Synthetic biology is a relatively recent and fast-developing interdisciplinary
field that combines different branches of biological sciences with an engineering
approach, with the main goal of designing new biological parts, devices,systems
or redesigning existing ones. [1]
Engineering contributes to this rapidly growing field by introducing the concept of
modularity and promoting a systematic approach to both the creation of new biological
components and the design of experiments and processes: the engineering cycle.
This approach consists of four different stages, design, build, test, and learn which are supposed to be repeatedly iterated until the developed systems are sufficiently matching the desired project specifications.
In our project, this cycle was applied to every step, from designing our intracellular and extracellular expression cassette to setting up new protocols and new experiments both in wet and dry labs.
Design:
We tried to build our expression vector by inserting our new composite part (BBa_K5109001) in pJUMP29-1A plasmid backbone using the BioBrick standard.
We opted for digesting both insert and vector with EcoRI and PstI, and soon after we proceeded to clone our new expression vector inside the E. coli DH5α strain.
before starting with cloning experiments, we designed our cloning protocols in the following way:
Design:
In the beginning, we planned to use the pTac as a constitutive promoter and then add a constitutive LacI expression cassette to make our protein of interest’s expression inducible with IPTG.
After many failed attempts, we hypothesised that DeHa2 may be toxic for E. coli. Some successful ligation products may have entered our chemically competent cells, but those cells may have not survived due to the fact that the expression of our heterologous protein was too high for a constitutive pTac promoter not blocked by Lac repressor.
Instead of trying to insert the LacI expression cassette in our genetic construct, making it more complex and harder to clone than it already was, or co-transform our expression vector with an another backbone containing the LacI gene, risking to increase cells’ metabolic burden, we decided to switch to an E. coli strain containing an episome that allowed the constitutive expression of LacI, Top10 F’.
Build:
We digested pJUMP29-1A and our intracellular expression cassette containing starting enzyme DeHa2 with the aforementioned restriction enzymes EcoRI and PstI, we performed electrophoresis and gel extraction on the digestion result of both the plasmid and the synthetic insert to remove the original plasmid insert between biobrick prefix and to maintain both digestion products sticky ends, and we then transformed chemically competent Top10 F’ cells.
Test:
The transformation result was plated on a LB petri dish with kanamycin and we saw some colonies the next day, so we picked all colonies grown and we ran a colony PCR.
Learn:
All the picked and tested colonies still gave us a negative result, meaning that changing host was not sufficient to achieve cloning success.
However, we decided to stick with this idea as avoiding cloning an additional LacI expression cassette would simplify our cloning strategy and avoid burdening our cells with plasmidic co-transformation.
This choice was revealed to be the correct decision later on, when we changed our set of primers as described in cycle C-2: this step was crucial for improving our experimental design’s efficiency by shortening the amount of trials to reach a positive result.
Design:
Two different primers mapping on Biobrick prefix and suffix were designed to amplify our synthetic intracellular expression cassette, so that we could use it for clonings later on.
Primers’ sequences are:
Prefix_fw: 5’- GAATTCGCGGCCGCTTCTAGAG -3’
Suffix_rv: 5’- CCTGCAGCGGCCGCTACTAG -3’
Build:
The synthetic sequence was amplified with PCR, then digested and used throughout different cloning attempts.
Test:
Transformation results were plated on a LB-agar Petri dish with kanamycin. The colony PCR result of the few colonies that were able to grow on our kanamycin plates was then ran on an electrophoresis gel. The gel always showed the presence of a 500bp band, which meant that the plasmid contained the original insert between the prefix and suffix regions.
Learn:
After many failed attempts, we hypothesised that maybe the ligation did not occur due to either the vector or the sequence not being correctly digested by EcoRI and PstI. Therefore we analysed the primers that we used to amplify the sequence, and decided to create new ones with a bigger amount of landing bases that could increase the probability of digestion to happen.
Design:
Given the negative outcome of the previous attempts, as mentioned above we designed a new set of primers to amplify our synthetic sequences that had the following sequences
fw: 5’- CATCATGGAATTCGCGGCCGCTTC -3’
rev: 5’- CAAGCCCTGCAGCGGCCGCTA -3’
Due to time limitations, we decided to amplify with this new set of primers and perform cloning attempts only with our extracellular expression cassettes.
Build:
Our synthetic sequences were amplified by performing PCR using a High Fidelity Taq polymerase and then subsequently digested with EcoRI and PstI and cloned into pJUMP29-1A.
Test:
Transformation results were plated on a petri dish with kanamycin to see whether there were any transformed cells. As before, we picked the colonies grown on the plate and set up a colony PCR and sent them to the sequencing facility.
Learn:
After a few attempts, we were able to see colonies that tested positive for the insertion of our Lpp-OmpT-DeHa2 expression cassette (BBa_K5109023) and Lpp-OmpT-Dehalogenase S (BBa_K5109020) expression cassette,
therefore confirming our cloning success as seen in our results page.
Three hypothesis we elaborated to explain our cloning success and they are the following:
The colony number #3 showed a significantly different growth in the 500 uM medium, therefore we decided to treat it separately in the creation of the curves and in the data analysis
Learn:
We noticed a significant difference between the growth of the two colonies transformed with the Lpp-OmpT-DeHa2 construct.
Although both colonies grew slower than the wild-type, we saw that the growth of colony #4 was strongly inhibited for concentration of IPTG higher than 5 μM, while the growth of colony #9 was only slightly affected by the variation of IPTG concentrations.
From this data we deduced that the standard IPTG concentration of 500 μM was not suitable for our protein of interest’s induction in the colony #4, since it led to dosage of protein production that was lethal for our host, but could be used for the colony #9.
The sequencing that we obtained for these colonies had a really poor quality, therefore we could not make any assumptions about the genetic differences between the colonies, and we were not able to justify the differences in the growths.
For this reason and for the shortage of time, we decided to make a conservative choice and use for our enzymatic tests the lowest concentration that could be suitable for both the colonies, being the best compromise between having the biggest hypothetical amount of expressed Lpp-OmpT-DeHa2 and having the smallest effect on E. coli’s growth, which corresponded to 5 μM.
Further investigation with more colony sequencing and protein expression analysis with experiments such as SDS-PAGE and western blot should be performed to properly understand the differences between the colonies.
Design:
The first prototype we used to attempt our measurements consisted of a simple gold nanoparticles (Au-NPs) surface, designed to allow us to use both measurement techniques.
Build:
After a 5-hour liquid ablation process, we obtained a solution containing the right concentration of Au-NPs. Then, we started a spray coating process using an airbrush on a glass plate. To create a more defined surface to work on, we used a mask over the plate during the process.
Test:
We performed measurements on this first prototype using the Surface Enhanced Raman Scattering (SERS) technology, both by solution analysis with a containment chamber and via drop-casting. We analysed PFOA and PFOS.
Learn:
The solution analysis did not produce any interesting signal via SERS. With drop-casting, we confirmed that there was no adhesion of PFAS molecules on the surface, as they seemed to prefer aggregating among themselves and crystallising during the evaporation of the drop. When pointing the laser for SERS analysis on these crystals visible under the microscope, we obtained good Raman signals. Pointing it towards other parts of the surface showed no new Raman peaks. We concluded that it is necessary to add a functionalization molecule to the surface to allow PFAS adhesion.
Design:
Based on the results of cycle A, we considered molecules that might work for our purpose. We identified 11-mercapto-1-undecanol as a possible candidate. It has a Tiole group (-SH) capable of bonding well to the gold nanoparticles present on our surface, an elongated carbon chain structure and a positively polarised functional group that could interact with PFOA molecules. The PFOA molecule has a slightly negative polarity.
Build:
After carrying out the usual Au-NPs surface development process as described in cycle A, we functionalized the surface. Functionalization was performed by incubating the surface in a solution of methanol and our molecule for 1 hour to ensure proper adhesion.
Test:
We performed Electrochemical Impedance Spectroscopy (EIS) and SERS analysis on the surface to verify the correct adhesion of the functionalization molecule and then tested with a solution containing 1mM PFOA in milliQ water at various time intervals. To perform the EIS analyses, 10mM NaCl was added as the electrolyte.
SERS results showing a small variation from the bare, probably due to a small PFOA-surface interaction. 785 nm wavelength, 10X, 0.1 % power, 6x30s acquisition. The graphic is the following:
Learn:
We obtained excellent signals from the functionalization molecules with both techniques, confirming their correct and stable adhesion to the surface. However, we observe a very small variation indicating PFOA adhesion is happening, but needs further improvement. We realised that while the Tiole group allowed very stable adhesion of the molecules to the surface, further assistance was needed on the other end of the chain to promote the approach of PFOA molecules.
Design:
The results of test B-1 showed us that PFOA molecules do not interact with the detection surface. Thanks to collaboration with a student from our university, we obtained a new functionalization molecule (referred as GV38) that has a shape more similar to PFOA. It still features a Tiole group, which we had found effective for adhesion to the gold surface in cycle B-1. This time the molecule has a C9 carbon chain and a Positive Guanidinium group for interaction with PFOA. We also changed the electrolyte in the test solutions, replacing NaCl. We chose Hepes because this compound acts as a buffer and keeps the pH stable at 7.55, a value we believe can facilitate the proper interaction of PFOA with the surface.
Build:
As described in the previous cycles, we performed the gold surface creation process. This time, the functionalization solution was modified and now consists of MeOH and GV38 1mM.
Test:
We conducted our tests using EIS and SERS techniques on the surface before and after functionalization, and then after adding the solution with milliQ water + PFOA 1mM + Hepes 10mM. SERS test is made with 633 nm laser wavelength. It detects PFOA molecules thanks to the presence of two characteristic C-F bonds peaks in the Raman spectra. The graphic is the following:
EIS results showing an impedance variation due to the attachment of PFOA molecules to the detection surface. The graphic is the following:
Learn:
The results were optimal with both techniques, confirming a stable long-term interaction between our functionalized surface and the PFOA molecules. From this point we can proceed to further characterise this result and try it under different conditions.
In order to cope with PFAS pollution, water service providers utilize filters composed of granular activated carbon (GAC) which adsorbs PFAS molecules on its surface.
When GAC reaches its PFAS sorption capacity it must be removed and replaced with a new one or the treatment system will not remain effective. Exhausted GACs are replaced every two or three months with virgin ones because the only
available reactivation technique is thermal, with temperatures up to 900°C, which lowers GAC sorption capacity.
For a more in-depth description visit
Plant Design - Filters.
Design:
To change the current situation we wanted to find a regeneration technique alternative to the thermal one; we opted for a chemical regeneration through the use of a desorption solution. After a review of the literature we decided to analyse two possible desorption solutions for GAC, one with methanol and NaOH and one with ethanol.
Build:
The desorption solutions analyzed were: MeOH : H2O + NaOH 0.1 M, 50:50 and EtOH : H2O, 50:50 with 2 possible GAC mass - desorption volume ratio (200 mg of GAC with 20 mL of solution and 10 mg of GAC with 100 mL of solution).
Test:
To analyze solvent regeneration of GAC we made 6 tests to compare the effectiveness of wet adsorbent with a dried one, select one of two possible GAC mass - desorption volume ratio and decide on the best desorption solution between the two proposed.
Learn:
Through the data obtained from our GAC desorption experiments we understood that the solutions proposed have not the efficacy required to be applied to an industrial context; moreover a scale-up of this chemical desorption technique would require elevated volume of methanol or ethanol, posing an environmental and economical issue (for the economical aspect visit
Entrepreneurship
). Further studies should be conducted on the subject, analyzing other organic and non-organic solutions and focusing on their effect on Filtrasorb 400, the GAC type used commercially. In addition, it is important to bear in mind the need to have low volumes of possible toxic solutions used in the scaleup system so as to be environmentally friendly and economically feasible.
Design:
We then focused our attention on finding an adsorbent with higher sorption capacity than GAC and that can be regenerated using a non-organic solution. This would reduce the need to replace filters so frequently, reducing costs and environmental impact.
Build:
We focused on AER (anion exchange resins) as multiple studies find them to have high sorption capacity and we found out it could be regenerated using a desorption solution made with a 10% w/V NaCl solution.
Test:
To understand the adsorption capacity of the resins selected (A860, A110, A111) we put them in contact with PFOA and PFBA solutions (CPFOA=3,75 * 10-3 mol/L and CPFBA=5,27* 10-3 mol/L ) for 2 hours and measured the concentration of pollutants every half hour.
To analyse the intended AER chemical regeneration, we adopted the NaCl solution for the 3 investigated resins.
Learn: