This invention relates to the use of ozone in the treatment of dental and oral conditions.
In order to treat a tooth that has diseased pulp material therein, it is necessary to remove the diseased pulp material from the pulp cavity, or root canal to prevent bacterial proliferation within the pulp canal of the tooth.
Subsequent to removal of diseased pulp material, the root canal is typically filled with an inert material before sealing off with an aseptic material to prevent continued or future infection of the tooth root.
It is apparent that during root canal therapy the entire root canal including the root tip, be cleaned and filled to eliminate all diseased material.
Typically, this includes opening the tooth to the pulp chamber and then manually cleaning the root canal with appropriate instruments.
Access to the pulp chamber is accomplished by drilling a hole through the tooth, which is subsequently widened for the use of endodontic instruments to large and clean the root canal to remove all the diseased pulp tissue.
Following removal, the root canal must be disinfected and dried prior to filling. A number of endodontic irrigating instruments are utilized and typically purge the root canal with a hydrogen peroxide solution or a sodium hypochloride solution.
Care in this procedure must be taken in order that the irrigating syringe is not inserted too deeply into the root canal or the pressure of the irrigating solutions to prevent flow into the apical dental formen and into the periapical area.
A further disadvantage of such irrigation is that a saliva remover must be inserted into or hanging from the mouth to extract the used irrigating solutions. This, in turn, may give discomfort to the patient and interfere with the dentist's work.
The present invention provides for disinfecting root canals through the use of ozone. Such treatment is preferred following pulp removal.
A method in accordance with the present invention for treating root canals includes directing an oxygen gas onto an open root canal through a needle, maintaining a pressure of the oxidizing gas into the root canal for a period of time sufficient to kill micro organisms therein, and preventing escape from the oxidizing gas from the root canal.
In addition, a method in accordance with the present invention may include flushing the oxidizing gas from the root canal with a reductant.
Apparatus for the hereinabove treatment of root canals generally includes a source of oxidizing gas, a handpiece, a needle extending from the handpiece and receivable in a tooth root canal with the needle including an oxidizing gas delivering a lumen therethrough. A cup is provided and attached to the handpiece which surrounds the needle. Preferably, the oxidizing gas comprises ozone. In order facilitate entry of the needle into the root canal, the needle may be flexible.
Preferably, the cup includes a resilient edge engageable with a cusp area of the tooth and the source of oxidizing gas includes an ozone pump.
The apparatus may further include an aspiration pump and an aspiration line connected to the handpiece for circulating the gas through the needle lumen and out of a cup chamber subtending a cup edge.
The apparatus in accordance with the present invention may further include an ozone and aspiration pump controller to circulate the gas through the needle lumen and out of the cup chamber any pressure insufficient to escape past a sealed engagement between the cup and the tooth.
The apparatus may further include a source of reductant interconnected with the handpiece in order to flush the gas from the cup. In addition, the waste reductant accumulator may be provided to connect to the aspiration line along with a residual oxidizing gas aspiration line filter.
The advantages and features of the present invention will be better understood by the following description when considered in conjunction of the accompanying drawings, in which:
With reference to
As illustrated in
As noted in the referenced international patent application, ozone is delivered at a pressure, concentration and for a period of time sufficient to penetrate the carious tissue and kill substantial all of the microorganism within a carious lesion. Specific examples of the use of ozone are set forth in the referenced patent application and are incorporated herewith by the specific reference thereto.
As shown in
Many different sized and shaped cups may be utilized, as for example shown in
A further cup embodiment 64 is shown in cross-section in
While a resilient edge or sidewall may be used to couple the cup to the selected area 38 on the tooth 40, it should be appreciated that a separate sealant 68 (See
Another embodiment of a cup 70 is shown in cross-section in
All of the cups 34, 64, 70, cross-sectionally illustrated in
As shown in
As shown in
Following the removal of diseased pulp, the oxidizing gas is directed into the root canal 15 through the needle 13. The presence of oxidizing gas in the root canal is provided for a period of time sufficient to kill the microorganisms therein. The cup 27 prevents escape of the oxidizing gas from the root canal 15. A seal 35 may be provided to seal across a tooth crown 27. A single line 39 connected to the needle lumen 33 may be provided for both introducing ozone and reductant to the root canal 15, or alternating a separate aspiration line 41 may be provided.
In addition, as hereinafter discussed in greater detail, the oxidizing gas may be flushed from the root canal 15 with a reductant.
With reference again to
A controller 126, which may be of any conventional circuit design, is provided for regulating the ozone and aspiration pumps 22, 120 in order to circulate the gas into and out of the cup chambers 92, 94, 96 at a pressure insufficient to permit escape of the gas past a sealed engagement between the cup 31 and teeth 40, 86, 88.
The gas may be circulated through the lumen 23 and out of the cup chamber 31 at a pressure insufficient to permit escape of the gas past a needed engagement between the cup 27 and the tooth 19. Control of the gas flows may also be effected through valves 127, 127 regulated by the controller 126.
Additionally, the apparatus 10 may include a reductant source 128, which is in fluid communication with the cup chambers 31, 92, 94, 96 through lines 30, 130 and a parastalic pump 131. The reductant, which may be a solution of thiocyanate or peppermint, is utilized to flush the cup chambers 31, 92, 94, 96 of oxidizing gas. The oxidizing gas is flushed into the aspiration line 122 following ozone treatment of the tooth 19, 40, 86, 88. The reductant is then aspirated through line 122 and into a waste accumulator 132.
Any residual ozone is then aspirated from the accumulator 132 through the line 124 and into a canister 134 through line 136 for final elimination of the ozone. Thus, the apparatus 12 provides for a totally closed system for the application and removal of ozone to and from teeth 19, 40, 86, 88.
It should also be appreciate that when the cups 34, 36, 64 are utilized between teeth 40, 138 (not shown in
Many studies concerning the clinical evaluation of ozone have been based on assessments of its harmful effects rather than demonstrating any therapeutic benefits it may offer. Ozone is one of nature's most powerful oxidants which accounts for its ability to kill bacteria, spores and viruses. Uniquely, ozone decomposes to a harmless, non-toxic and environmentally safe material (oxygen). In this investigation, a multicomponent evaluation of the oxidative consumption of salivary biomolecules by ozone (O3) has been performed using high resolution proton (1H) nuclear magnetic resonance (NMR) spectroscopy. The ozone-generating equipment employed in this study was designed by Purezone Ltd. (Ipswich, U.K.). Unstimulated human saliva samples were collected from 8 patients and each of them was divided into two equivalent portions (0.60 ml). The first of these was treated with O3 generated from the above device for a period of 30 seconds; the second group of portions served as controls. Samples were subjected to 1H NMR analysis at an operating frequency of 600 MHz. Results acquired revealed that O3 treatment gave rise to (1) the oxidative decarboxylation of the salivary electron-donor pyruvate (generating acetate and CO2, as products), (2) oxidation of the volatile sulphur compound precursor methionine to its corresponding sulphoxide and (3) the oxidative consumption of salivary polyunsaturated fatty acids. Moreover, evidence for the O3-mediated oxidation of salivary 3-D-hydroxybutyrate was also obtained. High field 1H NMR spectroscopy provides much useful analytical data regarding the fate of O3 in human saliva, information which is of much relevance to its potential therapeutic actions in vivo.
Ozone Effect on Microflora from Primary Root Caries Ex-Vivo
Primary root carious lesions (PRCL) are a major clinical problem. The aim of this study was to establish if ozone could achieve effective microbial killing in PRCL. An ozone producing generator (Purezone Ltd., Ipswich, U.K.) was used in this ex-vivo study assessing the use of ozone on PRCL. In this study, soft PRCL requiring restoration were used as these are the most severe type of lesion found in humans. 20 freshly extracted teeth with PRCL requiring restoration were used. After plaque removal using a hand held standard fine nylon fiber sterile toothbrush with sterile water as a lubricant to cleanse the surface, each tooth was then isolated using sterile cotton wool rolls and dried using a dry sterile cotton wool roll. A sample of PRCL was taken using a sterile excavator from half of the most active part of the lesion. Subsequently, 10 seconds of the ozonized water was applied to the lesion and another sample was taken from the other half of the most active part of the lesion. Each sample was weighed and immediately placed in 1 ml of Fastidious Anaerobe Broth (FAB). To each 1 ml of FAB containing a biopsy o carious or ozone treated carious dentine, sterile glass beads were added. They were vortexed for 30 seconds to facilitate the extraction of any micro-organisms from the carious dentine and disperse any aggregates. After decimal dilution with FAB, 100 ml aliquots of these was spread on Fastidious Anaerobe Agar (LabM, Bury, Lancs., U.K.) supplemented with 5% (v/V) horse blood in an anaerobic chamber at 37° C. for four days. The mean±SE number of each colony type was counted and calculated.
Using the paired Student t-test a significant difference (p<0.001) was observed between the two groups. Clearly, the percentage of micro-organisms killed associated with the use of ozone was more than 99%.
Ozone Effect on Microflora from Primary Root Caries Ex-Vivo
The procedure of Example 2 was repeated except that ozonized water was applied to the lesion for 20 seconds. Using the paired student t-test, a significant difference was observed in the ozonized water group (log10 3.77±0.42, mean±SE) compared with the control group (log10 6.18±0.21) (p<0.001).
The results of these tests show that the use of ozone can provide an effective, rapid and simple means for killing micro-organisms in carious lesions.
Sealant Shear Bond Strength to Sound and Carious Radicular Dentine
These has been little research on the interaction between primary root carious lesions (PRCL) and adhesive materials. The aim of this study was to examine the shear bond strength of four adhesive systems to PRCL with sound dentine acting as a control. The adhesive systems used were:
The materials were applied to sound radicular dentine and PRCL in vitro in freshly extracted teeth. The bonding site was macroscopically intact, was flat and had at least a 3.5 mm diameter. 37% phosphoric acid was used for 15 seconds in samples in groups 1->3 whilst 25% polyacrylic acid was used in group 4. After bonding the samples were stored for seven days in a moist atmosphere at 37° C. A shearing force was applied at 1 mm/minute. There were at least 10 samples in each group. The mean (s.e.) shear bond strengths were (MPa);
While statistical testing showed that the shear bond strength of the OptiBond FL Prime/OptiBond FL Adhesive/OptiGuard was significantly the highest, (p<0.001), the caries status of the root surface had no significant influence on the bond strength. OptiGuard in combination with OptiBond FL Prime and OptiBond Adhesive had the highest bond strength and this was not influenced by the caries status of the surface.
The Effect of Ozone on Primary Root Caries and Associated Micro-organisms
The aims of these studies were to evaluate the efficiency of ozone on primary root caries and associated micro-organisms (Streptococcus sobrinus; TH 21 Streptococcus mutans; NCTC 10449). In study 1, 40 soft primary root carious lesions (PRCLs) from freshly extracted teeth were used and randomly divided into two groups to test the exposure to ozone for either 10 or 20 seconds. There was a significant (p<0.001) difference (Mean±SE) between the control samples for either 10 seconds (log10 5.91±0.15) or 20 seconds (log10 6.18±0.21) and ozone treated samples for either 10 seconds (log10 3.57±0.37) or 20 seconds (log10 3.77±0.42). In study 2, 40 sterile saliva coated glass beads were put into bijoux bottles with 3 mls of Todd Hewitt broth for control and test groups. S. sobrinus and S. mutans were inoculated and incubated anaerobically overnight. Each glass bead was washed with 2 mls of PBS. Immediately, 10 seconds of ozone was applied to the glass beads in the test groups. Subsequently, each glass bead in the test and control groups was placed in 3 mls of Todd Hewitt broth with six more sterile glass beads and were vortexed for 30 seconds. After decimal dilutions, 100 ml aliquots were spread on blood agar plates supplemented with 5% (V/V) horse blood and placed in an anaerobic chamber at 37° C. for two days. The number of each colony type was counted and calculated. Using the paired student t-test, there was a significant reduction (p<0.0001) (Mean±SE) between the control samples for S. sobrinus (log10 4.61±0.13) and S. mutans (log10 3.93±0.07) and ozone treated samples for S. sobrinus (log10 1.09±0.36). This treatment regime is therefore an effective, quick, conservative and simple method to kill micro-organisms in primary root carious lesions.
The Effect of Ozone on Gum Disease
Inflamed human gingivitis is exposed to ozone using the techniques herein described. After exposure to ozone, the inflammation is illuminated or reduced. In addition, enzyme levels in extracts from inflamed human gingiva are alleviated and/or reduced.
The Effect of Ozone on the Treatment of Root Canals
Bacteria cultures of Streptococcus aurous, Lactobacillus salivarius and Lactobacillus acidophilus, known as being associated with dental diseases are exposed to ozone using the techniques herein described and growth of the bacteria cultures is eliminated or inhibited.
The Effect of Ozone in the Treatment of Month Ulcerations
Month ulcerations are exposed to ozone using the techniques herein described and microorganisms in the ulceration are eliminated or reduced. In addition, enzyme levels in the month ulcerations are alleviated and/or reduced.
The Effect of Ozone in the Treatment of Bad Breath
Bad breath is caused, in part, by the retention and subsequent degradation of dead cellular material, by microorganisms, sloughed off continuously by a normal, healthy mouth. A mouth is exposed to ozone using the techniques herein described and the microorganisms associated with bad breath are eliminated or reduced. In addition enzyme levels in the month are alleviated and/or reduced.
The present invention further relates to apparatus for the treatment of dental caries utilizing an oxidizing gas.
The role of specific micro-organism such as, for example, streptococcus mutants in dental caries is well documented. Enzymes produced by such micro-organisms synthesize dextran from the sucrose passing through the month with food or drink resulting in the formation of dental plaque and dental caries.
Dental caries is the decay of teeth caused by demineralization of the enamel surface with organic acids produced by bacteria which adhere to teeth surfaces.
Heretofore, dental caries have been removed through the use of conventional grinding handpieces, lasers and air-blasting apparatus. However high-speed turbine drills or low-speed drills unfortunately will grind both caries and sound dentine. Accordingly, a practitioner must select and grind only caries and consequently, this method depends upon this skill of the practitioner. Lasers have been utilized to remove caries, however, not much success has been achieved for varies reasons. For example, blackened charred tissue blocks the laser radiation which, in turn, prevents the laser from reaching caries therebelow. In addition, heating also interrupts the ablation process.
With regard to air-blasting treatment of caries sound, dentine may also be easily removed, and accordingly, the skill of the practitioner is of outmost importance.
The present invention provides for the treatment of caries without the disadvantages of the prior art hereinabove noted.
Study or Test: Ozone Detection (ppm) Around the Cup 34 Using a Ozone Analyzer after Either 10 or 20 s of Ozone Application In Vivo
Purpose: To assess the maximum ozone detectable level (ppm) around the cup 34 after either 10 s or 20 s of ozone application in vivo.
Study or Test Protocol: 20 primary root carious lesions (PRCLs) were randomly selected when the cross-sectional study was conducted. The tip of the sensor was always held within 2 mm of the edge of the cup, positioned half way between the mesial and occlusal sides of the cup. The maximum ozone detectable level (ppm) around the cup from the extracted teeth using an ozone analyzer after 10 s of ozone application. The ozone analyzer used was an API 450 model available from ENVIRO Technologies, UK, and was calibrated by the supplier within the previous week of delivery and this device was not used for any other purpose other than this study in the interim.
Overlying plaque was then removed using a hand held standard fine nylon fiber sterile toothbrush with water as a lubricant. Each tooth was dried using dry sterile cotton wool rolls and a dental 3 in 1-air syringe. The excavator blade was used to traverse the lesion in line with long axis of the tooth across the maximum gingival/occlusal dimension. Half of each lesion was removed using a sterile excavator. Subsequently, the remaining lesion was exposed to the ozone gas for a period of either 10 s or 20 s at room temperature (23° C.) and maximum detectable ozone level was also measured using this ozone analyzer.
Test Results:
The maximum ozone detectable level (ppm) around the cup from lesions for a period of either 10 s (Table 1 and
Conclusion: The use of a cup is a safe way of delivering ozone when ozone was applied for a period of either 10 s or 20 s on the root carious lesions.
Study or Test: Assessment of the maximum detectable ozone levels, detected adjacent to the cup, from extracted teeth after the use of ozone for 10 s in vitro.
Purpose: To assess the maximum ozone detectable level (ppm) around a cup from the extracted teeth after a 10 s application of ozone.
Study or Test Protocol: 14 extracted teeth were selected. The tip of the sensor was always held within 2 mm of the edge of the cup, positioned half way between the mesial and occlusal sides of the cup. The maximum ozone detectable level (ppm) around the cup from the extracted teeth using an ozone analyzer was recorded during 10 s of ozone application with the generator setting on maximum at level 10. The ozone analyzer used was the API 450 model and this was calibrated by the supplier within the previous week of delivery. This device was not used for any other purpose other than this study in the interim.
The Ozone Delivery System
After plaque removal with 2 sterile cotton wool rolls, ozone gas was delivered onto the surface of each primary root carious lesion in each extracted tooth for 10 s after the lesion was dried for three seconds with a standard three in one dental syringe.
Test Results:
The maximum ozone detectable level (ppm) around the cup from the extracted teeth after a 10 s application of ozone during the treatment of root carious lesions were as shown in Table 3.
Conclusion: The use of a cup is a safe way of delivering ozone when ozone was applied for a period of 10 s on the root carious lesions on extracted teeth.
The handpiece 16 from the ozone generator 20 was attached directly to the inlet pipe a Mini-HiCon™ the ozone detector (not shown).
Peak readings from Mini-HiCon™ (g/Nm3)
Peak readings from Mini-HiCon™ (ppm)
The peak reading was obtained after about 8 seconds (even when the generator was switched on for only 5 seconds) and perhaps represented an “overshoot” before the generator/detector combination stabilized for the >20 second durations. The level then remained fairly constant at between 3.6 and 4.7 g/Nm3.
To Convert from g/m3 to ppm:
The formula weight of ozone is 48 g and therefore 1 g of ozone is 1/48th of a mole.
The molar volume of an ideal gas (at standard temperature and pressure) is 0.0224138 m3/mol.
0.0224138/48=467×10−6 m3.
Therefore 1 g/m3 of ozone in air is 467 ppm.
(The ozone detector gives readings as g/Nm3 which is “normalized” to standard temperature and pressure).
Measurement of the Ozone Dissolving in a Potassium Iodide Solution
Ozone was passed through the handpiece 16, immersed in 100 ml of a 20 mM potassium iodide solution in a 250 ml conical flask covered with parafilm for the stated durations. The handpiece was then removed and the flask sealed with a neoprene bung and shaken vigorously. A 1.50 ml aliquot was removed and its electronic absorption spectrum acquired. (These measurements were taken before a diffuser was fitted.) The generator settings were:—air=1, O3=1, vac=0, red=0, regulator-setting=10.
To calculate the Concentration from the Peak Absorbance:
NMR Analysis of Plaque/Caries
(5 mM in D2O) were added prior to NMR analysis.
NMR Analysis of Saliva
(5 mM in D2O) were added prior to NMR analysis.
Iodine Standards (in 20 mM Potassium Iodide)
Although there has been hereinabove described a specific method apparatus for the treatment of dental and oral conditions, specifically root canals, in accordance with the present invention for the purpose of illustrating the manner in which the invention may be used to advantage, it should be appreciated that the invention is not limited thereto. That is, the present invention may suitably comprise, consist of, or consist essentially of the recited elements. Further, the invention illustratively disclosed herein suitably may be practiced in the absence of any element which is not specifically disclosed herein. Accordingly, any and all modifications, variations or equivalent arrangements which may occur to those skilled in the art, should be considered to be within the scope of the present invention as defined in the appended claims.
The present application is a continuation-in-part of U.S. Ser. No. 11/087,452 filed Mar. 23, 2005, now abandoned which is a continuation of U.S. Ser. No. 10/097,758 filed Mar. 13, 2002, now U.S. Pat. No. 6,875,018 claiming the benefit of U.S. Ser. No. 60/279,360 filed Mar. 28, 2001. All of these applications/patent are to be incorporated herein in this entirety including all specifications and drawings.
Number | Name | Date | Kind |
---|---|---|---|
860555 | Middaugh | Jul 1907 | A |
2662523 | Badan | Dec 1953 | A |
3816921 | Malmin | Jun 1974 | A |
3871099 | Kahn | Mar 1975 | A |
3882865 | Hatzitheodorou | May 1975 | A |
4021921 | Detaille | May 1977 | A |
4247288 | Yoshii et al. | Jan 1981 | A |
4422450 | Rusteberg | Dec 1983 | A |
4438100 | Balslev et al. | Mar 1984 | A |
4526544 | Kahn | Jul 1985 | A |
4608017 | Sadohara | Aug 1986 | A |
4664906 | Sipos | May 1987 | A |
4743199 | Weber et al. | May 1988 | A |
4991570 | Bullard | Feb 1991 | A |
4993947 | Grosrey | Feb 1991 | A |
5055043 | Weiss et al. | Oct 1991 | A |
5197876 | Coston | Mar 1993 | A |
5356292 | Ho | Oct 1994 | A |
5505914 | Tona-Sera | Apr 1996 | A |
5547376 | Harrel | Aug 1996 | A |
5928187 | Glukhov et al. | Jul 1999 | A |
5942125 | Engelhard et al. | Aug 1999 | A |
6305936 | Jensen et al. | Oct 2001 | B1 |
6464498 | Pond | Oct 2002 | B1 |
6479037 | Montgomery | Nov 2002 | B1 |
6454566 | Lynch | Apr 2003 | B1 |
6649148 | Lynch et al. | Nov 2003 | B2 |
6669931 | Lynch et al. | Dec 2003 | B2 |
6743016 | Lynch et al. | Jun 2004 | B1 |
6971878 | Pond | Dec 2005 | B2 |
7021931 | Lynch et al. | Apr 2006 | B1 |
20020172707 | Joyce | Nov 2002 | A1 |
Number | Date | Country |
---|---|---|
3825824 | Feb 1990 | DE |
0 988 834 | Mar 2000 | EP |
2187288 | Jan 1974 | FR |
62047355 | Mar 1987 | JP |
WO9964020 | Dec 1999 | WO |
Number | Date | Country | |
---|---|---|---|
20060110710 A1 | May 2006 | US |
Number | Date | Country | |
---|---|---|---|
60279360 | Mar 2001 | US |
Number | Date | Country | |
---|---|---|---|
Parent | 10097758 | Mar 2002 | US |
Child | 11087452 | US |
Number | Date | Country | |
---|---|---|---|
Parent | 11087452 | Mar 2005 | US |
Child | 11266614 | US |