Idea

We sought to create genetically engineered strains of E.coli that could sequester the heavy metals nickel, mercury, and lead from water sources. Each strain included a metal transport protein specific to the respective metal as well as a metallothionein to bind metal ions intracellularly. We first generated basic, functional BioBricks containing: a glutathione-s-transferase and yeast metallothionein (CRS5) fusion for metal binding (BBa_K1460001); the nickel transport protein nixA for selective nickel uptake (BBa_K1460003); the mercury transporters merT and merP for selective mercury uptake (BBa_K1460004); and a putative lead transport protein CPB4 for selective lead uptake (BBa_K1460005).

To test for sequestration ability of combined systems, each transport protein in the amp^r vector pUC57 was co-transformed with the metallothionein fusion in the cm^r plasmid pSB1C3 and selected for using both markers. These strains are the functional equivalents of the BioBricks BBa_K1460006, BBa_K1460007, and BBa_K1460008, and these strains were tested for sequestration ability of nickel, mercury, and lead respectively. The sequestering strains can be placed into fiber reactors to develop functional sequestering filters as part of the dry lab portion of our project.

Components

Experiments

The growth rates of the sequestering strain were measured using spectrophotometry. In addition, two methods were used to determine heavy metal sequestration efficiency.

1. Spectrophotometer was used to analyze and compare the kinetic growth rates of E. coli cultures expressing only the metallothionein protein, only the transporter proteins, both metallothionein and transporter proteins, and just the vector backbone as a control.
• We hypothesized that the control culture would be mildly sensitive to growth in metal-containing media, while the cultures with the transport protein would be more sensitive to growth in metal-containing media due to increased access of the heavy metal to cellular machinery. Finally, bacteria transformed with both the metal transporter and metallothionein protein would be the least sensitive in metal-containing media. Each strain was grown in different heavy metal concentrations.


2. Sequestration efficiency was measured by growing both the wild type strains as well as sequestering strains in different concentrations of heavy metals. The concentration of heavy metals after growth was measured in two ways:
• Nutrient Analysis Lab at Cornell University using ICP-AES
• Using green-fluorescent heavy metal indicator Phen Green

Results

1. BL21 strains with the merT/merP transporters showed increased sensitivity to mercury concentrations as expected. In addition, in high mercury concentrations, wild type strain growth was inhibited more than sequestration strain growths were inhibited. However, there was no inhibition of growth with wild type BL21 or strains with transporters for lead and nickel even at very high metal concentrations.

2. When considering cell density, both lead and nickel sequestering strains removed significantly more metal compared to the wild type BL21 strain. The mercury sequestering strain did not sequester significantly more metal compared to the wild type strain.

Lead Data

Mercury Data

Nickel Data

References

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1. Wilson, D. B. Construction and characterization of Escherichia coli genetically engineered for Construction and Characterization of Escherichia coli Genetically Engineered for Bioremediation of Hg 2 ϩ -Contaminated Environments. 2–6 (1997).
2. Krishnaswamy, R. & Wilson, D. B. Construction and characterization of an Escherichia coli strain genetically engineered for Ni(II) bioaccumulation. Appl. Environ. Microbiol. 66, 5383–6 (2000).
3. Huang, J. et al. Fission yeast HMT1 lowers seed cadmium through phytochelatin-dependent vacuolar sequestration in Arabidopsis. Plant Physiol. 158, 1779–88 (2012).