microcystis 中文意思是什麼

microcystis 解釋
微胞藻屬
  1. A year - rounded investigation on biomass of microcystis bloom, physiochemical factors and microcystin contents was conducted. also, the inhibitory test of microcystin on algae - lying bacteria was carried out

    對富營養化池塘中微囊藻水華的生物量、各種理化因子及微囊藻毒素進行了年度調查，並開展了微囊藻毒素抑制細菌的試驗。
  2. Water fleas daphnia magna was fed both toxic alga microcystis aeruginosa ds and nontoxic alga m. aerztginosa 573 for 7 ~ 14 days under laboratory condition

    摘要用銅綠微囊藻有毒株ds和無毒株573喂養大型? ，觀察微囊藻對蟲體的生長和繁殖的影響。
  3. During this time both the monthly average algae density and lasting time increased year after year. the main algae forming algae bloom was cyanophyta and the dominant generas were microcystis. the accumulation of nutrients ( such as total nitrogen and total phosphorus ) with high concentration, high temperature of water and strong sunshine caused the algae bloom

    結果表明，水溫較高的夏秋季（一般為7 9月）是天津市城市供水水源的藻類高發期；近幾年，高藻期含藻量呈逐年增加趨勢，持續時間呈逐年延長趨勢；高藻期水源水以藍藻為主，所佔藻類總數最高和最低比例分別為91和70 ，其中的優勢屬為微囊藻屬；水源水中高含量的氮、磷等營養鹽是藻類高發的內在因素，水溫、光照等是外在誘發因素。
  4. A strain of bloom cyanobacterium ( blue - green alga ), microcystis aeruginosa, which dominated in an eutrophic pond, was isolated and purified for physiological study in laboratory conditions. various environment factors, like light, temperature, nutrient, cu2 +, ect were tested for growth and lexicological effects of m. aeruginosa

    在純化培養的基礎上，我們開展了光照、溫度、營養鹽及cu ~ （ 2 + ）對該銅綠微囊藻生長及毒理學影響的研究。光照、溫度及營養鹽對銅綠微囊藻生長影響1
  5. Effects of pb2 on inter - specific competition of microcystis aeruginosa and chlamydomonas reinhaidtii

    對衣藻和微囊藻種間競爭的影響
  6. It was suggested that the ecological function of toxin - producing was most likely inhibiting the growth of other organisms so as to resuming growth of microcystis and further, forming a new bloom

    微囊藻產毒受營養條件、水溫和生物量的影響較大；產毒的生態功能很可能是抑制其他生物生長，恢復種群優勢。
  7. The result shows : microcystis produced all 3 variants of microcystin, but the content of mc - rr was much larger than mc - lr and mc - yr. in most cases, mc - yr content was rather low for hplc analysis

    結果表明，富營養化池塘中微囊藻均產生3種異構體，但mc - rr的含量遠大於其他兩種異構體， mc - yr在全年中檢出率很低。
  8. The toxicity peaks always lagged the growth peaks, furthermore, the greater the biomass, the longer the lagging days. both mc - rr and mc - lr gave rise to their maximum value at the end of every single bloom and soon after a new bloom began. in general, the ratio of mc - rr and mc - lr remained comparatively constant during every bloom, but no obvious change characteristic was observed on mc - yr content. in the discussion, in was found that toxin - producing of microcystis was related to biomass, nutrients and water temperature

    分析各個階段的水華，我們發現毒性峰總是滯後於生長峰，且生物量越大，滯后的時間越長； mc - rr與- lr的含量在每個階段水華的末期達到最大，之後新一輪的水華開始出現，並且mc - rr與- lr的比例保持基本恆定，但是mc - yr的變化無明顯的規律。
  9. Concretely, the growth of bacteria taking advantage of nutrients after cell broken of microcystis was inhibited by maximal microcystins, thus, it was superior for the algae to uptake the released nutrients and recovered from the compacting environments

    特別是在水華消退、細胞解體時產毒量達到最大，這可能是為了阻止細菌利用釋放的營養物質進行增殖，而使藻自身重新利用營養物質，實現生長的優勢。
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