Sandbox Reserved 1643

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Some scientists believe that PET degrading bacteria have developped only in recent years due to the accumulation of plastics, including PET, in the environment <ref>DOI: 10.1073/pnas.1718804115</ref>. In 2016, Yoshida et al. <ref name="discovery I. saka" /> discovered the bacterium ''Ideonella sakaiensis'' 201-F6. This bacterium uses PET as its main carbon and energy source. The enzyme PETase is essential to the bacterium's growth, as its primary function is to create molecules that can be assimilated by the micro organism. Thanks to bacteria's rapid adaptation to their environment, we found a potential solution to our plastic polution problem.
Some scientists believe that PET degrading bacteria have developped only in recent years due to the accumulation of plastics, including PET, in the environment <ref>DOI: 10.1073/pnas.1718804115</ref>. In 2016, Yoshida et al. <ref name="discovery I. saka" /> discovered the bacterium ''Ideonella sakaiensis'' 201-F6. This bacterium uses PET as its main carbon and energy source. The enzyme PETase is essential to the bacterium's growth, as its primary function is to create molecules that can be assimilated by the micro organism. Thanks to bacteria's rapid adaptation to their environment, we found a potential solution to our plastic polution problem.
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== Structure ==
== Structure ==
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Although the catalytic triad remains the same between cutinases, there are some residue substitutions in the PETase active site compared to its homologs. These substitutions play a major role in the substrate binding. Indeed, the H132W, F211S, H187S substitution modify the active site’s environment with their side chains leading to a “widening of the ends of the binding cavity” REF1 and thus an enhancement of the PETase activity. For instance, in homologs, the phenylalanine’s side chain “interacts with the terephthalic ring of PET at the entrance of the binding cavity”. Because there is no phenylalanine in PET but a serine, there is no interaction with the substrate before its binding to the enzyme. The binding is therefore facilitated and the hydrolysis enhanced.
Although the catalytic triad remains the same between cutinases, there are some residue substitutions in the PETase active site compared to its homologs. These substitutions play a major role in the substrate binding. Indeed, the H132W, F211S, H187S substitution modify the active site’s environment with their side chains leading to a “widening of the ends of the binding cavity” REF1 and thus an enhancement of the PETase activity. For instance, in homologs, the phenylalanine’s side chain “interacts with the terephthalic ring of PET at the entrance of the binding cavity”. Because there is no phenylalanine in PET but a serine, there is no interaction with the substrate before its binding to the enzyme. The binding is therefore facilitated and the hydrolysis enhanced.
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==== '''Disulfide bridges''' ====
==== '''Disulfide bridges''' ====
PETase possesses two disulfide bridges, C246 - C262 common to all cutinases and C176 - C212 specific to PETase. The first one plays an important role in the stability of cutinases. The second one is the consequence of the substitution of two highly conserved alanines in other cutinases by cysteines. It links a strand of the enzyme to the loop of the active site containing the catalytic residue H210. REF 1 This results in a rigidification of the catalytic site. Thereby, its stability is better and its hydrolysis activity is enhanced. In PETase, the loop containing the residue H210 has three more residues than its homologs. REF 1 In this way, the loop is longer and pushes away the side chain of other residues contained in the neighbouring helices and strands, allowing a better binding of the substrate to the binding cavity. It “keeps the active site flexible enough to compensate for substrate rigidity without compromising the enzyme’s structural integrity.” REF 1
PETase possesses two disulfide bridges, C246 - C262 common to all cutinases and C176 - C212 specific to PETase. The first one plays an important role in the stability of cutinases. The second one is the consequence of the substitution of two highly conserved alanines in other cutinases by cysteines. It links a strand of the enzyme to the loop of the active site containing the catalytic residue H210. REF 1 This results in a rigidification of the catalytic site. Thereby, its stability is better and its hydrolysis activity is enhanced. In PETase, the loop containing the residue H210 has three more residues than its homologs. REF 1 In this way, the loop is longer and pushes away the side chain of other residues contained in the neighbouring helices and strands, allowing a better binding of the substrate to the binding cavity. It “keeps the active site flexible enough to compensate for substrate rigidity without compromising the enzyme’s structural integrity.” REF 1
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== Applications ==
== Applications ==

Revision as of 18:47, 15 January 2021

This Sandbox is Reserved from 26/11/2020, through 26/11/2021 for use in the course "Structural Biology" taught by Bruno Kieffer at the University of Strasbourg, ESBS. This reservation includes Sandbox Reserved 1643 through Sandbox Reserved 1664.
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PET Hydrolase

PET Hydrolase

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References

  1. Danso D, Schmeisser C, Chow J, Zimmermann W, Wei R, Leggewie C, Li X, Hazen T, Streit WR. New Insights into the Function and Global Distribution of Polyethylene Terephthalate (PET)-Degrading Bacteria and Enzymes in Marine and Terrestrial Metagenomes. Appl Environ Microbiol. 2018 Apr 2;84(8). pii: AEM.02773-17. doi:, 10.1128/AEM.02773-17. Print 2018 Apr 15. PMID:29427431 doi:http://dx.doi.org/10.1128/AEM.02773-17
  2. 2.0 2.1 Yoshida S, Hiraga K, Takehana T, Taniguchi I, Yamaji H, Maeda Y, Toyohara K, Miyamoto K, Kimura Y, Oda K. A bacterium that degrades and assimilates poly(ethylene terephthalate). Science. 2016 Mar 11;351(6278):1196-9. doi: 10.1126/science.aad6359. PMID:26965627 doi:http://dx.doi.org/10.1126/science.aad6359
  3. Panda T, Gowrishankar BS. Production and applications of esterases. Appl Microbiol Biotechnol. 2005 Apr;67(2):160-9. doi: 10.1007/s00253-004-1840-y. , Epub 2005 Jan 4. PMID:15630579 doi:http://dx.doi.org/10.1007/s00253-004-1840-y
  4. P. Dockrill, « Scientists Have Accidentally Created a Mutant Enzyme That Eats Plastic Waste », ScienceAlert. https://www.sciencealert.com/scientists-accidentally-engineered-mutant-enzyme-eats-through-plastic-pet-petase-pollution Retrieved 2021-01-11.
  5. Kim JW, Park SB, Tran QG, Cho DH, Choi DY, Lee YJ, Kim HS. Functional expression of polyethylene terephthalate-degrading enzyme (PETase) in green microalgae. Microb Cell Fact. 2020 Apr 28;19(1):97. doi: 10.1186/s12934-020-01355-8. PMID:32345276 doi:http://dx.doi.org/10.1186/s12934-020-01355-8
  6. Austin HP, Allen MD, Donohoe BS, Rorrer NA, Kearns FL, Silveira RL, Pollard BC, Dominick G, Duman R, El Omari K, Mykhaylyk V, Wagner A, Michener WE, Amore A, Skaf MS, Crowley MF, Thorne AW, Johnson CW, Woodcock HL, McGeehan JE, Beckham GT. Characterization and engineering of a plastic-degrading aromatic polyesterase. Proc Natl Acad Sci U S A. 2018 Apr 17. pii: 1718804115. doi:, 10.1073/pnas.1718804115. PMID:29666242 doi:http://dx.doi.org/10.1073/pnas.1718804115
  7. Fecker T, Galaz-Davison P, Engelberger F, Narui Y, Sotomayor M, Parra LP, Ramirez-Sarmiento CA. Active Site Flexibility as a Hallmark for Efficient PET Degradation by I. sakaiensis PETase. Biophys J. 2018 Mar 27;114(6):1302-1312. doi: 10.1016/j.bpj.2018.02.005. PMID:29590588 doi:http://dx.doi.org/10.1016/j.bpj.2018.02.005
  8. 8.0 8.1 8.2 8.3 8.4 8.5 8.6 Carr CM, Clarke DJ, Dobson ADW. Microbial Polyethylene Terephthalate Hydrolases: Current and Future Perspectives. Front Microbiol. 2020 Nov 11;11:571265. doi: 10.3389/fmicb.2020.571265., eCollection 2020. PMID:33262744 doi:http://dx.doi.org/10.3389/fmicb.2020.571265
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