Results and Discussion
This is the page were we present our results. This is where we discover if genetically modified gut bacteria can be a part of the solution against exposure to toxic metals.
Overview
We have successfully sequenced the following parts:
- BBa_K3282003 (arsR-T7)
- BBa_K3282004 (arsR-Tac)
We have successfully transformed E.coli Nissle 1917 to absorb:
- ~40% of lead in a concentration of ~2 mg/L, in 2.5 hours.
- ~20% of arsenic in a concentration of ~16 mg/L, in 2.5 hours.
We have failed on the following points:
- To see evidence of protein expression using SDS-page.
- To sequence the parts BBa_K3282005 (pbrD-T7) and BBa_K3282007 (pbrD-Tac).
Parts
The following parts were designed:
Composite part with arsR and a T7 promoter: BBa_K3282003
Composite part with arsR and a Tac promoter: BBa_K3282004
Composite part with pbrT, pbrD and a T7 promoter: BBa_K3282005
Composite part with pbrT, pbrD and a Tac promoter: BBa_K3282007
From now on the parts will be reffered to as the following:
- arsR-T7: BBa_K3282003
- arsR-Tac: BBa_K3282004
- pbrD-T7: BBa_K3282005
- pbrD-Tac: BBa_K3282007
Isolation of E. coli Nissle 1917
E. coli Nissle 1917 (EcN) was isolated from a probiotic pharmaceutical Mutaflor. It was resuspended and plated on MacConkey agar that is used to select several E. coli strains, among them EcN [1]. In order to confirm the identity of the strain a colony PCR was performed with primers specific for genomic island II (GEI II) and for cryptic plasmid pMUT2 that are specific for EcN. For GEI II the bands were expected at 400bp, while for pMUT2 at 313 bp [2,3]. The results of the colony PCR can be seen in figure 1 below.
Figure 1: Colony PCR result showing well-defined bands with various annealing temperatures, and pMUT2 and GEI II primers.
All colonies picked from MacConkey agar have shown the expected band with GEI II primers but no bands at all with pMUT2. These results confirm the identity of the strain to be EcN, despite negative results for pMUT2 primers since the GEI II primers are specific for chomrosomal region of EcN [2].
Sequencing of Composite Parts
The following parts were sequenced ars-T7, ars-Tac, pbrD-T7 and pbrD-Tac.
The sequences of ars-T7 and ars-Tac showed 100% and 99.6% similarity, the alignment results can be found here and here respectively. For ars-Tac there are two base substitutions in the sequence. The first one is in the region that is only used for amplification PCR and hence it had no effect on protein structure or expression. However, the second substitution is in the protein coding region and resulted in R18L mutation.
Unfortunately, in the case of pbrD-T7 and pbrD-Tac, samples were mixed up or contaminated with ars-T7 and ars-Tac and therefore it was not possible to align the sequences. Due to lack of time it was not possible to repeat sequencing for those composite parts.
Cultivation of Transformed Bacteria
The E. coli BL21(DE3) strain was transformed with biobrick ars-T7 in pUC19 plasmid by heat shock. Similarly, the BL21(DE3) was transformed with part pbrD-T7 and EcN strain with part pbrD-Tac in pUC19. Unfortunately, arsR-Tac arrived late and cultivation could therefore not be performed. The growth rate of the transformed and wild type strains were compared by cultivating the cells in LB media at 37 °C and measuring OD every hour. The cultivation was carried out to investigate if the presence of plasmid acts as a burden for the cells. As is evident from figure 2, the growth rate of the control and the transformed bacteria are very similar. This is unexpected since arsR expression has shown to be toxic to cells [4]. This conclusion is a positive indicator that the cells would not die before their intended use of absorbing arsenic.
Figure 2: Comparison of the growth rate of E. coli BL21(DE3) transformed with ars-T7 inserted into pUC19 and wild type E. coli BL21(DE3).
Figure 3: Comparison of growth rate of E coli BL21(DE3) transformed with pbrD-T7 inserted into pUC19 and wild type E coli BL21(DE3).
The growth rate of E. coli BL21(DE3) containing the lead construct was compared with the wild type BL21(DE3). Figure 3 displays growth of cells over time. The growth rate of the cells containing the construct had a growth rate of 0.474 h-1, and the control of BL21(DE3) cells had a growth rate of 0.263 h-1. The cells containing the constructs grow at a pace that is a bit faster than the control. This result is unexpected, since cells that are forced to express heterologous proteins often have a lower growth rate because of the burden it bears on the cell. The linear fit is also not perfect, with low R2 values compared to what would be wanted. The results could be accidental. However, the results also give an indicator that the cells would not die before they have a chance to perform the desired function of lead uptake.
Figure 4: Comparison of growth rate of EcN transformed with pbrD-Tac inserted into pUC19 and wild type EcN.
Figure 4 above shows the growth rate of both transformed and untransformed EcN containing pUC19 with the lead construct. The results are analogous to the E. coli BL21(DE3). The growth rate of the EcN containing the plasmid and the control are similar, with the cells containing the construct exhibiting a slightly higher pace. Growth rates of transformed EcN was 0.697 h-1, while the rate for the untransformed control was 0.556 h-1. Since the result is similar to the results in figure 3, so is the discussion. The results could be random from looking at the relatively poor linear fit. The plasmid does from this result not appear to be a burden to the cell and would have a chance to perform the desired function of lead uptake before cell death.
Toxic Metal Analysis
Investigation of Composite Parts for Arsenic Accumulation
The part ars-T7 consists of a T7 promoter (BBa_I719005), Anderson RBS (BBa_J61109), arsenic resistance operon repressor (BBa_K3282000) and TE terminator (BBa_B0012), whereas ars-Tac (arsR-Tac)comprises the same basic parts but with a Tac promoter (BBa_K3282006).
The Escherichia coli chromosomal ars operon confers resistance to trivalent and pentavalent salts of the metalloids arsenic and antimony. ArsR is the first gene in the ars operon containing a very specific binding site towards As(III) [4].
Experiment
ars-T7 was inserted into pUC19 and successfully transformed in E. coli BL21(DE3), and ars-Tac was transformed in the probiotic strain EcN. arsR protein expression was demonstrated by performing SDS-PAGE. The cells were cultured in enriched media (containing peptone, yeast extract, phosphates, chlorides and sulphates) at 37°C. They were grown overnight and were harvested in their late exponential phase in order to normalize the OD values to 2. After normalization, the cells were resuspended in fresh enriched medium containing 10 µM, 50 µM and 200 µM of As2O3. As a negative control, the experiment was also performed with wild type E. coli BL21(DE3) and wild type EcN in growth medium containing 50 µM As2O3.
Results
The SDS-PAGE analysis result can be seen in figure 5 and figure 6. The expected band for arsR protein has a molecular weight of 13.5 kDa, therefore it should appear between the two marked points as shown in figure 5 and 6. The gel shows that the engineered bacterial strains, as well as the negative controls have a band with the expected molecular weight. Thus, we can not confirm that it corresponds to arsR. It is possible that there are other proteins expressed in E. coli of the same molecular weight, masking the expression of arsR.
Figure 5: Samples were harvested at different time points, and the total cellular proteins were analyzed by SDS-PAGE. Protein bands of BL21(DE3) can be seen after induction with IPTG, showing arsR at 13.5 kDa. The control shown is wild type BL21(DE3) without arsR.
Figure 6: Samples were harvested at different time points, and the total cellular proteins were analyzed by SDS-PAGE. Image with protein bands of EcN after induction with IPTG, showing ArsR at 13.5 kDa. The control shown is wild EcN without arsR.
Arsenic accumulation over time
Figure 7: Arsenic concentration in media contaning BL21 transformed with the composite part ars-T7 or non-transformed E. coli BL21 (DE3).
Arsenic accumulation over time at varying pH
Figure 8: Arsenic accumulation over time at varying pH. The blue line represents the arsenite concentration in a culture maintained at pH 3 containing the composite part while the red line represents arsenite concentration in a culture maintained at pH 5 containing the composite part. The yellow line represents the arsenite concentration in a culture with wild type EcN.
Figure 7 and figure 8 compare the arsenite accumulation over time whereas figure 9 and figure 10 compare the growth of engineered as well as wild type strains. It can be seen in figure 7 that the initially added arsenite had a concentration of 3.745 mg/L for both engineered as well as wild type BL21(DE3), and the arsenite concentration measured at 0 hours was 0.014 mg/L and 0.013 mg/L respectively. Similarly, it can be seen in figure 8 that the initially added arsenite had a concentration of 3.745 mg/L (ars-Tac at pH3 and Control) and 14.98 mg/L (ars-Tac at pH5), and the arsenite concentration measured at 0 hours was 0.012 mg/L, 0.012 mg/L, and 0.024 mg/L respectively. This rapid decrease in both cases was unexpected. The relative concentration of arsenic in media where transformed and non transformed bacteria were present is showcased in figure 11.
Growth comparison between transformed and non-transformed E. coli BL21(DE3)
Figure 9: Comparison of growth of engineered BL21(DE3) with wild type BL21(DE3) in the presence of arsenic oxide.
Growth comparison between transformed and non-transformed EcN
Figure 10: Comparison of growth of engineered EcN with wild type EcN in the presence of arsenic oxide.
Relative Concentration of Arsenite in Media Containing Transformed and Non-Transformed Bacteria
Figure 11: Relative concentration of arsenite in growth media at different timepoints (0, 2.5 and 5 h) with transformed and untransformed (control) strains of E. coli.
Discussion
Arsenite does not suffer from sorption to glass surfaces as it forms oxy ions which are partly dissociated leading to negatively charged ions [5]. Therefore, this decrease cannot be accounted for by the sticking of ions to the glass surface. It might be the case that the engineered bacteria, as well as the control, have a capacity to uptake arsenite. According to Chen et al., when the cells are depleted of endogenous energy reserves, arsenite enters whether or not the cells carry a resistance plasmid [7]. The ars operon carried on the Escherichia coli R-factor R773 encodes the transport system that extrudes arsenite, and the lowering of the intracellular concentration of toxic oxyanion produces resistance. However, plasmid lacking strains of E. coli have also been shown to be intrinsically resistant to arsenite due to the presence of chromosomal ars operon. It has also been found that the R773 arsR protein is 75 % identical with the chromosomal product in E. coli strains [6]. The wild type E. coli strains are resistant to arsenite up to a concentration of 1 mM. This might explain the similarity in growth and arsenite uptake between the engineered EcN and BL21(DE3) strains, and the wild type strains. However, if the measured arsenite concentration at 0 hour is compared with the concentration at 2.5 hours, the engineered BL21(DE3) shows a 21 % accumulation of arsenite, compared with only 8 % arsenite accumulation in the control. Similarly, for EcN, the comparison of measured arsenite concentration at 0 hours with the concentration at 2.5 hours, shows that the engineered EcN accumulated 22 % arsenite, whereas the control accumulated 13 % arsenite. This can be considered as a proof of concept; showing that the engineered EcN and BL21(DE3) strains express arsR and have an improved ability to uptake arsenite. The slight increase in the arsenite concentration at 5 hours might suggest that some cells died and released the accumulated arsenite. The growth curves in figure 10 and figure 11 imply that the wild type, as well as engineered strains were able to survive in the presence of arsenite and at pH 5. However, EcN had a very low growth rate at pH 3, suggesting that the cumulative effect of low pH and the presence of toxic arsenite might be inhibitory for the cells.
Investigation of Composite Parts for Lead Accumulation
pbrD-T7 composite part consists of a T7 promoter (BBa_I719005), two Anderson RBS (Part:BBa_J61109), separating two coding regions of lead binding protein (BBa_K3282002) and lead transport protein (BBa_K3282001), followed by a TE terminator (Part:BBa_B0012), whereas the pbrD-Tac (pbrD-Tac) comprises the same basic parts but with a Tac promoter (BBa_K3282006).
The pbrD gene encodes a Pb(II)-binding protein which is essential for functional lead sequestration, whereas the expression of pbrT leads to uptake of lead into the cytoplasm to reduce interaction of free Pb(II) with side chains of membrane and periplasmic proteins, which would cause extensive cellular damage [8].
Experiment
The pbrD-T7 part was inserted into pUC19 and successfully transformed in E. coli BL21(DE3), and the pbrD-Tac part was transformed in the probiotic strain EcN. pbrD and pbrT protein expression was demonstrated by performing SDS-PAGE. The cells were cultured in enriched media (containing peptone, yeast extract, phosphates, chlorides and sulphates) at 37 °C. They were grown overnight and were harvested in their late exponential phase to normalize the OD values to 2. After normalization, the cells were resuspended in fresh enriched medium containing 10 µM, 50 µM, and 200 µM of Pb(NO3)2. As a negative control, the experiment was also performed with the wild type E. coli BL21(DE3), and wild type EcN in growth medium containing 50 µM Pb(NO3)2.
Samples were collected every hour for OD measurement. For investigating the arsenic accumulation by engineered bacteria, samples were collected at 0 hours, 2.5 hours and 5 hours after the addition of Pb(NO3)2.
Results
The SDS-PAGE analysis result can be seen in figure 12 and figure 13. The PbrD is a 26.7 kDa and PbrT 68.3 kDa protein. Therefore, the bands were expected to be just above the 25kDa band, and just below the 70 kDa band for PbrD and PbrT respectively. The gel shows that the engineered bacteria, as well as the control, have bands with the expected molecular weight. Thus, we can not confirm that the bands corresponds to the desired proteins. It is possible that there are other proteins expressed in E. coli with the same molecular weight, masking the expression of pbrD and pbrT.
Figure 12: Samples were harvested at different time points, and the total amount of cellular proteins were analyzed by SDS-PAGE. Image with protein bands of BL21(DE3) after induction with IPTG, showing pbrD at 26.7 kDa and pbrT at 68.3 kDa. The control shown is wild type BL21(DE3) without pbrD and pbrT.
Figure 13: Samples were harvested at different time points, and the total amount of cellular proteins were analyzed by SDS-PAGE. Image with protein bands of BL21(DE3) after induction with IPTG, showing PbrD at 26.7 kDa and pbrT at 68.3 kDa. The control shown is wild type BL21(DE3) without pbrD and pbrT.
Lead Accumulation Over Time
Figure 14: Lead accumulation over time. The red line represents the lead concentration in a culture that contains the composite part, while the blue line represents the lead concentration in a culture with wild type E. coli BL21(DE3).
Lead Accumulation Over Time at Varying pH
Figure 15: Lead accumulation over time. The blue line represents the lead concentration in a culture maintained at pH 3 containing the composite part, while the red line represents lead concentration in a culture maintained at pH 5 containing the composite part. The yellow line represents the lead concentration in a culture with wild type EcN.
Figure 14 and figure 15 compares the lead accumulation over time, whereas figure 16 and figure 17 compares the growth rates of engineered as well as wild type strains. It can be seen in figure 14 that the initially added lead concentration to both engineered and wild type cells was 10.63 mg/L, and the concentration at 0 hours was 0.63 mg/L and 0.66 mg/L respectively. Similarly, it can be seen in figure 15 that the initially added lead concentration was 41.44 mg/L, maintained at pH 3 and the concentration at 0 hours was 6 mg/L, showcasing an 86 % decrease. The culture maintained at pH 5 with an initial lead concentration of 10.36 mg/L also showed an 89 % decrease in lead concentration at time 0 hours. In comparison, the control shows no decrease in lead concentration. The overall lead accumulation was calculated to be 41 % by the engineered EcN, and 40 % by the engineered BL21(DE3) after 2,5 hours. The relative concentration of lead in media where transformed and non transformed bacteria were present is showcased in figure 18.
Growth comparison between transformed and non-transformed E. coli BL21(DE3)
Figure 16: Comparison of the growth rate of engineered BL21(DE3) with wild type BL21(DE3) in the presence of lead nitrate over 6 hours.
Growth comparison between transformed and non-transformed EcN
Figure 17: Comparison of the growth rate of engineered EcN with wild type EcN in the presence of lead nitrate over 6 hours.
Relative Concentration of Lead in Media Containing Transformed and Non-Transformed Bacteria
Figure 18: Relative concentration of lead in growth media at different time points (0, 2.5 and 5 h) with transformed and untransformed (control) strains of E. coli.
Discussion
The rapid decrease in the concentration as seen in figure 14 and 15 is similar to the decrease in arsenite concentration as explained in the previous discussion. A percentage of this rapid decrease can be attributed to the use of borosilicate Erlenmeyer flasks, since it was found that borosilicate glass can adsorb lead ions [9]. However, the study also mentions that adsorption of lead by borosilicate glass is time-dependent and adsorption was found to be only 17.2% over a period of 20 hours. This concludes that not all the lead adsorption was by borosilicate glass but also by the bacterial strains. The slight increase in lead concentration at hour 5 in figure 14 can be explained by the death of cells and release of the accumulated lead. Figure 16, 17 and 18 indicate that the engineered cells are capable of accumulating lead and can survive under conditions simulated.
In Conclusion
Our results indicate an increase in the bacteria capability to bioaccumulate the toxic metals when the composite parts were introduced. However, due to lacking data points we cannot establish statistical significance. Our composite parts and our concept of using microbes to accumulate toxins in the human body deserves further investigation.
Future Plans
We have failed on the following points:
- To see evidence of protein expression using SDS-page.
- To sequence the parts BBa_K3282005 (pbrD-T7) and BBa_K3282007 (pbrD-Tac).
More testing needs to be conducted in order to establish a significant result regarding the effeciveness of our composite parts. If significance is found, the bacteria should be tested in vivo, possibly in worms as we first planned. From thereon we can use the experimental data to validate our model further, in order to safely predict the outcome if applied in humans. A viable solution and risk-assessement for the leakage of GMMs into the environment needs to be found before further trials regaring animal and human trials may begin.
Our concenpt of using microbes to remove toxins from the human body is worthy of further exploration. It may be a viable solution in removing pesticides and carcinogenic chemicals.
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