Team:Hong Kong-CUHK/Project/light

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<p><strong>3. Pgad has the capability to control downstream gene expression according to intracellular chloride concentration.</strong></p>  
<p><strong>3. Pgad has the capability to control downstream gene expression according to intracellular chloride concentration.</strong></p>  
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<p>Sanders J.W. et al. succeeded in constructing Pgad expression cassette in L. lactis in 1997<sup>1</sup>. We borrowed  
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<p>Sanders J.W. et al. succeeded in constructing Pgad expression cassette in L. lactis in 1997<sup>1</sup> (For more details, please see "<a href="https://2011.igem.org/Team:Hong_Kong-CUHK/Project/Chloride_Sensing_Unit">Chloride Sensing Unit</a>" session). We borrowed their design and tried to

Revision as of 03:22, 25 October 2011

Light Intra-tunable System




Summary
  • Halorhodopsin complete system (BBa_K559010) was successfully constructed.
  • Halorhodopsin can be properly expressed in BL21(DE) and the cell survival was not significantly affected.
  • Chloride absorption by halorhodopsin was optimized under different extracellular NaCl concentration, input light wavelength, intensity and illumination duration.
  • Pgad was feasible to control downstream gene expression according to intracellular chloride concentration.



A. Validation of halorhodopsin System


We successfully construct three biobricks: halorhodopsin (BBa_K559000), halorhodopsin under T7 promoter (BBa_K590001) and halorhodopsin complete system (BBa_K559010) and all biobricks were sent to part-registry. In this session, we are going to show the data proving that our biobricks function properly.



1. Halorhodopsin was correctly inserted to pSB1C3 and expressed in BL21(DE) properly.

We use PCR with six pairs of primers and gel electrophoresis to confirm that we have properly constructed halorhodopsin complete system (BBa_K559010) (Fig. 1). All bands in each lane match their theoretical sizes. Halorhodopsin complete system then was transformed to BL21(DE). Since our halorhodopsin has been HIS-tagged, we performed western blot to confirm the expression of halorhodopsin in BL21(DE)(Fig. 2). The PCR and western blot results indicate that our biobricks is successfully constructed and halorhodopsin can be properly expressed in BL21(DE).

Fig. 1 Halorhodopsin complete system (BBa_K559010) was correctly constructed. Components in the plasmid were amplified by standard PCR using corresponding primers. The PCR conditions were 95°C denature for 30s, 54 °C annealing for 15s and 72°C extension for 30s. The number of PCR cycle was 30. The PCR products of corresponding lanes are shown on the table. T7 was amplified by T7 F and T7 R, HR was amplified by HR F and HR R, 24C was amplified by 24C F and 24C R, T7 HR was amplified by T7 F and HR R, T7 24C was amplified by T7 F and 24C R and HR 24C was amplified by HR F and 24C R.




To optimize the expression of halorhodopsin, induction by different concentration of IPTG was carried out and SDS-PAGE was done to investigate the results. 0.10mM concentration of IPTG was found to be optimum to induce halorhodopsin expression. We thus decided to use this condition to induce expression afterwards.

Fig.2 Optimization of halorhodopsin expression in BL21(DE). BL21(DE) was transformed according to standard protocol. Bacterial culture grew from a single colony at 37℃ in the presence of chloramphenicol. Different concentration of IPTG was used to induce gene expression of halorhodopsin when OD600 reached 0.4. After IPTG induction for 4




2. BL21(DE) transformed with complete halorhodopsin system (BBa_K559010) grows normally in LB medium with additional sodium chloride concentrations ranged from 0 M to 0.4 M.

In order to determine whether halorhodopsin would affect the survival of E. coli, we performed an assay to examine the growth curve of BL21(DE) transformed with the complete halorhodopsin system (BBa_K559010) in different sodium chloride concentrations (Fig. 5). Our data show that the bacteria expressing halorhodopsin grew normally in LB medium with additional sodium chloride concentration ranged from 0 M to 0.4 M. When the sodium chloride concentration was above 0.4 M, the growth of the bacteria was inhibited due to extremely high salinity conditions. Halorhodopsin does not affect the growth and survival of E. coli.

Fig. 3 Growth curve of bacteria under different NaCl concentration. BL21(DE) was transformed according to standard protocol. Bacterial culture grew from a single colony at 37°C. 0.1 mM of IPTG was used to induce halorhodopsin expression. 1% (v/v) inoculum was used as start culture at 0 hour. The change in OD600 was monitored.




3. Halorhodopsin functions properly in BL21(DE).

To test the function of halorhodopsin, we performed MQAE assay to measure intracellular chloride concentration right after light illumination to bacterial samples (Fig. 6, Fig. 7). After light illumination, the bacteria expressing halorhodopsin have significantly higher intracellular chloride concentrations compared with the bacteria without halorhodopsin. Our data show that halorhodopsin pumps chloride ions from medium into bacteria during light illumination. In conclusion, our biobricks can function properly in E. coli. In additional, we also proved that function of halorhodopsin is light depended (Fig. 7).

Fig. 4 Halorhodopsin expressing bacteria absorbed chloride ions. BL21(DE) was transformed and bacterial culture grew from a single colony at 37°C in the presence of light. 0.1 mM of IPTG and 0.4 M of NaCl were included in the culture medium. Intracellular chloride ion concentration was determined by MQAE after 4 hours induction. Error bar represents SEM.



Fig. 5 Halorhodopsin expressing bacteria absorbed chloride ions under different condition. BL21(DE) was transformed and bacterial culture grew from a single colony at 37°C under different conditions. Bacterial samples were collected when OD600 reached 0.4. Bacteria from different growth conditions were disrupted. The intracellular chloride ion concentration was determined by MQAE. Light: bacteria grew in the presence of light. IPTG: 0.1 mM of IPTG was used to induce gene expression. NaCl: the LB contained 0.4 M of NaCl. “+” indicates the corresponding component was included. “-” indicates the corresponding component was not included. Error bar represents SEM.




From the results, light, IPTG and NaCl are all required for the large amount increase in the chloride ion absorption by halorhodopsin. The comparative increase in set up 4, 5 and 7 are due to the addition of NaCl, which causes a greater diffusion of chloride ions into the cell.





B. Light-coupled expression platform


Fig. 6 Computer-aided light-coupled gene expression regulation platform




We propose this computer-aided light-coupled gene expression regulation platform for the purpose of dynamically controlling the expression and function of construct genes (Fig. 6). In this platform, we utilize E. coli transformed with halorhodopsin to modulate intracellular chloride level by light, and Pgad expression cassette to induce gene expression according to the variation in intracellular chloride level.

This platform consists of three components: computer instruction, bacteria expression and signal feedback. In computer instruction, a laser power device is controlled by computer and illuminates towards cell culture with desirable intensity, wavelength and duration. When genetically modified E. coli receives light illumination, halorhodopsin pumps chloride ions from medium into cytoplasm. Thereafter intracellular chloride ion level keeps increasing and chloride concentration in medium keeps decreasing. Inside the bacteria, gadR up-regulates target genes and feedback signal (e.g. green fluorescence protein) downstream of Pgad according to the increasing intracellular chloride level. Detector thus can sense the feedback signal as well as the regulated amount of target genes expression back to computer. Meanwhile, the pair of ion absorption electrodes can also detect the change in chloride ion concentration in the medium and return this information to computer, which could analyze intracellular chloride level and target gene expression speed. Therefore the target gene expression in this platform becomes dynamically tunable and programmable with the aid of computer.

To illustrate the feasibility of this design, we performed the following assays:


1. Intracellular chloride ion concentration of halorhodopsin-expressed bacteria is controllable by regulating the wavelength, intensity and duration of light illumination.

We followed MQAE method to determine intracellular chloride ion concentrations after the cells were treated with different wavelength, intensity and duration of illumination. Previous study shows that halorhodopsin mainly absorbs photons with wavelength around 600 nm1. Our data agree with this conclusion and we find that halorhodopsin functions with maximum efficiency at 530 nm (Fig. 7) and changing the wavelength can significantly reduce its efficiency.

Then we fixed the wavelength to 530 nm and measured the pumping efficiency of halorhodopsin under different light intensity. First we tested the survival of halorhodopsin-transformed E. coli under different light intensities (Fig. 8). The light intensity was indicated by the percentage of full LASER power supply under confocal microscope. The growth of transformed E. coli was not significantly affected when they were exposed to the light intensity below 25 percent of full power. E. coli could still grow normally when they were exposed under the light with intensity between 30 percent and 40 percent of the full power. However, when the LASER power exceeded 40 percent, the bacterial growth was significantly inhibited. In the next step, we examined the chloride absorption efficiency of halorhodopsin under different light intensity (Fig. 9). We found that the highest chloride pumping efficiency appeared at 25 percent of full power. When the intensity kept increasing, the intracellular concentration dropped due to death of E. coli. Furthermore, we studied the relation between intracellular chloride ion concentration and illumination duration under 25 percent of full power (Fig. 10). The highest intracellular chloride concentration was 0.55 M after samples was illuminated for 210 seconds. Afterwards intracellular chloride ions kept decreasing due to cell death caused by high LASER power.

In conclusion, our data present the feasibility where intracellular chloride concentration can be accurately controlled by the wavelength, intensity and duration of light illumination.



Fig. 7 Halorhodopsin expressing bacteria absorbed chloride ions induced by laser with different wavelengths. BL21(DE) was transformed by BBa_K559010 and the bacterial culture grew from a single colony in LB with 0.4 M of NaCl at 37°C in the absence of light. Bacterial samples were collected when OD600 reached 0.4. 500 μl of bacterial sample was excited by 20% laser power with different wavelength for 2 minutes under confocal microscope. 200 μl of excited bacteria was collected and disrupted. Its intracellular chloride ion concentration was measured by MQAE. Error bar represents SEM.



Fig. 8 Bacterial growth after exposure to different power of laser with wavelength 530 nm. Transformed BL21(DE) grew in LB with 0.4 M of NaCl. 500 μl of bacteria culture was used for laser exposure when OD600 reach 0.4. Bacteria were exposed to different laser power for 2 minutes. After the exposure, 200 μl of the bacteria was cultured in 2 ml of LB. OD600 was determined immediately after inoculation (0 hour) and after 2 hour grew in LB. Table shows the value of OD600 at corresponding time point. Data was expressed as mean ± SEM.



Fig. 9 Laser (530 nm) induced Chloride ion absorption. BL21(DE) was transformed and a single colony was picked to grow in LB with 0.4 M of NaCl. 500 μl of bacterial sample with OD600 reached 0.4 was excited by laser (530 nm) with different LASER power (%). 200 μl of excited bacteria was collected and disrupted. The intracellular concentration of chloride ion was determined by MQAE. Error bar represents SEM.



Fig. 10 Chloride ions absorption responded differently with the length of laser (530 nm) exposure. BL21(DE) was transformed and a single colony was picked to grow in LB with 0.4 M of NaCl. 500 μl of bacterial sample with OD600 reached 0.4 was excited by LASER (530 nm) with different exposure time. The LASER power was fixed at 25%. 200 μl of excited bacteria was collected and disrupted. The intracellular concentration of chloride ion was determined by MQAE. Error bar represents SEM.




2. Mixing-entropy electrodes can monitor extracellular change of sodium chloride concentration.

In our design, we utilize the voltage between mixing-entropy electrodes (For more details, please see "Solar Electricity Generation" session) to monitor the extracellular change in sodium chloride concentration. Thus we measured the steady voltage against sodium chloride concentration to prove our concept (Fig. 11). In these data, the steady voltage increases along with the increase of sodium chloride concentration. It shows that the voltage between the electrodes could be utilized as a feedback signal to monitor extracellular sodium chloride concentration. However, the sensitivity of voltmeter would limit the resolution of sodium chloride concentration, which should be improved in the future.



Fig. 11 Voltage against sodium chloride concentration test shows the capability using entropy-mixing electrodes to monitor extracellular sodium chloride concentration. The electrodes were immersed in 25 ml sodium chloride solutions with different concentrations until the voltage achieved a steady level. The steady voltages were recorded and plotted.




3. Pgad has the capability to control downstream gene expression according to intracellular chloride concentration.

Sanders J.W. et al. succeeded in constructing Pgad expression cassette in L. lactis in 19971 (For more details, please see "Chloride Sensing Unit" session). We borrowed their design and tried to

References

1. Sanders, J.W., Venema, G. & Kok, J. A chloride-inducible gene expression cassette and its use in induced lysis of Lactococcus lactis. Applied and environmental microbiology 63, 4877(1997).





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