diamondback moth, plutella xylostlla

    生物制劑對小菜蛾自然種群的控製作用
  8. Based on the field investigations and laboratory examinations, a study of the population of the epiphytic dolichomitriopsis diversformis ( mitt. ) nog. in fanjing mountain reveals that its habitats are different among different host trees, but that there lies the common habitat characteristics of not more than 2m height from the bottoms of host trees trunks, less light, high relative humidity, slow wind speed, slow evaporation speed and long time of remaining humid in middle - lower tree bark ; that it is one dioecious moss species, the morphology is remarkably different between its perichaetium and perigonium, the number of its perichaetia is much more than that of its perigonia, its perigonium is difficult to find out, its sporophyte is upright, its seta is long and thin, its capsule is regular long oval and its calyptra is cucullate

    摘要通過野外調查和室內觀測對貴州省梵凈山樹附生尖葉擬船葉蘚種群的研究表明,其生境因其所附生不同而有所不同,但具有共同特點:附生在樹干下部距地面2m高范圍之內,光照弱、濕度大、風速小、蒸發量小、中下部樹皮保持濕潤持續時間長;其為雌雄異株蘚,雌、雄器苞形態差異明顯,雌器苞數量多,雄器苞數量少並且難于發現,孢子體直立,蒴柄細長,孢蒴規則長卵形,蒴帽兜形。
  9. The metabolism and succession of microbial population took place ceaselessly during the fermentation and led to microbial polymorphism which mainly presented as anaerobe, methane bacteria, caproic acid bacteria, lactic acid bacteria, sulfate reducing bacteria, and nitrate reducing bacteria etc

    其微生物種群的多態性主要表現為厭氧異氧菌、甲烷菌、己酸菌、乳酸菌、硫酸鹽還原菌、硝酸鹽還原菌等。
  10. Periodic local catastrophes reduce populations.

    周期性局部地區災變降低了種群的數量。
  11. Zerg 4 : " agents of the swarm " | | - protect the chrysalis until it is | | ready to hatch. -

    蟲族4 : "種群的使者" | | -保護異蛹直到它孵化出來
  12. The populations of cathaica cavimargo are distributed in a number of heterogeneous habitats, from the hillside to the valley. these populations ( more precisely, subpopulations ) have pronounced variations in population density, shell biometric characters and shell colouration

    從山腰到山谷, cathaicacavimargo在許多異質環境中均有分佈,這些這些(或更準確地講亞密度、貝殼大小和貝殼顏色之間存在一定程度差異。
  13. Three individuals, c9904, xfi9915 and xf ] 9933, were found with more genetic diversity in current study, so it will be better to offer more copulation chance to these individuals in captive breed plan

    在飼養種群的人工選擇交配中應增加c9904 , xf _ 19915和xf _ 19933個體與其他鱷進行交配機會。
  14. The results showed that plant height, crown breadth, leaf number, leaf breadth and sporophyll number of dryopteris crassirhizoma populations were influenced by forest crown density and light condition

    結果表明:林分郁閉度和光照條件顯著影響粗莖鱗毛蕨種群的株高、冠幅、葉片數量、葉片寬度、孢子葉數等形態指標。
  15. It influences dispersion of the population.

    它影響種群的擴散。
  16. A side effect of increasing genetic variance following disruptive selection is often greater genetic flexibility of the population.

    經分裂選擇后遺傳變量增加附帶作用,往往使種群的遺傳可塑性有所增加。
  17. A side effect of increasing genetic variance following disruptive selection often causes greater genetic flexibility of the population.

    經分裂選擇后遺傳變量增加附帶作用,往往使種群的遺傳可塑性有所增加。
  18. Small changes in the gene pool of a population may actually initiate a flush.

    種群的基因庫中,微小改變均可實際地誘發一次暴長。
  19. The tiller - nodes of 6 species of rhizome grass, including leymus chinensis, hemarthriajaponica, arundinella hirta, calamagrostis epigeios, c. rigidula, hordeum brevisubulatum in songnen plain, can live at best for 2 to 5 years, and do 2 to 4 propagating generations which is the same as the age class of tiller in number. the age structure of population is an increasing model which the young tiller is more than the old at quantity and biomass. during the whole growing season, the age spectrum varies for each species

    松嫩平原,羊草、牛鞭草、野古草、拂子茅、硬拂子茅和野大麥等6根莖型禾草種群的分蘗節最多可以存活2 5個年度,可以進行營養繁殖2 4個世代,分蘗株齡級數與分蘗節營養繁殖世代數相同,在分蘗株數量和生物量上,生長季各個時期均以幼齡分蘗株占較大比例,呈現為明顯增長型年齡結構,各年齡譜組成各異。
  20. Previous researchers have always determined the sp atial distribution patterns ( sdp ) of castanopsis kawakamii with a sample - dis tance method. however, the distribution patterns may be affected by the quadrat si ze and, in the course of analysis, the density differences among the cluster plots are not considered ; therefore, differences of cluster plot size and the dispersi on degree among individuals of cluster plots can not be known. authers of this pa per have determined the spatial distribution patterns of castanopsis kawakamii population in different habitats by means of non - quadrat distance method and a nalysed the pattern intensity and grain of the sdp. the pattern intensity is defi ned with the relative density differences and the pattern grain can embody the d ispersion degree of the individuals in the plots, and the dispersion degree among the plots. the determined results are as follows. the intensities of the species range in order from strong to week : litsea mollifolia p. kawakamii i. purpure a r. cochinchinensis c. kawakamii c. carlessii d. oldphamii s. superba. the gra ins of the species queue in order from coarse to close : s. superba = litsea mollif olia r. cohinchinensis c. kawakamii = i. purpurea c. carlessii p. racemosam d. oldp hamii. these determined results tally basiclly with the results authers of this paper have got in determining the same plots by means of aggregate index access ing method. in view of this, it is held that the sdp of c. kawakamii is closely related to the habitats and biological features

    前人都是採用樣方方法對格氏栲數量空間格局進行測定,而格局分佈有可能受樣方大小影響,且分析過程中沒有涉及聚塊間密度差問題,因而無法掌握種群的聚塊大小差別及聚塊內個體間離散程度.本研究採用無樣方距離法,測定不同生境格氏栲空間格局,分析格氏栲格局強度和紋理.強度以聚塊和間隙密度差來定義,紋理則是體現聚塊內個體間離散程度與諸聚塊間分離程度.測定結果表明,格氏栲格局強度從高到低排列次序為:木姜子蚊母樹冬青茜草樹格氏栲米櫧虎皮楠木荷;格局紋理從粗到細順序是:木荷=木姜子茜草樹格氏栲=冬青米櫧蚊母樹虎皮楠.這一測定結果與作者採用聚集度指標測定相同樣地格氏栲空間格局結果基本相符.因此,格氏栲空間格局類型及分佈與格氏栲生物學特性及生境關系密切
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