Carbonic Anhydrase II Based Biosensing of Carbon Dioxide at High Temperature: An Analytical and MD Simulation Study

Concentration of carbon dioxide (CO2) in the atmosphere has increased significantly due to anthropogenic activities and attributed as a major factor to global warming. Its detection by biosensing methods will provide an alternative for the assessment of CO2 concentration. Biomineralization of CO2 is one of the available methods for the biological conversion of CO2 to carbonate using a highly active enzyme, carbonic anhydrase II (CAII). CAII was used for the carbonation reaction to convert CO2 to CaCO3. The precipitation of calcium carbonate (CaCO3) was promoted in the presence of the CAII at 325 K. CAII showed an enhanced formation of solid CaCO3 through the acceleration of CO2 hydration rate at 325 K. Furthermore, the electrocatalytic properties of glassy carbon electrode enable us to determine the reduction peak potential values of CO2 through cyclic voltammetry at –1.75 and 0.3 V at 325 K. Molecular dynamic (MD) simulations were performed each at 50 ns time scale provided a deeper insight into the molecular basis of the CAII interaction with CO2 at different temperatures, highlighted that the CAII can detect CO2 up to 325 K. We assume that CAII could be an effective and economical biosensor for biomineralization of CO2 at high temperature 325 K.


Introduction
Carbon dioxide (CO 2 ), gas is considered as one of the main atmospheric components responsible for a greenhouse effect and also responsible for the increase of atmospheric temperature [1,2]. Hence, it is demand for increasing environmental awareness to find a solution for CO 2 mitigation [3]. The capture of anthropic CO 2 released in the atmosphere by human activities is one of the challenging problems worldwide [4]. Two significant approaches are used to reduce the concentration of CO 2 in the atmosphere, in which CO 2 can either recovered from industrial flue gases and transport it to suitable locations for storage or CO 2 can be sequestered using chemical fixation method to get carbomate minerals, such as calcite, magnesite, and dolomite [5,6]. The conversion of CO 2 into solid carbonates offers a possibility of a safe and stable ecofriendly product for long term carbon sequestration. Moreover, mineral based sequestration produces useful products such calcium carbonate (CaCO 3 ) or magnesium carbonate (MgCO 3 ), which are solid and can easily be precipitated [7]. The hydration of CO 2 to form carbonic acid is the slowest and ratelimiting step [8]. The conversion of CO 2 into carbonate ions was found to be a forward reaction with a rate constant of 6.2 × 10 -3 s at 25°C [9]. A biological catalyst, carbonic anhydrase (CA) has been used to increase the rate of hydration of CO 2 , to overcome the rate-limiting step, a biological catalyst.
Carbonic anhydrase (CA, EC 4.2.1.1) is a metallo-enzyme, present in both prokaryotes and eukaryotes and perform varieties of functions such as pH homeostasis, renal acidification, gluconeogenesis, bone resorption, respiration and ion transport [10,11]. CA catalyzes the reversible hydration and dehydration of CO 2 and bicarbonate, respectively. CA has the high affinity for CO 2 and easy to capture the atmospheric. Human CAII is highly active and has a kcat/KM of 1.5 × 10 8 Ms -1 [12,13] with highest turnover number (kcat 10 6 s -1 ).
Thus, CAII is a suitable candidate for sequestration of CO 2 because of its increasing industrial interest. CAII has already been reported as a bio-catalyst for carbon sequestration of the flue gas from coal-fired power plants [14]. In addition, there is also interest in exploiting CA in algae as a way to capture CO 2 and convert it into biofuels or other valuable products [15,16]. Furthermore, CO 2 hydration can be significantly enhanced (10 7 times) by CA [17,18]. However, use of the free enzyme in solution has also many serious drawbacks, such as low stability that limits re-usability, recovery and cost in an industrial setting [19].
In the present work, MD simulations of CAII at different temperature ranges were performed to investigate the stability of CAII against temperature. The molecular mechanism of CO 2 detection at three different temperatures (300 K, 310 K and 325 K) was understood

Journal of Bioremediation & Biodegradation
on the basis of the outcome obtained from MD simulations, in which behavior was analyzed at three different temperatures for 50 ns time scale. To validate the outcome of MD simulations, CAII was subcloned cDNA of human CAII in the expression vector pET15d. Open reading frame (ORF) for CAII is of 801 base pairs encoded 267-amino acids. We constructed vector including the sequence coding for a CAII protein and an N-terminal poly-histidine (6XHis) tag to simplify the detection of protein expression using antibodies specific for the tag.
Purification of recombinant protein was performed using immobilized metal affinity chromatography followed by gel filtration. The purified protein was used for precipitation of CO 2 (aq) into CaCO 3 in the presence of calcium ions at high temperature (325 K). Furthermore, the CAII based detection of the CO 2 at 325 K was analyzed by using the electrochemical methods.

Molecular dynamic simulations
The structure of CAII was modelled by using the MODELLER module of the Discovery Studio 2016 (DS, http://accelrys.com/ products/collaborative-science/biovia-discovery-studio/). The modelled structure of CAII was minimized by using the CHARMM force field [20] based optimization modules of DS. Similarly, the structure of CO 2 was constructed by utilizing the drawing utilities present in the DS and structure was optimized by using the DFT method implemented in the Dmol3 module of the DS. Furthermore, the molecular docking was performed by using the CDOCKER module which is a CHARMM [20] force field based docking algorithm implemented in DS. The understanding about the active site of the CAII was obtained from the literature [21]. The CO 2 was docked in the active site of CAII and around 10 conformations generated for the further study. The generated conformations were rescored, and best docked pose was selected for the MD simulation studies.
The selected docked structures of CAII and CO 2 were subjected to MD simulations using GROMACS [22] (version 5.1.2, installed on the Center for High Performance Computing (CHPC), Cape Town which provide 10 nodes with 24 cores per node of space for computation). The topology of CAII was produced on the basis of GROMOS96 53a6 force field [23]. Due to the unavailability of suitable force field parameters for drug-like molecules in the GROMACS package, the PRODRG server [24] was used for the generation of the CO 2 topologies and coordinate files. The partial charges were corrected by using DFT method of Gaussian which utilized the B3LYP 6-31G (d,p) basis set and CHELPG program [25]. After the successful topology generation, the docked complex was immersed in SPC/E water model [26] and the system was neutralized by adding the counter ions. The neutralized system was energetically minimized by utilizing the steepest descent and conjugate gradient algorithms with a convergence criterion of 0.005 kcal mol -1 . In order to increase the reliability of the MD simulations the restrains were applied to the structure of the piperine before the equilibration phase.
The equilibration phase was carried out separately in NVT (constant volume) as well as NPT (constant pressure) ensemble conditions, each for 100 ps time scale. The temperature of the system was changed from 300 K-325 K in both ensemble conditions along with pressure which was maintained at 1 bar by utilizing Parrinello-Rahman barostat in constant pressure ensemble. The final MD simulations were produced on the basis of LINCS algorithm at 50 ns time scale. The knowledge extracted from the trajectory files were utilized for the analyses of each complex behavior in the explicit water environment. The distances, H-bonds and RMSD (Root Mean Square Deviations) and several other parameters were analyzed for CAII -CO 2 complex.

Cloning and expression of CAII
The CAII gene was subcloned into pET15d vector (Novagen, EMD Biosciences, Madison, Wisconsin, USA) and cloning was confirmed through colony PCR and restriction digestion. The expression vector, pET15d, containing the full-length coding region of CAII gene was transformed into E. coli BL21(DE3) host cells by following the standard molecular biology protocol. The overnight culture of the expression cells from a freshly transformed plate was inoculated in LB media, containing 100 µg/µl ampicillin, and incubated, with constant agitation at 220 rpm in an incubator shaker until the absorbance was 0.6 at 600 nm. The culture was induced by 0.25 mM IPTG, and incubated for 4 hours with constant shaking. The cells were harvested, resuspended and sonicated. Cell extract after sonication was centrifuged at 12000 g for 30 min, and the pellets were discarded while supernatant was collected for the purification.

Protein purification
The filtered supernatant was loaded on previously equilibrated Ni-NTA column, with 5 column volumes (CV) of equilibration buffer. Elution was performed with increasing concentration of imidazole. Fractions were analyzed by sodium dodecyl sulphate-polyacrylamide gel electrophoresis (SDS-PAGE). Fractions containing CAII were pooled together, concentrated and loaded on the size exclusion column, HiPrep Superdex 75 (GE Healthcare Bio-Sciences), equilibrated with 150 ml of buffer and run at 0.5 ml/min. The chromatogram was monitored using Unicorn software (GE Healthcare Bio-Sciences). Fractions containing pure CAII were used for further analysis. The purity of purified protein was checked by SDS-PAGE. Furthermore, purified CAII was confirmed by Western blot.

Determination of CAII activity
The CAII activity was measured according to Sharma et al. [27]. In brief, CO 2 saturated water prepared by introducing CO 2 in 500 ml of Milli Q pure water for 1 h at 325 K. CO 2 saturated water (3 ml) was immediately added to 2 ml of Tris-HCl buffer (100 mM; pH 8.3), and 0.1 ml of free purified CA (1 mg/ml stock). The time required for the pH change 8.0-7.0 (t) was measured using Beetrode electrode with separate reference electrode (Dri-Ref), manufactured by World Precision Instruments Incorporation (WPI). The time required for the pH change (8.0-7.0) was used as control (tc), when buffer was substituted for test sample. The enzyme assay was carried out at 325 K. The Wilbur Anderson units were calculated with the equation (tc−t)/t. The measurements were carried out in three replicates.

Enzymatic carbon dioxide capture
The CA purified was used as a catalyst in the capture of CO 2 by precipitation in the form of CaCO 3 at high temperature (325 K). The reaction mixture consists of 7.5 mL of the purified enzymatic extract, 7.5 mL of 1.2 M Tris-HCl buffer pH 10.5 solution containing 4.5% (w/v) CaCl 2 and 30 mL of the CO 2 solution. The CO 2 solution was prepared by bubbling deionized water with gaseous CO 2 at 325 K. The reaction started when the CO 2 solution was added into the flask that was immediately closed with a sealing film. In all experiments the temperature was maintained at 325 K. The mixture was then filtered and dried after 8 and 120 min of reaction to determine the weight of CaCO 3 precipitated (enzymatic assay). At the same time samples were prepared by replacing the enzyme with deionized water (nonenzymatic assay) and the results expressed as the difference between the values obtained in the enzymatic assay and those obtained in the non-enzymatic assay (∆CaCO 3 ), calculated according to Eq. (1). For use in CO 2 capture, the enzyme purified by ammonium sulfate precipitation was dialyzed to remove the salt. The reaction was performed at 325 K. CaCO 3 ¼ m CaCO 3 EA _ m CaCO 3 NEA ð1Þ where m CaCO 3 EA is the weight of CaCO 3 in the enzymatic assay (g) and m CaCO 3 NEA is the weight of CaCO 3 in the non-enzymatic assay (g).

XRD and WDXRF analysis
XRD pattern of powdered samples were recorded with X-ray diffractometer (Rigaku D-max 2500 PC, Japan) in the 2θ range of 3 to 75° at a scanning speed of 2 deg/min and a step size of 0.01°. The XRD pattern was processed and presence of various crystalline phases in the sample was determined by search match software. To confirm the presence of the phases identified by XRD, elemental analysis was carried by WDXRF. Crystallite size of the crystalline phases was obtained from FWHM of the XRD peaks. Elemental analysis of the sample was carried out by WDXRF (Axios, PANalytical, Netherlands). The sample was packed in the sample cell and then analyzed by WDXRF using standard-less semi-quant software. XRF spectra were processed and presence of various elements was identified using the software. Semi-quantitative results were obtained from standard-less semi-quant software.

TEM analysis
TEM experiments were performed on a JEOL JEM 2100 TEM (200 kV accelerating voltage). The powdered samples were dispersed in ethanol solvent by ultrasonication and the resulting suspension was deposited onto 200 mesh Cu grids covered with formvar and a holey carbon support film. Particle size and shape were obtained from the TEM image.

Electrochemical measurements
The electrochemical behavior of CO 2 was studied using a threeelectrode system (working electrode: glassy carbon electrode; auxiliary electrode: platinum wire; reference electrode: SCE). Prior to analysis of the analyte, the glassy carbon electrode was polished using 0.5 μm alumina powder followed by electrochemical cycles in 0.5M H 2 SO 4 solution till a stable voltammetric response was achieved.
To ensure that there was continuous flow of CO 2 into the polarographic cell, the VA computrace setup was modified accordingly by connecting an addition gas tube that delivered CO 2 directly into the measuring solution. The CO 2 gas was produced from the reaction of 0.5 g Na 2 CO 3 with 6 M HCl. The 18 ml of HCl was allowed to react drop by drop (18 ml/25 s) in a closed system allowed for consistent flow of CO 2 into the measuring cell in which the three-electrode system was immersed. Cyclic Voltammetry measurements were performed from -2 to 2 V and 0 to 0.8 V at high temperature. Differential Pulse Voltammery (DPV) was performed from -2.0 to 0 V. All electrochemical measurements were performed at 100 mV. S -1 and deposition time of 40 s following the two approaches: (a) buffer, CAII and CO 2 ; (b) buffer, saturation with CO 2 and CAII.

Molecular dynamic simulations
MD simulations provide a dynamic picture of CAII and CO 2 complex. MD simulations were performed at different temperature each for 50 ns and their trajectories were analyzed by using the utilities of the GROMACS. The distance between the CAII and CO 2 of the complex were remaining relatively similar at all different temperature (Figure 1). Dynamic stability of CAII and CO 2 complex, over the simulation of 50 ns was analyzed using backbone RMSD of Cα atoms. RMSD result showed a varied nature. At 300 K, the RMSD values were fluctuating and the magnitude of the values decreases. The similar fluctuating behavior was observed for CAII and CO 2 complex at 310 K and 325 K with the RMSD values increases (Figure 2A). Furthermore, the Rg analysis was performed to measure the compactness of CAII and CO 2 complex. The average value of Rg, calculated from trajectory showed similar behavior for all different temperatures, relatively larger fluctuations were observed at 325 K ( Figure 2B). The RMSF was also calculated at all different temperature and found to consistent with RMSD and Rg. The RMSF values showed higher fluctuation at 325 K as compared to the other conditions ( Figure 2C).

Expression and purification of CAII
CAII was cloned in pET15d, and then constructed plasmid was verified by DNA sequencing. This constructed plasmid pET15d-CAII was transformed into E. coli BL21 (DE3) strain, and induced with 0.25 mM IPTG accumulates high amounts of a soluble protein migrating in SDS-PAGE with an apparent molecular weight of 29 kDa. SDS PAGE analysis also showed that CAII was expressed as a monomer and CAII was found in the soluble bacterial extract (supernanat).
CAII purified from the Ni-NTA affinity showed contamination by other proteins (Figure 3A). We used gel filtration chromatography to further purify the CAII. We found that CAII was eluted at 70 ml of elution volume which is an indication that the existence of monomer form ( Figure 3B). The purity of gel filtration eluent was further confirmed using SDS-PAGE that clearly showing a single band ( Figure  3C).  The total amount of CAII being purified from a 20 g pellet is 60 mg. Recombinant CAII protein was confirmed by Western blot that showing a molecular weight of about 29 kDa ( Figure 3D). CAII was further confirmed by MALDI-TOF and its peptide mass fingerprint. The CAII was confirmed by peptide sequences shown in Table 1 which were used for homology search.

Hydration of carbon dioxide with and without CAII
CA catalyzes the hydration of CO 2 , and consequently hydrogen ions are transferred between the active site of the enzyme and the surrounding buffer. These results in the decrease of pH at a formation of HCO 3 rate so fast that the over-all precipitation of CaCO 3 rate may itself decrease. Therefore, measuring the pH is a viable method to monitor the progress of this enzymatic reaction at high temperature 325 K. Figure 4 shows the decrease in pH during the assay for CA using the enzyme obtained. The curves show that this enzyme was a very effective catalyst for hydration of CO 2 .

Acceleration of carbonate formation by CA
As shown in Table 2, the amounts of calcium carbonate precipitated after 15, 30, and 60 sec is significantly higher than the control without enzyme at high temperature. CAII accelerates the formation of bicarbonate ions by lowering the activation energy required for hydration of CO 2 . The conversion of CO 2 into H 2 CO 3 is the rate controlling step catalyzed by CAII, while the formation of HCO 3 is nearly diffusion controlled [28]. However, the conversion of HCO 3 to CO 3 2is pH dependent. An enzyme can only increase the rate of the reaction, but could not alter it, thus CA is deemed to accelerate the formation of bicarbonate ions. Under the precipitation conditions (pH 9.0-9.5) bicarbonate ions exist in equilibrium with carbonate ions and in presence of calcium ions result in calcium carbonate precipitation. Thus, CA plays the important role in hydration reaction corresponding to calcium carbonate formation; hence the in presence of enzyme the higher amount of the CaCO 3 is obtained.  Table 2: Results obtained in the enzymatic precipitation of carbon dioxide.
The effect of the concentration of enzyme on the time to onset the start of precipitation and amount of the precipitation was also studied (data not shown). We found to direct relation between the concentration of enzyme with time taken to onset of precipitation and amount of precipitation. Ores et al. and Byung also demonstrated that the total mass of CaCO 3 (s) precipitated do not depend on the concentration of the enzyme which, as a catalyst, can only change the kinetics to reach equilibrium that occurs in the first minutes of reaction, not the equilibrium thermodynamics [29][30][31]. The XRD spectra of calcium carbonate (CaCO 3 ) which has three crystal phases (calcite, aragonite, and vaterite). Among three the calcite phase is a thermodynamically most stable phase under the ambient conditions ( Figure 5).
The TEM analysis showed that in the presence of enzyme CAII nano particle of CaCO 3 was found irregular in size from 60 to 150 nm in presence of enzyme while without enzyme the size was not irregular in shape with size around 500 nm as shown in Figures 5A and 5B.

Electrochemical measurements
Electrochemical measurements demonstrated three significant observations within the potential range -2.0 to 0.1 V. The observable peaks were further explored in a narrow potential range namely: -2.0 to 0.0 V; -1.4 to -0.6 and lastly at 0.0 to 0.8 V (vs Ag/AgCl). The two approaches used complemented one another in a sense that they confirmed that CAII participate in the detection of CO 2 . The obtained peaks in the electrochemical detection were illustrated in Figure 6.

Discussion
The hydration of CO 2 is the rate limiting step in current industrial carbon capture methods. Carbonic anhydrases have been used as biological catalysts for rapid hydration/ dehydration of industrial CO 2 . Human CAII offers several advantages over other isoforms of CA as it shows a very high catalytic activity for the conversion of CO 2 to HCO 3 and proton. CAII is an extremely efficient and specific means for CO 2 capture. However, current utilization of CAII in carbon capture is limited by the relative instability of the enzyme in high temperature. Hence, there is a need to improve upon the stability of CAII for the use in an industrial carbon sequestration. To achieve these aims, a prerequisite is to prepare the recombinant pure protein in high concentration. Bacterial expression system has been used to express CAII and purified from it. MD simulations were performed at different temperatures to check its stability. In vitro studies carried out to establish a correlation between in vitro and MD simulations results.
In all studied conditions the distance between the two entities of the complex were remain relatively similar (Figure 1), which was observed in the range of 0.2 nm-0.3 nm. Furthermore, the RMSD values of the Cα atoms showed a varied nature. At 300K, the RMSD values were fluctuating around 0.3 nm up to 40 ns and the after that the magnitude of the values decreases (Figure 2A). The CAII showed similar fluctuating behavior at 310 K and 325 K with the RMSD values increases after 35 ns (Figure 2A). Moreover, the Rg curves showed similar behavior for 300 K and 310 K as the Rg values were obtained between 1.70 nm-1.75 nm, while relatively larger fluctuations were observed at 325 K, as the Rg values (<1.70 nm) were observed up to 25 ns and after that the Rg values may fluctuate beyond 1.75 nm ( Figure  2B). Due to high temperature, the RMSF values showed higher fluctuation at 325 K as compared to the other conditions ( Figure 2C). This indicates that the structural compactness of the CAII was maintained even at the higher temperatures and it can successfully detect the CO 2 even at the higher temperatures.

Expression and purification of CAII
CAII was successfully cloned and transformed into E. coli BL21 (DE3) strain for protein expression. CAII in E. coli BL21 (DE3) expressed and showing very high yield. SDS PAGE analysis showing that CAII found in the soluble bacterial extracts (supernanat). Furthermore, this supernatant was subjected to Ni-NTA affinity chromatography. The purified protein from Ni-NTA affinity showed contamination by other proteins ( Figure 3A). The gel filtration chromatography was used to further purify the CAII. The purity of CAII was further confirmed by SDS-PAGE that clearly showing a single band ( Figure 3C). Western blot and MALDI-TOF were also confirmed the CAII ( Figure 3D).

Hydration of carbon dioxide with and without CAII
The rate limiting step in current industrial carbon capture methods is the hydration of CO 2 . Figure 4 shows the curves show that this enzyme was a very effective catalyst for hydration of CO 2 . CA catalyzes the hydration of CO 2 at high temperature (325 K) but below its melting temperature and it is an extremely efficient and specific method.

Acceleration of carbonate formation by CA
CAII provides bicarbonate at a rapid rate through the catalytic hydration of CO 2 by lowering the activation energy. As shown in Table  2, the amounts of calcium carbonate precipitated after 15, 30, and 60 sec is significantly higher than the control without enzyme at 325 K. The bicarbonate ions exist in equilibrium with carbonate ions and in presence of calcium ions result in calcium carbonate precipitation under the precipitation conditions (pH 9.0-9.5). Thus, CA plays the important role in hydration reaction corresponding to calcium carbonate formation; hence in the presence of enzyme the higher amount of the CaCO 3 is obtained at high temperature. Figure 5 shows the XRD spectra of calcium carbonate obtained from CA (partially purified) and standard CaCO 3 . Calcium carbonate (CaCO 3 ) has three crystal phases (calcite, aragonite, and vaterite). The calcite phase is a thermodynamically most stable phase under the ambient conditions. The XRD patterns of precipitates show major peaks at 23 [29] and Sharma et al. [27]. WDXRF analysis shows presence of Ca as major element correlating well with XRD data. The TEM analysis showed nano particle of CaCO 3 was found with size from 60 to 150 nm in presence of enzyme while without enzyme the size was not irregular in shape as shown in Figures  5A and 5B. This shows enzyme can be used for converting CO 2 to nano sized CaCO 3 which have several industrial applications. These finding are in good agreement with Sondi and Matijevi [32]. Therefore, CA could be used not only to sequester CO 2 but also to produce a valuable product even at high temperature. These nano-particles could be used in other industrial processes such as paper, ink, paint, or coating production plants which make the sequestration process economically desirable, and even profitable.

Electrochemical measurements
With reference to voltammogram in Figure 6A, shows that as we bubble more and more CO 2 in solution, the intensity of the current signal at E1/2 of -1.15 V is proportionally becoming more prominent while the opposite is true in Figure 6B. The peak observed is not well defined and it is understandable as reduction of CO 2 is a difficult problem owing to the fact that CO 2 is a very stable molecule [33].
In Figure 6A, there is a significant shift of the reduction potential from the catalytic run for CO 2 reduction versus the high-current irreversible electrochemical response in the presence of CAII [34]. This observation is agreement with the report by Reche and co-workers although the medium of electrochemical measurement is not the same [35,36]. Furthermore, Figure 6B shows an irreversible reduction peak at 0.276 ± 0.03 V (vs. Ag/AgCl) that is probably due to the reduction of the quinolone ring present in the CAII protein. As we bubble more and more CO 2 the intensity of the current signal is lowered. Altogether these results confirm that the prepared CAII is suitable for detection of the CO 2 at high temperature. It has been reported that a quinolone ring is reduced in the presence of CO 2 . As the carbonic solution in the voltammetric cell becomes saturated with CO 2 , at the pH of 6.8 there is an intense voltammetric peak at 0.6 V (vs Ag/AgCl) which appears to increase in current response arising from the response of the formic acid oxidation. CO 2 (g) → CO 2 (ads) → CO(g)+CO 3 2-(aq) The formation of CO 2 -• (aq) is followed by disproportionation of CO 2 -• (ads) and CO 2(g) to give CO and CO 3 2-. There is also a high possibility of protonation of the CO 2 -• , and likewise there is reduction of COOH • to formate. Overall, it is understandable that CO 2 can produce a variety of intermediate/products which includes carbonates, oxalate, formate because there is a high density of LUMO of CO 2 that is found mainly on the carbon atom. Thus, during the electrochemical measurement there is a pH shift towards acidic medium and ultimately hinders detection as the hydrogen evolved reaction becomes a major interference.
hydration activity and converts CO 2 to CaCO 3 very efficiently. The potential for acceleration of CO 2 capture impressively illustrate the importance of CAII. The present work showed the biomineralization process for CO 2 hydration into calcium carbonate at high temperature. Furthermore, the voltammetric studies confirmed that CAII can successfully detect CO 2 in solution through the electrocatalytic performance of glassy carbon electrode even at 325 K. These results are very encouraging for the future development in which the electrode can be turned into an ideal tool of a CAII based biosensor. Moreover, the MD simulations results have been validated by In vitro studies that the CAII can detect the CO 2 even at higher temperatures and can be used for the detection of the pollutant CO 2 . The studies showed the stability of CAII under high temperature (325 K) and confirmed the potential role in CO 2 sequestration. This study may be valuable in future to design the biodegradable industrial catalyst based on CAII to enhance CO 2 capture rate and to diminish its environmental collision.