Sandbox Reserved 1845
From Proteopedia
(Difference between revisions)
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=== Ser 283 & Asp 238 === | === Ser 283 & Asp 238 === | ||
- | Two wild-type residues, <scene name='10/1075247/S283-d238/5'>Ser283 and Asp238</scene>, were engineered to form a disulfide bond by replacing them with Cys. This decision was based on their spatial proximity in the 3D structure and their location in a region that resembles metal-binding sites in homologous PET-degrading enzymes. Unlike those metal-dependent sites, the LCC structure lacked coordinated ions. For that reason, the researchers engineered a covalent linkage instead to increase thermal stability without requiring additives like calcium. The wild-type protein has a melting point of 84.7°C, while the <scene name='10/1075248/C283-c238/2'>S283C and D238C mutant</scene> increased the melting point to 94.5°C, a 9.8°C improvement, which is higher than any other mutations. However, this increase in stability was accompanied by a 28% decrease in enzymatic activity compared to the wild-type. This trade-off between stability and activity shows the balance in enzyme engineering, as increasing structural integrity can sometimes restrict the flexibility needed for catalytic function. | + | Ser 283 and Asp 238, are located outside of the binding pocket in the <scene name='10/1075247/Start_material_for_s283_and_d2/2'>Original Protein</scene>.Two wild-type residues, <scene name='10/1075247/S283-d238/5'>Ser283 and Asp238</scene>, were engineered to form a disulfide bond by replacing them with Cys. This decision was based on their spatial proximity in the 3D structure and their location in a region that resembles metal-binding sites in homologous PET-degrading enzymes. Unlike those metal-dependent sites, the LCC structure lacked coordinated ions. For that reason, the researchers engineered a covalent linkage instead to increase thermal stability without requiring additives like calcium. The wild-type protein has a melting point of 84.7°C, while the <scene name='10/1075248/C283-c238/2'>S283C and D238C mutant</scene> increased the melting point to 94.5°C, a 9.8°C improvement, which is higher than any other mutations. However, this increase in stability was accompanied by a 28% decrease in enzymatic activity compared to the wild-type. This trade-off between stability and activity shows the balance in enzyme engineering, as increasing structural integrity can sometimes restrict the flexibility needed for catalytic function. |
== Group Mutations == | == Group Mutations == |
Revision as of 19:50, 27 April 2025
This Sandbox is Reserved from March 18 through September 1, 2025 for use in the course CH462 Biochemistry II taught by R. Jeremy Johnson and Mark Macbeth at the Butler University, Indianapolis, USA. This reservation includes Sandbox Reserved 1828 through Sandbox Reserved 1846. |
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Leaf Branch Compost Cutinase
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References
- ↑ 1.0 1.1 1.2 1.3 1.4 1.5 1.6 1.7 Tournier V, Topham CM, Gilles A, David B, Folgoas C, Moya-Leclair E, Kamionka E, Desrousseaux ML, Texier H, Gavalda S, Cot M, Guemard E, Dalibey M, Nomme J, Cioci G, Barbe S, Chateau M, Andre I, Duquesne S, Marty A. An engineered PET depolymerase to break down and recycle plastic bottles. Nature. 2020 Apr;580(7802):216-219. doi: 10.1038/s41586-020-2149-4. Epub 2020 Apr, 8. PMID:32269349 doi:http://dx.doi.org/10.1038/s41586-020-2149-4
- ↑ 2.0 2.1 2.2 2.3 2.4 Sui B, Wang T, Fang J, Hou Z, Shu T, Lu Z, Liu F, Zhu Y. Recent advances in the biodegradation of polyethylene terephthalate with cutinase-like enzymes. Front Microbiol. 2023 Oct 2;14:1265139. PMID:37849919 doi:10.3389/fmicb.2023.1265139
- ↑ Ueda H, Tabata J, Seshime Y, Masaki K, Sameshima-Yamashita Y, Kitamoto H. Cutinase-like biodegradable plastic-degrading enzymes from phylloplane yeasts have cutinase activity. Biosci Biotechnol Biochem. 2021 Jul 23;85(8):1890-1898. PMID:34160605 doi:10.1093/bbb/zbab113
- ↑ Kolattukudy PE. Biopolyester membranes of plants: cutin and suberin. Science. 1980 May 30;208(4447):990-1000. PMID:17779010 doi:10.1126/science.208.4447.990
- ↑ 5.0 5.1 5.2 5.3 5.4 Khairul Anuar NFS, Huyop F, Ur-Rehman G, Abdullah F, Normi YM, Sabullah MK, Abdul Wahab R. An Overview into Polyethylene Terephthalate (PET) Hydrolases and Efforts in Tailoring Enzymes for Improved Plastic Degradation. Int J Mol Sci. 2022 Oct 20;23(20):12644. PMID:36293501 doi:10.3390/ijms232012644
- ↑ 6.0 6.1 Burgin T, Pollard BC, Knott BC, Mayes HB, Crowley MF, McGeehan JE, Beckham GT, Woodcock HL. The reaction mechanism of the Ideonella sakaiensis PETase enzyme. Commun Chem. 2024 Mar 27;7(1):65. PMID:38538850 doi:10.1038/s42004-024-01154-x
- ↑ 7.0 7.1 7.2 Zhang J, Wang H, Luo Z, Yang Z, Zhang Z, Wang P, Li M, Zhang Y, Feng Y, Lu D, Zhu Y. Computational design of highly efficient thermostable MHET hydrolases and dual enzyme system for PET recycling. Commun Biol. 2023 Nov 9;6(1):1135. PMID:37945666 doi:10.1038/s42003-023-05523-5
- ↑ 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
- ↑ Landrigan PJ, Stegeman JJ, Fleming LE, Allemand D, Anderson DM, Backer LC, Brucker-Davis F, Chevalier N, Corra L, Czerucka D, Bottein MD, Demeneix B, Depledge M, Deheyn DD, Dorman CJ, Fénichel P, Fisher S, Gaill F, Galgani F, Gaze WH, Giuliano L, Grandjean P, Hahn ME, Hamdoun A, Hess P, Judson B, Laborde A, McGlade J, Mu J, Mustapha A, Neira M, Noble RT, Pedrotti ML, Reddy C, Rocklöv J, Scharler UM, Shanmugam H, Taghian G, van de Water JAJM, Vezzulli L, Weihe P, Zeka A, Raps H, Rampal P. Human Health and Ocean Pollution. Ann Glob Health. 2020 Dec 3;86(1):151. PMID:33354517 doi:10.5334/aogh.2831
- ↑ Jambeck JR, Geyer R, Wilcox C, Siegler TR, Perryman M, Andrady A, Narayan R, Law KL. Marine pollution. Plastic waste inputs from land into the ocean. Science. 2015 Feb 13;347(6223):768-71. PMID:25678662 doi:10.1126/science.1260352
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