Turkish Journal of Biology Turk J Biol (2016) 40: 1303-1310 © TÜBİTAK doi:10.3906/biy-1602-40 http://journals.tubitak.gov.tr/biology/ Research Article Construction of an oxygen detection-based optic laccase biosensor for polyphenolic compound detection 1 1 2 2,3 1,4, 2 Kadir BİLİR , Marie-Theres WEIL , Julia LOCHEAD , Fatma Neşe KÖK *, Tobias WERNER Molecular Biology-Genetics and Biotechnology Program (MOBGAM), İstanbul Technical University, Maslak, İstanbul, Turkey 2 Institute of Analytical Chemistry, Faculty of Biotechnology, University of Applied Sciences, Mannheim, Germany 3 Institute for Pharmacy and Molecular Biotechnology, Heidelberg University, Heidelberg, Germany 4 Department of Molecular Biology and Genetics, İstanbul Technical University, Maslak, İstanbul, Turkey Received: 11.02.2016 Accepted/Published Online: 25.04.2016 Final Version: 16.12.2016 Abstract: A fiber optic biosensor was constructed from Pleurotus ostreatus laccase for the detection of polyphenolic compounds. Laccase was immobilized on the surface of the commercially available fiber optic oxygen sensor spots by using 3-aminopropylsilanetriol, glutaraldehyde, and amino-modified carboxycellulose. A diffusion layer containing tetramethyl orthosilicate (TMOS), trimethoxymethylsilane (Tri-MOS), and polyvinyl alcohol (PVA) was added to the immobilized laccase layer. The consumption of oxygen as a result of laccase activity was monitored using a fiber optical measuring setup with catechol as a model substrate. The optimal enzyme amount was determined as 1.5 mg per 50 µL of enzyme layer mixture, and with one diffusion layer and at pH 6.9, optimum detection conditions were attained. The biosensors have high reproducibility, stability (at least 85 days if stored in PBS at 4 °C), and convenient measurement duration (ca. 25 min between two successive measurements). The biosensor was found to have a broad linear working range for catechol (40–600 µM) and to be applicable to a flow-through system. In summary, an easy-to-produce, reproducible, and stable laccase sensor with a broad linear working range was produced. The sensor has potential in the food industry as well as in environmental monitoring for the detection of phenolic compounds. Key words: Laccase biosensor, phenolic compounds, catechol, oxygen-based optic sensor 1. Introduction Detection of polyphenolic compounds has been drawing attention both in the environmental control of toxic contaminants (side products of industrial and agricultural processes) and in food quality analysis (Moccelini et al., 2008; Barrosso et al., 2011; Prehn et al., 2012; Singh et al., 2012; Neoh et al., 2013). Detection could be done by various methods involving spectrophotometry, gas and liquid chromatography, electrochemical methods, and capillary electrophoresis (Karim and Fakhruddin, 2012; Alshahrani et al., 2014). Both spectrophotometry and chromatography, however, need time-consuming pretreatment steps. In addition, spectrophotometry is prone to interference and chromatography requires expensive instruments and is not suitable for on-site detection (Karim and Fakhruddin, 2012; Alshahrani et al., 2014). These limitations make the design of a portable device that does not require pretreatment steps inevitable for rapid on-site monitoring of phenolic compounds and biosensors are attractive candidates for this purpose. *Correspondence: [email protected] In food analysis, laccase (Rahman et al., 2008; DiFusco et al., 2010), tyrosinase (Kim et al., 2009; Cortina-Puig et al., 2010), and peroxidase (Mello et al., 2005) enzymes have been used to detect different phenolic compound of natural origin such as chlorogenic acid (Moccelini et al., 2008), catechin (Rahman et al., 2008), caffeic acid (Cortina-Puig et al., 2010), or food additives like propyl gallate (Morales et al., 2005). The majority of currently available sensors for phenolic compound monitoring are based on electrochemical principles (Barrosso et al., 2011). One disadvantage of these sensors is their limited electrochemical selectivity because of the electrooxidation of species other than the target phenolic compound. In contrast to electrochemical biosensors, fiber optic sensors have extremely selective transducers whose signals are not disturbed by diverse interferences. They also do not have direct interference from surrounding electric or magnetic fields because their signal is optic (Mazhorova et al., 2012; Narsaiah et al., 2012). Fiber optics are self-sufficient and do not require an external reference signal as electrochemical 1303 BİLİR et al. / Turk J Biol biosensors do (Shaikh and Patil, 2012). Laccases belong to the blue-copper family of oxidases and have been widely used in biotechnological applications ranging from textile and food industries to fuel cell applications (RomanGusetu et al., 2009; Arora and Sharma, 2010; Tastan et al., 2011; Andreu-Navarro et al., 2012; Betancor et al., 2013). They could oxidize different substrates with the reduction of oxygen to water, without hydrogen peroxide generation. In this study, the aim was to construct a reliable and easy-to-use laccase biosensor based on a fiber optic system for on-site detection of phenolic compounds. The principle of detection was based on the emission of luminescence from oxygen-sensitive dyes contained in sensor spots. After excitation, when the luminescent dyes encounter an oxygen molecule, the excess energy is transferred to that molecule through a process called dynamic quenching (Figure 1). The light emission intensity of the sensor spot is decreased (fewer excited dyes emit photons) as well as the average excitation lifetime (many dyes reach ground level rapidly). The relationship between the excitation lifetime and the oxygen concentration is quantified by the Stern–Volmer relationship (Carraway et al., 1991). For precise referencing, the phase modulation technique is applied (Trettnak et al., 1996). The sensor spot is excited with sinusoidally modulated light from a light-emitting diode and therefore the emitted light is also sinusoidally modulated. The average excitation lifetime is then detected as the phase angle between these two light emissions. To construct a biosensor for polyphenol detection, laccase from Pleurotus ostreatus was immobilized on planar oxygen sensor spots (SP-PSt3) using 3-aminopropylsilanetriol (APST) for surface activation, glutaraldehyde (GA) as a cross-linker, and amino-modified carboxycellulose (AMC) to form a mechanically stable matrix. Thereafter, optimum construction and working conditions, e.g., reproducibility, measurement duration, response time, repeatability of response, dynamic working range, storage stability, and applicability, were investigated. Flow-through oxygen minisensors (FTC-PSt3) were also prepared to develop a stable, reproducible laccase sensor for continuous detection of phenolic compounds. The construction method is easy and rapid and the resulting easy-to-use biosensor could allow on-site detection of phenolic compounds in the food industry and the environment. The fiber optic system offers flexibility to the design, which allows for multiple sample detection or adaptation to flow-through systems and so could be explored for different applications. Optic measurements, especially fluorescence measurements, generally require nonturbid, clear solutions and simple matrices; if not, the signal intensity is affected. The proposed detection method, however, involves the use of oxygen-sensitive dye attached to a fiber optic cable. In this system, the optic signal is formed on the biosensor surface depending on oxygen concentration and is transferred directly to the detector through fiber optics so the fluorescent signal will not be affected by the turbidity of the solution. 2. Materials and methods 2.1. Materials The fiber-optic oxygen sensors and transmitters were purchased from PreSens Precision Sensing GmbH (Regensburg, Germany). Laccase (EC 1.10.3.2 from Pleurotus ostreatus, ≥4.0 U/mg) and freshly prepared catechol (on a weekly basis) were obtained from SigmaAldrich. 3-Aminopropylsilanetriol was purchased from Degussa AG Aerosil & Silanes, glutaraldehyde from Carl Roth, and tetramethyl orthosilicate (TMOS), 2-propanol, and trimethoxymethylsilane (Tri-MOS) from Fluka. Figure 1. Detection of mechanism of the oxygen detection-based optic system: the emission of luminescence from oxygen-sensitive dyes contained in sensor spots depends on the amount of oxygen in the environment. 1304 BİLİR et al. / Turk J Biol Mowiol was obtained from Kuraray and glycerol from Carl Roth. 2.2. Methods 2.2.1. Activity determination of laccase The immobilized laccase activity was determined spectrophotometrically in 0.1 M sodium acetate buffer (pH 5) containing catechol (50 mM) or 2,2’-azino-bis(3ethylbenzothiazoline-6-sulfonic acid) (ABTS) (5 mM) as the substrate at 404 nm (for catechol) or 414 nm (for ABTS) at room temperature. Laccase-immobilized sensor spots were fixed into cuvettes with silicone glue. All measurements were run in parallel with a negative control containing no enzyme. The value of the extinction coefficient for the oxidized products of catechol is 740 M–1 cm–1 and for ABTS it is 36,800 M–1 cm–1. 2.2.2. Construction of the laccase-immobilized SP-PSt3 sensor spots 2.2.2.1. Preparation of amino-modified cellulose Ten grams of carboxycellulose (CC) was washed for 1 h with 200 mL of Millipore filtered deionized water containing 5 g of sodium chloride. After that, CC was vacuum filtered and a second wash was carried out with 200 mL of deionized water (Millipore) for another hour. After the vacuum filtration, a last wash was done for 1 h using 70% ethanol. The filtered CC was then resuspended in 200 mL of deionized water. To obtain amino-modified CC, 4 g of ethylenediamine-dihydrochloride (EDD) was added into CC solution in small portions under continuous stirring. Ten minutes later, 350 mg of carbodiimide (EDC) was added and the pH was set to 4.6 by the addition of 0.1 M hydrochloride acid. The solution was stirred for 4 h and the cellulose was filtered off. The cellulose was then resuspended in 200 mL of water, stirred for 15 min, and vacuum filtered. This step was repeated five times. In the next step, the cellulose was successively washed with NaOH solution (100 mL, 1 M) and water. Finally, the powder was washed with 100 mL of ether and dried over silica gel in a desiccator at room temperature for at least 2 days. 2.2.2.2. Immobilization of laccase Planar oxygen sensor SP-PSt3 (Figure 2A), a matrix of polymers with an oxygen-quenchable luminescent dye and an additional overcoat of medical grade silicone, was used for the construction of the biosensor. These matrices were first cut into small round pieces (Ø 3 mm) and washed with 75% (v/v) 2-propanol (1 mL) and distilled water twice. The sensor’s nonshiny side was then laid on the 3-aminopropylsilanetriol (APST, 20%) overnight at room temperature under light protection for activation. The next day, the sensors were washed twice in water. In order to immobilize laccase on the sensor spots, three different solutions were prepared by dissolving enzyme (1.0, 1.5, and 3.0 mg) in sodium phosphate buffer (0.1 M, pH 6.9, 22 µL). The cross-linker (glutaraldehyde, 25%, 3 µL) and a matrix stabilizer (amino-modified carboxycellulose, AMC, 25 µL) were then added and the well-mixed suspension (50 µL per sensor) was transferred onto the upper (nonshiny) surface of the sensor. The enzyme layer dried overnight at room temperature under light protection. 2.2.2.3. Addition of diffusion layer The diffusion layer was prepared by using TMOS:PVA:HCl:Tri-MOS in a volumetric ratio of 2:8:5:1. After preparation, 40 µL of this mixture was pipetted onto the laccase layer and left to dry overnight at room temperature under light protection. To evaluate the effect of the diffusion layer on sensor performance, the absence and presence of the diffusion layer (single or double layers) were tested. To prepare the double diffusion layer containing sensor spots, the first layer was left to dry for 2 h before pipetting the second layer. Figure 2. a) Planar oxygen sensor SP-PSt3 and b) fiber-optic chemical sensor that is integrated in a T-shaped flowthrough cell (FTC). 1305 BİLİR et al. / Turk J Biol 2.2.2.4. Measurement After the diffusion layer dried, sensor spots were glued (RS 692-542, silicone glue) into vials that were rinsed prior to use with acetone to remove all fatty residues and sensors were left to dry for 24 h at room temperature under light protection. Phosphate buffer saline (PBS, 20 mL, pH 6.9) was added to each vial after the glue dried and vials were connected to an OXY-4 transmitter with fiber optic cables. The measurements were done under continuous stirring with the help of a magnetic stirrer with measurement intervals of 15 s. When the background signal was stabilized, an increasing concentration of catechol solution was added into vials step by step and the phase angles for different catechol concentrations were plotted. 2.2.3. Characterization of the laccase-immobilized SPPSt3 sensor spots 2.2.3.1. Optimization of enzyme and diffusion layer amount In order to determine the laccase amount needed for optimum response, three different enzyme amounts (1.0, 1.5, and 3.0 mg/sensor) were tested. The effect of diffusion layer presence and its quantity on sensor response was evaluated by preparing sensors with (one or two layers) or without a diffusion layer. For all cases, 1.5 mg/sensor laccase concentration was used. 2.2.3.2. Determination of optimum pH The performances of the sensors prepared with optimum enzyme amount and diffusion layer quantity were evaluated at three different pH conditions that corresponded to acidic, neutral, and basic pH, namely 5, 6.9, and 9, using PBS as a buffering system. Since the immobilization of the enzyme and its storage were carried out at pH 6.9, this value was also used for activity assays. 2.2.3.3. Determination of dynamic working range The maximum and minimum phenol detection limit of the biosensor was investigated in PBS buffer (pH 6.9) by using optimum sensor conditions. For the highest detection limit, catechol concentrations between 0.1 and 5.0 mM were used and were added up to 0.6 mM final concentration step by step (0.1 mM at each step), and then the buffer was refreshed. This procedure was performed before each measurement for 1 mM, 2 mM, and 5 mM catechol. After that, catechol samples with concentrations between 0.01 and 0.1 mM were used to find the lowest limit of detection and the linear working range of the biosensor. 2.2.3.4. Determination of reproducibility and hysteresis behavior To determine the reproducibility of sensor spots, five spots were produced simultaneously and the responses of each sensor were compared using catechol as an analyte. To determine the hysteresis of the biosensors, first different 1306 concentrations of catechol were added gradually to the same sensor spot, and then the buffer was refreshed. When the signal reached equilibrium, measurements were done in the opposite order, gradually decreasing the catechol concentration, and the results were compared. 2.2.3.5. Storage stability of the biosensor The sensor spots were stored in PBS (pH 6.9) at 4 °C, and at different time points (1, 30, and 85 days), three sensor spots were randomly taken out and activity measurements were done using catechol (5 mM). 2.2.3.6. Measurement duration of the biosensor To determine the measurement duration of the biosensor, the time necessary for the sensor to complete detection, i.e. the time between the addition of sample and the equilibration of the signal, was measured by using samples of different catechol concentrations, where the final concentrations ranged between 0.1 and 1.5 mM. 2.2.4. Construction of the laccase-immobilized FTCPSt3 sensor spots 2.2.4.1. Activation and immobilization For the flow-through system, an oxygen minisensor (FTC-PSt3) was used. This is a miniaturized fiber-optic chemical sensor that is integrated in a T-shaped flowthrough cell (FTC) (Figure 2B). One arm of the T-shape serves as a connection point to the FIBOX oxygen meter via a polymer optical fiber (Ø 2 mm) as the light guide. The activation was done as explained in Section 2.2.2.2. Laccase (10 mg), bovine serum albumin (BSA, 10 mg), and glycerol (6 mg) were then mixed thoroughly in 100 µL of dH2O and glutaraldehyde (25 µL, 2.5%) was added to this solution. For the immobilization, 2.6 µL of this mixture was pipetted onto the surface of each sensor and left to dry overnight at room temperature in the dark. 2.2.4.2. Addition of the diffusion layer The diffusion layer was prepared using ethylcellulose:D4:ethanol solution (90%) with a mass ratio of 2:1:27. The prepared mixture (1.6 µL) was pipetted once onto each sensor surface and left to dry overnight at room temperature in the dark. 2.2.4.3. Measurement Sensor spots were glued to the head of a plastic tube attached to the fiber optic cable with the help of silicone glue and were left to dry for 24 h at room temperature in the dark. Plastic tubes containing sensor spots were incubated in PBS (0.1 M, pH 6.9) overnight in order to humidify the matrix of the sensors. Measurements were done the following day with the FIBOX 3 transmitter, introducing catechol solution with a known concentration via a peristaltic pump after the background signal was stabilized. BİLİR et al. / Turk J Biol 60 Phase Angle [°] 55 50 45 40 35 30 25 0 0.2 0.4 0.6 0.8 Catechol concentration (mM) 1 Figure 3. Determination of optimum enzyme amount (● 3 mg, ■ 1.5 mg, and ▲ 1 mg) based on comparison of sensors’ phase angles for different catechol concentrations (three independent sensors were used and three measurements were performed with each). 55 50 Phase Angle [°] 3. Results and discussion 3.1. Optimization of the SP-PSt3 fiber optic biosensor 3.1.1. Effect of enzyme amount Sensors with different laccase amounts (1.0, 1.5, and 3.0 mg/sensor) and without a diffusion layer were used. The change in the phase angles based on catechol concentration was plotted (Figure 3). It could be seen that sensors constructed with 1 mg of laccase could not respond effectively to the changes in catechol concentration. When the laccase amount was increased to 1.5 mg, there was a dramatic increase in the sensor response. A further increase in the laccase amount (3 mg), however, led to a decrease in the phase angle values. This could be due to the excessive amount of enzyme on the surface (an increased enzyme layer thickness), which could limit the free movement of the enzyme needed for enzymatic activity and slow the mass transport rate of the analyte. This type of behavior has been reported in the literature for different enzyme sensors (Mulchandani et al., 1999; Kushwah et al., 2011). The optimum laccase amount was therefore determined as 1.5 mg per sensor and used in further studies. 3.1.2. Effect of diffusion layer quantity Sensors (1.5 mg of laccase) with (one or two layer) or without a diffusion layer were prepared and the results were plotted according to the changes in phase angle values (Figure 4). The presence of the diffusion layer affected the maximum phase angle reached by the system; biosensors with two diffusion layers reached a lower phase angle (ca. 48°), while biosensors with one diffusion layer reached the highest one (ca. 55°). Without a diffusion layer, the reusability of the sensors was limited because of external factors that led to the easy loss of enzyme layer from the sensor surface. This could be the reason for the 45 40 35 30 25 0.0 0.2 0.4 0.6 0.8 Catechol concentration (mM) 1.0 Figure 4. Effect of diffusion layer (DL) on biosensor response: (●) without DL, (■) with one DL, and (▲) with two DLs. lower phase angle values obtained in the absence of the diffusion layer. A biosensor with one diffusion layer was chosen for further studies. 3.2. Characterization of the biosensor 3.2.1. Effect of pH The effect of pH was evaluated with the optimized sensor (1.5 mg of enzyme and 1 diffusion layer) and the measurements were done in PBS buffer with different pH values (5, 6.9, and 9) (Figure 5). Optimum pH was found to be shifted to pH 6.9 upon immobilization when compared with that of the free form (pH 4.5). This shift in optimum pH is generally caused by the proton exchange properties of the immobilization matrix (Cho et al., 2008). The microenvironment surrounding the immobilized enzymes affects their apparent optimum values and anionic polymers, for example, were shown to shift the pH optimum of the enzyme to more basic values (Tastan et al., 2011). The biosensor still had considerable activity at pH 5, but its activity was almost completely hindered at pH 9. It was seen that the loss of activity in alkaline conditions (e.g., pH 9.0) was not a permanent one and activity could be restored when the optimum pH value (pH 6.9) was reached again (data not shown). Laccases generally tolerate acidic conditions well (4.0–5.5), but their activity drops abruptly at more basic pH values (>6.0) (Li et al., 2014). The constructed biosensor therefore has the advantage of being used in the measurement of samples with pH values near neutral as opposed to other laccase sensors and it seemed to keep its activity considerably in mildly acidic conditions. 3.2.2. Linear working range and limit of detection (LOD) of the biosensor The lowest detection phase value (LDPV) was calculated as 27.76 by the formula LDPV = 3 × (standard deviation 1307 BİLİR et al. / Turk J Biol 60 Phase Angle [°] 55 50 45 40 35 30 25 0.0 0.2 0.4 0.6 0.8 Catechol concentration(mM) 1.0 Figure 5. Optimum pH determination of the fiber optic biosensor. pH (▲) 5.0, (●) 6.9, and (■) 9.0 value of 0 mM) + (phase angle value of 0 mM). A catechol concentration of 0.04 mM yielded a phase number of 27.88 (±0.04), so it was noted as the LOD of the biosensor for catechol. When a wide range of catechol concentrations (0.1–0.6 mM) was used to determine the linear working range, a linear regression analysis result with a good R2 value (0.9876) was obtained (Figure 6). When the concentration range was narrowed down to lower concentrations, however, a different linear relation with a better R2 value (0.9985) was attained. This clearly showed that the biosensor could be used for the prediction of catechol concentrations over a broad range of values (0.1–0.6 mM), but the calibration curve obtained for this concentration range could fail to determine the lower concentrations with high accuracy, so one should be careful in the interpretation of the signal at low concentrations. For the optical laccase sensor developed by Abdullah et al. (2007), the LOD was determined as 0.33 mM. A 55 30 29 60 y = 27.307x + 26.749 R² = 0.9985 55 28 45 27 26 40 0 0.05 Phase Angle [°] Phase angle [°] 50 0.1 35 y = 47.057x + 25.624 R² = 0.9876 30 25 0 0.2 0.4 50 45 40 35 30 0.6 Catechol concentration (mM) Figure 6. Linear working range of the biosensor (insert shows the behavior of the sensor at low catechol concentrations). 1308 similar LOD (0.3 mM) was found by Singh et al. (2013) using tyrosinase for amperometric detection of catechol with a linear working range of 1.0–6.0 mM. To obtain better LOD values, incorporation of nanoparticles was generally proposed by different groups. The usage of gold nanoparticles, for example, has been found to decrease the LOD down to 0.03 µM (Brondani et al., 2013). It could therefore be said that a better LOD value was obtained when compared with similar electrochemical biosensors without any nanoparticle incorporation. 3.2.3. Reproducibility of the biosensor Five sensor spots were produced simultaneously according to protocol and their responses were tested with different concentrations of catechol. The slopes of phase angle vs. catechol concentration graphs were found to be similar with an acceptable standard deviation (46.8 ± 0.6), indicating that the reproducibility of the biosensor was high. 3.2.4. Hysteresis behavior of biosensor response Different concentrations of catechol were added gradually up to 0.6 mM (1st measurement). The buffer was then refreshed and measurements were done in the opposite order by gradually decreasing the catechol concentration. During this step, buffer was changed and a specific buffer + catechol mixture was added before each measurement (2nd measurement). Results of sensor response according to phase angle values were compared (Figure 7). The biosensor showed almost the same response against the same catechol concentrations whether the catechol’s concentration was decreased or increased gradually, so no detectable hysteresis on biosensor response was observed. 3.2.5. Storage stability of the biosensor Activity measurements of the immobilized system were done at different time intervals (1st, 30th, and 85th days after production) and phase angle vs. catechol 25 0 0.1 0.2 0.3 0.4 0.5 0.6 Catechol concentration (mM) Figure 7. Comparison of 1st (■) and 2nd (●) measurements’ phase angles to determine hysteresis behavior. BİLİR et al. / Turk J Biol 48 2 mM Phase angle [°] 44 6 mM 3 mM 40 0.5 mM 36 32 0.2 mM 6 mM 1 mM 0.5 mM 0 mM 28 2 mM 0.5 mM 0.2 mM 0.2 mM 0 mM 24 20 0 100 200 300 400 500 Time (min) Figure 8. Determination of sensor applicability to the flowthrough system. concentration graphs were compared. The slope of these curves was found to be 44.0, 43.5, and 41.7, respectively, meaning that no significant change could be detected after a month and ca. 95% of the biosensor’s initial activity was retained after 85 days. This result was found to be better than that of the laccase biosensor constructed by Gomes and Rebelo (2003), who reported a 62% decrease in activity after 38 days. Abdullah et al. (2007), on the other hand, reported a comparable result with almost 90%–98% activity after 2 months of storage at 4 °C. 3.2.6. Measurement duration When the measurements were carried out by gradually increasing the catechol concentration from 0.1 mM to 1.5 mM, a measurement period of around 13 min was needed for the stabilization of the signal. When the signal recovery after the washing step, etc. was taken into account, 25–30 min were needed between two successive sample measurements. It could therefore be concluded that the biosensor has a short measurement duration (ca. 25 min between two successive measurements) at optimum conditions, i.e. with one diffusion layer and at pH 6.9. 3.3. Applicability to flow-through system FTC-PSt3 sensor spots were prepared considering the optimum parameters of the previous sensor (SP-PSt3) and measurements were done with randomly chosen catechol concentrations to determine the response and reliability of the sensor. Figure 8 shows that the signal could be reproduced at each attempt, showing that FTC-PSt3 sensors work properly in a flow-through system. Acknowledgment The grant from the EU Erasmus Student Exchange Program for Kadir Bilir is gratefully acknowledged. Julia Lochead is a student of the HBIGS graduate program and received a PhD grant from the Albert and Anneliese Konanz foundation. The authors would also like to acknowledge that for the preparation of the amino-modified cellulose and diffusion layer, a method used for glucose oxidase during the successful acquisition of the project “Enzyme Immobilization on Commercial Optical Oxygen Sensor Membranes” [Justice C, Werner T (2007), University of Applied Sciences Mannheim, data not shown] was adapted. References Abdullah J, Ahmad MH, Karuppiah N, Sidek H (2007). An optical biosensor based on immobilization of laccase and MBTH in stacked films for the detection of catechol. Sensors 7: 22382250. Brondani D, de Souza B, Souza BS, Neves A, Vieira IC (2013). PEIcoated gold nanoparticles decorated with laccase: A new platform for direct electrochemistry of enzymes and biosensing applications. Biosens Bioelectron 42: 242-247. Alshahrani LA, Li X, Luo H, Yang L, Wang M, Yan S, Liu P, Yang Y, Li Q (2014). The simultaneous electrochemical detection of catechol and hydroquinone with [Cu(Sal-β-Ala)(3,5DMPz)2]/SWCNTs/GCE. Sensors 14: 22274-22284. Carraway ER, Demas JN, DeGraff BA (1991). Luminescence quenching mechanism for microheterogeneous systems. Anal Chem 63: 332-336. Andreu-Navarro A, Fernández-Romero JM, Gómez-Hens A (2012). Determination of polyphenolic content in beverages using laccase, gold nanoparticles and long wavelength fluorimetry. Anal Chim Acta 713: 1-6. Arora DS, Sharma RK (2010). Ligninolytic fungal laccases and their biotechnological applications. App Biochem Biotech 160: 1760-1788. Barroso FM, de-los-Santos-Alvarez N, Delerue-Matos C, Oliveira MBPP (2011). Towards a reliable technology for antioxidant capacity and oxidative damage evaluation: electrochemical (bio)sensors. Biosens Bioelectron 30: 1-12. Cho N, Cho H, Shin S, Choi Y, Leonowicz A, Ohga S (2008). Production of fungal laccase and its immobilization and stability. J Fac Agr Kyushu U 53: 13-18. Cortina-Puig M, Munoz-Berbel X, Calas-Blanchard C, Marty JL (2010). Diazonium-functionalized tyrosinase-based biosensor for the detection of tea polyphenols. Mikrochim Acta 171: 187193. Di Fusco M, Tortolini C, Deriu D, Mazzei F (2010). Laccase-based biosensor for the determination of polyphenol index in wine. Talanta 81: 235-240. Gomes SASS, Rebelo MJF (2003). A new laccase biosensor for polyphenols determination. Sensors 3: 116-175. 1309 BİLİR et al. / Turk J Biol Karim F, Fakhruddin ANM (2012). Recent advances in the development of biosensor for phenol: a review. Rev Environ Sci Biotechnol 11: 261-274. Narsaiah K, Shyam NJ, Rishi B, Rajiv S, Ramesh K (2012). Optical biosensors for food quality and safety assurance-a review. J Food Sci Tech 49: 383-406. Kim KI, Kang HY, Lee JC, Choi SH (2009). Fabrication of a multiwalled nanotube (MWNT) ionic liquid electrode and its application for sensing phenolics in red wines. Sensors 9: 67016714. Neoh CH, Yahya A, Adnan R, Majid ZA, Ibrahim Z (2013). Optimization of decolorization of palm oil mill effluent (POME) by growing cultures of Aspergillus fumigatus using response surface methodology. Environ Sci Pollut R 20: 29122923. Kushwah BS, Upadhyaya SC, Shukla S, Sikarwar AS, Sengar RMS, Bhadauria S (2011). Performance of nanopolyaniline-fungal enzyme based biosensor for water pollution. Adv Mat Lett 2: 43-51. Li D, Luo L, Pang Z, Ding L, Wang Q, Ke H, Huang F, Wei Q (2014). Novel phenolic biosensor based on a magnetic polydopaminelaccase-nickel nanoparticle loaded carbon nanofiber composite. Appl Mater Inter 6: 5144-5151. Mazhorova A, Markov A, Ng A, Chinnappan R, Skorobogata O, Zourob M, Skorobogatiy M (2012). Label-free bacteria detection using evanescent mode of a suspended core terahertz fiber. Opt Express 20: 5344-5355. Mello LD, Sotomayor MDPT, Kubota LT (2005). HRP-based amperometric biosensor for the polyphenols determination in vegetables extract. Sensor Actuat B-Chem 96: 636-645. Moccelini SK, Spinelli A, Vieira IC (2008). Biosensors based on bean sprout homogenate immobilized in chitosan microspheres and silica for determination of chlorogenic acid. Enzyme Microb Tech 43: 381-387. Morales MD, Gonzalez MC, Reviejo AJ, Pingarro JM (2005). A composite amperometric tyrosinase biosensor for the determination of the additive propyl gallate in foodstuffs. Microchem J 80: 71-78. Mulchandani A, Pan S, Chen W (1999). Fiber-optic enzyme biosensor for direct determination of organophosphate nerve agents. Biotechnol Progr 15: 130-134. 1310 Prehn R, Gonzalo-Ruiz J, Cortina-Puig M (2012). Electrochemical detection of polyphenolic compounds in foods and beverages. Curr Anal Chem 8: 472-484. Rahman MA, Noh HB, Shim YB (2008). Direct electrochemistry of laccase immobilized on au nanoparticles encapsulateddendrimer bonded conducting polymer: application for a catechin sensor. Anal Chem 80: 8020–8027. Roman-Gusetu G, Waldron KC, Rochefort D (2009). Development of an enzymatic microreactor based on microencapsulated laccase with off-line capillary electrophoresis for measurement of oxidation reactions. J Chromatogr A 1216: 8270-8276. Shaikh S, Patil MA (2012). Analysis, designing and working principal of optical fiber (OF) biosensors. Int J Eng Sci 1: 52-57. Singh S, Jain DVS, Singla ML (2013). Sol-gel based composite of gold nanoparticles as matix for tyrosinase for amperometric catechol biosensor. Sensors Actuat B-Chem 182: 161-169. Singh SK, Kraemer M, Trebouet D (2012). Studies on treatment of a thermo-mechanical process effluent from paper industry using ultrafiltration for water reuse. Desalin Water Treat 49: 208-217. Tastan E, Onder S, Kok FN (2011). Immobilization of laccase on polymer grafted polytetrafluoroethylene membranes for biosensor construction. Talanta 84: 524-530. Trettnak W, Kolle C, Reininger F, Dolezal C, O’Leary P (1996). Miniaturized luminescence lifetime-based oxygen sensor instrumentation utilizing a phase modulation technique. Sensors Actuat B-Chem 35-36: 506-512.
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