An on-chip pollutant toxicity determination based on marine microalgal swimming inhibition
We report the use of microalgal swimming behavior as a sensor signal integrated into microfluidics for a rapid and high-throughput determination of pollutant toxicity. There are two types of chip. A poly(dimethylsiloxane) (PDMS) 12-well chip, used for optimization of experimental conditions ( i.e. l...
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Veröffentlicht in: | Analyst (London) 2016-03, Vol.141 (5), p.1761-1771 |
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Format: | Artikel |
Sprache: | eng |
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Zusammenfassung: | We report the use of microalgal swimming behavior as a sensor signal integrated into microfluidics for a rapid and high-throughput determination of pollutant toxicity. There are two types of chip. A poly(dimethylsiloxane) (PDMS) 12-well chip, used for optimization of experimental conditions (
i.e.
light level, temperature, initial cellular density and exposure time), can perform twelve parallel tests simultaneously. In a concentration gradient generator (CGG) chip, a CGG connected with diffusible chambers enables a large number of dose-response bioassays to be performed in a simple way. Microalgal swimming was set as a microfluidic bioassay signal and was evaluated as swimming manner, motile percentage (%MOT), curvilinear velocity (VCL), average path velocity (VAP) and straight line velocity (VSL). Under optimized physical conditions, the toxicities of Cu, Pb, phenol and nonylphenol (NP) towards four mobile marine microalgae,
Platymonas subcordiformis
,
Platymonas helgolandica var. tsingtaoensis
,
Isochrysis galbana
and
Isochrysis zhanjiangensis sp. nov
, were investigated. In all cases, a toxic response (
i.e.
a dose-related inhibition of swimming) was detected, and a time of only 2 h was needed to predict EC
50
values. The 2h-EC
50
s showed that
I. galbana
was the most tolerant and that
P. subcordiformis
was one of the most sensitive. Based on the relative motile percentage data, the EC
50
values for Cu of
I. galbana
and
P. subcordiformis
were 6.04 and 1.67 μM, respectively, while for Pb the EC
50
values were 15.30 and 3.87 μM, for phenol the EC
50
values were 8.69 and 6.08 mM, and for NP the EC
50
values were 29.65 and 14.47 μM, respectively. Taking into account all the swimming inhibition parameters, MOT provided more sensitive EC results. The sensitivity differences between the velocity parameters (VCL, VAP and VSL) were ascribed to differences in swimming manner of the different classes of microalgae.
Microfluidics using marine microalgal swimming behavior as a sensor signal were developed for a rapid and high-throughput determination of pollutant toxicity. |
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ISSN: | 0003-2654 1364-5528 |
DOI: | 10.1039/c5an02384j |