Solid phase biosensors for arsenic or cadmium composed of A trans factor and cis element complex.

The presence of toxic metals in drinking water has hazardous effects on human health. This study was conducted to develop GFP-based-metal-binding biosensors for on-site assay of toxic metal ions. GFP-tagged ArsR and CadC proteins bound to a cis element, and lost the capability of binding to it in their As- and Cd-binding conformational states, respectively. Water samples containing toxic metals were incubated on a complex of GFP-tagged ArsR or CadC and cis element which was immobilized on a solid surface. Metal concentrations were quantified with fluorescence intensity of the metal-binding states released from the cis element. Fluorescence intensity obtained with the assay significantly increased with increasing concentrations of toxic metals. Detection limits of 1 µg/L for Cd(II) and 5 µg/L for As(III) in purified water and 10 µg/L for Cd(II) and As(III) in tap water and bottled mineral water were achieved by measurement with a battery-powered portable fluorometer after 15-min and 30-min incubation, respectively. A complex of freeze dried GFP-tagged ArsR or CadC binding to cis element was stable at 4 °C and responded to 5 µg/L As(III) or Cd(II). The solid phase biosensors are sensitive, less time-consuming, portable, and could offer a protocol for on-site evaluation of the toxic metals in drinking water.

Application of fluorescent protein-tagged trans factors and immobilized cis elements to monitoring of toxic metals based on in vitro protein-DNA interactions.

Environmental toxic metals cause serious global public health problems. On-site monitoring protects people from exposure to such harmful elements. In this study, the bacterial transcriptional switches were applied to monitoring of toxic metals. ArsR and CadC, trans factors of Escherichia coli and Staphylococcus aureus, were fused to GFP. The fusion proteins, ArsR-GFP and CadC-GFP, associated with cis elements, P(ars)-O(ars) and P(cad)-O(cad), respectively and dissociated from those upon recognition of As(III) or Pb/Cd. Cell lysates containing ArsR-GFP were pre-incubated with As(III) standard solutions for 15 min and loaded into P(ars)-O(ars)-immobilized microplate wells. Cell lysates containing CadC-GFP were pre-incubated with Pb or Cd solutions and loaded into P(cad)-O(cad)-immobilized wells. The cell lysates were incubated for 15 min and removed from the wells. Fluorescence intensity in the wells dose-dependently decreased in response to As(III) up to 200 µg/l or Pb/Cd up to 100 µg/l. Detection limits were 10 µg/l for As(III) 10 µg/l for Cd, and 20 µg/l for Pb with a microplate fluororeader, whereas 5.0 µg/l for As(III), 1.0 µg/l for Cd, and 10 µg/l for Pb with a handheld fluorometer. This method was available to detect Pb/Cd or As(III) in water containing soil extracts. This is the first demonstration of a simple and rapid fluorometry to detect analytes based on in vitro interaction between a cis element and a trans factor.