Team:Bielefeld-Germany/Results/comparison

Activity Test

Comparison of our produzed enzymes and TVEL0 regarding their activity in a pH of 5. BPUL clearly shows the highest specific enzyme activity of 38 U mg^-1.

Comparison of our produzed enzymes and TVEL0 regarding their activity in a pH of 7. BPUL clearly shows the highest specific enzyme activity of 11 U mg^-1.

To optimize the application of our enzymes [http://partsregistry.org/wiki/index.php?title=Part:BBa_K863000 BPUL], [http://partsregistry.org/wiki/index.php?title=Part:BBa_K863005 ECOL], [http://partsregistry.org/wiki/index.php?title=Part:BBa_K863022 BHAL] and [http://partsregistry.org/wiki/index.php?title=Part:BBa_K863010 TTHL] in a waste water treatment plant the obtained results were compared and further analyzed. All laccases show an optima at pH 5. However BPUL distinguishes from the other enzymes by showing a signigicantly higher enzyme activity. At pH 7 respectively the maximal activity is as well seen in the BPUL sample. At pH 5 ECOL, BPUL, BHAL, TTHL and TVEL0 show an average activity of 10-15 U mg^-1. Though at pH 7 the enzymes activities were calculated to not exceed 2 U mg^-1, respectively. This indicates that at pH values of around 7 BPUL is the best choice for our filter and if other enzymes are desired or needed an higher amount has to be used.

Comparison of our produzed enzymes and TVEL0 regarding their activity at 10°C. BPUL clearly shows the highest specific enzyme activity of 37 U mg^-1.

Regarding the temperature characterizations BPUL is observed to show an enzyme activity of 37 U mg^-1. ECOL, BPUL, BHAL, TTHL and TVEL0 show an activity of 2 to 13 U mg^-1. Thus BPUL and also TTHL are very feasible for an application even in cold environments. For a usage of BHAL and ECOL a longer incubation time of the laccases and the substrates needs to take place to ensure a proper degradations of microcontaminents.

Immobilization

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 2. 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 3. 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 2: 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 3: 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)