Composite

Part:BBa_K1866008

Designed by: Stefan Oehler   Group: iGEM15_IIT_Delhi   (2015-09-18)

Promoter+RibosomeBindingSite+NrfA+SuperYellowFluorescenceProtein (in pSB1C3)

This part has the Super Yellow Fluorescence Protein tagged to the NrfA gene product.

The Promoter+RBS+NrfA construct was obtained from our biobrick BBa_K1866000. The RBS+SYFP construct was procured from the biobrick BBa_K864101.

Gene construction & cloning:

The general cloning strategy for P+RBS+NrfA+SYFP consists of the following steps.

  • 1. The biobrick BBa_K1866000 (P+RBS+NrfA) was constructed by Team IIT Delhi iGEM 2015.
  • 2. Another biobrick consisting of the Ribosome Binding Site and SYFP BBa_K864101 was also procured.
  • 3. (P+RBS+NrfA) was doubly digested by EcoRI and SpeI enzymes to yield Eco-(P+RBS+NrfA)-Spe construct.
  • 4. (RBS+SYFP) was doubly digested by XbaI and PstI to yield Xba-(NrfA)-Pst construct.
  • 5. A linearized vector was prepared by double-digestion with EcoRI and PstI.
  • 6. The 3A assembly was performed to clone the desired construct as shown below into the linearized backbone.

    EcoRI-XbaI-(P+RBS+NrfA)-(SYFP)-SpeI-PstI


    Confirmation of the clone:

    We performed a double digestion by EcoRI and PstI to release the cloned fragment from the recombinant vector. The digestion products were resolved on an Agarose Gel by Electrophoresis and the size of the fragment confirmed the correct clone.

    Figure1: Clone confirmation

    Clone_confirmation_IIT_D_2015.jpg


    Characterization of the construct


    To check the expression of the gene, we analyzed the proteome on an SDS-PAGE. The profile that was obtained is given below:

    Figure2: SDS PAGE to check expression

    SDS_PAGE_IIT_Delhi.jpg



    Functional assay of Assimilatory Nitrite Reductase (Concept proof):


    Product Estimation:

  • 1. Minimal media growth- Following a research paper by Clarke et al., a culture of our cloned E.coli DH5α culture was grown on a minimal media containing 5% Luria Broth (by volume), 40mM Potassium Nitrate, 20mM Fumarate and 0.4% glycerol for 16 hours, in anaerobic conditions. The cells were then pelleted by centrifugation and were then to be sub cultured. This experiment failed, even though we saw a pellet after centrifugation following growth. However, we later realised that the pellet was not of our cells, but of ampicillin, which had formed some sort of white precipitate with the media. Hence, this resulted in a failure.
  • 2. pH Monitoring (LB Growth)- Cultures of our clones were grown anaerobically in 5ml of luria broth, along with standard DH5α cells, used as control. These were then subcultured into 50 ml cultures, also grown anaerobically, with different concentrations of Sodium Nitrite. After 16 hours of growth, the cultures were taken out and the pH of the solution was taken for all different concentrations of Nitrite.
  • 3. Indophenol Reagent test: The outlet stream was treated with the Phenol solution (10% Phenol w/v solution in 95% Ethanol) and Sodium Nitroprusside solution (0.5% w/v in deionized water) sequentially. Then the content was treated with an Oxidizing solution of 100ml of Alkaline solution (20% Trisodium citrate and 1% Sodium Hydroxide w/v) and 25ml Sodium Hypochlorite. The absorbance was measured at 640nm after 1 hour incubation.
  • a. Monitoring with time- For a concentration of 1mM Nitrite, multiple cultures were inoculated. After regular intervals of time, the indophenol test was carried out, and OD540 values were noted.
  • b. Monitoring with different nitrite concentrations- 50 ml Cultures were inoculated with different concentrations of Sodium nitrite. After 16 hours of growth, the indophenol test was carried out, and OD Values were taken.
  • 4. Nesseler's Reagent test: Cultures of our clones were grown anaerobically in 5ml of luria broth, along with standard DH5α cells, used as control. These were then subcultured into 50 ml cultures, also grown anaerobically, with different concentrations of Sodium Nitrite. After 16 hours of growth, the cultures were taken out and nessler’s reagent was added to a 1ml aliquot. Nessler’s reagent forms a reddish brown precipitate on reacting with ammonia, and is extremely sensitive. This culture was then centrifuged at maximum speed (13,400 rpm) for 10 minutes, and the media was decanted and dried out, leaving only the red ammonia pellet. This was then weighed against DH5α culture (given the same treatment), using the DH5α treated sample as blank (mass of ammonia pellet taken = 0).
  • 5. Fluorescence microscopy: We planned to perform the Fluorescence microscopy to check the expression of the Super Yellow Fluorescence Protein. However, we could not perform the test due to unavailability of the yellow filter. It is planned in the near future.

    Practical application of Nitrite Reductase- The Prototype

    The real-life problem that we thought of addressing was the reduction of the levels of harmful greenhouse gases like Nitrogen oxides that are usually found in the exhaust fumes of Diesel-based engines.


    We designed a prototype model to address the issue. A schematic representation of the model is given below.

    Figure5: Schematic representation of the Prototype

    CAD_prototype_model_IIT_D.png

    To test the effectiveness of our prototype, we used the exhaust of a diesel generator as a feed to the system and analyzed the outlet for the presence of the Nesseler-Ammonium precipitate based on the idea that the quantity of the precipitate would be proportional to the quantity of the reactant (Nitric Oxide) in the feed.
    Feed processing: The feed had to be processed before passing to the engineered bacterial system. It consisted of following stages.

  • 1. Removal of insolubles.
  • 2. Silica Gel-based catalysis for conversion of Nitrates in the exhaust to Nitric Oxide.
  • 3. Bubbling Nitric Oxide-containing feed through the medium containing the engineered bacterium to yield Nitrite.


    Results:


    1. Minimal Media Growth:
    This experiment failed, even though we saw a pellet after centrifugation following growth. However, we later realised that the pellet was not of our cells, but of ampicillin, which had formed some sort of white precipitate with the media. Hence, this resulted in a failure.


    2. pH monitoring:
    The experiment showed results as expected, with the pH of our clones being higher than the control, which can be attributed to the presence of excess ammonia in the solution. We also saw that at concentrations of Nitrite greater than 2mM, the pH showed a sharp decline. This could be due to the fact that high concentrations of nitrite (NO¬2-) become toxic for the cells, due to which cell death occurs.

    PH_monitoring.png


    3. Indophenol test:
    a. Monitoring with time- This experiment was successful, as it showed an increase of OD values with increase in time, before finally saturating. The OD values were more than that of DH5α cultures throughout, pointing to the fact that more ammonia was being formed in our clone cultures.

    Indophenol_test%2C_monitoring_with_time.png



    b. Monitoring with different nitrite concentrations- This experiment was also successful, with OD values showing a trend similar to the one above. At high concentrations of Sodium nitrite, the OD values showed a sharp decline, which can again be attributed to high concentrations of nitrite (>2mM) being toxic to the cells.

    Indophenol_test%2C_monitoring_with_different_nitrite_conc..png



    4. Nessler’s test (LB growth):
    This experiment was also successful, showing trends as expected. At high nitrite concentrations, the pellet size reduced drastically (the reason being toxicity at high nitrite concentration).

    Nessler%27s_test.png


    Prototype Results:

    Tests were carried out on the prototype, taking in exhaust from a diesel burner and passing it through the system. The desooter tank worked even better than expected, collecting soot out from the exhaust (which was weighed after each run). NOx sensors placed at the edge of the silica gel tube confirmed that the gel was catalysing the reaction that we intended to do, converting NO2 to NO. Proto_run_4.png

    We could, thus, successfully confirm the reduction in the levels of Nitrogen Dioxide (NO2) in the exhaust fumes of an actual diesel generator. The prototype can be optimized further for increasing the efficiency of the system.

    Sequence and Features


    Assembly Compatibility:
    • 10
      COMPATIBLE WITH RFC[10]
    • 12
      INCOMPATIBLE WITH RFC[12]
      Illegal NheI site found at 7
      Illegal NheI site found at 30
    • 21
      COMPATIBLE WITH RFC[21]
    • 23
      COMPATIBLE WITH RFC[23]
    • 25
      INCOMPATIBLE WITH RFC[25]
      Illegal AgeI site found at 380
    • 1000
      COMPATIBLE WITH RFC[1000]


  • [edit]
    Categories
    Parameters
    None