layer community 中文意思是什麼

layer community 解釋
層別群集
  • layer : n 1 放置者,鋪設者,計劃者。2 【賽馬】(一般)賭客。3 產卵的雞。4 【軍事】瞄準手。5 層;階層;地...
  • community : n. 1. 村社;社會,集體;鄉鎮,村落;【生物學】群落,群社。2. 共有,共用;共同體,共同組織;聯營(機構)。3. 共(通)性;一致(性);類似性。
  1. They are jinfo mountain in nanchuan county ( natural protection section ), wuling mountain in qianjiang county ( national emphases forest demonstration county which forest cover rate is beyond 50 % ) and zhongliang mountain in beibei county ( artificial destruction is very grave ). some main land use patterns i. e. woodland, garden, infield, abandon infield, shrub and grassplot are selected in those three sample sites. four aspects on soil fertility index of karst environment under different land use patterns in these three sample sites, are revealed in this paper, by using the field test, indoor measure and analysis, outdoor experiment and field investigation, and the knowledge and technique of soil, ecology, physics and chemistry etc. they are physical characteristic ( effective soil thickness, organic layer thickness, soil texture, water - stable aggregate and soil water etc. ), chemical fertility ( organism, omni - n, omni - p, omni - k, alkali - nitrogen, available p, available k and rapid available k etc. ), soil animalcule ( bacteria, fungi, actinomyces and their grosses ) and soil - seed - pool ( plant community diversity index ) in karst ecosystem

    本研究以重慶市的南川金佛山(自然保護區) 、黔江武陵山(國家重點退耕還林示範縣,森林覆蓋率50以上)和北碚中梁山(遭人為破壞嚴重)典型巖溶區為對象,選擇了幾種重要的利用方式,包括林地、果園、耕地、棄耕地和灌草坡,採用野外巖溶生態調查和室內試驗測量分析相結合的方法,以不同土地利用方式巖溶土壤肥力為重點,對不同土地利用方式土壤肥力特徵進行量化分析,找出巖溶土壤肥力差異的主要方面及其根本原因,論文主要從土壤剖面物理退化指標(有效土層厚度、有機質層厚度、質地、團聚體、水分含量等) ,化學肥力退化指標(有機質、全n 、全p 、全k 、堿解n 、速效p和速效k等) ,樣地土壤微生物指標(細菌、真菌、放線菌數量及總量)以及樣地土壤種子庫植物群落多樣性等4個方面對重慶典型巖溶區的土壤肥力特徵進行了較為詳細的分析研究,為巖溶地區士壤資源的合理利用及結構的調控管理提供依據。
  2. The vertical structure of each forest community were obvious and could be divided into tree layer, shrub layer, herbage layer and lianas

    各群落垂直結構十分明顯,可分為喬木層、灌木層、草本層和層間植物。
  3. At the same time from the deep layer mental state that the farmer settle the community to set out, bring up the policy of the cowgirl the suggestion, and point out the farmer to settle the area should still the appropriate considerations is not permanent setting area exist of possibility

    以及從農民安置群體的深層心理出發,提出相應的政策建議,指出農民安置區還應適當考慮非永久性安置區存在的可能。第四章是對「原生態」鄉土方言的總結與實踐,並給出單體與組團示例。
  4. Special landform condition accomplishes extremely characteristic space relationship of landform, plant and water, and water goes down continually along the layer stone, building dynamic and capricious waterscape, luxuriant plant community forms green barrier, increasing the ecology effect of garden region

    特殊的地形環境成就極具特色的地形、植物與水的空間關系,水體順疊砌的整石源源不斷的跌落,營造動態多變的水景,茂密的植物群落形成綠色屏障,更增添園區的生態效果。
  5. According to the sample area survey ; there are 120 species of plants belonging to 84 gener 47families in the 25 - year - old chinese fir plantation community which will succeed toward the direction simi - ler to the community type before the felling of evergreen broadleaved forest if it is let to develop naturally or the logging residues are not burnt after the felling of the chinese fir plantation due to the superiority of cas - tanopsis carlesii and schima superba in the aspling layer in it

    據樣地調查,該25年生杉木人工林群落的植物有41科84屬120種,群落的外貌特徵以包括藤本在內的高位芽占絕對優勢,葉特徵以革質,單葉,中小型葉為主,由於該群落的幼樹層以米儲和木荷等占優勢,若讓其自然發展或杉木林採伐后不煉山,並排除其它人為干擾,該群落將向與常綠闊葉林採伐前的群落類型相似的方向演替。
  6. The research result is following : the annual species richness index of studied forest plant community averaged 64. 688, the species diversity index was 2. 982. the proportion of every functional group of forest plant community is : herbaceous layer ( average is 68. 89 % ) > tall tree layer ( average is 15. 266 % ) > shrub layer. ( average is 15. 845 % ) the proportion of every functional group in forest insect communities is remarkably different, and the order of the proportion is herbivorous insect group ( average 0. 729 ) > predatory natural enemy insect group ( average 0. 136 ) > parasitical insect group ( average 0. 135 ). with seasonal change, the proportion of herbivorous and predatory insect group decreased obviously, while that of parasitical insect group increased on average by 147 %

    研究結果如下:森林植物群落種的全年物種豐富度指數平均為64 . 688種,多樣性指數為2 . 982森林植物群落內各功能類群物種所佔比重依次為:草本層(平均為68 . 89 ) >喬木層(平均為15 . 266 )灌木層(平均為15 . 845 ) 。森林昆蟲群落中,全年各功能類群所佔比重以植食性昆蟲類群為最大,平均佔0 . 729 ;捕食性昆蟲類群次之,平均佔0 . 136 ;寄生性天敵類群為最小,平均為0 . 135 。
  7. In 0 - 200cm light dried layer was formed and can be recovered partly after rainfall, but beneath 200cm the serious perpetual dried layer has lower water content and larger thickness and is very difficult to be recovered in short period because of the special hydrological characteristics in the loess plateau where infiltration depth is about 200cm and could not percolate into deeper layer. ( 4 ) the landscape ecology in fuxian county shows that the two kinds of forest community have not declined

    ( 4 )富縣天然山楊林和天然遼東櫟林的景觀生態特徵表明,兩類森林群落沒有出現衰退的跡象,這說明森林群落合理的內部結構不會造成林地土壤水分的嚴重虧缺,其自然氣候條件可以滿足森林群落生存、發展的需要。
  8. At first, the relations between vegetation structures and their controlling soil erosion are discussed. the results show that magnitude of plant community coverage or canopy closure is n ' t certainly the adequate condition of an anti - erosive effective community because the community function of soil and water conservation is related to height of coverage layer as well as community coverage or canopy closure

    首先,討論了植被結構與其防止土壤侵蝕作用的關系,結果表明,植被蓋度或郁閉度的大小並不一定就是防蝕有效植被的充分條件,植被保持水土功能還與覆蓋層的高度密切相關,覆蓋層高度大並不有利於植被保持水土。
  9. Analysis on the species richness and diversity index, community evenness in different plots and layers of evergreen broad - leaved forest in shiyang forest center in wencheng, zhejiang province resulted that species richness and diversity index, community evenness of the second sublayer of tree layer was much greater than that of the first sublayer in the vertical structure of the community

    對文成縣石?林場常綠闊葉林的不同樣地、不同層次的物種豐富度、物種多樣性指數和群落均勻度進行了分析,結果表明:在群落垂直結構中,喬木層第2亞層的物種豐富度、物種多樣性指數、群落均勻度顯著大於第1亞層。
  10. The results shows that the community richness, species diversity indices and evenness of tree layer and shrub layer share the same order, of which is higher in pure limestone region than that of in pure dolomite region, but it reverse in herb layer ; the coefficient of similarity is considerably low between all plots, while species turnover rate is quite high among the plots and is higher in dolomite region than that of in limestone ; in different karst regions, karst processing leads to niches diversity characterized by special morphologies and special element geochamical features, and therefore affect the dynamic and features of plant communities

    我們在最有代表性之一的貴州茂蘭喀斯特森林保護區選取純灰巖和純白雲巖兩種巖性的喀斯特環境,對其元素地球化學特徵及其中原生性植物群落的相異性和物種多樣性進行了對比,結果發現:不同巖性區域多樣性:喬木層和灌木層為純灰巖區純白雲巖區,草本層為純白雲巖區純灰巖區,總體上純灰巖區的高於純白雲巖區的;各樣地間的相似性系數都很低,相同巖性類型內的明顯高於不同巖性類型之間的相似度;物種周轉率高,且白雲巖區高於石灰巖區,種類組成差異明顯;喀斯特區可溶巖地球化學背景通過喀斯特作用導致特殊的地形條件與元素地球化學特徵,並引起局部小生境的分異從而影響植物群落特徵。
  11. There were 83 species in the community 4 ( castanopsis sclerophylla - camellia oleifera - maesa japonica community ), and castanopsis sclerophylla, castanopsis fargesii and schima superba were the dominant species of tree layer, and camellia oleifera, itea chinensis and symplocos sumuntia were the dominant species of succession layer, and maesa japonica was the absolute dominant species of regeneration layer. there were 76 species in the community 5 ( castano

    用物種重要值代替物種多度來測定物種多樣性,結果表明: margalef豐富度指數隨著群落層次的物種數增加而增加,與群落各層次的個體數無關,各群落的喬木層的simpson多樣性、 shannon一wiener多樣性、 simpson均勻度、 shannon一wiener均勻度4個指數一般小於其演替層的相應指數,演替層與更新層的相應指數之間無必然大小關系。
  12. There were 88 species in the community l ( castanopsisfargesii - symplocossumuntia - acidosasa longiligula community ), and castanopsis fargesii, castanopsis carlesii and schima superba were the dominant species of tree layer, and symplocos sumuntia and acidosasa longiligula were respectively the dominant species of succession layer and regeneration layer

    各群落中有許多層間植物黃茵嶺生態保護小區常綠闊葉林生態特徵研究?藤本,主要有網脈酸藤子、香花崖豆藤、菠葵等。
  13. There were 71 species in the community 2 ( castanopsis fargesii - itea chlnensis - maesa japonica community ), and castanopsis fargesii and itea chinensis were respectively the absolute dominant species of tree layer and succession layer, maesa japonica was the dominant species of regeneration layer

    群落次生天然演替過程是以地帶性植被殼斗科、茶科、冬青科等物種為主。總體上黃茵嶺生態保護小區群落種子植物屬的分佈類型是以熱帶分佈成分佔絕對優勢,種子植物以熱帶起源為主。
  14. In preliminary vegetation succession from abandoned land community to herbage community, the increasing degree is higher. and with further succession which is herbage - shrub - early forest - liaotungesis forest community it goes down gradually. ( 2 ) the water content in 0 - 5cm soil layer increases significantly and the water content in > 5cm soil layer decreases in the course of vegetation succession

    演替初期(棄耕-地先鋒群落草本群落)有機碳含量的增加幅度較大,而後,隨植被的進一步演替(草本群落灌叢群落早期森林群落遼東櫟群落) ,有機碳含量增加幅度變小。
  15. Main results are summarized as follows. ( 1 ) the content of soil organic c in 0 - 25cm soil layer increases significantly in the course of vegetation succession from abandoned land to liaotungesis forest community. but the content of soil organic c in > 25cm layer does n ' t change obviously ( 3 ~ 4g kg - 1 )

    主要結果如下: ( 1 )從棄耕地到頂極群落(遼東櫟群落)的正向演替過程中, 0 25cm土層的土壤有機碳含量顯著增加,但25cm以下土層有機碳含量基本一致( 3 4gkg ~ ( - 1 ) ) 。
  16. There were 66 species in the community 3 ( castanopsis fargesii + schima superba - itea chinensis - maesa japonica community ), and castanopsis fargesii and schima superba were the dominant species of tree layer, and itea chinensis and symplocos sumuntia were the dominant species of succession layer, and maesa japonica and ardisia japonica was the dominant species of regeneration layer

    採用物種數、 m雌alef豐富度指數、 simpson和shannon一wiener多樣性指數、 simpson和shannon一wiener均勻度指數對黃茵嶺生態保護小區森林群落多樣性進行測定,結果表明該地區有較高的物種多樣性。
  17. The community structure of ultraphytoplankton is very different in autumn and spring concluded by data comparison of two cruises. the cell density of synechococcus in autumn is significantly higher than that in spring. during autumn cruise a high value synechococcus density was observed by flow cytometry in upper layer of e2 and e6, which was 25

    秋季及春季航次結果表明兩季節超微型浮游植物群落結構有很大不同,秋季各站位聚球藻密度明顯高於春季,秋季在黃海e2站的上混合層、東海e6站表層均檢測到密度高值,最高分別達25 . 73 10 ~ 4cells ml 、 15 . 92 10 ~ 4cells ml ,而在春季時聚球藻密度較大值是在東海e6 、 p2站,但在表層僅為2 . 46 10 ~ 4和2 . 01 10 ~ 4cells ml ,其餘站位平均值均在1 . 00 10 ~ 4cells ml以下。
  18. Compared to non - tourist areas, in recreational areas, the number of plant species and coverage of vegetation in arbor layer and shrub layer decreased and the composition and community structure of vegetation trended to be simple. at the same time, regeneration of vegetation were suppressed

    景點活動區與背景區相比:喬木層、灌木層植物種數及蓋度減少,群落組成及結構趨向簡單化,更新受抑,草坪生物量、高度、蓋度明顯受到沖擊。
  19. With the functions of high - rise buildings becoming more and more diversified, general structions can not meet the rigidity, intensity, ductility of the modern constructions. now there are some engineer ing cases, in which, the change of column grid between the standard layer upper part and community services layer under part could accomplished by the structural transfer floor

    隨著現代高層建築功能的日趨復雜,常規結構已不能滿足剛度、強度及延性的要求,將上部標準層的小柱網變為下部公共服務層的大柱網,設置結構轉換層,目前在國內已有一些工程實踐。
  20. So, we put forward the concept of " fit to reside in " just by building up a kind of walking space of much proper and many ideas so as to break single transportation function of exterior space of previous living community. so that we can cause the activities and intercourses of residents in walking space area, shape an interact and parallelism between the walking space which contains abundant layer and contents and diversified lives of residents, further build up the approbation of the residents to live area thus

    所以,我們提出「適宜居住性」概念,就是通過建立一種多適、多意的步行空間,打破以往居住社區外部空間單一的交通功能,從而引發居民在步行空間領域的活動與交往,讓具有豐富層次和內容的步行空間與居民多樣化、多元化的生活形成一種互動與對應,從而進一步建立居民對住區的認同。
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