Difference between revisions of "Part:BBa K863012"

Latest revision as of 03:33, 27 October 2012

tthl laccase from T. thermophilus with constitutive promoter J23100, RBS and His-tag

tthl laccase (T. thermophilus) with constitutive promoter and HIS tag

Sequence and Features

Initially some trials of shaking flask cultivations were made with different parameters to identify the best conditions for the production of the His-tagged laccase LttH from [http://www.dsmz.de/catalogues/details/culture/DSM-7039.html?tx_dsmzreso Thermus thermophilus HB27] named TTHL. Due to the absence of enzyme activity of the enzyme in the cell lysate a purification method was established (using Ni-NTA-His tag resin). Using E. coli KRX containing BioBrick BBa_K863010, TTHL could not be detected by SDS-PAGE (molecular weight of 53 kDa) or by activity test. Therefore a new BioBrick BBa_K863012 was constructed and expressed in E. coli Rosetta-Gami 2. With this expression system the TTHL could be detected by SDS-PAGE and purified by using a small scale Ni-NTA column. The fractionated samples were tested regarding their activity. TTHL was shown to oxidize ABTS. After measuring activity of TTHL a scale up of the fermentation was successfully implemented up to 6 L.

Cultivation, Purification and SDS-PAGE

Shaking Flask Cultivation

• flask design: shaking flask without baffles
• medium: [http://2012.igem.org/Team:Bielefeld-Germany/Protocols/Materials#LB_medium LB-Medium]
• antibiotics: 60 µg mL^-1 chloramphenicol and 300 µg mL^-1 ampicillin
• temperature: 37 °C
• cultivation time: 24 h

The reproducibility of the measured data and results were investigated for the shaking flask cultivation, but not yet for the bioreactor cultivation.

Fermentation of E. coli KRX with BBa_K863012

Figure 1: Fermentation of E. coli Rosetta-Gami 2 with BBa_K863012 (TTHL) in a Bioengineering NFL22. Conditions: 6 L of [http://2012.igem.org/Team:Bielefeld-Germany/Protocols/Materials#Autoinduction_medium autoinduction medium] + 60 µg/mL chloramphenicol at 37 °C, pH 7. Agitation increased when pO₂ was below 30 % and OD₆₀₀ was measured each hour.

Purification of TTHL

The cells were harvested by centrifugation and resuspended in [http://2012.igem.org/wiki/index.php?title=Team:Bielefeld-Germany/Protocols/Materials#Buffers_for_His-Tag_affinity_chromatography Ni-NTA-equilibrationbuffer], mechanically disrupted by [http://2012.igem.org/Team:Bielefeld-Germany/Protocols/Production#Mechanical_lysis_of_the_.28bio-reactor.29_cultivation high pressure homogenization] and centrifuged. After preparing the cell paste the TTHL could not be purified with the 15 mL column, due to a not available column. For this reason a small scale purification (6 mL) of the supernatant of the homogenisation was made with a 1 mL Ni-NTA-column.

SDS-PAGE of purified TTHL

Figure 2: SDS-PAGE of purified E. coli Rosetta-Gami 2 containing BBa_K863012 lysate (fermented in 6 L Bioengineering NFL22). The flow-through, wash and elution fraction 1 to 5 are shown. The arrow marks the TTHL band with a molecular weight of 53 kDa.

Figure 2 shows the SDS-PAGE of the purified E. coli Rosetta-Gami 2 lysates fermented in 6 L Bioengineering NFL22 fermenter. Additionally the flow-through, wash and all elution fractions (1 to 5) are shown. TTHL has a molecular weight of 53 kDa and the corresponding band is marked with a red arrow. The TTHL band can be found in fractions 1 to 3, but not in the other two elution fractions. Furthermore there are some other non-specific bands, which could not be identified. To improve the purification an 15 mL column was implemented.

Activity analysis of TTHL

Initial activity tests of purified fractions

There was no activity measurable after cultivation and purification of BBa_K863022 under the control of a T7 promoter. Activity tests of TTHL under a constitutive promoter did reveal TTHL laccases capable of oxidizing ABTS. The purificated fractions of the cultivation were tested concerning their protein concentration. After re-buffering the protein concentration was determined again and all fraction were incubated with 0.4 mM CuCl₂. For the initial activity test the protein amount was adjusted for comparison. The fractions were measured in Britton-Robinson buffer at pH 5 with 0.1 mM ABTS. Fraction 50 % 1 showed the highest activity (Fig. 3). Regarding the protein amount of this fraction and the statement, that 90 % of this are TTHL laccase, fraction 50 % 1 contains 4,03 µg mL^-1. To ensure enough protein for further experiments, the second best fraction, which is fraction 5 % 3 was added to fraction 50 % 1. The first number indicates the percentage of used elution buffer, whereas the second number stands for the fraction number of this elution. In total, both fraction contain [http://2012.igem.org/Team:Bielefeld-Germany/Amsterdam/Labjournal#Tuesday_October_19th/ 4,4 µg mL^-1].

Figure 3: Activity assay of each purified fraction of the new cultivation with TTHL. Samples were re-buffered into H₂O and the protein amount in each fraction has been adjusted. The measurements were done using the [http://2012.igem.org/Team:Bielefeld-Germany/Protocols/Analytics#General_setup_of_enzyme_activity_measurements/ standard activity assay protocol] over night. The first number indicates the percentage of used elution buffer, whereas the second number stands for the fraction number of this elution.

Based on these results protein concentrations have to be determined and the activity of the TTHL laccase can be characterized in further experiments including pH optimum and activity in regard of temperature shifts.

Since regionals: TTHL activity depending on different ABTS concentrations

In order to find the substrate saturation, laccase activity was measured with ABTS concentrations ranging from 0.1 mM to 8 mM. 616 ng TTHL laccase were used for measurements with ABTS concentrations of 0.1 mM to 5 mM, 308 ng TTHL laccase were used for measurements with ABTS concentrations of 5 mM to 8 mM. Measurements were done in Britton-Robinson buffer (pH 5) at 25 °C for 30 minutes taking the OD₄₂₀ every 5 minutes. Comparing the graphs in Figure 4 and Figure 5, the substrate saturation is not reached with 5 mM ABTS. An application of 8 mM shows less oxidized ABTS as measurements with 7 mM ABTS. Further experiments were done with 7 mM ABTS.

Figure 4: Activity assay to determine the substrate saturation with ABTS as a substrate. Measurements were done with 616 ng TTHL laccase in Britton-Robinson buffer (pH 5) at 25 °C. ABTS concentrations ranged from 0.1 mM to 5 mM.

Figure 5: Activity assay to determine the substrate saturation with ABTS as a substrate. Measurements were done with 308 ng TTHL laccase in Britton-Robinson buffer (pH 5) at 25 °C. ABTS concentrations ranged from 5 mM to 8 mM. An ABTS concentration of 7 mM was determined as substrate saturated.

TTHL pH optimum

Figure 6: Microtiter plate of the measurements for pH optimum determination. The more intensive the blue color the more ABTS got oxidized. At pH 5 the darkest color has been reached.

The pH of the medium containing the enzyme is very important for its activity. The pH optimum of TTHL is at pH 5. This is the result of activity measurements using Britton-Robinson buffer with differently adjusted pHs. TTHL laccase was re-buffered into H₂O and incubated with 0.4 mM CuCl₂. The range from pH 4 to pH 9 was tested under substrate saturation at 25 °C for 30 minutes. At pH 5 ABTS gets oxidized the fastest (see Fig. 6 and 7). At higher and lower pHs than pH 5, the activity of TTHL is decreased considerably. The resulting Units mg^-1 support the observed data (see Fig. 12). At pH 5 TTHL shows a specific enzyme activity of ~15 U mg^-1. The higher the pH, the less U mg-1 can be calculated for TTHL. At pH 4 and 6 the activity is decreased to 42 % and at pH 7 even to 14 % in comparison to pH 5. But still TTHL is active at this pH allowing an application of this laccase in a waste water treatment plant where the average pH is a pH of 6.9. However, a combination with a more effective enzyme should be considered.

Figure 7: Oxidized ABTS by TTHL laccases at different pH adjustments. The experimental setup included CuCl₂ incubated TTHL laccase (308 ng), Britton Robinson buffer adjusted to the tested pHs and 5 mM ABTS. Measurements were done at 25 °C for 30 minutes. The most amount of oxidized ABTS can be detected at pH 5.

Figure 8: Calculated specific enzyme activity of TTHL at different pH conditions. The highest specific enzyme activity for ABTS is under pH 5 conditions. The higher the pH, the less ABTS gets oxidized. One unit is defined as the amount of laccase that oxidizes 1 μmol of ABTS substrate per minute.

TTHL activity at different temperatures

Figure 9: Standard activity test for TTHL measured at 10 °C and 25 °C resulting in a decreased activity at 10 °C. As a negative control the impact of 0.4 mM CuCl₂ in oxidizing ABTS at 10 °C and 25 °C were analyzed.

Figure 10: Deriving from the obtained values of oxidized ABTS in time at 10 °C and 25 °C the specific enzyme activity was calculated. For the temperatures a difference of 2 U mg^-1 could be detected. One unit is defined as the amount of laccase that oxidizes 1 μmol of ABTS substrate per minute.

To investigate the activity of TTHL at temperatures that will apply at a waste water treatment plant throughout the year, activity tests as described above were performed at 10 °C and 25 °C. The measurements were conducted for 30 minutes. The obtained results reveal an activity decrease of about 35 % of TTHL at 10 °C in comparison to 25 °C (see Fig. 9). The obtained results were used to calculate the specific enzyme activity which was at 13 and 15 U mg^-1, respectively (see Fig. 10). The negative control without TTHL laccase but 0.4 mM CuCl₂ at 10 °C and 25 °C show a negligible oxidation of ABTS. The low difference observed between the two samples is great news for the possible application in waste water treatment plants.

Substrate Analysis

The measurements were made to test if the produced laccases were able to degrade different hormones. Therefore the produced laccases were inserted in the same concentrations (3 µg mL^-1) to the different measurement approaches. To work with the correct pH value (which were measured by the Team Activity Test) Britton Robinson buffer at pH 5 was used for all measurements. The initial substrate concentration was 5 µg mL^-1. The results of the reactions without ABTS are shown in Figure 11. On the Y-axis the percentages of degraded estradiol (blue) and ethinyl estradiol (red) are indicated. The X-axis displays the different tested laccases. The degradation was measured at t₀ and after five hours of incubation at 30 °C. The negative control was the substrate in Britton Robinson buffer and showed no degradation of the substrates. The bought laccase TVEL0 which is used as positive control is able to degrade 94.7 % estradiol and 92.7 % ethinyl estradiol. The laccase BPUL (from Bacillus pumilus) degraded 35.9 % of used estradiol after five hours. ECOL was able to degrade 16.8 % estradiol. BHAL degraded 30.2 % estradiol. The best results were determined with TTHL (laccase from Thermus thermophilus). Here the percentage of degradation amounted 55.4 %.

The results of the reactions of the laccases with addition of ABTS are shown in Figure 12. The experimental set ups were the same as the reaction approach without ABTS described above. The X-axis displays the different tested laccases. On the Y-axis the percentages of degraded estradiol (blue) and ethinyl estradiol (red) are shown. The degradation was measured at t₀ and after five hours of incubation at 20 °C. The negative control showed no degradation of estradiol. 6.8 % of ethinyl estradiol was decayed. The positive control TVEL0 is able to degrade 100 % estradiol and ethinyl estradiol. The laccase BPUL (from Bacillus pumilus) degraded 46.9 % of used estradiol after ten minutes incubation. ECOL was able to degrade 6.7 % estradiol. BHAL degraded 46.9 % estradiol. With TTHL (laccase from Thermus thermophilus)a degradation 29.5 % were determined.

Figure 11: Degradation of estradiol (dark green) and ethinyl estradiol (light green) with the different laccases after 5 hours without ABTS. In the graph it is shown that the bought laccase TVEL0 which was used as positive control is able to degrade more than 90 percent of the used substrates. None of the bacterial laccases are able to degrade ethinyl estradiol without ABTS but estradiol is degraded in a range from 16 %(ECOL) to 55 % (TTHL). The original concentrations of substrates were 2 µg per approach. (n = 4)

Figure 12: Degradation of estradiol (blue) and ethinyl estradiol (red) with the different laccases after 10 minutes hours with ABTS added. The commercial laccase TVEL0 which was used as positive control is able to degrade all of the used substrates. The bacterial laccase BPUL degraded 100 % of ethinyl estradiol and estradiol. ECOL the laccase from E. coli degraded 6.7 % estradiol and none of the used ethinyl estradiol. BHAL degraded 46.9 % of estradiol but no ethinyl estradiol. The laccase TTHL from Thermus thermophilus degraded 29.5 % of estradiol and 9.8 % ethinyl estradiol. The original concentrations of substrates were 2 µg per approach. (n = 4)

Immobilization

Figure 13: The percentage of laccases immobilized to CPC-Beads. 99 % of ECOL, 97 % of BPUL and 79 % of BHAL and TTHL laccases were bound to the beads.

Figure 14: Illustration of ABTS oxidation by TTHL with time compared to the negative control. The increase in ABTS oxidized proves laccase activity.