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BioRefine Project: Detection of bioavailability of Metallic Trace Elements in soils by the use of microbial biosensors

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BioRefine Project: Detection of bioavailability of Metallic Trace

Elements in soils by the use of microbial biosensors

Introduction

Soils contaminated with MTEs can be treated by

various methods

Some GFP-based biosensors can detect heavy metals

quantitatively

C. Tarayre1, Q. Hurdebise1, C. Fischer1, G. Colinet1,

J. Buysse2, E. Michels2, E. Meers2, F. Delvigne1

1 - Bio-Industries unit - Gembloux Agro-Bio Tech, University of Liège, Belgium 2 - Faculty of Bioscience Engineering, Ghent University, Belgium

This work is supported by the BioRefine Project (INTERREG IVB NWE

Programme) (ref. 320J-BIOREFINE)

Acknowledgements

Methodology of the work

Zinc, lead and cadmium are the main Metallic Trace Elements (MTEs) found in soils contaminated by the mining industry in Europe. MTEs are spread in the environment because of the disruption of biogeochemical cycles caused by human activities. Due to their low mobility and biodegradability, they accumulate in soils where they are strongly bound to particles. It has become necessary to understand interactions between MTEs and the environment and to implement remediation actions. This work is focused on remediation monitoring techniques by using whole cell microbial biosensors able to detect zinc, lead and cadmium. Biosensors provide a signal in response to the bio-available concentration in MTEs, which are valuable for the design of efficient techniques involving bioremediation. Whole cell biosensors used in this work are based on Escherichia coli strains carrying a fluorescent reporter system. The reporter element contains a promoter sensitive to MTEs and a gene coding for the Green Fluorescent Protein (GFP). MTEs activate the synthesis of GFP, which is a very stable protein, causing the accumulation of GFP inside the cells. Then, fluorescence can be measured by flow cytometry. In this study, two biosensors were investigated: E. coli pPzraPgfp and E. coli pPzntAgfp. The last strain provided a linear response to zinc up to 20 mg/l and a curvilinear

response to cadmium up to 0.15 mg/l. No detection was highlighted regarding lead. In practical cases, soils and wastes are contaminated by several types of MTEs. Consequently, combined contaminations were also tested. This work allowed highlighting that the strain E. coli pPzntAgfp can be used to assess the

bioavailability of cadmium in soils, although the experimental procedure must be improved. This work is supported by the BioRefine Project, a European project in which various member states focus on recovery of inorganics from organic wastestreams. We gratefully acknowledge the INTERREG IVB NWE programme, which financed the BioRefine Project (ref. 320J-BIOREFINE).

Zn Cu Ni Co Cd Pb Electrokinetic remediation Thermal desorption Chemical leaching Chemical fixation Vitrify technology Phytoremediation Bioremediation Animal remediation

Some of those techniques require a follow-up

FOCUS ON BIOSENSORS Cd2+ Zn2+ Pb2+ Cd2+ Zn2+ Pb2+ Promoter sensitive to Pb, Cd, Zn Recombinant plasmid Genomic DNA GFP coding sequence Fluorescent GFP Recombinant bacterium Fluorescence analysis through flow cytometry Quantification and signal analysis Fluorescent GFP

1) Check of the biosensors E. coli pPzraPgfp and E. coli

pPzntAgfp in LB medium

(microplate assays)

 Assay with Zn at 0,65 mg/l (a)

 Assay with Zn at 10,65 mg/l (b)

(a) (b) Good sensitivity

to Zn for E. coli pPzntAgfp

2) Check of the incubation time and linearity (E. coli pPzntAgfp)  Linear signal from 0 to 20 mg/l

in Zn2+(LB medium)

 Maximal fluorescence after 3h

3) Check of the effect of Pb2+and Cd2+

 Linearity of the signal according to Zn2+, Pb2+and Cd2+(a)

 Linear signal from 0 to 2,5 mg/l for

Cd2+, and very low signal for Pb2+ Concentration in MTEs (mg/l)

Concentration in Zn2+(mg/l)

4) Linearization of Lineweaver-Burk

 FL1maxis the maximal induction  Kmis the affinity      

  

Concentration in MTEs (x)

5) Assays on polluted soils

 Soil samples must be diluted in liquid

 The ratio Zn2+/Cd2+must be close to 10

 For this ratio, only Cd2+is detected

 E. coli pPzntAgfp can detect

concentrations in Cd2+close to 0,2 mg/kg

 Bioavailability can be assessed on the basis of the equation of Michaelis-Menten F lu o re sc en ce F lu o re sc en ce F L 1 Concentration in Zn2+ (ppm) Concentration in Cd2+ (ppm) F lu o re sc en ce Soil samples BUT no results for E. coli pPzraPgfp

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