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Workshop 
Laboratory for Aquatic 
Microbiology and Chemistry 
(The Miller Laboratory) 
Milwaukee - Wisconsin
School of Public Health
Todd R. Miller
Lucas Beversdorf - Post Doctoral 
Studying the regulation of hepatotoxin synthesis in cyanobacteria and factors 
leading to the formation of toxic cyanobacterial blooms in lakes using 
automated samplers and mass spectrometry
Chelsea Weirich - Doctoral Student 
Chelsea is investigating factors leading to algal toxin production in lakes and their 
subsequent occurrence in drinking water. She is leading a project with the Global 
Lakes Ecological Observatory Network to examine global patterns in cyanobacterial 
toxin production
Sarah Bartlett - Doctoral Student 
Sarah is investigating bioaccumulation and occurrence of algal toxins, primarily 
anatoxin-a in fish at all trophic levels. She is also investigating the relationship 
between gross primary productivity and algal toxin production.
Mutagenicidade in vitro e carcinogenicidade in vivo (Humpage et al, 2000; Falconer e Humpage, 2001). 
Bioacumulação em peixe (Saker e Eaglesham, 1999), em moluscos (Saker et al., 2004) e em Cladóceros 
(Nogueira et al., 2004). Em mamíferos provoca lesão necrótica generalizada, afetando fígado, rins, 
pulmões, baço, intestino, timo e coração (Chorus e Bartmann, 1999). 
Bloqueia os canais de sódio na membrana do axônio e induzir disfunção do nervo, 
causando paralisia e então a morte por insuficiência respiratória (van Apeldoorn et al., 2007). 
Altamente tóxicas para os animais e, em doses elevadas o suficiente, letais para humanos 
(Landsberg, 2002). 
Cylindrospermopsis raciborskii 
(Woloszynska) e Seenayya Subba Raju 
Amostra da Lagoa do Peri – março/2014
Fatores abióticos e produção de toxinas por C. raciborskii 
Fator Abiótico Observação Referências Bibliográficas 
CYL 
Temperatura Forte correlação negativa Saker e Griffiths (2000) 
STX 
Temperatura Não há variação entre 19 e 25oC 
Em 25oC produz dcSTX 
Castro et al. (2004) 
N e P Correlação positiva com altas relações N:P Chislock et al. (2014) 
Dureza Correlação positiva Carneiro et al. (2013)
Lagoa do Peri 
Abastece 102 a 113 mil habitantes na Ilha de Santa Catarina (Pereira e Zanin, 2012) 
Comunidade fitoplantônica apresenta dominância da cianobactéria 
Cylindrospermopsis raciborskii (Woloszinska) Seenayya et Subba-Raju. 
STX, 
Neo-STX, 
GTX-1, 
GTX-2, 
GTX-3, 
GTX-4, 
GTX-5, 
dcGTX-2 
dcGTX-3 
Gonyautoxina 
Decarbamoylsaxitoxina 
(Grellmann, 2006; Melo Filho, 2006; Mondardo, 2009; Machado, 2011; Machado e Sens, 2012) .
Objetivo 
Determinar a relação entre variáveis abióticas, 
produção de cianotoxinas e densidade de 
Cylindrospermopsis raciborskii “in locu”; 
Sample STX_q Peak Area STX_q Peak Height 
0 0,00E+00 0,00E+0,1 7,15E+02 5,49E+0,5 3,66E+03 3,07E+1 7,68E+03 6,15E+5 3,75E+04 3,40E+10 7,16E+04 6,00E+0 0,00E+00 0,00E+DB001FH 5,92E+03 6,18E+DB002FH 6,72E+03 7,17E+DB003FH 3,19E+03 2,75E+DB004FH 2,21E+03 2,48E+DB005FH 1,73E+03 2,32E+
Metodologia 
Transporte 
Identificação 
Sample Name Date Received State Fraction Site Sample Date Note 
DB001W 11/18/14Frozen Whole water Peri Lake 21/08/2013 
DB002W 11/18/14Frozen Whole water Peri Lake 24/09/2013 
DB003W 11/18/14Frozen Whole water Peri Lake 15/10/2013 
DB004W 11/18/14Frozen Whole water Peri Lake 19/11/2013 
DB005W 11/18/14Frozen Whole water Peri Lake 10/12/2013 
DB006W 11/18/14Frozen Whole water Peri Lake 22/01/2014 
… 
DB001F 11/18/14Filter Filter Peri Lake 21/08/20132 X 300 ML 
DB002F 11/18/14Filter Filter Peri Lake 24/09/20134 X 300 ML 
DB003F 11/18/14Filter Filter Peri Lake 15/10/20134 X 300 ML 
DB004F 11/18/14Filter Filter Peri Lake 19/11/20134 X 300 ML 
DB005F 11/18/14Filter Filter Peri Lake 10/12/20134 X 300 ML 
DB006F 11/18/14Filter Filter Peri Lake 22/01/20143 X 300 ML 
DB007F 11/18/14Filter Filter Peri Lake 11/02/20141 X 300 ML 
DB008F 11/18/14Filter Filter Peri Lake 18/02/20142 X 300 ML 
… 
DB002D 11/18/14Frozen Filtrate Peri Lake 24/09/2013 
DB004D 11/18/14Frozen Filtrate Peri Lake 19/11/2013 
DB006D 11/18/14Frozen Filtrate Peri Lake 22/01/2014 
DB008D 11/18/14Frozen Filtrate Peri Lake 18/02/2014 
DB012D 11/18/14Frozen Filtrate Peri Lake 25/03/2014
Extração 
Amostra líquida 
(whole and fitrated) 
H=Hydrophilic 
Interaction Liquid 
Chromatography 
(HILIC) 
column/extraction 
for anatoxin-a, 
homoanatoxin-a, 
saxitoxin, 
cylindrospermopsin 
C=C18 
(18-Carbon chain) 
column / extraction 
for microcystins 
and peptides 
Filtro 
(filter) 
HILIC C18
Extraction of Microcystins & Cyanobacterial Peptides with 70% Methanol from 
Whole Water Samples 
Reagents: 
Water with 0.1% formic acid 
100% Methanol 
Lyophilize 20 mL of each water sample for 48 hours. 
Pipet 20 mL sample into a 50 mL Falcon tube. 
Wrap one-and-a-half squares of Parafilm around the top of each tube. 
Use a small pipet tip to poke holes in the tops of the Parafilm. 
Cap and freeze on an angle in -80°C freezer for >1 hour. 
Samples are lyophilized for 24-48 hours at -50°C until complete dryness. This 
is to concentrate and preserve cells and dissolved toxins.
Cut Parafilm circles with razor blade so that they fall into the tubes; discard Parafilm 
wrapped around tubes. Letting Parafilm that covers the top of the tube during 
lyophilization fall into the tube allows it to be “washed” for maximum extraction 
recovery of toxins. 
Add 1 ml of water/0.1% formic acid (vortex) 
Three 30-minute freeze-thaw cycles between the -80°C freezer and 50°C water bath; 
turn on sonicating water bath during freeze-thaw cycles so it warms up.
Add 2 mL 100% methanol (vortex; final concentration methanol ~70%). 
Sonicate in the 45°C sonicating water bath for 10 minutes – make sure the bath is at 
least 2/3 of the way full with distilled water (vortex). 
Centrifuge at maximum speed (11,000 rpm) for 15 minutes. 
Transfer 1000 μL of the supernatant to a labeled LC vial; make sure not to suck up any 
particulates as these could clog the LC lines.
Extraction of Neurotoxins & Cylindrospermopsin from Whole Water Samples 
Reagents: 
Water with 0.1% formic acid 
Lyophilize 20 mL of each water sample for 48 hours. 
Pipet 20 mL sample into a 50 mL Falcon tube. 
Wrap one-and-a-half squares of Parafilm around the top of each tube. 
Use a small pipet tip to poke holes in the tops of the Parafilm. 
Cap and freeze on an angle in -80°C freezer for >1 hour. 
Samples are lyophilized for 24-48 hours at -50°C until complete dryness. This is to 
concentrate and preserve cells and dissolved toxins. 
Cut Parafilm circles with razor blade so that they fall into the tubes; discard Parafilm 
wrapped around tubes. Letting Parafilm that covers the top of the tube during 
lyophilization fall into the tube allows it to be “washed” for maximum extraction 
recovery of toxins. 
Add 1 mL of water/0.1% formic acid (vortex) 
Three 30-minute freeze-thaw cycles between the -80°freezer and 50°C water bath; turn 
on sonicating water bath during freeze-thaw cycles so it warms up. 
Sonicate in the 45°C sonicating water bath for 10 minutes – make sure the bath is at 
least 2/3 of the way full with distilled water (vortex). 
Centrifuge at maximum speed (11,000 rpm) for 15 minutes. 
Transfer 750 μL of the supernatant to a labeled LC vial; make sure not to suck up any 
particulates as these could clog the LC lines.
HILIC Extraction Method 
1) Cut filters (300 mL per filter) in half with scissors – place each 
half filter in each 15 mL Falcon tube to represent biomass from 150 
mL water sample. Wash each filter with ethanol and Smartwater in 
between each sample filter. 
2) Add 4 mL HPLC water with 0.1% formic acid into the conical and 
vortex to mix well. 
3) Freeze (-80°C) the samples for 30 minutes and then thaw in a 
50°C water bath. 
4) Vortex and place in a sonicating water bath at 45°C for 5 minutes, 
then vortex again. 
5) Repeat steps 3 and 4 two more times. 
6) Place 15 mL tubes in a swinging bucket rotor and centrifuge for 
15 minutes at maximum speed. 
7) Transfer 1 mL of supernatant to LC vial for LC-MS/MS analysis. 
8) Add 5 μL of 1000 μg/L 13C6-phenylalanine (extracts spiked at 5 
μg/L) for 1) determination of difference between phenylalanine and 
anatoxin-a retention time and 2) examining ion suppression among 
LCMS runs. 
C18 (Microcystin/Peptide) ExtractionMethod 
1-5) Same steps that you did in HILIC 
6) Add 8 mL 100% methanol to each tube so the total methanol 
concentration is ~70%. Vortex and let this incubate on the benchtop 
for one hour with intermittent vortexing (3-4 times or approx. every 
15 minutes). 
If having trouble resuspending with methanol addition, try 
vortexing sample upside down and/or place samples in 
sonicating water bath (45°C) for 5 minutes to try to release 
pellet from sides of tube. 
7) Place in sonicating water bath for 5 minutes. 
8) Place 15 mL tubes in a swinging bucket rotor and centrifuge for 
15 minutes at maximum speed (5000 rpm). 
9) Pour off supernatant into 20 mL scintillation vial and begin drying 
down with heat and N2 gas. 
10) Add 5 mL of 100% methanol to the 15 mL Falcon tube and let 
incubate for one more hour on the benchtop with intermittent 
vortexing. 
11) Repeat steps 7-9. 
12) Dry down entire extract to a residue in the bottom of the 
scintillation vial. Resuspend each residue in 1 mL 70% methanol. 
13) Sonicate the scintillation vials in the water bath for 5 minutes 
(tightly capped) to help remove the residue stuck to the glass. 
14) Transfer 1 mL of suspended toxin extract into 1.5 mL mini-centrifuge 
tube, and centrifuge at max speed for 12 minutes. 
15) Transfer 750 μL of supernatant to LC vial for LC-MS/MS analysis. 
Filters
HighPerformance LiquidChromatography 
CLAD = Cromatografia a Líquido de Alto Desempenho 
CLAE = Cromatografia a Líquido de Alta Eficiência
1 
2 
3 
4 
5
O objetivo da cromatografia é separar individualmente os diversos constituintes de uma 
mistura de substâncias. 
Tal separação dá-se através da migração da amostra através de uma fase estacionária 
(FE) por intermédio de um fluido (fase móvel - FM). 
Após a introdução da amostra no sistema cromatográfico, os componentes da amostra 
se distribuem entre as duas fases e viajam mais lentamente que a fase móvel devido ao 
efeito retardante da fase estacionária. 
O equilíbrio de distribuição determina a velocidade com a qual cada componente migra 
através do sistema.
DESCRIÇÃO GERAL DE HPLC 
•A amostra é dissolvida em um solvente e introduzida na coluna cromatográfica 
preenchida com a fase estacionária (FE) 
•Um solvente (FM) é bombeado com vazão constante e desloca os componentes 
da mistura através da coluna. Esses se distribuem entre as duas fases de acordo 
com suas afinidades 
•As substâncias com maior afinidade com a FE movem-se mais lentamente. Já as 
substâncias com pouca afinidade com a FE movem-se mais rapidamente. 
•Ao sair da coluna, os componentes passam por um detector que emite um sinal 
elétrico o qual é registrado, constituindo um cromatograma.
Cromatograma 
Lagoa do Peri
Sample: DB019FD
Resultados 
- Quantification Limit 0,005 μg.L-1; Detection Limit 0,0025μg.L-1 
- STX 
- Concentração intracelular 
Sample 
STX_q Peak 
Area 
STX_q Peak 
Height 
Calculated 
Concentration_q 
Volume (Filtered or 
Lyophilized) 
Final 
Volume 
Dilution 
factor 
Lake Concentration 
(ug/L) STX_q 
0 0,00E+00 0,00E+00N/A NA NA NA NA 
0,1 7,15E+02 5,49E+01< 0 NA NA NA NA 
0,5 3,66E+03 3,07E+02 0,472NA NA NA NA 
1 7,68E+03 6,15E+02 1,27NA NA NA NA 
5 3,75E+04 3,40E+03 7,22NA NA NA NA 
10 7,16E+04 6,00E+03 14NA NA NA NA 
0 0,00E+00 0,00E+00N/A NA NA NA NA 
DB001FH 5,92E+03 6,18E+02 0,922 150 4 0,026666667 0,024586667 
DB002FH 6,72E+03 7,17E+02 1,08 150 4 0,026666667 0,0288 
DB003FH 3,19E+03 2,75E+02 0,379 150 4 0,026666667 0,010106667 
DB004FH 2,21E+03 2,48E+02 0,183 150 4 0,026666667 0,00488 
DB005FH 1,73E+03 2,32E+02 0,0873 150 4 0,026666667 0,002328 
DB006FH 4,08E+03 4,61E+02 0,557 150 4 0,026666667 0,014853333 
0 0,00E+00 0,00E+00N/A NA NA NA NA 
DB007FH 2,84E+03 3,19E+02 0,31 150 4 0,026666667 0,008266667 
DB008FH 4,50E+03 4,53E+02 0,64 150 4 0,026666667 0,017066667 
DB009FH 3,68E+03 3,73E+02 0,477 150 4 0,026666667 0,01272 
DB012FH 2,65E+03 3,21E+02 0,272 150 4 0,026666667 0,007253333 
DB013FH 3,40E+03 3,68E+02 0,421 150 4 0,026666667 0,011226667 
DB014FH 3,42E+03 3,63E+02 0,425 150 4 0,026666667 0,011333333 
10 4,67E+04 4,05E+03 9,04NA NA NA NA 
0 0,00E+00 0,00E+00N/A NA NA NA NA 
DB015FH 4,03E+03 4,33E+02 0,546 150 4 0,026666667 0,01456
Thank you!

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SEMINARIO LIMNOS DEBORA #7

  • 1. Workshop Laboratory for Aquatic Microbiology and Chemistry (The Miller Laboratory) Milwaukee - Wisconsin
  • 2.
  • 5. Lucas Beversdorf - Post Doctoral Studying the regulation of hepatotoxin synthesis in cyanobacteria and factors leading to the formation of toxic cyanobacterial blooms in lakes using automated samplers and mass spectrometry
  • 6. Chelsea Weirich - Doctoral Student Chelsea is investigating factors leading to algal toxin production in lakes and their subsequent occurrence in drinking water. She is leading a project with the Global Lakes Ecological Observatory Network to examine global patterns in cyanobacterial toxin production
  • 7. Sarah Bartlett - Doctoral Student Sarah is investigating bioaccumulation and occurrence of algal toxins, primarily anatoxin-a in fish at all trophic levels. She is also investigating the relationship between gross primary productivity and algal toxin production.
  • 8.
  • 9.
  • 10.
  • 11. Mutagenicidade in vitro e carcinogenicidade in vivo (Humpage et al, 2000; Falconer e Humpage, 2001). Bioacumulação em peixe (Saker e Eaglesham, 1999), em moluscos (Saker et al., 2004) e em Cladóceros (Nogueira et al., 2004). Em mamíferos provoca lesão necrótica generalizada, afetando fígado, rins, pulmões, baço, intestino, timo e coração (Chorus e Bartmann, 1999). Bloqueia os canais de sódio na membrana do axônio e induzir disfunção do nervo, causando paralisia e então a morte por insuficiência respiratória (van Apeldoorn et al., 2007). Altamente tóxicas para os animais e, em doses elevadas o suficiente, letais para humanos (Landsberg, 2002). Cylindrospermopsis raciborskii (Woloszynska) e Seenayya Subba Raju Amostra da Lagoa do Peri – março/2014
  • 12. Fatores abióticos e produção de toxinas por C. raciborskii Fator Abiótico Observação Referências Bibliográficas CYL Temperatura Forte correlação negativa Saker e Griffiths (2000) STX Temperatura Não há variação entre 19 e 25oC Em 25oC produz dcSTX Castro et al. (2004) N e P Correlação positiva com altas relações N:P Chislock et al. (2014) Dureza Correlação positiva Carneiro et al. (2013)
  • 13. Lagoa do Peri Abastece 102 a 113 mil habitantes na Ilha de Santa Catarina (Pereira e Zanin, 2012) Comunidade fitoplantônica apresenta dominância da cianobactéria Cylindrospermopsis raciborskii (Woloszinska) Seenayya et Subba-Raju. STX, Neo-STX, GTX-1, GTX-2, GTX-3, GTX-4, GTX-5, dcGTX-2 dcGTX-3 Gonyautoxina Decarbamoylsaxitoxina (Grellmann, 2006; Melo Filho, 2006; Mondardo, 2009; Machado, 2011; Machado e Sens, 2012) .
  • 14. Objetivo Determinar a relação entre variáveis abióticas, produção de cianotoxinas e densidade de Cylindrospermopsis raciborskii “in locu”; Sample STX_q Peak Area STX_q Peak Height 0 0,00E+00 0,00E+0,1 7,15E+02 5,49E+0,5 3,66E+03 3,07E+1 7,68E+03 6,15E+5 3,75E+04 3,40E+10 7,16E+04 6,00E+0 0,00E+00 0,00E+DB001FH 5,92E+03 6,18E+DB002FH 6,72E+03 7,17E+DB003FH 3,19E+03 2,75E+DB004FH 2,21E+03 2,48E+DB005FH 1,73E+03 2,32E+
  • 15. Metodologia Transporte Identificação Sample Name Date Received State Fraction Site Sample Date Note DB001W 11/18/14Frozen Whole water Peri Lake 21/08/2013 DB002W 11/18/14Frozen Whole water Peri Lake 24/09/2013 DB003W 11/18/14Frozen Whole water Peri Lake 15/10/2013 DB004W 11/18/14Frozen Whole water Peri Lake 19/11/2013 DB005W 11/18/14Frozen Whole water Peri Lake 10/12/2013 DB006W 11/18/14Frozen Whole water Peri Lake 22/01/2014 … DB001F 11/18/14Filter Filter Peri Lake 21/08/20132 X 300 ML DB002F 11/18/14Filter Filter Peri Lake 24/09/20134 X 300 ML DB003F 11/18/14Filter Filter Peri Lake 15/10/20134 X 300 ML DB004F 11/18/14Filter Filter Peri Lake 19/11/20134 X 300 ML DB005F 11/18/14Filter Filter Peri Lake 10/12/20134 X 300 ML DB006F 11/18/14Filter Filter Peri Lake 22/01/20143 X 300 ML DB007F 11/18/14Filter Filter Peri Lake 11/02/20141 X 300 ML DB008F 11/18/14Filter Filter Peri Lake 18/02/20142 X 300 ML … DB002D 11/18/14Frozen Filtrate Peri Lake 24/09/2013 DB004D 11/18/14Frozen Filtrate Peri Lake 19/11/2013 DB006D 11/18/14Frozen Filtrate Peri Lake 22/01/2014 DB008D 11/18/14Frozen Filtrate Peri Lake 18/02/2014 DB012D 11/18/14Frozen Filtrate Peri Lake 25/03/2014
  • 16. Extração Amostra líquida (whole and fitrated) H=Hydrophilic Interaction Liquid Chromatography (HILIC) column/extraction for anatoxin-a, homoanatoxin-a, saxitoxin, cylindrospermopsin C=C18 (18-Carbon chain) column / extraction for microcystins and peptides Filtro (filter) HILIC C18
  • 17. Extraction of Microcystins & Cyanobacterial Peptides with 70% Methanol from Whole Water Samples Reagents: Water with 0.1% formic acid 100% Methanol Lyophilize 20 mL of each water sample for 48 hours. Pipet 20 mL sample into a 50 mL Falcon tube. Wrap one-and-a-half squares of Parafilm around the top of each tube. Use a small pipet tip to poke holes in the tops of the Parafilm. Cap and freeze on an angle in -80°C freezer for >1 hour. Samples are lyophilized for 24-48 hours at -50°C until complete dryness. This is to concentrate and preserve cells and dissolved toxins.
  • 18. Cut Parafilm circles with razor blade so that they fall into the tubes; discard Parafilm wrapped around tubes. Letting Parafilm that covers the top of the tube during lyophilization fall into the tube allows it to be “washed” for maximum extraction recovery of toxins. Add 1 ml of water/0.1% formic acid (vortex) Three 30-minute freeze-thaw cycles between the -80°C freezer and 50°C water bath; turn on sonicating water bath during freeze-thaw cycles so it warms up.
  • 19. Add 2 mL 100% methanol (vortex; final concentration methanol ~70%). Sonicate in the 45°C sonicating water bath for 10 minutes – make sure the bath is at least 2/3 of the way full with distilled water (vortex). Centrifuge at maximum speed (11,000 rpm) for 15 minutes. Transfer 1000 μL of the supernatant to a labeled LC vial; make sure not to suck up any particulates as these could clog the LC lines.
  • 20. Extraction of Neurotoxins & Cylindrospermopsin from Whole Water Samples Reagents: Water with 0.1% formic acid Lyophilize 20 mL of each water sample for 48 hours. Pipet 20 mL sample into a 50 mL Falcon tube. Wrap one-and-a-half squares of Parafilm around the top of each tube. Use a small pipet tip to poke holes in the tops of the Parafilm. Cap and freeze on an angle in -80°C freezer for >1 hour. Samples are lyophilized for 24-48 hours at -50°C until complete dryness. This is to concentrate and preserve cells and dissolved toxins. Cut Parafilm circles with razor blade so that they fall into the tubes; discard Parafilm wrapped around tubes. Letting Parafilm that covers the top of the tube during lyophilization fall into the tube allows it to be “washed” for maximum extraction recovery of toxins. Add 1 mL of water/0.1% formic acid (vortex) Three 30-minute freeze-thaw cycles between the -80°freezer and 50°C water bath; turn on sonicating water bath during freeze-thaw cycles so it warms up. Sonicate in the 45°C sonicating water bath for 10 minutes – make sure the bath is at least 2/3 of the way full with distilled water (vortex). Centrifuge at maximum speed (11,000 rpm) for 15 minutes. Transfer 750 μL of the supernatant to a labeled LC vial; make sure not to suck up any particulates as these could clog the LC lines.
  • 21. HILIC Extraction Method 1) Cut filters (300 mL per filter) in half with scissors – place each half filter in each 15 mL Falcon tube to represent biomass from 150 mL water sample. Wash each filter with ethanol and Smartwater in between each sample filter. 2) Add 4 mL HPLC water with 0.1% formic acid into the conical and vortex to mix well. 3) Freeze (-80°C) the samples for 30 minutes and then thaw in a 50°C water bath. 4) Vortex and place in a sonicating water bath at 45°C for 5 minutes, then vortex again. 5) Repeat steps 3 and 4 two more times. 6) Place 15 mL tubes in a swinging bucket rotor and centrifuge for 15 minutes at maximum speed. 7) Transfer 1 mL of supernatant to LC vial for LC-MS/MS analysis. 8) Add 5 μL of 1000 μg/L 13C6-phenylalanine (extracts spiked at 5 μg/L) for 1) determination of difference between phenylalanine and anatoxin-a retention time and 2) examining ion suppression among LCMS runs. C18 (Microcystin/Peptide) ExtractionMethod 1-5) Same steps that you did in HILIC 6) Add 8 mL 100% methanol to each tube so the total methanol concentration is ~70%. Vortex and let this incubate on the benchtop for one hour with intermittent vortexing (3-4 times or approx. every 15 minutes). If having trouble resuspending with methanol addition, try vortexing sample upside down and/or place samples in sonicating water bath (45°C) for 5 minutes to try to release pellet from sides of tube. 7) Place in sonicating water bath for 5 minutes. 8) Place 15 mL tubes in a swinging bucket rotor and centrifuge for 15 minutes at maximum speed (5000 rpm). 9) Pour off supernatant into 20 mL scintillation vial and begin drying down with heat and N2 gas. 10) Add 5 mL of 100% methanol to the 15 mL Falcon tube and let incubate for one more hour on the benchtop with intermittent vortexing. 11) Repeat steps 7-9. 12) Dry down entire extract to a residue in the bottom of the scintillation vial. Resuspend each residue in 1 mL 70% methanol. 13) Sonicate the scintillation vials in the water bath for 5 minutes (tightly capped) to help remove the residue stuck to the glass. 14) Transfer 1 mL of suspended toxin extract into 1.5 mL mini-centrifuge tube, and centrifuge at max speed for 12 minutes. 15) Transfer 750 μL of supernatant to LC vial for LC-MS/MS analysis. Filters
  • 22. HighPerformance LiquidChromatography CLAD = Cromatografia a Líquido de Alto Desempenho CLAE = Cromatografia a Líquido de Alta Eficiência
  • 23. 1 2 3 4 5
  • 24. O objetivo da cromatografia é separar individualmente os diversos constituintes de uma mistura de substâncias. Tal separação dá-se através da migração da amostra através de uma fase estacionária (FE) por intermédio de um fluido (fase móvel - FM). Após a introdução da amostra no sistema cromatográfico, os componentes da amostra se distribuem entre as duas fases e viajam mais lentamente que a fase móvel devido ao efeito retardante da fase estacionária. O equilíbrio de distribuição determina a velocidade com a qual cada componente migra através do sistema.
  • 25.
  • 26.
  • 27. DESCRIÇÃO GERAL DE HPLC •A amostra é dissolvida em um solvente e introduzida na coluna cromatográfica preenchida com a fase estacionária (FE) •Um solvente (FM) é bombeado com vazão constante e desloca os componentes da mistura através da coluna. Esses se distribuem entre as duas fases de acordo com suas afinidades •As substâncias com maior afinidade com a FE movem-se mais lentamente. Já as substâncias com pouca afinidade com a FE movem-se mais rapidamente. •Ao sair da coluna, os componentes passam por um detector que emite um sinal elétrico o qual é registrado, constituindo um cromatograma.
  • 30. Resultados - Quantification Limit 0,005 μg.L-1; Detection Limit 0,0025μg.L-1 - STX - Concentração intracelular Sample STX_q Peak Area STX_q Peak Height Calculated Concentration_q Volume (Filtered or Lyophilized) Final Volume Dilution factor Lake Concentration (ug/L) STX_q 0 0,00E+00 0,00E+00N/A NA NA NA NA 0,1 7,15E+02 5,49E+01< 0 NA NA NA NA 0,5 3,66E+03 3,07E+02 0,472NA NA NA NA 1 7,68E+03 6,15E+02 1,27NA NA NA NA 5 3,75E+04 3,40E+03 7,22NA NA NA NA 10 7,16E+04 6,00E+03 14NA NA NA NA 0 0,00E+00 0,00E+00N/A NA NA NA NA DB001FH 5,92E+03 6,18E+02 0,922 150 4 0,026666667 0,024586667 DB002FH 6,72E+03 7,17E+02 1,08 150 4 0,026666667 0,0288 DB003FH 3,19E+03 2,75E+02 0,379 150 4 0,026666667 0,010106667 DB004FH 2,21E+03 2,48E+02 0,183 150 4 0,026666667 0,00488 DB005FH 1,73E+03 2,32E+02 0,0873 150 4 0,026666667 0,002328 DB006FH 4,08E+03 4,61E+02 0,557 150 4 0,026666667 0,014853333 0 0,00E+00 0,00E+00N/A NA NA NA NA DB007FH 2,84E+03 3,19E+02 0,31 150 4 0,026666667 0,008266667 DB008FH 4,50E+03 4,53E+02 0,64 150 4 0,026666667 0,017066667 DB009FH 3,68E+03 3,73E+02 0,477 150 4 0,026666667 0,01272 DB012FH 2,65E+03 3,21E+02 0,272 150 4 0,026666667 0,007253333 DB013FH 3,40E+03 3,68E+02 0,421 150 4 0,026666667 0,011226667 DB014FH 3,42E+03 3,63E+02 0,425 150 4 0,026666667 0,011333333 10 4,67E+04 4,05E+03 9,04NA NA NA NA 0 0,00E+00 0,00E+00N/A NA NA NA NA DB015FH 4,03E+03 4,33E+02 0,546 150 4 0,026666667 0,01456

Editor's Notes

  1. Palm Island, na Austrália, em 1979, onde um surto de hepatoenteria ocorreu numa população, que havia sido abastecida com a água de um reservatório infestado com cianobactérias (Bourke et al., 1983). 138 pessoas Nas investigações posteriores, isolou-se uma estirpe de C. raciborskii, que demostrou hepatotoxicidade grave a ratos e, portanto, tornou-se o organismo suspeito causador do surto (Hawkins et al., 1985). CYL - Mais tarde, um alcalóide incomum, cilindrospermopsina (CYL), constituído por uma porção de guanidina tricíclico combinados com hidroximethiluracil foi isolado a partir desta estirpe (Ohtani et al., 1992). inibidor da síntese proteica que necrosa as células do fígado provocando o acúmulo de gordura neste órgão STX - compostos tricíclicos que pode ser não-sulfatados, isoladamente sulfatada ou duplamente sulfatada
  2. há lacuna de informação sobre a correlação da produção de cianotoxinas, fatores abióticos e densidade de C. raciborskii nesta área de estudo, o que é imprescindível em termos de saúde pública. Tal informação também incrementaria o pouco conhecimento que há sobre a regulação entre densidade C. raciborskii, fatores abióticos e produção de cianotoxinas em ambientes naturais.