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Simulation Study of Polyethylene Terephthalate Hydrolase Adsorption on Self-Assembled Monolayers
Lijian Gao1, Zhiyong Xu1, Jian Zhou1
1School of Chemistry and Chemical Engineering, Guangdong Provincial Key Lab for Green Chemical Product Technology, South China University of Technology, Guangzhou 510640, P. R. China.
Langmuir : the ACS Journal of Surfaces and Colloids
|March 19, 2024
Summary
Polyethylene terephthalate hydrolase (IsPETase) immobilization on charged surfaces was studied. Simulations reveal "end-on" adsorption on COOH-SAM, optimizing enzyme orientation for PET biodegradation.
Area of Science:
- Biocatalysis
- Protein Immobilization
- Computational Chemistry
Background:
- Polyethylene terephthalate (PET) hydrolase (IsPETase) from Ideonella sakaiensis offers mild PET biodegradation but suffers from poor thermal stability.
- Efficient immobilization and controlled orientation of IsPETase on solid substrates are crucial for enhancing its industrial applicability.
Purpose of the Study:
- To elucidate the adsorption mechanism, orientation, and conformational changes of IsPETase on charged self-assembled monolayers (SAMs).
- To investigate the influence of surface charge density (SCD) on IsPETase adsorption and catalytic site accessibility.
Main Methods:
- Combined parallel tempering Monte Carlo (PTMC) and all-atom molecular dynamics (MD) simulations were employed.
- IsPETase adsorption on COOH-SAM and NH2-SAM with varying SCDs was analyzed at the atomistic level.
Main Results:
- Protein adsorption orientation is governed by both attractive and repulsive interactions.
- IsPETase adopts an "end-on" orientation on COOH-SAM, exposing the catalytic triplet to the solution.
- A larger catalytic active center entrance was observed on COOH-SAM surfaces with low SCD.
Conclusions:
- This study provides atomistic insights into the controlled orientation and conformational dynamics of IsPETase on charged surfaces.
- Findings support the rational design of immobilization substrates to enhance IsPETase performance in PET biodegradation.
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