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12th International Conference on Harmful Algae

12th International Conference on Harmful Algae

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INTERNATIONAL SOCIETY FOR THE STUDY OF HARMFUL ALGAE12 th <str<strong>on</strong>g>Internati<strong>on</strong>al</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>ference</str<strong>on</strong>g> <strong>on</strong> <strong>Harmful</strong> <strong>Algae</strong>, Copenhagen, Denmark, 4-8 September 2006The c<strong>on</strong>gener was identified as adeoxy GTX4-12ol lacking an oxygenatom at positi<strong>on</strong> C12. This is thefirst report of the c<strong>on</strong>gener.PO.02-09Is applicati<strong>on</strong> of quantitative-PCRpossible for measurements intoxic Microcystis populati<strong>on</strong>s?Sessi<strong>on</strong>: PO.02 - GenomicsJZ Lin, HN ChouNati<strong>on</strong>al Taiwan University, TAIPEI, TaiwanSix characteristic segments,mcyA~E, and the promoter of themicrocystin synthetase genecluster, designed in a Quantitative-PCR amplificati<strong>on</strong> were applied forquantitative measurements of toxicpopulati<strong>on</strong>s in envir<strong>on</strong>mentalsamples. Observati<strong>on</strong>s during themethod-development experimentsagainst 8 toxic and 4 n<strong>on</strong>-toxiccl<strong>on</strong>es of Microcystis were: (i) theexpected specific amplic<strong>on</strong>s werefound in all toxic cl<strong>on</strong>es but wereabsent or less abundant in n<strong>on</strong>-toxiccl<strong>on</strong>es; (ii) all the toxic cl<strong>on</strong>esshowed c<strong>on</strong>sistent Tm values ofmcyD, implying this partial mcyDsegment as the most c<strong>on</strong>servedam<strong>on</strong>g the tested mcys; (iii) a linearcorrelati<strong>on</strong> was obtained betweenthe microscopically determined cellnumbers and the PCR thresholdcycles; (iv) cell c<strong>on</strong>centrati<strong>on</strong> of thetoxic Microcystis from Q-PCRmeasurement was not affected byadditi<strong>on</strong> of n<strong>on</strong>-toxic populati<strong>on</strong>s; (v)gene copy number per cell wasvariable during the different growthstages and a maximal of 20 at theearly logarithmic and stati<strong>on</strong>aryphase of batch cultures of toxicMicrocystis. This Q-PCR can beapplied in the envir<strong>on</strong>mentalsamples to as few as 800 toxiccells. The selecti<strong>on</strong> of suitableprimer pairs for specific mcysegments is important to avoidmisleading results.PO.10-01Effects of UVBR <strong>on</strong> differentstrains of the cyanobacteriumNodularia spumigena from theBaltic SeaSessi<strong>on</strong>: PO.10 - Ecophysiology &autecologyV Lindberg, M Mohlin, A WulffGöteborg University, GÖTEBORG, SwedenNodularia spumigena is <strong>on</strong>e ofseveral toxin-producingcyanobacteria in the Baltic Sea. Itproduces the hepatoxin nodularin, atumour promoter known to havekilled wild and domestic animals.Nodularia spumigena blooms occurduring late summer, a period withstr<strong>on</strong>g light, calm weather andstable water-column stratificati<strong>on</strong>.The tolerance to high lightintensities of three different strainsof N. spumigena was tested for 10days in two different laboratoryexperiments. Cultures were kept insemi-c<strong>on</strong>tinuous growth andexposed to UVBR and UVAR, up to0.8 W/m 2 and 5 W/m 2 , respectively.Variables measured: growth (lightmicroscope), photosyntheticcapacity (phyto-PAM, Walz),c<strong>on</strong>tent and compositi<strong>on</strong> ofphotosynthetic pigments, phycobilinpigments and UV-absorbingcompounds (HPLC). Despite sometreatment effects, UVBR intensitiesup to 0.4 W/m 2 do not seem to havea negative impact <strong>on</strong> the threestrains <strong>on</strong> day 10. However, whenexposed to UVBR intensities up to0.8 W/m 2 all strains were to someextent negatively affected by alower maximum quantum yield ofphotosynthesis but not growth. Inc<strong>on</strong>clusi<strong>on</strong>, this toxiccyanobacterium appear to have the221

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