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水樣調(diào)制葉綠素?zé)晒鈨x——WATER-PAM

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  • 公司名稱 上海澤泉科技有限公司
  • 品牌
  • 型號(hào)
  • 所在地
  • 廠商性質(zhì) 經(jīng)銷商
  • 更新時(shí)間 2020/11/27 18:48:03
  • 訪問次數(shù) 171

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主要功能

  • 可測熒光誘導(dǎo)曲線并進(jìn)行淬滅分析

  • 可測光響應(yīng)曲線和快速光曲線(RLC)

  • 可測量水樣的下列光合指標(biāo)活性:

  •        光合效率和光合速率(相對電子傳遞速率)

  •        藻類的潛在大光合效率(“生長潛能”)

  •        藻類的光保護(hù)能力

  • 藻類耐受強(qiáng)光的能力

  • 51 個(gè)內(nèi)置模式菜單,方便參數(shù)設(shè)置和標(biāo)準(zhǔn)測量

  • 系統(tǒng) I 用于浮游植物研究,系統(tǒng) II 用于大型藻類研究,系統(tǒng) III 用于連續(xù)監(jiān)測水體光合作用

 

測量參數(shù)

Fo, Fm, Fv/Fm, F, Fm’, Fo’, Y(II) 即 ΔF/Fm’, qP, qN, NPQ, ETR 和 PAR 等

 

應(yīng)用領(lǐng)域

測量野外自然水樣或?qū)嶒?yàn)室培養(yǎng)的微藻樣品的光合作用,三套系統(tǒng)可供選擇,可應(yīng)用于水生生物學(xué)、水域生態(tài)學(xué)、海洋學(xué)、湖沼學(xué)等領(lǐng)域,檢測限達(dá) 0.1 μgChl/L??捎糜谟泻υ迦A的早期預(yù)警。與 PHYTO-PAM 的大區(qū)別在于,WATER-PAM 不能進(jìn)行浮游植物分類。

 

主要技術(shù)參數(shù)

  • 測量光:3 個(gè)波長為 650 nm 的 LED 陣列。

  • 光化光:12 個(gè)波長為 660 nm 的 LED 陣列,大連續(xù)光強(qiáng) 2000 μmol m-2 s-1。

  • 飽和脈沖:12 個(gè)波長為 660 nm 的 LED 陣列,大閃光強(qiáng)度 4000 μmol m-2 s-1。

  • 遠(yuǎn)紅光源:3 個(gè)波長為 740 nm 的 LED 陣列。

  • 信號(hào)檢測:光電倍增管檢測器(H6779-01,Hamamatsu),過載保護(hù)功能,檢測信號(hào) λ > 710 nm。

  • 數(shù)據(jù)存儲(chǔ):CMOS RAM 128 KB,可存儲(chǔ)4000組數(shù)據(jù)。

 

選購指南

Water-PAM-1.jpg

系統(tǒng) I(主機(jī) PAM-Control 和激發(fā)-檢測單元 WATER-ED),

適合現(xiàn)場采水樣測量或室內(nèi)微藻測量
       
WATER-EDF-0060.jpg-1.jpgWATER-PAM-02.jpg

系統(tǒng)II 激發(fā)-檢測單元 WATER-EDF1.5,

適合大型海藻、附著藻類、水生植物等的測量

系統(tǒng)III 激發(fā)-檢測單元 WATER-FT,

適合隨船走航測量

  

三套系統(tǒng)的組成比較

系統(tǒng)組成
系統(tǒng)I
浮游植物版
系統(tǒng)II
附著藻類/大型藻類版
系統(tǒng)III
連續(xù)監(jiān)測版
野外現(xiàn)場或室內(nèi)測量,樣品為水樣或藻液野外現(xiàn)場或室內(nèi)測量,樣品為大型海藻、附著藻類、水生植物、苔蘚、地衣、植物葉片等 
野外現(xiàn)場或室內(nèi)測量,需要抽水上來,連續(xù)監(jiān)測光合活性
可選附件 1:攪拌器,對于易發(fā)生沉降或上浮的樣品非常重要2.jpg
可選附件 1:平面狀微型光量子探頭,用于測量樣品接收到的光強(qiáng)1.jpg 

可選附件 2:球狀微型光量子探頭,可放入系統(tǒng) I 的樣品杯中測量 PAR,也可放入水面下測量水體光場3.jpg
可選附件 2:手持式多功能 PAR 輻射儀,用于連接平面狀微型光量子探頭后,進(jìn)行獨(dú)立的光強(qiáng)測量4.jpg 

可選附件 3:手持式多功能 PAR 輻射儀,用于連接球狀微型光量子探頭后,進(jìn)行獨(dú)立的光強(qiáng)測量4.jpg




 

產(chǎn)地:德國 WALZ

 

參考文獻(xiàn)

數(shù)據(jù)來源:光合作用文獻(xiàn) Endnote 數(shù)據(jù)庫,更新至 2016 年 9 月,文獻(xiàn)數(shù)量超過 6000 篇

原始數(shù)據(jù)來源:Google Scholar

 

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Li, T., et al. (2016). "Effects of laser irradiation on a bloom forming cyanobacterium Microcystis aeruginosa." Environmental Science and Pollution Research: 1-10.

Maat, D. S., et al. (2016). "Increasing P limitation and viral infection impact lipid remodeling of the picophytoplankter Micromonas pusilla." Biogeosciences 13(5): 1667-1676.

Maat, D. S., et al. (2016). "Virus production in phosphorus limited Micromonas pusilla stimulated by a supply of naturally low concentrations of different phosphorus sources, far into the lytic cycle." FEMS microbiology ecology.

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Navarro, N. P., et al. (2016). "Stress tolerance of Antarctic macroalgae in the early life stages." Revista Chilena de Historia Natural 89(1): 1-9.

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Rantalankila, M., et al. (2016). "Inactivation of Asterionellopsis glacialis in seawater using combinations of deep ultraviolet light emitting diodes." Separation and Purification Technology.

Ritchie, R. J. and N. Mekjinda (2016). "Arsenic toxicity in the water weed Wolffia arrhiza measured using Pulse Amplitude Modulation Fluorometry (PAM) measurements of photosynthesis." Ecotoxicology and Environmental Safety 132: 178-185.

Slagter, H. A., et al. (2016). "Phytoplankton Virus Production Negatively Affected by Iron Limitation." Frontiers in Marine Science 3(156).

Strauch, S. M., et al. (2016). "Delayed fluorescence, steady state fluorescence, photosystem II quantum yield as endpoints for toxicity evaluation of Cu2+ and Ag+." Environmental and Experimental Botany 130: 174-180.

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Vadiveloo, A., et al. (2016). "Photosynthetic performance of two Nannochloropsis spp. under different filtered light spectra." Algal Research 19: 168-177.

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