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| | Achieving high expression rates of recombinant proteins is often difficult in <i>C. reinhardtii</i>. Transgenes are randomly integrated into the genome and consequently their expression is influenced by the genetic surrounding of the insertion site. We hoped to <a href="/Team:Humboldt_Berlin/Design">increase expression</a>, by inserting our DNA construct into a defined region of the <i>C. reinhardtii</i> genome. | | Achieving high expression rates of recombinant proteins is often difficult in <i>C. reinhardtii</i>. Transgenes are randomly integrated into the genome and consequently their expression is influenced by the genetic surrounding of the insertion site. We hoped to <a href="/Team:Humboldt_Berlin/Design">increase expression</a>, by inserting our DNA construct into a defined region of the <i>C. reinhardtii</i> genome. |
| − | With CRISPR/Cas9, we targeted three different loci to insert our expression constructs. | + | With CRISPR/Cas9, we targeted three different loci to insert our transgenic constructs. |
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| − | To see if our Cas9 assays work in general, we first used the easy screenable SNF-related serine/threonine-protein kinase (<i>SNRK2.2</i>) locus. Inactivation of the <i>SNRK2.2</i> gene leads to the constitutive expression of arylsulfatase, which gets secreted into the media. The presence of arylsulfatase can easily monitored with a color reaction. By cleaving the sulfate group from the colourless substrate 5-bromo-4-chloro-3-indolyl-sulfate (X-SO<sub>4</sub>) the indolblue dye is formed (Fig. 8). This blue-green screen allows an efficient screening of CRISPR/Cas9-directed insertion mutants. | + | To see if our Cas9 assays work in general, we first used the easy screenable SNF-related serine/threonine-protein kinase (<i>SNRK2.2</i>) locus. Inactivation of the <i>SNRK2.2</i> gene leads to the constitutive expression of arylsulfatase, which gets secreted into the medium. The presence of arylsulfatase can easily monitored with a color reaction. By cleaving the sulfate group from the colourless substrate 5-bromo-4-chloro-3-indolyl-sulfate (X-SO<sub>4</sub>) the dye indole blue is formed (Fig. 8). This blue-green screen poses as an efficient method of finding CRISPR/Cas9-directed insertion mutants. |
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| − | The first construct we inserted into the <i>SNRK2.2</i> locus was the level 1 construct <a href="http://parts.igem.org/wiki/index.php?title=Part:BBa_K2984019" >L1c-Psad-YFP-Rbcs2</a>. This experiment delivered us our first positive YFP-expressed clone, which exhibits a robust expression of mVenus. Subsequently, we performed a colony PCR with <i>SNRK2.2</i> locus specific primers, to amplify the insert. The <i>SNRK2.2</i> specific amplification without an insert would lead to bands with a length of approximately 200 bp. If the insert was successfully inserted into the <i>SNRK2.2</i> gene, we expect a band of approximately 2000 bp. The PCR results showed that the insertion of the YFP construct into the <i>SNRK2.2</i> locus was only partly successful (Fig. 9). We can see a bigger band at around 5000 bp. The YFP clone is labeled on Fig. 9 as A4. We sent the bands of a length of 5000 bp to sequencing but obtained only overlayed signals from a mix of PCR products. So the <i>SNRK2.2</i> target site was cut by CRISPR/Cas9 but we can't say, if the YFP construct is inserted along with other sequences, inserted twice or not inserted at all. | + | The first construct we inserted into the <i>SNRK2.2</i> locus was the level 1 construct <a href="http://parts.igem.org/wiki/index.php?title=Part:BBa_K2984019" >L1c-Psad-YFP-Rbcs2</a>. This experiment delivered us our first positive YFP-expressing clone exhibiting a robust expression of mVenus. Then, we performed a colony PCR with <i>SNRK2.2</i> locus-specific primers to amplify the insert. The <i>SNRK2.2</i> specific amplification without an insert would lead to bands with a length of approximately 200 bp. If the insert was successfully inserted into the <i>SNRK2.2</i> gene, we expected a band of approximately 2000 bp. The PCR results showed that the insertion of the YFP construct into the <i>SNRK2.2</i> locus was only partly successful (Fig. 9). We can see a bigger band at around 5000 bp. The YFP-expressing clone is labeled on Fig. 9 as A4. We sent the bands of a length of 5000 bp to sequencing but obtained only overlayed signals from a mix of PCR products. So the <i>SNRK2.2</i> target site was cut by CRISPR/Cas9 but we have no certainty if the YFP construct is inserted along with other sequences, inserted twice or not inserted at all. |
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| − | After the <a href="https://2019.igem.org/Team:Humboldt_Berlin/Experiments">transformation of our algae with CRISPR/Cas9 ribonucleoproteins</a> we did colony PCRs as a screening method to examine if the insertion into the loci was successful. Hereby we designed primers that bind to the <i>PSAD</i> and <i>RBCS2</i> genes to investigate if the insertion worked as planned. | + | After the <a href="https://2019.igem.org/Team:Humboldt_Berlin/Experiments">transformation of our algae with CRISPR/Cas9 ribonucleoproteins</a> we performed colony PCRs as a screening method to examine if the insertion into the loci was successful. For this, we designed primers that bind to the <i>PSAD</i> and <i>RBCS2</i> genes to investigate if the insertion worked as planned. |
| | </p> | | </p> |
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| − | The PCR result, seen on Fig. 10, shows the analysis of 96 clones that were transformed to target a YFP construct into <i>PSAD</i> and <i>RBCS2</i>. Only for the wild type (WT) probe of RbcS2, a clear PCR band can be seen at the expected length. No clear bands can be observed in the other samples. This indicates that there was a problem with the PCR parameters and fragments were not amplified correctly. Due to the fact that we did this experiment at the end of our project, we did not have enough time to do further screening or transformations to answer the question of high expression loci in <i>C. reinhardtii</i>. | + | The PCR result, seen on Fig. 10, shows the analysis of 96 clones that were transformed to target a YFP construct into <i>PSAD</i> and <i>RBCS2</i>. Only for the wild type (WT) probe of RbcS2 a clear PCR band can be seen at the expected length. No clear bands can be observed in the other samples. This indicates that there was a problem with the PCR parameters and fragments were not amplified correctly. Due to the fact that we did this experiment at the end of our project we did not have enough time to do further screening or transformations to identify high expression loci in <i>C. reinhardtii</i>. |
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| − | We had a <i>C. reinhardtii</i> clone which was successfully transformed with our <a href="http://parts.igem.org/wiki/index.php?title=Part:BBa_K2984019">YFP mVenus construct</a> and showed abundant expression of the protein. We wanted to investigate in which locus our transgene was inserted, so we planned a RESDA PCR. | + | We cultivated a <i>C. reinhardtii</i> clone which was successfully transformed with our <a href="http://parts.igem.org/wiki/index.php?title=Part:BBa_K2984019">YFP mVenus construct</a> and showed abundant expression of the protein. We wanted to investigate in which locus our transgene was inserted, so we planned a RESDA PCR. |
| | </p> | | </p> |
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| − | The RESDA PCR method is a PCR method designed to identify the insertion locus of transgenes. The method was developed by González-Ballester et al. (2005) and is based on the amplification of the transgene from the genome using primers that bind on recurrent restriction sites in the genome (González-Ballester et al. 2005) . For the amplification of the transgene, a primer is used that binds on the insert, and another primer that bind on one of the recurrent enzymes in the genome, in hope that the insert is close enough to a restriction site to be amplified. The amplification is done through two different rounds, where the second round uses nested primers to narrow down the specificity of the amplification. After the amplification the fragment can be sequenced to determine its locus. | + | The RESDA PCR method is a PCR method designed to identify the insertion locus of transgenes. The method was developed by González-Ballester and his colleagues and is based on the amplification of a transgene from the genome using primers that bind on recurrent restriction sites in the genome (González-Ballester et al. 2005). To amplify the transgene, one primer that binds to the insert is used and another primer that binds to one of the recurrent enzymes in the genome, in hope that the insert is close enough to a restriction site to be amplified. The amplification is done through two different rounds where the second round uses nested primers to narrow down the specificity of the amplification. After the amplification the fragment can be sequenced to determine its locus. |
| | </p> | | </p> |
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| − | Our goal was to determine the locus of insertion of our YFP mVenus construct, to see if we could use this locus for future directed insertion of transgenes with CRISPR-Cas9. Additionally, we also performed the RESDA-PCR with a luciferase expressing clone kindly provided by the research group of Prof. Dr. Hegemann of the Humboldt University of Berlin. | + | Our goal was to determine the locus of insertion of our YFP mVenus construct, to see if we could use this locus for future directed insertion of transgenes with CRISPR/Cas9. Additionally, we also performed the RESDA-PCR with a luciferase-expressing clone kindly provided by the research group of Prof. Dr. Hegemann of the Humboldt University of Berlin. |
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| | <!--- IMAGE ---> | | <!--- IMAGE ---> |
| | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/9/97/T--Humboldt_Berlin--RESDA-PCR.jpg" /> | | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/9/97/T--Humboldt_Berlin--RESDA-PCR.jpg" /> |
| − | <figcaption>Fig. 11 - Agarose of a RESDA-PCR. There are no clear bands to be observed, only primer clouds at the bottom of the probes. Labels: TM05 and F7: luciferase expressing clone, A4: YFP expressing clone, WT: wild type.</figcaption> <figure> | + | <figcaption><b>Fig. 11 - Agarose gel of a RESDA-PCR; there are no clear bands to be observed, only primer clouds at the bottom of the probes. </b>Labels: TM05 and F7: luciferase expressing clone, A4: YFP expressing clone, WT: wild type.</figcaption> <figure> |
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| | <!-----------------------------------------------------------------------> | | <!-----------------------------------------------------------------------> |
| − | <!------------------PET Degradiation in-silico-----------------------> | + | <!------------------PET Degradation in-silico-----------------------> |
| | <!-----------------------------------------------------------------------> | | <!-----------------------------------------------------------------------> |
| − | <h3 class="headline3">PET-degradation in-silico</h3> | + | <h3 class="headline3">PET-degradation <i>in-silico</i></h3> |
| | </div> | | </div> |
| | <div class="expandable-preview"> | | <div class="expandable-preview"> |
| | <p class="medium-sized"> | | <p class="medium-sized"> |
| − | The viability of PET degradation by <i>C. reinhardtii</i> at a larger scale is yet unknown. Models of biological systems allow us to design experiments <i>in silico</i> that are difficult to reproduce <i> in vivo</i> and give us special insights into the role that parameters might play in the given biological system. Therefore, to assess the efficiency of PET degradation by <i>C. reinhardtii</i>, a model of PET degradation in continuous culture of <i>C. reinhardtii</i> was designed. | + | The viability of PET degradation by <i>C. reinhardtii</i> at a larger scale is yet unknown. Models of biological systems allow us to design experiments <i>in silico</i> that are difficult to reproduce <i> in vivo</i> and give us special insights into the role that parameters might play in the given biological system. Therefore, to assess the efficiency of PET degradation by <i>C. reinhardtii</i>, a mathematical model of PET degradation in a continuous culture of <i>C. reinhardtii</i> was designed. |
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| − | The overall goal of the model is to determine the time needed to degrade 1 mg of PET. The model took into account enzyme expression, secretion and kinetics and also the cultivation density of the algae as decisive factors for the PET degradation rate. The model predicted that for a cultivation density of 1:10, a 40 g PET bottle would be degraded in approximately 10 years. For a cultivation density of 1:100, the predicted time to degrade a bottle was 100 years. Additionally, an improvement of the PETase enzyme by a factor 1000 was made. For a cultivation density of 1:10 and the improved enzyme, the time needed to degrade a bottle was 119 days. For a cultivation density of 1:100 and the improved enzyme, the time needed to degrade a bottle was 3,3 years. The results of the model led us to take several decisions regarding the improvement of the PET degradation. We chose to use the light-inducible PsaD promoter for our constructs, the secretion enhancing glycomodule SP<sub>20</sub>, the specialized <i>C. reinhardtii</i> strain UVM4 for transgene expression and the flat panel cultivation method to achieve higher cultivation densities. For more information please visit our model page <a href="/Team:Humboldt_Berlin/Model">here</a>. | + | The overall goal of the model is to determine the time needed to degrade 1 mg of PET. The model takes into account enzyme expression, secretion and kinetics and also the cultivation density of the algae as decisive factors for the PET degradation rate. It predicted that for a cultivation density of 1:10, a 40 g PET bottle would be degraded in approximately 10 years. For a cultivation density of 1:100, the predicted time to degrade a bottle was 100 years. Additionally, an improvement of the PETase enzyme by a factor 1000 was made. For a cultivation density of 1:10 and the improved enzyme, the time needed to degrade a bottle was 119 days. For a cultivation density of 1:100 and the improved enzyme, the time needed to degrade a bottle was 3,3 years. The results of the model led us to take several decisions regarding the improvement of the PET degradation. We chose to use the light-inducible PsaD promoter for our constructs, the secretion enhancing glycomodule SP<sub>20</sub>, the specialized <i>C. reinhardtii</i> strain UVM4 for increased transgene expression and the flat panel cultivation method to achieve higher cultivation densities. For more information please visit our <a href="/Team:Humboldt_Berlin/Model">model page</a>. |
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| | <!--- IMAGE ---> | | <!--- IMAGE ---> |
| | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/6/6e/T--Humboldt_Berlin--PETase_Model_1_to_10.png" alt="PET 1 to 10" alt="PET degradation" /> | | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/6/6e/T--Humboldt_Berlin--PETase_Model_1_to_10.png" alt="PET 1 to 10" alt="PET degradation" /> |
| − | <figcaption> Fig. 12 - Results of the PET degradation simulation for the cultivation density 1:10 </figcaption> </figure> | + | <figcaption> Fig. 12 - Results of the PET degradation simulation for the cultivation density 1:10. </figcaption> </figure> |
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| | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/7/7f/T--Humboldt_Berlin--PETase_Model_1_to_100.png" alt="PET 1 to 100" /> | | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/7/7f/T--Humboldt_Berlin--PETase_Model_1_to_100.png" alt="PET 1 to 100" /> |
| − | <figcaption> Fig.13 - Results of the PET degradation simulation for the cultivation density 1:100 </figcaption> </figure> | + | <figcaption> Fig. 13 - Results of the PET degradation simulation for the cultivation density 1:100. </figcaption> </figure> |
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| | <div class="expandable-preview"> | | <div class="expandable-preview"> |
| | <p class="medium-sized"> | | <p class="medium-sized"> |
| − | Expressing and secreting PETase in <i>C. reinhardtii</i> was one of the main goals of our project. To be able to express the PETase, we designed a wide variety of constructs with functional parts from our <a href="/Team:Humboldt_Berlin/Part_Collection">Chlamy-HUB Collection</a>. | + | Expressing and secreting PETase and MHETase in <i>C. reinhardtii</i> was one of the main goals of our project. To be able to express the PETase, we designed a wide variety of constructs with functional parts from our <a href="/Team:Humboldt_Berlin/Part_Collection">Chlamy-HUB Collection</a>. |
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| − | These constructs were systematically designed to experimentally test the expression and secretion of PETase. Additionally, we designed the constructs with different markers for detection or measurement of the enzyme, like the yellow fluorescent protein mVenus, HA-tags and His-tags. Construct <a href="http://parts.igem.org/Part:BBa_K2984028">BBa_K2984028 </a> was for example designed for enhanced secretion of PETase, marked with the YFP mVenus. Or construct <a href="http://parts.igem.org/Part:BBa_K2984039">BBa_K2984039</a>, designed for expression of the enzyme, marked with a HA-tag for detection, isolation and purification. For more constructs you can visit our <a href="/Team:Humboldt_Berlin/Composite_Part">composite parts</a> page. | + | These constructs were systematically designed to experimentally test the expression and secretion of PETase. Additionally, we designed the constructs with different markers for detection or measurement of the enzyme, like the yellow fluorescent protein mVenus, HA-tags and His-tags. Construct <a href="http://parts.igem.org/Part:BBa_K2984028">BBa_K2984028 </a> was for example designed for enhanced secretion of PETase, marked with the YFP mVenus. Or construct <a href="http://parts.igem.org/Part:BBa_K2984039">BBa_K2984039</a>, designed for expression of the enzyme, marked with a HA-tag for detection, isolation and purification. To see more constructs you can visit our <a href="/Team:Humboldt_Berlin/Composite_Part">composite parts</a> page. |
| | </p> | | </p> |
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| | <!-- IMAGE --> | | <!-- IMAGE --> |
| − | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/3/39/T--Humboldt_Berlin--PETase.jpg" alt="PETase" /><figcaption>Fig. 14 - Crystal structure of the PETase enzyme</figcaption></figure> | + | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/3/39/T--Humboldt_Berlin--PETase.jpg" alt="PETase" /><figcaption><b>Fig. 14 - Crystal structure of the PETase enzyme.</b></figcaption></figure> |
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| − | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/1/1b/T--Humboldt_Berlin--PETase_Gel.jpg" alt="PETase Gel" /><figcaption>Fig. 15 - Amplification of the PETase transgene out of <i>C. reinhardtii</i> through a colony PCR. Successful transformation of the construct. Expected band length: 885 bp </figcaption></figure> | + | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/1/1b/T--Humboldt_Berlin--PETase_Gel.jpg" alt="PETase Gel" /><figcaption><b>Fig. 15 - Amplification of the PETase transgene of <i>C. reinhardtii</i> through a colony PCR shows successful transformation of the construct.</b> Expected band length: 885 bp. </figcaption></figure> |
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| − | <img class="is-revealing" src="https://2019.igem.org/wiki/images/1/12/T--Humboldt_Berlin--MHETase.jpg" alt="MHETase" /><figcaption>Fig. 16 - Crystal structure of the MHETase enzyme</figcaption> | + | <img class="is-revealing" src="https://2019.igem.org/wiki/images/1/12/T--Humboldt_Berlin--MHETase.jpg" alt="MHETase" /><figcaption><b>Fig. 16 - Crystal structure of the MHETase enzyme.</b></figcaption> |
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| − | <img class="is-revealing" src="https://2019.igem.org/wiki/images/0/0a/T--Humboldt_Berlin--MHETase_Gel_2.jpg" alt="MHETase Gel" /><figcaption>Fig. 17 - Amplification of the MHETase transgene out of <i>C. reinhardtii</i> through a colony PCR. Due to problems with the primer we had issues with unspecific bands in the gel. The successful transformation of the construct could not be confirmed. </figcaption> | + | <img class="is-revealing" src="https://2019.igem.org/wiki/images/0/0a/T--Humboldt_Berlin--MHETase_Gel_2.jpg" alt="MHETase Gel" /><figcaption><b>Fig. 17 - Amplification of the MHETase transgene out of <i>C. reinhardtii</i> through a colony PCR.</b> Due to problems with the primer we had issues with unspecific bands in the gel. The successful transformation of the construct could not be confirmed. </figcaption> |
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| − | The constructs were all assembled using the MoClo standard and then transformed into <i>C. reinhardtii</i>. After the transformation, the clones had to be screened for positive transgene insertion. The screening was done through colony PCRs, where the inserted fragments were fully or partially amplified to verify transgene insertion. Unfortunately, our initial PETase level 0 part was missing one nucleotide, which led to a frameshift of all subsequent parts in the construct. Although we had done many transformations of PETase constructs, it was not until two months into our transformation workflow that we discovered this mistake. This made our PETase impossible to screen, because all markers for detection were located after the PETase sequence and had the aforementioned frameshift. | + | The constructs were all assembled using the MoClo standard and then transformed into <i>C. reinhardtii</i>. After the transformation, the clones had to be screened for positive transgene insertion. The screening was done through colony PCRs, where the inserted fragments were fully or partially amplified to verify transgene insertion. Unfortunately, our initial PETase level 0 part was missing one nucleotide, which led to a frameshift of all subsequent parts in the construct. Although we had done many transformations of PETase constructs it was not until two months into our transformation workflow that we discovered this mistake. This made our PETase impossible to screen, because all markers for detection were located after the PETase sequence and had the aforementioned frameshift. |
| | </p> | | </p> |
| | <p class="block-text medium-sized"> | | <p class="block-text medium-sized"> |
| − | After successfully correcting the mistake in the PETase sequence, we were able to successfully transform a PETase construct into <i>C. reinhardtii</i>. We transformed construct <a href=”http://parts.igem.org/wiki/index.php?title=Part:BBa_K2984032”>BBa_K2984032</a> into <i>C. reinhardtii</i>, which contains the secretion signal ARS and a HA-tag to detect and isolate the enzyme. In Fig. 15, the successful amplification of the PETase enzyme out of <i>C. reinhardtii</i> via colony PCR can be seen. The expected length of the fragment was 885 bp or approximately 900 bp. The probes were sent to sequencing and we could verify that the sequence of the PEtase was intact after the insertion into <i>C. reinhardtii</i>. Unfortunately we did not have enough time to do further tests and experiments with the transformed clone. | + | After successfully correcting the mistake in the PETase sequence, we were able to successfully transform a PETase construct into <i>C. reinhardtii</i>. We transformed construct <a href=”http://parts.igem.org/wiki/index.php?title=Part:BBa_K2984032”>BBa_K2984032</a> into <i>C. reinhardtii</i>, which contains the secretion signal ARS and an HA-tag to detect and isolate the enzyme. In Fig. 15, the successful amplification of the PETase enzyme of <i>C. reinhardtii</i> via colony PCR can be seen. The expected length of the fragment was 885 bp or approximately 900 bp. The samples were sent to sequencing and we could verify that the sequence of the PETase was intact after the insertion into <i>C. reinhardtii</i>. Unfortunately we did not have enough time to do further tests and experiments with the transformed clone. |
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| − | When it comes to cultivating our transgenic alga in the bioreactor it is not only important to know about the toxicity of the PET degradation products. Since the alga should degrate PET, we also checked if the presence of substantial amounts of microplastic in the media affects the growth of <i>C. reinhardtii</i>. | + | When it comes to cultivating our transgenic alga in the bioreactor it is not only important to know about the toxicity of the PET degradation products. Since the alga should degrade PET, we also checked if the presence of substantial amounts of microplastic in the media affected the growth of <i>C. reinhardtii</i>. |
| − | To determine the range of possible applications for <i>C. reinhardtii</i> for plastic degradation we performed toxicity tests of different strains. We assessed whether the degradation products of MHET, terephthalic acid (TPA) and ethylene glycol (EG) are toxic for <i>C. reinhardtii</i> and showed that TPA is not toxic for the alga whereas EG was toxic in concentrations only above 7%. As shown by our model, even the most optimistic catalytic rates would not yield such high EG concentrations. Therefore, we can be confident that Chlamy can survive degrading PET in a bioreactor setup. | + | To determine the range of possible applications for <i>C. reinhardtii</i> for plastic degradation we performed toxicity tests on different strains. We assessed whether the degradation products of MHET, terephthalic acid (TPA) and ethylene glycol (EG) are toxic for <i>C. reinhardtii</i> and showed that TPA is not toxic for the alga whereas EG is toxic in concentrations only above 7%. As shown by our model, even the most optimistic catalytic rates would not yield such high EG concentrations. Therefore, we can be confident that our algae can survive degrading PET in a bioreactor setup. |
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| | <p><b>Toxicity test setup</b></p> | | <p><b>Toxicity test setup</b></p> |
| | <p> | | <p> |
| − | We performed our toxicity tests inside a Multi-cultivator “MC1000”. This cultivator enables measurement observation of growth curves with different media.</p> | + | We performed our toxicity tests in a Multi-cultivator “MC1000”. This cultivator enables measurement of growth in different media creating growth curves.</p> |
| − | <p>The growth of <i>C. reinhardtii</i> was observed by measuring the optical density at OD 680 nm. At this wavelength, photosystem II has its absorption maximum, so this measurement is typical for phototrophic organisms. To exclude a possible contamination, the cultivator also measured the OD at 720 nm where every other organism absorbs. The ratio of both measurements shows the reproduction of either <i>C. reinhardtii</i> or a contamination (e.g. bacteria). | + | <p>The growth of <i>C. reinhardtii</i> was observed by measuring the optical density at OD 680 nm. At this wavelength, photosystem II has its absorption maximum, so measuring at this wavelength is common when cultivating phototrophic organisms. To exclude a possible contamination the cultivator also measured the OD at 720 nm where every other organism absorbs. The ratio of both measurements shows the reproduction of either <i>C. reinhardtii</i> or a contamination (e.g. bacteria). |
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| | <!--- IMAGE ---> | | <!--- IMAGE ---> |
| | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/3/34/T--Humboldt_Berlin--results_reactor_set-up.png" alt="Multi-cultivator MC1000" /> | | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/3/34/T--Humboldt_Berlin--results_reactor_set-up.png" alt="Multi-cultivator MC1000" /> |
| − | <figcaption>Fig. 18 - Multi-cultivator “MC-1000” cultivating <i>C. reinhardtii</i> at different cell densities</figcaption></figure> | + | <figcaption><b>Fig. 18 - Multi-cultivator “MC-1000” cultivating <i>C. reinhardtii</i> at different cell densities. </b></figcaption></figure> |
| | | | |
| | </div> | | </div> |
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| | <p><b>Toxicity test for Terephthalic acid (TPA)</b></p> | | <p><b>Toxicity test for Terephthalic acid (TPA)</b></p> |
| | <p> | | <p> |
| − | To determine the toxicity of TPA, growth experiments were performed with the wild type <i>C. reinhardtii</i> strain CC125. The solubility of TPA is fairly low with ~15 µg/l. For these measurements, different dilutions of TPA in the standard TAP medium were tested inside the Multicultivator 1000. Figure 19 shows the growth curve of <i>C. reinhardtii</i> measured by an OD at 680nm (shown in green). TPA was dissolved in TAP medium, where TPA reaches its saturation at 15 µg/l. Even concentrations more than 15 µg/l (where TPA precipitates) did not have an influence on the reproduction of <i>C. reinhardtii</i>. The red curve illustrates the OD at 720nm. Since these curves do not show an abnormal increase, the cultivator was not contaminated. | + | To determine the toxicity of TPA growth experiments were performed with the wild type <i>C. reinhardtii</i> strain CC-125. The solubility of TPA is fairly low with ~15 µg/l. In these measurements different dilutions of TPA in the standard TAP medium were tested inside the Multi-cultivator 1000. Figure 19 shows the growth curve of <i>C. reinhardtii</i> determined at 680 nm (shown in green) by measuring the OD. TPA was dissolved in TAP medium. Even concentrations of more than 15 µg/l (where TPA precipitates) did not have an influence on the reproduction of <i>C. reinhardtii</i>. The red curve illustrates the OD at 720nm. Since these curves do not show an abnormal increase, the cultivator was not contaminated. |
| | This shows that growth of <i>C. reinhardtii</i> is not influenced by TPA. | | This shows that growth of <i>C. reinhardtii</i> is not influenced by TPA. |
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| | <!--- IMAGE ---> | | <!--- IMAGE ---> |
| | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/a/ac/T--Humboldt_Berlin--results_toxtest_tpa_cc125.png" alt="fluorescence intensity" /> | | <figure class="is-revealing"> <img src="https://2019.igem.org/wiki/images/a/ac/T--Humboldt_Berlin--results_toxtest_tpa_cc125.png" alt="fluorescence intensity" /> |
| − | <figcaption>Fig. 19 - Growth of <i>C. reinhardtii</i> wild type CC125 at 680 nm and 720 nm under soluble and saturated (15 µg/l) TPA concentration in comparison to a TAP control. Cells were cultivated inside the Multicultivator MC100 under 150 µE light at 30°C.</figcaption> | + | <figcaption><b>Fig. 19 - Growth of <i>C. reinhardtii</i> wild type CC-125 at 680 nm and 720 nm under soluble and saturated (15 µg/l) TPA concentration in comparison to a TAP control. </b>Cells were cultivated inside the Multi-cultivator 100 under 150 µE light at 30°C.</figcaption> |
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| | </div> | | </div> |
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| | <p><b>Toxicity test for ethylene glycol</b></p> | | <p><b>Toxicity test for ethylene glycol</b></p> |
| | <p> | | <p> |
| − | Ethylene glycol, Ethan-1,2-diol (EG) is a colourless organic compound with the formula (CH<sub>2</sub>OH)2. It has a LD<sub>50</sub> in rats (orally) 4700 mg·kg−1. The toxic effect comes through its byproducts glycolaldehyde, glyoxal and glyoxylic acid. To determine the toxic effect of EG on <i>C. reinhardtii</i> the growth of several strains at concentrations of 1% to 10% EG were tested. | + | Ethylene glycol, Ethan-1,2-diol, (EG) is a colourless organic compound with the formula (CH<sub>2</sub>OH)2. It has a LD<sub>50</sub> in rats (orally) 4700 mg·kg<sup>−1</sup>. The toxic effect relies on its byproducts glycolaldehyde, glyoxal and glyoxylic acid. To determine the toxic effect of EG on <i>C. reinhardtii</i> the growth of several strains at concentrations of 1 % to 10 % EG was tested. |
| | </p> | | </p> |
| − | <p>Figure 20 shows that <i>C. reinhardtii</i> wild type CC125 is able to tolerate EG concentrations up to 5% without showing growth limitation. A concentration of 4% decreases the growth speed but growth maximum is reached. Concentrations starting at 7% are lethal to the alga. | + | <p><b>Figure 20 shows that <i>C. reinhardtii</i> wild type CC125 is able to tolerate EG concentrations up to 5 % without showing growth limitation. </b>A concentration of 4 % decreases the growth speed but nevertheless growth maximum is reached. Concentrations starting at 7 % are lethal to the alga. |
| | + | But due to the turnover rate of the enzymes PETase and MHETase the concentration of EG will never reach a concentration more than 1-2 %. |
| | + | This fact makes it possible for <i>C. reinhardtii</i> to survive in an environment where these products arise. Thus, <i>Chlamydomonas</i> represents a good model organism to tolerate the process of PET degradation. |
| | | | |
| − | But due to the turnover rate of the enzymes PETase and MHETase, the concentration of EG will never reach a concentration more than 1-2%.
| + | We further did the same measurement using the <i>C. reinhardtii</i> mutant strain UVM4 that lacks a cell wall. The graph in figure 21 also demonstrates that already concentrations of 6 % inhibit the growth of this mutant strain. |
| − | This fact makes it possible for <i>C. reinhardtii</i> to survive in an environment where these products arise. Thus, Chlamy represents a good model organism to tolerate the process of PET degradation.
| + | |
| − | | + | |
| − | We further did the same measurement using the <i>C. reinhardtii</i> mutant strain UVM4 that does not have a cell wall. The graph in figure 21 also demonstrates that already concentrations of 6% inhibit the growth of this mutant strain. | + | |
| | | | |
| | </p> | | </p> |
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| | <p><b>Toxicity test on the effect of microplastic</b></p> | | <p><b>Toxicity test on the effect of microplastic</b></p> |
| | <p> | | <p> |
| − | When it comes to cultivating our transgenic alga in the bioreactor it is not only important to know about the toxicity of the PET degradation products. Since the alga should degrate PET, we also checked if the presence of substantial amounts of microplastic in the media affects the growth of <i>C. reinhardtii</i> . From our visit at the “wastewater treatment facility” we learned that the cleaned water, that leaves the facility, has an average microplastic concentration of 15 mg/L.(A. Matzinger 2018). We set up cultivation experiments with varying concentrations of microplastic particles (<40 µm). | + | When it comes to cultivating our transgenic alga in the bioreactor it is not only important to know about the toxicity of the PET degradation products. Since the alga should degrade PET, we also checked if the presence of substantial amounts of microplastic in the media affects the growth of <i>C. reinhardtii</i>. From our visit at the wastewater treatment facility we learned that the cleaned water that leaves the facility has an average microplastic concentration of 15 mg/L (A. Matzinger, 2018). We set up cultivation experiments with varying concentrations of microplastic particles (<40 µm). |
| | </p> | | </p> |
| | </div> | | </div> |
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| | <figure class="is-revealing" > | | <figure class="is-revealing" > |
| | <img src="https://2019.igem.org/wiki/images/5/54/T--Humboldt_Berlin--results_toxtest_microplastic_sag11-32b.png" alt="fluorescence intensity" /> | | <img src="https://2019.igem.org/wiki/images/5/54/T--Humboldt_Berlin--results_toxtest_microplastic_sag11-32b.png" alt="fluorescence intensity" /> |
| − | <figcaption>Fig. 22 - For the amount of microplastic and the period of time that we tested, we could not measure an effect on the alga growth. For some measurements we observed deviations which could be due to microplastic particles interfering with the OD sensores of the multi-cultivator. | + | <figcaption><b>Fig. 22 - For the amount of microplastic and the period of time that we tested we could not measure an effect on the alga growth. </b>For some measurements we observed deviations which could be due to microplastic particles interfering with the OD sensores of the multi-cultivator. |
| | </figcaption></figure> | | </figcaption></figure> |
| | </br></br></br> | | </br></br></br> |
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| | <div class="expandable-preview"> | | <div class="expandable-preview"> |
| | <p class="medium-sized"> | | <p class="medium-sized"> |
| − | One of the main goals targeted by projects like ours is the development of a use-case scenario. We therefore visited the wastewater facility in Berlin to test <i>C. reinhardtii</i> growth under natural and industrial conditions. Our idea: The <i>C. reinhardtii</i> mutant strain UVM4 should degrade microplastic from inside a wastewater facility plant. | + | One of the main goals targeted by projects like ours is the development of a use-case scenario. We therefore visited a wastewater treatment facility in Berlin to test growth of <i>C. reinhardtii</i> under natural and industrial conditions. Our idea: The <i>C. reinhardtii</i> mutant strain UVM4 should degrade microplastic inside a wastewater treatment facility. |
| | </p> | | </p> |
| | </div> | | </div> |
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| | <div> | | <div> |
| | <p> | | <p> |
| − | As UVM4 has no flagella, it will sediment. Together with the sinking terephthalic acid (TPA), both can be pumped out. This could be included into the existing cleaning process: Inside the secondary clarifier, the sewage sludge settles on the ground of the pond and gets pumped out. The clean top layer of this water flows into the river system of Berlin. To test this if such a system would be feasible we took some water samples from the wastewater facility into our lab and performed growth tests for <i>C. reinhardtii</i> . We took samples from the secondary clarifier as well as water that were cleaned by UV light in the facility. </p> | + | As UVM4 has no flagella it sediments. Together with the sinking terephthalic acid (TPA) both can be pumped out. This could be included into the existing cleaning process: Inside the secondary clarifier the sewage sludge settles on the ground of the pond and gets pumped out. The clean top layer of this water flows into the river network of Berlin. To test this if such a system would be feasible we took some water samples from the different cleaning stages of the wastewater treatment facility into our lab and performed growth tests with <i>C. reinhardtii</i> in it. We took samples from the secondary clarifier as well as water that had been cleaned by UV light in the facility. </p> |
| − | <p>Unfortunately Chlamy did not grow in any taken wastewater samples. We realized that cultivating Chlamy in wastewater requires much more further examinations, experiments and modifications. Thus, different water conditions, tolerable by <i>C. reinhardtii</i> must be examined. | + | <p>Unfortunately Chlamy did not grow in any taken wastewater samples. We realized that cultivating Chlamy in wastewater requires many further examinations, experiments and modifications. Thus, different water conditions tolerable by <i>C. reinhardtii</i> must be examined. |
| | </p> | | </p> |
| | </div> | | </div> |
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| | <!--- IMAGE ---> | | <!--- IMAGE ---> |
| | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/d/db/T--Humboldt_Berlin--secondary-clarifier.jpeg" alt="Secondary_clarifier" alt="PET degradation" /> | | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/d/db/T--Humboldt_Berlin--secondary-clarifier.jpeg" alt="Secondary_clarifier" alt="PET degradation" /> |
| − | <figcaption> Fig. 23 - water received from wastewater facility in Berlin</figcaption></figure> | + | <figcaption> <b>Fig. 23 - Water received from wastewater facility in Berlin. </b></figcaption></figure> |
| | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/8/86/T--Humboldt_Berlin--growth_uvm4_od680_wastewater.png" alt="PET 1 to 10" alt="Chlamy growth in wastewater" /> | | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/8/86/T--Humboldt_Berlin--growth_uvm4_od680_wastewater.png" alt="PET 1 to 10" alt="Chlamy growth in wastewater" /> |
| − | <figcaption> Fig. 24 - Growth of <i>C. reinhardtii</i> at OD 680 under 150 µE light. Incubation of 1ml | + | <figcaption><b> Fig. 24 - Growth of <i>C. reinhardtii</i> at OD 680 under 150 µE light. </b>Incubation of 1ml |
| − | UVM4 strain at OD 1,7 in 50 ml media. (e.g freshwater from lab sink, secondary clarifier and the UV cleaned water from a wastewater facility). | + | UVM4 strain at OD 1,7 in 50 ml media (e.g freshwater from lab sink, secondary clarifier and the UV cleaned water of the wastewater facility). |
| | </figcaption></figure> | | </figcaption></figure> |
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| | <!------------------Filtration-----------------------> | | <!------------------Filtration-----------------------> |
| | <!-----------------------------------------------------------------------> | | <!-----------------------------------------------------------------------> |
| − | <h3 class="headline3">Filtration of <i> C. reinhardtii </i> for selection inside the bioreactor</h3> | + | <h3 class="headline3">Filtration of <i> C. reinhardtii</i> for selection inside the bioreactor</h3> |
| | </div> | | </div> |
| | <div class="expandable-preview"> | | <div class="expandable-preview"> |
| | <p class="medium-sized"> | | <p class="medium-sized"> |
| − | When using a bioreactor to degrate PET, Chlamy will form a mixture with PET, MHET, EG and TPA. We wanted to find a way to separate <i>C. reinhardtii</i> from the other components and to extract the cells out of our bioreactor. Therefore we tested several microfilters with different pore widths. | + | When using a bioreactor to degrade PET, Chlamy will mix with PET, MHET, EG and TPA. We wanted to find a way to separate <i>C. reinhardtii</i> from the other components and to extract the cells out of our bioreactor. Therefore we tested several microfilters with different pore widths. |
| − | For this test we used the <i>C. reinhardtii</i> cell-wall deficient UVM4 mutant strain. By using vacuum filtration, UVM4 cells were filtered through different filters. | + | For this test we used the <i>C. reinhardtii</i> cell-wall-deficient UVM4 mutant strain. By using vacuum filtration, UVM4 cells were filtered through different filters. |
| | </p> | | </p> |
| | </div> | | </div> |
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| | <div> | | <div> |
| | <p> | | <p> |
| − | We tested three different pore sizes: 7 µM, 5 µM, 0.8 µM. | + | We tested three different pore sizes: 7 µM, 5 µM, 0.8 µM for filtration success. To determine the efficiency of the filtration process we measured the optical density of the culture and the weight of the filters. The table shows that with decreasing pore size the filter gains weight and the optical density of the filtrate decreases. By the second filtration through a 0.8 µM filter less cells stick to the filter.</p> |
| − | To determine the efficiency of the filtration process we measured the optical density of the culture and the weight of the filters. The table shows that with decreasing pore size the filter gains weight and the optical density of the filtrate decreases. By the second filtration through a 0.8 µM filter less cells stick to the filter.</p> | + | |
| | <table> | | <table> |
| | | | |
| | <tr> | | <tr> |
| | <th scope="col">filter pore size</th> | | <th scope="col">filter pore size</th> |
| − | <th scope="col">filter's increase</th> | + | <th scope="col">filter's weight increase</th> |
| − | <th scope="col">filter's decreasre of OD</th> | + | <th scope="col">culture's decrease of OD</th> |
| | </tr> | | </tr> |
| | <tr> | | <tr> |
| | <td>7 µM </td> | | <td>7 µM </td> |
| − | <td>0.0007g</td> | + | <td>0.0007 g</td> |
| | <td>0.0007</td> | | <td>0.0007</td> |
| | </tr> | | </tr> |
| | <tr> | | <tr> |
| | <td>5 µM </td> | | <td>5 µM </td> |
| − | <td>0.0043g</td> | + | <td>0.0043 g</td> |
| | <td>0.159</td> | | <td>0.159</td> |
| | </tr> | | </tr> |
| | <tr> | | <tr> |
| | <td>0.8 µM (first filtration step)</td> | | <td>0.8 µM (first filtration step)</td> |
| − | <td>0.0061g</td> | + | <td>0.0061 g</td> |
| | <td>0.277</td> | | <td>0.277</td> |
| | </tr> | | </tr> |
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| | | | |
| | </table> | | </table> |
| − | <p>The pictures taken of the filters after the filtration process are shown in the figure. The first filtration through a 0.8 µM filter yielded the greenest color and therefore shows the highest net filtration. | + | <p>The pictures taken of the filters after the filtration process are shown in Figure 25. The first filtration through a 0.8 µM filter yielded the greenest color and therefore shows the highest net filtration. |
| − | By this measurement we could show that only a pore size of 0.8 µM can sufficiently filter <i>C. reinhardtii</i> cells. Since <i>C. reinhardtii</i> cells have a size of 10 µM this result is surprising. However, since we used the cell wall deficient mutant strain the missing cell wall could be the reason for the small required pore size. | + | By this measurement we could show that only a pore size of 0.8 µM can filter <i>C. reinhardtii</i> cells sufficiently well. Since <i>C. reinhardtii</i> cells have a size of 10 µM this result is surprising. An explanation for the small required pore size could be the missing cell wall, as we used the cell-wall-deficient mutant strain. |
| − | With this knowledge we can build filter systems inside our bioreactor to sufficiently separate <i>C. reinhardtii</i> out of the bioreactor and to separate it from other components. </p> | + | With this knowledge we can build filter systems inside our bioreactor to sufficiently filter <i>C. reinhardtii</i> out of the bioreactor and to separate it from other components. </p> |
| | </div> | | </div> |
| | <div> | | <div> |
| | <!--- IMAGE ---> | | <!--- IMAGE ---> |
| | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/7/72/T--Humboldt_Berlin--filtration_set-up.png" alt="vacuum filtration setup with different filter pads." /> | | <figure class="is-revealing"><img src="https://2019.igem.org/wiki/images/7/72/T--Humboldt_Berlin--filtration_set-up.png" alt="vacuum filtration setup with different filter pads." /> |
| − | <figcaption> Fig. 25 - Vacuum filtration set-up with different filter pads.</figcaption></figure> | + | <figcaption><b> Fig. 25 - Vacuum filtration set-up with different filter pads.</b></figcaption></figure> |
| | <figure class="is-revealing"> | | <figure class="is-revealing"> |
| | <img src="https://2019.igem.org/wiki/images/2/23/T--Humboldt_Berlin--filters_green.png" alt="Different pore sizes and their cut-off rate" /> | | <img src="https://2019.igem.org/wiki/images/2/23/T--Humboldt_Berlin--filters_green.png" alt="Different pore sizes and their cut-off rate" /> |
| − | <figcaption> Fig. 26 - <i>C. reinhardtii</i> cell-wall deficient UVM4 mutant strain filtered through microfilters with different pore sizes. cells stick to the filter with 0.8µM sized pores. </figcaption></figure> | + | <figcaption> <b>Fig. 26 - <i>C. reinhardtii</i> cell-wall-deficient UVM4 mutant strain filtered through microfilters with different pore sizes. </b>Cells stick to the filter with 0.8 µM sized pores. </figcaption></figure> |
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