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浮游植物熒光儀Phyto-PAM

簡(jiǎn)要描述:浮游植物熒光儀Phyto-PAM可對(duì)自然水樣中發(fā)浮游植物自動(dòng)分類(lèi)、自動(dòng)測(cè)葉綠素含量和光合活性的調(diào)制熒光儀,三探頭可選。

  • 更新日期:2024-11-11
  • 訪  問(wèn)  量: 14503

詳細(xì)介紹

  浮游植物熒光儀Phyto-PAM款可自動(dòng)對(duì)浮游植物分類(lèi)的熒光儀
 
  schreiber教授因發(fā)明pam系列調(diào)制葉綠素?zé)晒鈨x而獲得首屆光合作用協(xié)會(huì)(ispr)創(chuàng)新獎(jiǎng)
 
  1983年,walz公司*科學(xué)家、德國(guó)烏茲堡大學(xué)的ulrich schreiber教授設(shè)計(jì)制造了**臺(tái)調(diào)制熒光儀——pam-101/102/103,并在植物生理、生態(tài)、農(nóng)學(xué)、林學(xué)、水生生物學(xué)等領(lǐng)域得到廣泛應(yīng)用,出版了大量高水平研究文獻(xiàn)。但該儀器由于采用光電二極管為檢測(cè)器,因此只能檢測(cè)高等植物、室內(nèi)培養(yǎng)的微藻等葉綠素含量較高(> 10 mg l-1)的樣品。
 
  在pam-101/102/103出現(xiàn)的同時(shí),schreiber教授就有了設(shè)計(jì)一臺(tái)多波長(zhǎng)調(diào)制熒光儀的構(gòu)想。1988年,schreiber教授和他的博士后kolbowski博士*次設(shè)計(jì)出了16波長(zhǎng)(led)熒光分光光度計(jì)。
 
  1995年,schreiber教授和kolbowski博士一起設(shè)計(jì)出了**臺(tái)可對(duì)浮游植物自動(dòng)分類(lèi)的調(diào)制葉綠素?zé)晒鈨xphyto-pam。phyto-pam采用調(diào)制技術(shù),利用4種不要波長(zhǎng)的led作為光源,利用光電倍增管作為檢測(cè)器,可以對(duì)水樣中的藍(lán)藻、綠藻、硅藻/甲藻自動(dòng)分類(lèi),并分別測(cè)量它們的葉綠素含量和光合活性。
 
  phyto-pam由于采用光電倍增管作為檢測(cè)器,因此檢測(cè)限達(dá)到 0.1
 
  μg l-1 chl。根據(jù)研究對(duì)象和研究目的不同,可有3套系統(tǒng)供您選擇。
 
  phyto-pam是水域生態(tài)學(xué)、海洋與湖沼學(xué)、水質(zhì)監(jiān)測(cè)等領(lǐng)域的有效工具。
 
  系統(tǒng)描述:
 
  脈沖-振幅-調(diào)制(pulse-amplitude-modulation, pam)技術(shù)的測(cè)量原理是基于對(duì)調(diào)制測(cè)量光激發(fā)的熒光信號(hào)的選擇性放大。在phyto-pam浮游植物熒光儀中,微秒級(jí)的測(cè)量光脈沖是由4種不同顏色的發(fā)光二極管(led)陣列發(fā)出的:藍(lán)色(470 nm)、綠色(520 nm)、淺紅色(645 nm)和深紅色(665 nm)。不同顏色的測(cè)量光脈沖在高頻率下交替應(yīng)用,就可以獲得4種波長(zhǎng)的光激發(fā)出的半同步的熒光信號(hào)。結(jié)合不同藻類(lèi)的參考光譜(reference spectrum)就可區(qū)分不同藻類(lèi),并分別測(cè)量它們的光合活性和葉綠素含量。
 
  phyto-pam可以對(duì)藍(lán)藻、綠藻和硅/甲藻進(jìn)行分類(lèi)。由于硅藻和甲藻的色素組成差別不大,目前技術(shù)上還很難對(duì)它們進(jìn)行區(qū)分。要想對(duì)它們區(qū)分,除了考慮色素組成外,更重要的是考慮捕光色素-蛋白復(fù)合體的結(jié)構(gòu)特別是橫向截面積,這必須結(jié)合“泵”和“探針”法測(cè)量熒光。目前walz公司正結(jié)合“泵”和“探針”法開(kāi)發(fā)對(duì)微藻分類(lèi)更多、更精確的儀器。phyto-pam還可以測(cè)量這些藻類(lèi)的葉綠素濃度(檢測(cè)限為0.1
 
  μg l-1 chl)。phyto-pam更加強(qiáng)大的功能是可以探測(cè)自然水樣中藍(lán)藻、綠藻和硅/甲藻的光合活性和光適應(yīng)狀態(tài)。
 
  phyto-pam采用微型光電倍增管作為檢測(cè)器,可以檢測(cè)及其微弱的靈敏變化,同時(shí)還具備強(qiáng)光自動(dòng)關(guān)閉的保護(hù)功能,因此儀器操作和維護(hù)更加容易。
 
  特點(diǎn):
 
  1) 可對(duì)浮游植物自動(dòng)分類(lèi)的調(diào)制葉綠素?zé)晒鈨x
 
  2) 4波長(zhǎng)光源:470、520、645和665 nm
 
  3) 對(duì)藍(lán)藻、綠藻和硅/甲藻進(jìn)行分類(lèi)
 
  4) 可選配室內(nèi)系統(tǒng)(i)、野外系統(tǒng)(ii)和測(cè)附著藻類(lèi)/大型藻類(lèi)的系統(tǒng)(iii)
 
  5) 靈敏度高,檢測(cè)限為0.1μg l-1 chl
 
  6) 專(zhuān)業(yè)phytowin操作軟件,數(shù)據(jù)收集、分析和存貯功能強(qiáng)大
 
  7)用戶(hù)可利用培養(yǎng)的微藻做參考光譜,非“黑匣子”
 
  8)可在野外測(cè)量后根據(jù)水體藻類(lèi)組成利用優(yōu)勢(shì)種(一種或多種)的參考光譜校對(duì)實(shí)驗(yàn)結(jié)果
 
  功能:
 
  1) 可對(duì)藍(lán)藻、綠藻和硅/甲藻自動(dòng)分類(lèi)(定性)
 
  2) 可自動(dòng)測(cè)量水樣中藍(lán)藻、綠藻和硅/甲藻的葉綠素含量(定量)和總?cè)~綠素含量
 
  3) 可同時(shí)測(cè)量水樣中藍(lán)藻、綠藻和硅/甲藻的光合作用和總光合活性
 
  4) 可測(cè)量光合作用的量子產(chǎn)量和相對(duì)電子傳遞速率
 
  5) 可自動(dòng)記錄量子產(chǎn)量和相對(duì)電子傳遞速率的快速光響應(yīng)曲線
 
  6) 用戶(hù)可做自己的參考光譜
 
  7) 可連接記錄儀或示波器記錄原始熒光誘導(dǎo)動(dòng)力學(xué)曲線
 
  應(yīng)用領(lǐng)域:
 
  浮游植物熒光儀Phyto-PAM 多用于水生生物學(xué)、水域生態(tài)學(xué)、海洋學(xué)、湖沼學(xué)、水質(zhì)監(jiān)測(cè)和預(yù)警、微藻生理學(xué)、微藻抗逆性、環(huán)境科學(xué)、生態(tài)毒理學(xué)、極地藻類(lèi)(冰藻)研究等領(lǐng)域,對(duì)于了解自然水體中藻類(lèi)種群的動(dòng)態(tài)變化、水華/赤潮預(yù)警、野外水體中光合作用的時(shí)空變化、校正初級(jí)生產(chǎn)力的計(jì)算等有較大幫助。
 
  系統(tǒng)組成:
 
  phyto-pam的主機(jī)連接不同的檢測(cè)器可以組成3套不同的測(cè)量系統(tǒng):
 
  系統(tǒng)i
 
  實(shí)驗(yàn)室版本,利用光學(xué)單元ed-101us/mp和標(biāo)準(zhǔn)10×10 mm樣品杯檢測(cè)熒光
 
  系統(tǒng)i的所有光電元件均需安裝在鐵架臺(tái)上,適合實(shí)驗(yàn)室用。但由于主機(jī)phyto-c內(nèi)置大容量電池,因此它也可以在野外或在船上使用。系統(tǒng)i的一個(gè)突出優(yōu)點(diǎn)是光學(xué)單元ed-101us/mp的開(kāi)放式設(shè)計(jì),它允許安裝不同的濾光片或不同顏色的光化光led陣列。與系統(tǒng)ii的phto-ed相比,10×10 mm樣品杯中的光場(chǎng)分布更加均勻。同時(shí),系統(tǒng)i還可以連接溫度控制器us-t和微型磁力攪拌器phyto-ms。這些特點(diǎn)決定了系統(tǒng)i更加適合浮游植物光合作用的基礎(chǔ)研究。
 
  系統(tǒng)ii
 
  野外便攜式版本,利用phyto-ed和直徑15 mm的樣品杯檢測(cè)熒光
 
  在系統(tǒng)ii中,所有光電元件都整合在便攜式的激發(fā)-檢測(cè)單元phyto-ed中。phyto-ed密封防水。系統(tǒng)ii在野外或在船上工作,當(dāng)然室內(nèi)也*可以使用。
 
  系統(tǒng)iii
 
  光纖型版本,利用phyto-edf檢測(cè)附著藻類(lèi)或大型藻類(lèi)的熒光
 
  系統(tǒng)iii的光纖型激發(fā)-檢測(cè)單元phyto-edf可以檢測(cè)所有生長(zhǎng)在表面的光合生物的光合作用。比較適合的測(cè)試材料包括附著藻類(lèi)、底棲藻類(lèi)、藻墊(microbial mats)和大型藻類(lèi)等。由于采用光纖傳導(dǎo)信號(hào)而且測(cè)量面積小,因此靈敏度比系統(tǒng)i和ii要低。但是由于附著藻類(lèi)等材料的葉綠素含量遠(yuǎn)遠(yuǎn)高于水體中的浮游植物,因此系統(tǒng)iii的靈敏度*可滿(mǎn)足實(shí)驗(yàn)要求。

● 基礎(chǔ)配置
○ 可選配置

系統(tǒng)i

(實(shí)驗(yàn)室版)

系統(tǒng)ii

(野外版)

系統(tǒng)iii

(光纖版)

主機(jī)phyto-c

測(cè)量光led陣列phyto-ml

   
光化光led陣列phyto-al

   
光電倍增管pm-101p

   
光學(xué)單元ed-101us/mp

   
工作臺(tái)st-101

   
激發(fā)-檢測(cè)單元phyto-ed  

 
光纖型激發(fā)-檢測(cè)單元phyto-edf    

微型磁力攪拌器phyto-ms

   
球狀微型光量子探頭us-sqs

溫度控制器us-t

   
攪拌器water-s  

 
 
  


















浮游植物熒光儀Phyto-PAM 技術(shù)參數(shù):
 
  測(cè)量光:波長(zhǎng)470、520、645和665 nm的測(cè)量光led。
 
  光化光:波長(zhǎng)655 nm的led;光化光強(qiáng)度0~2000 μmol m-2 s-1 par(系統(tǒng)i和ii)或0~1300 μmol m-2 s-1 par(系統(tǒng)iii)。
 
  飽和脈沖:波長(zhǎng)655 nm的led;飽和脈沖強(qiáng)度4000 μmol m-2 s-1 par(系統(tǒng)i和ii)或2600 μmol m-2 s-1 par(系統(tǒng)iii)。
 
  信號(hào)檢測(cè):光電倍增管,帶短波截止濾光片(λ>710 nm);選擇性鎖相放大器。
 
  測(cè)量參數(shù):ft, f(或fo), fm(或 fm’), δf, y(δf/ fm’或fv/fm), etr和chl濃度等。
 
  環(huán)境溫度:-5~+45 ℃,已在極地成功應(yīng)用。
 
  部分文獻(xiàn)
 
  [1] howeth jg, leibold ma. planktonic dispersal dampens temporal trophic cascades in pond metacommunities. ecology letters 2008;11 (3):245-57.
 
  [2] ingleton t, kobayashi t, sanderson b, patra r, macinnis-ng cmo, hindmarsh b, bowling lc. investigations of the temporal variation of cyanobacterial and other phytoplanktonic cells at the offtake of a large reservoir, and their survival following passage through it. hydrobiologia 2008;603 (1):221-40.
 
  [3] schmitt-jansen m, altenburger r. community-level microalgal toxicity assessment by multiwavelength-excitation pam fluorometry aquatic toxicology 2008;86 (1):49-58.
 
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  [9] dimier c, corato f, tramontano f, brunet c. photoprotection and xanthophyll-cycle activity in three marine diatoms. journal of phycology 2007;43 (5):937-47.
 
  [10] domis lnds, mooij wm, huisman j. climate-induced shifts in an experimental phytoplankton community: a mechanistic approach. hydrobiologia 2007;584:403-13.
 
  [11] kim mk, park jw, park cs, kim sj, jeune kh, chang mu, acreman j. enhanced production of scenedesmus spp. (green microalgae) using a new medium containing fermented swine wastewater. bioresource technology 2007;98 (11):2220-8.
 
  [12] schmitt-jansen m, altenburger r. the use of pulse-amplitude modulated (pam) fluorescence-based methods to evaluate effects of herbicides in microalgal systems of different complexity toxicological and environmental chemistry 2007;89 (4):665-81.
 
  [13] tang d, shi s, li d, hu c, liu y. physiological and biochemical responses of scytonema javanicum (cyanobacterium) to salt stress journal of arid environments 2007;71 (3):312-20.
 
  [14] xing w, huang w-m, li d-h, liu y-d. effects of iron on growth, pigment content, photosystem ii efficiency, and siderophores production of microcystis aeruginosa and microcystis wesenbergii current microbiology 2007;55:94-8.
 
  [15] zhang m, kong f, xing p, tan x. effects of interspecific interactions between microcystis aeruginosa and chlorella pyrenoidosa on their growth and physiology. international review of hydrobiology 2007;92 (3):281-90.
 
  [16] 張曼, 曾波. phytopam浮游植物分析儀用于微藻光合作用研究中幾種參數(shù)設(shè)定的優(yōu)化. 植物生理學(xué)通訊 2007;43 (1):148-52.
 
  [17] ban a, aikawa s, hattori h, sasaki h, sampei m, kudoh s, fukuchi m, satoh k, kashino y. comparative analysis of photosynthetic properties in ice algae and phytoplankton inhabiting franklin bay, the canadian arctic, with those in mesophilic diatoms during cases 03-04. polar biosciences 2006;19:11-28.
 
  [18] bontes bm, pel r, ibelings bw, boschker hts, middelburg jj, donk ev. the effects of biomanipulation on the biogeochemistry, carbon isotopic composition and pelagic food web relations of a shallow lake. biogeosciences 2006;3:69-83.
 
  [19] liang y, beardall j, heraud p. changes in growth, chlorophyll fluorescence and fatty acid composition with culture age in batch cultures of phaeodactylum tricornutum and chaetoceros muelleri (bacillariophyceae). botanica marina 2006;49 (2):165-73.
 
  [20] lürling m, geest gv, scheffer m. importance of nutrient competition and allelopathic effects in suppression of the green alga scenedesmus obliquus by the macrophytes chara, elodea and myriophyllum hydrobiologia 2006;556 (1):209-20.
 
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  [22] quigg a, kevekordes k, raven ja, beardall j. limitations on microalgal growth at very low photon fluence rates: the role of energy slippage photosynthesis research 2006;88 (3):299-310.
 
  [23] roessink i, belgers jdm, crum sjh, van den brink pj, brock tcm. impact of triphenyltin acetate in microcosms simulating floodplain lakes. ii. comparison of species sensitivity distributions between laboratory and semi-field. ecotoxicology and environmental safety 2006:in press.
 
  [24] bontes bm, pel r, ibelings bw, boschker hts, middelburg jj, donk ev. the effects of biomanipulation on the biogeochemistry, carbon isotopic composition and pelagic food web relations of a shallow turf lake. biogeosciences discussions 2005;2:997-1031.
 
  [25] casotti r, mazza s, brunet c, vantrepotte v, ianora a, miralto a. growth inhibition and toxicity of the diatom aldehyde 2-trans, 4-trans-decadienal on thalassiosira weissflogii (bacillariophyceae). journal of phycology 2005;41 (1):7-20.
 
  [26] fietz s, bleiß w, hepperle d, koppitz h, krienitz l, nicklisch a. first record of nannochloropsis limnetica (eustigmatophyceae) in the autotrophic picoplankton from lake baikal. journal of phycology 2005;41 (4):780-90.
 
  [27] heraud p, roberts s, shelly k, beardall j. interations between uv-b exposure and phosphorus nutrition. ii. effects on rates of damage and repair. journal of phycology 2005;41 (6):1212-8.
 
  [28] jakob t, schreiber u, kirchesch v, langner u, wilhelm c. estimation of chlorophyll content and daily primary production of the major algal groups by means of multiwavelength-excitation pam chlorophyll fluorometry: performance and methodological limits. photosynthesis research 2005;83:343–61.
 
  [29] shelly k, roberts s, heraud p, beardall j. interactions between uv-b exposure and phosphorus nutrition. i. effects on growth, phosphate uptake, and chlorophyll fluorescence. journal of phycology 2005;41 (6):1204-11.
 
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