RESULTS:
1. Promoter Characterization:
Promoter consists of several discrete domains arranged in a specific orientation (modular in nature), such that redesigning of the ‘cis-architecture’ of a promoter DNA across its sequence backbone is feasible (Gurr and Rushton 2005; Rushton et al. 2002).
The resultant functionality of the newly derived synthetic module depends upon the altered positioning of discrete cis motif/s with respect to their positions, spacing, orientation and copy number/s (Fessele et al. 2002; Tjian and Maniatis 1994).
In an earlier study conducted by our primary investigator a very high expression was observed in Mirabalis Mosaic Virus promoter (pPMMVFLt12), thereby for the present study the strong promoter having the synthetic cis elements upstream was designed using online based software PLANT CARE (http://bioinformatics.psb.ugent.be/webtools/plantcare/html/). Figure 1: represents a pictorial view of cis-elements present in pPMMVFLt12 promoter.
Fig 1: Pictorial view of cis-elements present in pPMMVFLt12 promoter.
2. Cloning of Metallothionein:
Two different parts were created for our project:
1. BBa_K2441000: MT4MBP (Top-4 metal binder protein; Modified iGEM part BBa_K1478002), this part codes for a metal binding protein capable of binding Zinc (Zn), Cadmium (Cd), Copper (Cu), and Arsenic (As).
2. Human Metal Binding Protein-3 this part codes for a metal binding protein capable of binding Zinc, Cadmium, Copper, and Arsenic.
#unfortunately we are unable to submit this part due to its bio-brick incompatibility.
Successful clones are obtained (Figure 2). Sequencing was done in duplicates (two colonies of each clone) for sequence validation.
Figure 2: Picture of Agarose Gel conducted during cloning Experiments.
3. Bio-Beads Formation:
Different Concentration of Calcium Chloride was tested with varied concentration of Na-Alginate, among which beads formed in 1% Na-Alginate in 100 mM Cacl2 had shown the best results in terms of their shape and expressivity.
Bio-Beads were made from different cells of E. Coli BL-21 expressing our gene of Interest i.e MT4MBP and HMP of promoter our synthetically characterized promoter (Figure 4).
Fig 3: Immobilization of E Coli BL-21 cells expressing our protein of Interest
(a) Only Bio-Beads without any bacterial cells
(b) E.coli Bio-Beads does not expressing our protein of Interest
(c) E. coli Bio-Beads expressing MT4MBP
(d) E. coli Bio-Beads expressing HMP3
Figure 4: Treatment of water samples with
form Bio-Beads (a) Treatment of artificial water having 0.5mM CuCl2, 0.5mM ZnCl2 and 0.5mM CdCl2. with formed Bio-Beads (b) Treatment of Sewage Treatment Plant Inlet Water with formed
Bio-Beads (c) Treatment of Sewage Treatment Plant Outlet Water with formed
Bio-Beads
Figure 5: Visual observation of beads turning blue in 0.05 mM CuCl2 Solution after absorption with heavy metals
5. ICP OES: Heavy Metal Detection
Artificial water was created in laboratory having 0.5 mM (milli molar) of Calcium Chloride, Zinc Chloride, Cadmium Chloride was treated with Bio-Beads made up of cells expressing our gene of interest with two different sets of promoters. The heavy metal concentration was tested via ICP OES with a dilution factor of 50 (Table 1).
v Arsenic was not tested due to Biosafety issues.
Table 1: Detection of heavy metals in water sample via ICP OES
Heavy Metal |
S. No |
Bio-Beads |
Artificial Water |
Test Sample 1 |
Test Sample 2 |
|||
|
|
|
Reading (mg/L) |
Percentage Decrease (with respect to positive control) |
Reading (mg/L) |
Percentage Decrease
|
Reading (mg/L) |
Percentage Decrease
|
Copper (Cu) |
1 |
Negative Control |
-0.1350 |
-NA- |
-0.1781 |
-NA- |
-0.1871 |
-NA- |
2 |
Positive Control |
2.19540 |
0.00 |
5.7865 |
0.00 |
5.1789 |
0.00 |
|
3 |
MMV-MT4MBP |
1.07865 |
50.87 |
3.892 |
32.73 |
3.701 |
28.53 |
|
4 |
MMV-HMP |
0.36295 |
83.46 |
3.167 |
45.269 |
2.987 |
42.32 |
|
Zinc (Zn) |
1 |
Negative Control |
-0.1562 |
-NA- |
-0.1348 |
-NA- |
-0.1671 |
-NA- |
2 |
Positive Control |
51.09600 |
0.00 |
6.04695 |
0.00 |
5.9879 |
0.00 |
|
3 |
MMV-MT4MBP |
40.01135 |
21.63 |
5.0892 |
15.80 |
5.1981 |
13.18 |
|
4 |
MMV-HMP |
35.24370 |
31.02 |
4.9017 |
18.9 |
5.6897 |
4.98 |
|
Cadmium (Cd) |
1 |
Negative Control |
-0.1567 |
-NA- |
-0.1678 |
-NA- |
-0.1891 |
-NA- |
2 |
Positive Control |
73.4245 |
0.00 |
8.4955 |
0.00 |
7.9676 |
0.00 |
|
3 |
MMV-MT4MBP |
72.2775 |
1.56 |
8.071 |
4.99 |
6.6714 |
16.27 |
|
4 |
MMV-HMP |
54.3715 |
25.94 |
7.8991 |
7.02 |
6.2019 |
22.16 |
Figure 6(a): Linearity curve for Cd, Cu and Zn
Figure 6 (b): Peaks obtained of heavy metals for corresponding samples
Conclusion
Team DEI AGRA had initiated the project entitled as “Bio-Beads for removing heavy metal toxicity from Industrial effluents”, with a vision of contributing to a solution for a world-wide problem of heavy metal toxicity, which possess a serious threat to human health.
We had accomplished our objectives of cloning the mettalloprotein downstream to our characterized synthetic promoter, which are successfully immobilized in forms of Bio Beads. Our results indicated more than 80% decrease of copper, while 30% and 20% reduction in Zinc (Zn) and Cadmium (Cd) respectively in case of artificial water having 0.5mM CuCl2, 0.5mM ZnCl2 and 0.5mM CdCl2, while lesser but significant decrement observed in test samples collected from Sewage Treatment Plant of Agra, India.
Inference
We had fabricated Bio-Beads by immobilizing bacterial cells, which strongly expressing MT4MBP and HMP3 for fast, easy and user handy purification of water possessing heavy metal toxicity.