|
|
||||||||
RESEARCH REPORT |
1 Restorative Discipline and
2 Biomaterials Discipline, Faculty of Dentistry, University of Toronto, Toronto, ON, Canada M5G 1G6;
* corresponding author, paul.santerre{at}utoronto.ca
| ABSTRACT |
|---|
|
|
|---|
KEY WORDS: biodegradation biomaterial hydrolysis esterases serine esterase inhibitor dental resins
| INTRODUCTION |
|---|
|
|
|---|
Cholinesterases (ChE) consist of a group of esterases that hydrolyze choline esters at a higher rate than they do other esters (Ryhanen et al., 1983). Various types of ChE can be differentiated by the use of either specific substrates or selective inhibitors. In humans, two main types of ChE exist: acetylcholinesterase and pseudocholinesterase (PCE) (Ryhanen et al., 1983). More recently, ChE activity with respect to TEGDMA has been reported (Yourtee et al., 2001).
Mononuclear phagocytic cells, i.e., macrophages and monocytes, produce esterases and are present in normal and inflamed gingiva (Payne et al., 1975; Tenovuo, 1990; Lappin et al., 1999). Most of the esterase-related activity in mature macrophages is cholesterol esterase (CE) (Li and Hui, 1997). Cholesterol esterase generation increases in macrophages under a variety of conditions (Lindhorst et al., 1997; Labow et al. 2001).
It has been shown that both CE and PCE can hydrolyze the synthetic matrix components of commercial and model composite resin systems (Santerre et al., 1999, 2001). To determine the concentrations of such activities in human saliva, we profiled esterase activities using o- and p-isomers of nitrophenylacetate and nitrophenylbutyrate (Labow et al., 1994), as well as a PCE-specific substrate, butyrylthiocholine iodide (BTC).
| MATERIALS & METHODS |
|---|
|
|
|---|
Prior to the preparation of the cured composite resin samples, the composite pastes were warmed at room temperature for 1 hr. For sample preparation, this material was photo-polymerized into cylindrical pellets (4 mm height x 4 mm diameter) as previously described (Jaffer et al., 2002).
Enzyme Preparation
We prepared CE (Item No. 70-1081-01, Lot No. 9750, Genzyme, Cambridge, MA, USA) and PCE (C-5386, Sigma, St. Louis, MO, USA) by dissolving the enzymes at the desired concentrations (see below for specific experiments) in phosphate-buffered saline (D-PBS, 21600-010, Gibco, Grand Island, NY, USA). All solutions were sterile-filtered with the use of a 0.22-µm filter (Millex®-GP, 0.22 µm Filter unit, Cat. No. SLGPR25LS, Millipore, Bedford, MA, USA). The prepared CE and PCE solutions used for replenishing enzyme activity in the biodegradation experiments were stored at -80°C. One unit of CE activity was defined as a change of absorbance of 0.01 optical density (OD) per min at 410 nm with para-nitrophenylacetate (p-NPA) as a substrate at pH 7.0 and 25°C (Labow et al., 1994). We selected this definition of activity to allow comparisons to be made with previous degradation studies that used a similar definition of units (Santerre et al., 1999). We determined the PCE activity for this study by measuring changes in OD at a wavelength of 405 nm, using butyrylthiocholine iodide (BTC) as a substrate [cholinesterase (BTC) activity kit, Sigma, Procedure No. 421]. For PCE, a unit of enzyme activity was defined as 1 mmol butyrate released per 1 mL enzyme solution per min. The spectrophotometer unit was an Ultrospec® II (LKB Biochrom, Cambridge, England).
Enzyme Substrate Specificities
We prepared the nitrophenyl-isomerso-nitrophenylacetate (o-NPA) (N-9001 Sigma, St. Louis, MO, USA), p-nitrophenylacetate (p-NPA) (N-8130, Sigma), o-nitrophenylbutyrate (o-NPB) (N-9751, Sigma), and p-nitrophenylbutyrate (p-NPB) (N-9876, Sigma)by dissolving each agent in 1 mL methanol, which was then diluted with 100 mL of 0.1 M sodium acetate, pH 5.0, to yield a final concentration of 1 mM. We determined CE and PCE activities by incubating the enzymes in a solution containing 1.0 mL of 0.05 M phosphate buffer, pH 7.0, and 0.5 mL of the prepared nitrophenyl ester substrate solution. We took spectrophotometric measurements at 410 nm, as described above, to measure the unit of activity per µg protein. The enzymes were also assayed with BTC as a substrate as described above.
Hydrolase Activity in Human Saliva
Unstimulated whole human saliva (human ethics protocol approved by the Univ. of Toronto) was collected into 50-mL centrifuge tubes from seven healthy individuals and immediately stored on ice before being processed according to a method slightly modified from that previously reported (Munksgaard and Freund, 1990). Bulk debris was separated from whole saliva by centrifugation (Centrifuge international equipment Co., Needham, MA, USA) at 2400 RPM for 10 min at 4°C. The supernatant was collected and then filtered via 0.22-µm syringe filters (Millex®-GP, 0.22 µm Filter unit, Cat. No. SLGPR25LS, Millipore, Bedford, MA, USA). Aliquots of the filtered saliva were tested for hydrolase activity and compared with the stock CE and PCE enzymes with the use of 5 substratesp-NPA, o-NPA, p-NPB, o-NPB, and BTCas described above. The experiment was run with triplicate sample groups.
Inhibition of CE and PCE with PMSF
Prior to the biodegradation experiments, we measured the activity of the enzymes with and without the esterase inhibitor, phenylmethyl sulfonyl fluoride (PMSF) (P-7626, Sigma, St. Louis, MO, USA), by adding the inhibitor, dissolved in ethanol, to the enzyme solutions prior to their activity measurement (Labow et al., 1994). We also assayed the enzymes with the same volume of ethanol (PMSF carrier solvent) without the inhibitor to assess if this carrier solvent influenced the enzymes activity. PMSF dissolved in ethanol was also used as a non-enzyme control. The final concentration range of PMSF was adjusted to 1 mM in the CE solution (1 unit/mL) and 0.5 mM for PCE (1 unit/mL). These concentrations were established to provide approximately 60% inhibition values relative to their respective substrates.
Before the biodegradation experiment, the cured composite samples were pre-incubated in D-PBS for 48 hrs at 37°C to remove a significant fraction of the unreacted leachable monomers (Tanaka et al., 1991). Following pre-incubation, three cured pellets for each condition were placed in 2-mL sterile vials. The total surface area of the samples for each of these groups was 2.26 cm2. Each group was incubated (37°C and pH 7.0) in 1 mL of either buffer, CE, or PCE solution (n = 3). Ethanol alone (as a control) or PMSF dissolved in ethanol was added to either buffer, CE, or PCE replenishing solutions prior to their addition to the incubation solutions. A CE and PCE concentration of 0.1 unit/mL was chosen for the incubation, since the saliva analysis studies indicated that the esterase activity based on p-NPA substrate was about 0.1 unit/mL in saliva (see RESULTS). Accordingly, PMSF concentrations were scaled to 0.1 mM and 0.05 mM, respectively, for CE and PCE. The composite resin biodegradation experiment was run for 16 days with daily enzyme replenishment. The collected incubation solutions were filtered by means of a Millipore centrifuge filter device (Ultrafree®-CL, UFC4LCC00 5000 NMWL, Millipore, Bedford, MA, USA) and a centrifuge (Centrifuge international equipment Co., Needham, MA, USA) at 2400 RPM and kept refrigerated at 4°C until required for chromatographic analysis.
Product Isolation by High-performance Liquid Chromatography (HPLC)
A WatersTM HPLC system (Waters, Mississauga, ON, Canada) was used for the chromatographic separation of the degradation products. Specifically, the analyses of methacrylic acid (MA) derived from TEGDMA and bisGMA and bishydroxy propoxy phenyl propane (bisHPPP) derived from bisGMA were of interest. A Phenomenex Luna 5 µm C18 4.6 x 250 (Phenomenex, Torrance, CA, USA) column was used to separate and isolate the products. The mobile phase consisted of HPLC-grade methanol (Code 6701-7, Lot 34955, Caledon Laboratories LTD, Georgetown, ON, Canada) and a 2-mM buffer solution of ammonium acetate (37 233-1, Aldrich, Milwaukee, WI, USA). The pH of the buffer was adjusted to 3.0 with hydrochloric acid 6.00 N (VW3204-1, VWR, West Chester, PA, USA).
The HPLC fractions of interest were collected and then analyzed by mass spectrometry via a Perkin-Elmer/Sciex (Concord, ON, Canada) API-III triple-quadrupole mass spectrometer (LC/MS/MS) located in the Carbohydrate Research Center, University of Toronto, Ontario, Canada.
Statistical Analysis
For the enzyme substrate specificities, hydrolase activity in human saliva, and inhibition of the enzymes activity experiments, a Scheffé multiple comparison after one-way analysis of variance was applied for each experiment. The results were expressed as a mean ± standard error. For the enzyme substrate specificities, a factorial analysis was performed for the length and position of the side-chain.
| RESULTS |
|---|
|
|
|---|
|
|
|
|
| DISCUSSION |
|---|
|
|
|---|
The difference between the action of CE and that of PCE on the composite resin may be related to their different reactivities to natural and synthetic substrates. CE preferentially catalyzes the hydrolysis of long-chain fatty acid esters of cholesterol (Labow et al., 1983; Williams, 1985; Sutton et al., 1991; Feaster et al., 1996), while PCE catalyzes the turnover of low-molecular-weight choline esters, such as butyrylcholine. CE and PCE showed different activities with respect to the synthetic substrates, o- and p-nitrophenyl esters (Fig. 1
). In the factorial analysis for the length and position of the ester side-chain, only the length of the side-chain was a significant variable for CE activity (p < 0.001), with a higher hydrolysis rate for the longer side-chain nitrophenyl esters. This agrees with previous reports that CE-like activity hydrolyzes the non-water-soluble chains of synthetic polyurethane (Labow et al., 1994).
The analysis of saliva with the nitrophenyl substrates suggests the presence of a strong CE-like hydrolase activity associated with the oral environment (Fig. 2
). All human subjects showed activities toward all substrates, but the pattern of sensitivity was more similar to that of CE vs. PCE (compare Figs. 1
and 2
). This was demonstrated by the slightly higher specificity toward the para-isomer vs. other isomers and the selectivity of p-NPB over that of all other substrates for all subjects and the stock CE enzyme (Labow et al., 1994). The average activity level, measured with p-NPA as a substrate, was 0.19 ± 0.02 unit/mL. In previous work, lower CE activity levels, as measured with p-NPA, have been shown to degrade composite resin samples significantly (Shajii and Santerre, 1999; Finer and Santerre, 2003). Hence, CE-like activity is present in human saliva in levels high enough to warrant concern over the biodegradation of composite monomers.
The presence of PCE-like activity in human saliva was also confirmed, with an average activity level of 0.011 ± 0.001 unit/mL. Similar results, with respect to the PCE activity levels in saliva, were found by others (Ryhanen et al., 1983; Ryhanen, 1983; Yamalik et al., 1990, 1991).
In summary, these results support that CE and PCE are suitable models for salivary esterase activity which can catalyze the hydrolysis of composite resins in the oral cavity (Jaffer et al., 2002).
| ACKNOWLEDGMENTS |
|---|
Received November 11, 2002; Last revision September 18, 2003; Accepted September 19, 2003
| REFERENCES |
|---|
|
|
|---|
Feaster SR, Lee K, Baker N, Hui DY, Quinn DM (1996). Molecular recognition by cholesterol esterase of active site ligands: structure-reactivity effects for inhibition by aryl carbamates and subsequent carbamylenzyme turnover. Biochemistry 35:1672316734.[Medline]
Finer Y, Santerre JP (2003). Biodegradation of a dental composite by esterase-dependence on enzyme concentration and specificity. J Biomater Sci Polymer Ed 14:837849.
Jaffer F, Finer Y, Santerre JP (2002). Interactions between resin monomers and commercial composite resins with human saliva derived esterases. Biomaterials 23:17071719.[ISI][Medline]
Labow RS, Adams KA, Lynn KR (1983). Porcine cholesterol esterase, a multiform enzyme. Biochim Biophys Acta 749:3241.[Medline]
Labow RS, Duguay DG, Santerre JP (1994). The enzymatic hydrolysis of a synthetic biomembrane: a new substrate for cholesterol and carboxyl esterases. J Biomater Sci Polymer Ed 6:169179.
Labow RS, Meek E, Santerre JP (2001). Model systems to assess the destructive potential of human neutrophils and monocyte-derived macrophages during the acute and chronic phases of inflammation. J Biomed Mater Res 54:189197.[ISI][Medline]
Lappin DF, Koulouri O, Radvar M, Hodge P, Kinane DF (1999). Relative proportions of mononuclear cell types in periodontal lesions analyzed by immunohistochemistry. J Clin Periodontol 26:183189.[ISI][Medline]
Li F, Hui DY (1997). Modified low density lipoprotein enhances the secretion of bile salt-stimulated cholesterol esterase by human monocyte-macrophages. species-specific difference in macrophage cholesteryl ester hydrolase. J Biol Chem 272:2866628671.
Lindhorst E, Young D, Bagshaw W, Hyland M, Kisilevsky R (1997). Acute inflammation, acute phase serum amyloid A and cholesterol metabolism in the mouse. Biochim Biophys Acta 1339:143154.[Medline]
Lindqvist L, Nord CE, Söder PO (1977). Origin of esterases in human whole saliva. Enzyme 22:166175.[ISI][Medline]
Munksgaard EC, Freund M (1990). Enzymatic hydrolysis of (di)methacrylates and their polymers. Scand J Dent Res 98:261267.[ISI][Medline]
Nakamura M, Slots J (1983). Salivary enzymes. Origin and relationship to periodontal disease. J Periodontal Res 18:559569.[ISI][Medline]
Payne WA, Page RC, Ogilvie AL, Hall WB (1975). Histopathologic features of the initial and early stages of experimental gingivitis in man. J Periodontal Res 10:5164.[ISI][Medline]
Ryhanen RJ (1983). Pseudocholinesterase activity in some human body fluids. Gen Pharmacol 14:459460.[ISI][Medline]
Ryhanen R, Närhi M, Puhakainen E, Hanninen O, Kontturi-Närhi V (1983). Pseudocholinesterase activity and its origin in human oral fluid. J Dent Res 62:2023.
Santerre JP, Shajii L, Tsang H (1999). Biodegradation of commercial dental composites by cholesterol esterase. J Dent Res 78:14591468.
Santerre JP, Shajii L, Leung BW (2001). Relation of dental composite formulations to their degradation and the release of hydrolyzed polymeric-resin-derived products. Crit Rev Oral Biol Med 12:136151.[Abstract]
Shajii L, Santerre JP (1999). Effect of filler content on the profile of released biodegradation products in micro-filled bis-GMA/TEGDMA dental composite resins. Biomaterials 20:18971908.[ISI][Medline]
Sutton LD, Stout JS, Hosie L, Spencer PS, Quinn DM (1986). Phenyl-n-butylborinic acid is a potent transition state analog inhibitor of lipolytic enzymes. Biochem Biophys Res Commun 134:386392.[ISI][Medline]
Sutton LD, Lantz JL, Eibes T, Quinn DM (1990). Dimensional mapping of the active site of cholesterol esterase with alkylboronic acid inhibitors. Biochim Biophys Acta 1041:7982.[Medline]
Sutton LD, Froelich S, Hendrickson HS, Quinn DM (1991). Cholesterol esterase catalyzed hydrolysis of mixed micellar thiophosphatidylcholines: a possible charge-relay mechanism. Biochemistry 30:58885893.[Medline]
Tanaka K, Taira M, Shintani H, Wakasa K, Yamaki M (1991). Residual monomers (TEGDMA and Bis-GMA) of a set visible-light-cured dental composite resin when immersed in water. J Oral Rehabil 18:353362.[ISI][Medline]
Tenovuo J (1990). Patients with locally and generally reduced host defence. J Clin Periodontol 17:525526.[ISI][Medline]
Williams FM (1985). Clinical significance of esterases in man. Clin Pharmacokinet 10:392403.[ISI][Medline]
Yamalik N, Ozer N, Caglayan F, Caglayan G (1990). Determination of pseudocholinesterase activity in the gingival crevicular fluid, saliva, and serum from patients with juvenile periodontitis and rapidly progressive periodontitis. J Dent Res 69:8789.
Yamalik N, Ozer N, Caglayan F, Caglayan G, Akdoganli T (1991). The effect of periodontal therapy on salivary pseudocholinesterase activity. J Dent Res 70:988990.
Yourtee DM, Smith RE, Russo KA, Burmaster S, Cannon JM, Eick JD, et al. (2001). The stability of methacrylate biomaterials when enzyme challenged: kinetic and systematic evaluations. J Biomed Mater Res 57:522531.[ISI][Medline]
This article has been cited by other articles:
![]() |
S. C. Bayne Dental Biomaterials: Where Are We and Where Are We Going? J Dent Educ., May 1, 2005; 69(5): 571 - 585. [Abstract] [Full Text] [PDF] |
||||
![]() |
J. De Munck, K. Van Landuyt, M. Peumans, A. Poitevin, P. Lambrechts, M. Braem, and B. Van Meerbeek A Critical Review of the Durability of Adhesion to Tooth Tissue: Methods and Results J. Dent. Res., February 1, 2005; 84(2): 118 - 132. [Abstract] [Full Text] [PDF] |
||||
| ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| HOME | HELP | FEEDBACK | SUBSCRIPTIONS | ARCHIVE | SEARCH | TABLE OF CONTENTS |
| IADR Journals | Advances in Dental Research ® |
| Journal of Dental Research ® | Critical Reviews (1990-2004) |