Flow cytometric laboratory
Flow cytometry enables a differentiation of cell populations and determination of exact counts of cells suspended in the sample based on their optical characteristics. In spite of the fact that the method was primarily developed for mammalian cells, it may be also successfully used for phytoplankton analysis of samples originating from aquatic environment. Each particle is characterised by light scatter (both forward and side scatter) and fluorescence. The main advantage of phytoplankton cells is a presence of fluorescent pigments (chlorophyll of green algae, phycoerythrine or phycocyanin of cyanobacteria). On the other hand, heterotrophic cells or acellular structures (bacteria, viruses) have no fluorescent pigments but may be signed by various fluorescent substrates, which are bound to DNA in most cases.
Flow cytometry at our department
In our lab an instrument CyFlow ML (Sysmex Partec GmbH, Muenster, Germany) is used for the analysis of samples from freshwater aquatic environment. Our flow cytometer is equipped with four excitation sources – blue laser (488 nm/20 mW), green laser 532 nm/30 nm, red diode laser 635 nm/25 mW, UV diode (365 nm) and with detectors for 4 optical parameters (FSC488nm, SSC488 nm, FL1 and FL2). Five optical filters have been recently available, (527/30 nm for the detection of SYBR Green I, fluorescein or ELF fluorescence; 590/50 nm – phycoerythrine; 675/20 nm – chlorophyll; 630 LP filter and 450/50 nm for the detection of DAPI or Hoechst fluorescence), however optical system is modular and may be supplied up to 16 optical parameters. The great benefit of Partec CyFlow cytometers in comparison with instruments of other companies (BD Biosciences, Beckman Coulter) is a possibility of the measurement in so-called “true volumetric counting” regime, which enables determination of cell concentrations in the suspension without count-check beads or other reference particles.
CyFlow ML flow cytometer has been used mainly for the detection of phytoplankton in field samples and for toxicity testing using laboratory algal/cyanobacterial cultures. In addition to determination of abundances of phytoplankton groups, phytoplankton esterase metabolic activity has been also measured using fluorescein diacetate as a substrate. Total bacterial counts (using SYBR Green I) as well as bacterial viability (Nucleus Acid Double Staining protocol using SYBR Green I and propidium iodide) and cyanobacterial viability (SYTOX Green) in freshwater samples have been also investigated. In the future we would like to improve methodologies for the extraction of bacteria and cyanobacteria from sediments, measure respirative activity of bacteria using CTC and investigate extracellular phosphatase activity using ELF-97.
Last but not least, at the CCT flow cytometry has been recently used for the evaluation of cyanotoxin effects on HaCat keratinocytes. Cell cycle analysis of HaCat cells fixed by ethanol after propidium iodide staining has been performed by flow cytometry and the percentage of cells in individual phases of cell cycle has been detected using special cytometric software (Fig. 5).
Fig. 1) The measurement of metabolic (esterase) activity of cyanobacterium Microcystis aeruginosa. The kinetics of fluorescein diacetate (FDA) hydrolysis during 10 minute incubation period. While cyanobacterial autofluorescence remained approximately on the same level (picture on left), green fluorescence of cyanobacteria increased because of fluorescein accumulation inside the cell (picture on right).
Fig. 2) The determination of total E. coli counts in water filtered through various materials. Bacteria stained by SYBR Green I were enumerated after their gating in “total E. coli” region which includes bacterial subpopulations having low (LNA) or high nucleus acid content (HNA). Sample filtration (middle and right cytograms) led to significant decline of E. coli counts compared to non-filtered control (left).
Fig. 3) An analysis of membrane integrity of E. coli exposed to phthalocyanine using Nucleus Acid Double Staining (NADS ) protocol. Bacteria with intact membrane were gated in “live” region, whereas bacteria having damaged membrane were localized in “dead” region. Phthalocyanine exposure of bacteria under light (Fig. D) led to significant increase of membrane-compromised cells compared to non-exposed controls (both dark – A and light – B) as well as to phthalocyanine treated bacteria exposed in the dark (Fig. C).
Fig. 4) The investigation of viability (membrane integrity) of cyanobacterium Microcystis aeruginosa exposed to hydrogen peroxide using fluorescent stain SYTOX Green. Cells having intact cell membrane which can be considered as viable have been gated into SYTOX- region, non-viable cells having damaged cell membrane (possessing high green fluorescence) have been gated into SYTOX+ region. While after 7 hours of the exposure almost all cells were viable (picture on the left side), percentage of non-viable cells after 24 hours (picture in the middle) and after 72 hours (picture on the right) significantly increased.
Fig. 5) Cell cycle analysis of HaCat keratinocytes for the studies of cyanotoxin effects. Picture on the left side represents the histogram of control HaCat cells stained by propidiumiodide (PI), whereas the same histogram processed by cytometric software is depicted on right. While red fluorescence of G1 HaCat cells peaked approximately at 200 (blue peak), G2/M cells with duplicated DNA content form the peak (green colour) around 400. Additionally, cells just synthesizing DNA (S-phase of cell cycle) are situated in red area of the histogram between G1 and G2/M cells.