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Article

Factors Affecting Water Quality and Sustainability in Dental Practices in Greece

by
Maria Antoniadou
1,2,*,
Anestis Intzes
1,
Christos Kladouchas
1,
Iliana Christou
2,3,
Stavroula Chatzigeorgiou
2,3,
Martha Plexida
2,3,
Valantis Stefanidakis
1 and
Ioannis Tzoutzas
1
1
Dental School, National and Kapodistrian University of Athens, 115 27 Athens, Greece
2
CSAP, Executive Mastering Program in Systemic Management, University of Piraeus, 185 34 Pireas, Greece
3
EYDAP, Athens Water Supply & Sewerage Company S.A., 111 46 Athens, Greece
*
Author to whom correspondence should be addressed.
Sustainability 2023, 15(11), 9115; https://doi.org/10.3390/su15119115
Submission received: 11 May 2023 / Revised: 31 May 2023 / Accepted: 2 June 2023 / Published: 5 June 2023
(This article belongs to the Special Issue Advances and Challenges in the Sustainable Water Management)

Abstract

:
Good water quality, achieved with environmentally friendly means, is essential in ensuring the safe operation of a dental practice. Our aim was to evaluate procedures and protocols used by dentists for water quality and sustainability. Greek dentists (n = 206) participated in this questionnaire-based study. Statistically significant results (p < 0.05) have shown that (a) female dentists were more interested in additional information about water quality (87.5% vs. 71.8%), had water supply directly from the public network to the dental unit (68.8% vs. 73.8%), were more likely to disinfect surfaces between two appointments (97.7% vs. 88.0%) and were more likely to perform annual maintenance to the dental unit (66.3% vs. 57.9%). (b) More experienced dentists were also more likely to clean the waterline network of the unit with a large amount of fluid once a day (39.3–48.3%), had newer equipment, had more handpieces, and spent more time cleaning and disinfecting the unit (χ2 = 26.21). (c) Dentists who have studied abroad were more likely to perform less strict antiseptic protocols while believing that their practices are environmentally friendly (χ2 = 10.93). Dentists with some postgraduate education were more likely to have an assistant, know the active substance of the antiseptic, supply antiseptic to the handpieces automatically and maintain the dental unit annually (χ2 = 7.24). (d) Dentists who practiced general dentistry were less likely to have an assistant and performed less strict protocols while they cleaned suctions with a large amount of fluid less often (χ2 = 11.64). Dentists who practiced in a clinic (with employees) were more likely to have newer equipment, have an assistant and perform stricter water sustainability protocols. (e) Dentists with a higher annual income were also more likely to have an assistant, perform microbiological tests for the quality of the water of the unit, have a continuous water supply system and perform stricter protocols for water quality of the unit. Overall, less experienced (and younger) dentists are more informed about water quality legislation (27.6%) compared to more experienced and older dentists (13.2–17.5%). Gender, work experience, level of education and dental office characteristics are important factors determining water sustainability, waterlines, and equipment maintenance in dental practice. Dental associations should raise awareness regarding water quality and sustainability, investing in lifelong learning, while implementing protocols and green strategies.

1. Introduction

Sustainable entrepreneurship in the field of health depends on the breathing space that managers and employees give to nature and its resources [1]. The recent COVID-19 pandemic made the need to protect and restore natural resources and integrate human activities more effectively even more imperative [2]. The pandemic has raised awareness of the interconnectedness of our own health and the health of ecosystems [3,4,5]. It is vital then that stakeholders of the field avoid becoming stuck in destructive habits of the past towards environmentalism and protect air, water, and natural resources [6,7,8,9,10,11,12].
Water pollution is a key driver of biodiversity loss [12,13] and has harmful effects on our health and environment [14]. Biodiversity is affected by the release of nutrients, chemical pesticides, pharmaceuticals, hazardous chemicals, municipal and industrial wastewater, and other wastes, including litter and plastics, into water resources [15]. Dental offices have long waterline networks. In the field of eco-friendly dental practices, the reduction of water waste and the quality of water in the waterline network of the office and the dental unit, but also the prevention of infections, are challenges that every dentist must face [16,17]. Increasingly, low water quality has been recognized as a possible cause of biohazards and the spread of infections in the dental office [18,19]. A biofilm that forms inside the pipes of a building could contaminate the entire water supply network of that building, including the dental office [20]. Furthermore, within the dental clinic, water spreads as an aerosol, increasing both bacterial spread and the risk of infection to all people in the premises [12,21,22,23,24]. Oral flora [25] and human pathogens (e.g., Pseudomonas aeruginosa [26], various Legionella species (Legionella pneumophila) [27,28], non-tuberculous Mycobacterium species (Mycobacterium) [29], Helicobacter pylori [30] and other microorganisms including unicellular algae, bacteria, fungi, and protozoa [16,31]) have already been isolated from dental unit water systems [32]. They can coat and colonize almost any material in the dental clinic [33,34], especially the suction tube [16], forming biofilms. Biofilms in dental clinics have been shown to form a hazardous bacterial deposit, which can become resistant to various disinfectants [23,35,36,37] and serves as a reservoir that can enhance the number of floating (planktonic) microorganisms in the water used for dental treatment [38,39,40].
The trend and attention to this important matter is growing, in part due to the increasing needs for workplace safety for both workers and patients [12,41]. Good water quality is an important factor in ensuring the quality and safe operation of the dental practice [31,42]. The water network participates in all clinical protocols, in the antisepsis and disinfection procedures, the operation of the dental unit as well as all other areas (doctor’s office, waiting room, toilets, laboratory, rest room or kitchen). Infections in dental practices can occur very easily [13,43,44]. Therefore, there is considerable (and justified) attention to the sterilization protocols of dental instruments and handpieces [45], but less attention is usually paid to the treatment of water in the practice’s network even though it participates in these protocols [46,47] and may even cause an erosion effect in oral metal prostheses [48].
Biofilms within the waterlines of dental clinics originate from one of two possible sources of contamination: from the internal piping system using a direct supply from the public network or from the patient’s mouth [31,48]. The public water supply is not entirely sterile. Water circulating in the system of the city contains a diverse microbial flora which, depending on its type and concentration, is generally harmless to humans. However, under certain conditions, pathogenic microorganisms or opportunistic pathogens can reach the dental unit through the water supply chain [49]. The microbiological quality of the water samples collected throughout the city system does not necessarily correspond to the microbiological quality that could be detected at points closer to the dental practice [17,33,50,51,52].
According to the above, staff and patients are constantly exposed to risk of infection due to water installations [2,3,4,28,53,54]. Therefore, this study was carried out in dentists working in the vast area of Metropolitan Athens, the capital of Greece, during the third phase of the pandemic (March–October 2022), to investigate water quality procedures, maintenance issues of the water network and relevant equipment, educational needs, and proposals to form future eco-friendly water strategies. Water quality in the region of the study is controlled by EYDAP (Hellenic water supply and sewerage company of the capital) [55] and is considered as one of the best in Europe [56] with a performance of >99.8%, a value higher than the average scores of other Western European companies [57]. Our scope was to further analyze and evaluate factors influencing water sustainability practices of dentists in Greece. The research questions were the following: 1. What are the equipment and practices that ensure water quality in dental offices? 2. How do equipment and water sustainability processes differ according to the characteristics of dental practice? 3. Which equipment and practices lead to the strongest dentists’ perceptions of dental unit water quality?

2. Background of the Study

Procedures and Systems for Water Quality Control in the Handpieces and the Dental Unit

Bacteria populations can be spread during ongoing dental procedures when dentists are using high-speed handpieces [57,58,59,60] and come into direct contact with the wounds of the patient undergoing treatment [61]. There is a risk of water backflow into the dental unit waterline system from the handpieces known under the term of the suck-back phenomenon [62]. High-speed handpieces, in the deceleration phase of cutting, have a centrifugal suction effect that forces them to retract organic material especially from their head [27,63]. For this reason, many handpieces are equipped with special anti-retraction valves, which hold the suctioned material in the rotor [61]. These valves may not provide a perfect blockage (depending on how well the handpiece is maintained) and any leakage can lead to bacterial colonies inside the handpiece body [64]. This is an ideal environment for bacteria to grow, increasing the risk of cross-contamination. Consequently, all modern dental clinics need to have integrated disinfection systems [26,64,65].
There are various devices, materials, and filters within or in parallel connection with the dental unit, which make it possible to limit the risk of contamination of the water circulating within its piping: (1) Chlorine dioxide is a powerful and effective disinfecting agent capable of producing and maintaining safe drinking water through oxidation rather than a chlorination reaction [38]. (2) Reverse osmosis is the safest and most widespread water treatment system in the world and can guarantee absolute water purity for the dental unit [66]. The osmotic membrane can process water to the molecular size, making its characteristics optimal in terms of color, smell, and organoleptic purity. (3) Electrolysis apparatuses that use only the chlorine normally present in municipal water, such as the Poseidon-S system, an additive-free disinfectant system described in the study of Fujita et al. [67] can also control microbial contamination in contaminated dental unit waterlines [32]. (4) Positive relevant results can also be guaranteed with plasma devices [68] or (5) acoustic waves at high energy [69]. It was mentioned that the efficacy of acoustic waves in preventing Streptococcus mutans adhesion on dental unit waterlines can be important [12]. For surgical procedures, sterile saline or sterile water should be used as the coolant/irrigant. Conventional dental units cannot reliably provide sterile water even when equipped with independent water tanks containing sterile water because the water-carrying path cannot be reliably sterilized [65,70].
The guidelines on infection control in dental healthcare settings issued by the US Centers for Disease Control and Prevention [11] recommend that the level of the heterotrophic plate counts (HPCs) in dental unit water should not exceed 500 CFU/mL [71]. Moreover, the American Dental Association (ADA) has set a limit of ≤200 CFU/mL on the heterotrophic bacterial load in water from dental unit waterlines [72]. In the EU, however, there is no current guideline regarding a dental unit’s waterlines, though in some countries the drinking water standard is used as a reference (≤500 colony forming units (CFU)/mL of water heterotrophic bacteria) [63]. For this reason, dental units are designed to include (a) self-contained water systems (e.g., independent water tank) combined with chemical treatment (e.g., periodic or continuous chemical microbicide treatment protocols), (b) systems in parallel connection with one or more dental units within the same dental office that clean or treat incoming water to remove or inactivate microorganisms throughout the network and (c) combinations of these methods (Figure 1).
When the treatment of patients is completed, specific protocols should be followed for flushing the suction network to reduce residual microbial contamination [12]. All incoming waterlines of the public water supply system within the dental practice (e.g., taps, dental unit water mains/waterlines and other dental equipment such as the suction mains) should be flushed [35,73]. There is no agreement on the optimal duration of flushing procedures, but the recommendations suggest that the procedures take from 1 to 5 min [74]. The time required may vary depending on the type and length of the network in the dental practice [11,64,74]. After flushing the incoming lines of the public water system, the dental facility waterlines should be disinfected according to manufacturer’s instructions [28,31,54].

3. Research Method

3.1. Design and Validation of the Study Questionnaire

In this study, we used the questionnaire technique, which is a systematic method for data collection, and it has been already used to collect professional views on water sustainability attitudes before [24,26,54]. Standards assigned to the internal water network of modern dental units, explained before in the relevant review and shown in Figure 1, were used for the design of the study’s e-questionnaire. More specifically, the questionnaire consisted of three parts. Part A had nine questions concerning demographic statistics of the sample (gender, age, family status, place of work, dental educational level, ways of practicing dentistry, years of professional activity, family income) that were also mentioned in relevant studies as having a statistical impact in this sample [75,76]. Part B had thirty multiple choice questions describing ways of water circulation within the unit and handpieces, as well as attitudes and processes that dentists use for their maintenance, and disinfection as described in the previous review and elsewhere, too [77,78]. Part C had eight multiple choice questions addressing environmental and legislative issues based on current legislation directives [79,80]. Finally, part D had two questions about educational proposals on water quality assurance and the waterline network’s maintenance within the dental practice. One of the questions was open-ended to describe participants’ proposals and enquiries as mentioned elsewhere, too [75,76].
The validation procedure for the questionnaire consisted of an examination and filling-up procedure of the questionnaire by (a) 15 dentists working at the Department of Dentistry and 15 post graduate students, who voluntarily filled in the questionnaire and addressed issues of misconception, and (b) an independent panel of 6 experts in the field (a mechanical engineer and technician of dental units, 3 EYDAP experts and 2 dentists) reviewed and revised the survey questions to be relevant to the topic and expressed them correctly as mentioned elsewhere [81]. The members of the panel first worked alone and with the study team and then in a group with all the other experts. Necessary corrections were finally made to avoid possible misconceptions by participants.
The online questionnaire included a short introductory message describing the purpose of the study and stressing voluntary participation, confidentiality, and the right to refuse participation. Consent was obtained by asking participants to confirm that they agreed to complete the questionnaire by marking a “Yes, I agree to participate” box. Ethical approval was obtained from the Ethics and Scientific Board of the Athens Regional Dental Association, metropolitan area of the capital, No: 2660/08.12.2022. A QR code was assigned to the questionnaire link to provide direct access through participants’ smartphones. The questionnaires required approximately 12–15 min to complete. Answering all questions was obligatory to submit the form, while submission was only allowed once. All participants were voluntarily filling in the form and no reward was given.

3.2. The Study Sample

The study sample consisted of professional dentists, active members of the Athens Regional Dental Association. Dentists were practicing dentistry in the vast Metropolitan area of Athens, Prefecture of Attica, Greece. Exclusion criteria consisted of undergraduate dental students, retired dentists, dentists working abroad, dentists not performing dentistry although members of the association and non-dentists. The link to the questionnaire was sent three times through the association’s secretariat email list, once per week. The questionnaire was left open for 3 months. All members of the association had the same opportunity to participate in the study.

3.3. Statistical Analysis

The data collected from the survey were analyzed with the statistical package IBM SPSS v. 28. Absolute and relative frequencies (n, %) were calculated for all variables of demographic and dental practice characteristics, practices, and equipment for water quality. Following, to examine the associations between demographic and dental practice characteristics with adopted practices for water quality and equipment of dental offices, chi-square tests of independence were performed with Fisher’s exact test correction when needed. To detect the most influential factors that lead to dentists’ perception of good water quality in their dental practice, binary logistic regression analysis with backward elimination was performed with the dependent variable being the feeling of confidence about water quality and the independent variables being the adopted practices for water quality and equipment of dental offices. Stepwise backward elimination with a significance level of .10 is commonly used in situations where multiple variables are available, and the aim is to select only the variables that provide a stable, generalizable model [82]. When recording practices, opinions and equipment, there is no need for a correlation between the responses (what is also called internal consistency or reliability) [83].

4. Results

In Table 1, data on demographics and dental practice characteristics are provided.
Most dentists in our study (52.9%) do not have an assistant, were informed about water quality when acquiring the dental unit (61.2%) and are interested in learning more about water quality (78.6%). Yet only 55.3% reported that they were confident about the dental unit water quality regarding microbial load. A small percentage (21.8%) perform microbiological tests on the premises of the dental office. A continuous water supply system to the dental unit was reported by 30.1% of the dentists. A system of uninterrupted water supply to the handpieces and scalers, i.e., a feeding bottle that needs filling, was reported by 33.5% of participants. The water supply was mainly from the public network to the dental unit (65.0%), to the rotative cutting instruments (62.3%) and to ultrasonic and air-scaler devices (55.8%). Only about 25% of dentists reported that the water was filtered from a filter device directly connected to the supply. Dentists at a percentage of 55.8% stated that the water was filtered in the dental office by a simple filter (19.4%), a reverse osmosis filter (4.9%), a deionization or ion-exchange filter (2.9%) or an activated carbon filter (15.0%). Participants further reported that the water filter is replaced or cleaned every 6 months (18.9%) or every 12 months (11.1%). Most dentists (71.8%) do not know the active substance of the antiseptic used for the hydraulic piping of the dental unit, while only 9.4% and 14.4% report that the antiseptic is supplied to the handpieces automatically or manually, respectively. A total of 96.1% of the participants were aware of an antiseptic liquid reservoir embedded in the dental unit.
Dentists reported being equipped with a strong surgical suction (94.7%), with an electric motor (67.0%) and air or water vacuum (8.8%), while 18.9% of dentists did not know the type of surgical suction of their unit. Before the COVID-19 pandemic, 82.6% of dentists reported cleaning the saliva suction with a small amount of fluid suctioning at least once a day. Also, 63.1% of dentists reported cleaning the saliva suction with a large amount of fluid suctioning at least once a day, and 27.7% reported that they performed this once a week. Regarding the surgical suction, 84.0% of dentists reported cleaning with a small amount of fluid suctioning at least once a day. Also, 59.8% of dentists reported cleaning the surgical suction with a large amount of fluid suctioning at least once a day, and 28.2% reported that they performed this once a week. Cleaning the waterline network of the dental unit with a large amount of liquid was reported at least once a day (46.1%) or every week (26.2%). Most dentists (91.7%) disinfected the surfaces of the dental equipment after each appointment.
The dental unit was reported to be serviced annually (or after a failure) by 61.6% of participants, while 38.4% only performed service after a failure. A total of 70.0% of dentists reported having up to three micromotors/luftmotors and 57.8% reported up to three airotors. Micromotors and airotors are cleaned between appointments by decontamination (58.30%), decontamination and sterilization (6.8%), sterilization (17.5%) or only surface cleaning (17.5%). A total of 37.6% of the participating dentists had an implantology motor. Most participants (53.8%) preferred channeling sewage into the sewer through suction compared to connection to the central drainage system. Possession of an amalgam separator was reported by 64.6% of dentists (type: unknown 19.9%, filter cleaning 28.2%, full replacement 14.1%). Having a contract with a collection company for medical waste and amalgam removal was reported by 58.2% and 26.6% of participants, respectively.
Only 14.4% of the participants declared being informed about water quality legislation in health care facilities. A total of 69.9% of dentists spend more than 2 h per month on the cleaning/disinfection of the dental unit. Moreover, 64.6% of dentists estimated spending up to EUR 50 per month for cleaning/disinfection of the dental unit. Thus, 84.6% of dentists believe that their practices for cleaning/disinfection of the dental unit are environmentally friendly. The implementation of the disinfection protocol was the dentist’s own responsibility in 58.3% of cases, while 50.7% of participants reported adopting more strict practices of water management after COVID-19 (data available as Appendix A Table A1).
Following this, differences between demographic characteristics of dentists were examined. Table 2 presents only the significant results from the chi-square tests of associations performed between gender and variables of dentistry equipment and practices. Female dentists were more interested in additional information about water quality (females 87.5% vs. males 71.8%). Water supply directly from the public network to the dental unit, the handpieces and the ultrasonic devices was reported more frequently by female dentists (68.8% to 73.8%) compared to male dentists (51.8 to 58.3%). Moreover, female dentists were more likely to disinfect the dental office/equipment surfaces between two appointments compared to men (females 97.7% vs. males 88.0%). Also, female dentists were more likely to perform annual maintenance to the dental unit (females 66.3% vs. males 57.9%) and less likely to have an implantology motor (females 27.6% vs. males 44.6%).
Table 3 presents only the significant results from the chi-square tests of associations performed between the dentists’ work experience and variables of dentistry equipment and practices. More specifically, only 3.8–7.7% of dentists with less than 10 years of experience had a water filter to the dental unit, handpieces and ultrasonic scalers compared to 34.5–39.7% of dentists with over 30 years of experience. More experienced dentists were also more likely to clean the surgical suction with a large amount of fluid suctioning once a day (39.3–48.3%) compared to less experienced dentists who cleaned it likewise once per week (31.0%) or never (13.8%). Also, 61.1% of dentists with over 30 years of experience performed cleaning of the dental unit with a large amount of fluid suctioning at least once a day, while less experienced dentists were more likely to clean it once a week. More experienced dentists were also more likely to have more micromotors (χ2 = 25.92, p < 0.05) and airotors (χ2 = 29.17, p < 0.05) and spent more time cleaning and disinfecting the dental unit (χ2 = 26.21, p < 0.05). Yet, less experienced (and younger) dentists are more informed about water quality legislation (27.6%) compared to more experienced and older dentists (13.2–17.5%).
Table 4 presents only the significant results from the chi-square tests of associations performed between the dentists’ educational characteristics and variables of dentistry equipment and practices. Dentists who have studied abroad were more likely to supply antiseptic to the handpieces manually (χ2 = 7.15, p < 0.05), clean the surgical suction with a small amount of fluid suctioning once per day and not between appointments (χ2 = 13.26, p < 0.05) and believe that their practices are environmentally friendly (χ2 = 10.93, p < 0.05). Dentists who had some postgraduate education were more likely to have an assistant (χ2 = 13.66, p < 0.05), know the active substance of the antiseptic (χ2 = 5.86, p < 0.05) and supply antiseptic to the handpieces automatically (χ2 = 5.54, p < 0.05). Also, most of the more educated dentists clean the surgical suction with a small amount of fluid suctioning between appointments (51.0% and 18.9%) compared to less educated dentists that clean the surgical suction with a small amount of water between appointments (40.7%) or once per day (35.2%), χ2 = 13.26, p < 0.05. Dentists who had some postgraduate education were more likely to maintain the dental unit annually (χ2 = 7.24, p < 0.05), have more micromotors (χ2 = 12.72, p < 0.05) and airotors (χ2 = 8.94, p < 0.05), have a contract for amalgam removal (χ2 = 4.46, p < 0.05) and were less likely to be responsible for the implementation of the disinfection protocol (χ2 = 6.57, p < 0.05). Finally, dentists with a recognized specialization were more likely to have an assistant (χ2 = 5.56, p < 0.05), maintain the dental unit annually (χ2 = 4.40, p < 0.05), have less airotors (χ2 = 22.76, p < 0.05) and were more likely to not have an amalgam trap (χ2 = 8.56, p < 0.05).
In Figure 2, there is a graphical systemic presentation of factors affecting water maintenance of the dental unit.
Table 5 presents only the significant results from the chi-square tests of associations performed between the dental office characteristics and equipment/practices for water quality. Dentists who practiced general dentistry were less likely to have an assistant (χ2 = 25.32, p < 0.05), supply antiseptic to the handpieces manually (χ2 = 4.56, p < 0.05), clean the surgical suction with a large amount of fluid suctioning less often (χ2 = 11.64, p < 0.05) and have amalgam trap (χ2 = 4.38, p < 0.05). Dentists who practiced in a clinic (with employees) compared to a private practice were more likely to have newer equipment (χ2 = 16.12, p < 0.05), have an assistant (χ2 = 44.26, p < 0.05), supply antiseptic to the handpieces automatically (χ2 = 6.36, p < 0.05), have more micromotors (χ2 = 31.40, p < 0.05) and airotors (χ2 = 22.04, p < 0.05), have an implantology motor (χ2 = 7.37, p < 0.05), have a contract for amalgam removal (χ2 = 4.07, p < 0.05) and were less likely to be responsible for the implementation of the disinfection protocol (χ2 = 26.24, p < 0.05). Moreover, dentists with a higher annual income were more likely to have an assistant (χ2 = 4.36, p < 0.05), perform microbiological tests (χ2 = 7.60, p < 0.05), have a continuous water supply system to the dental unit (χ2 = 6.38, p < 0.05), supply antiseptic to the handpieces automatically (χ2 = 6.21, p < 0.05), clean the surgical suction with a small amount of fluid suctioning more often (χ2 = 23.24, p < 0.05), have more micromotors (χ2 = 24.39, p < 0.05) and were less likely to be responsible for the implementation of the disinfection protocol themselves (χ2 = 6.26, p < 0.05).
Finally, when questioned about the environment friendliness of the dental office “how environmentally friendly would you judge your practices in the dental office?”, only 13.3% were a little satisfied with their practices, 25.2% were enough satisfied and 40.5% were satisfied. Of the participants, 42.9% have tightened their water practices due to COVID-19, while 47.6% have kept the same protocols as before COVID-19. When they were asked whether they would like to participate in voluntary actions for the quality assurance of the water, 49.5% responded negatively. Regarding the open-ended question, there were answers ranging across the environmental friendliness and awareness spectrum: “We have a question of survival. Water does not concern me”, or “I consider plastic to be a more important issue than water”, or “I do not think it is possible to reduce water waste”, or “it should be mandatory to install biological filters in the dental equipment and the network of the clinic”, or “there should be a hygiene committee independent of the association to be able to carry out checks in dental practices and a clear legal framework that applies to the whole country territory”. Continuing education on the matter should be carried out by the associations (51%), sharing of relevant articles (45.7%) and workshops (40.5%).

5. Discussion

In this study, we searched for differences in processes and practices towards water quality and sustainability in the dental practice, maintenance of the relevant waterline network and relevant educational needs for professional dentists in Greece. To our best knowledge, there are a few studies presenting these issues according to certain demographic characteristics. To begin with, concerning gender differences found in our data, it is reported elsewhere that female dentists have different work patterns than their male colleagues [83,84,85,86,87,88]. This is assigned to psychological dissimilarities [89], as well as certain differences in their practical skills and roles within society [86,90,91,92,93]. Women, being culturally responsible for housekeeping [94,95], are more willing to perform accurate cleaning of the dental unit as already mentioned before [96]. In our study, female dentists were more interested in additional information about water quality, were more likely to disinfect the equipment between two appointments and were more likely to perform annual maintenance of the unit. In another study of female dentists, it was mentioned that they provide more scaling and restorative services than males although the differences might not be statistically significant [97] as in our study. This could also explain our findings, because after scaling it is known that the unit brings high levels of contaminant material into the system through blood suction during the process [49], thus forcing dentists to perform a stricter disinfection protocol. As reported in the study of Reza et al. [97], female dentists administered more pediatric treatments than their male colleagues, though this was not statistically significant. In our study, women were also less likely to have an implantology motor, indicating procedures other than implantology procedures being performed in their offices. Also, female dentists in our study were less willing to perform technical procedures for the equipment as in many cultures this is a male’s role [98], and secondly, they usually have no time in between their other social roles [99]. Thus, it is not surprising that in our study they just directly connect their unit to the public water network and use no filters while men are searching for different solutions (filters, equipment, etc.) for achieving a better quality of water for the unit.
Furthermore, experience in the profession is a statistically important factor in our study. There are certain differences in the knowledge level among professionals as discussed elsewhere, too [99,100]. We found that more experienced professionals are more likely to follow high quality water performance strategies such as the use of a filter device directly connected to the main supply, flushing the suction and the unit once per day with a large amount of water and searching for extra water quality equipment, while less experienced ones preferred the simplest methods for the water supply such as a direct connection to the public water network and flushing once per week. It is unclear whether this attitude is based on the concern of saving water rather than ignorance of safe antiseptic protocols. Further, as evidenced by the literature, transmission within the dental practice via direct contact is possible with the use of hollow instruments in dentistry [34,48]. So, effectively enough, more experienced dentists in our study had more micromotors and airotors and spent more time cleaning the unit, diminishing cross-contamination possibilities between appointments as reported elsewhere, too [28,101].
Several studies can report on the efficacy of methods to clean and disinfect hollow instruments such as airotors and (high-speed) handpieces [44,60,102,103]. The presence of bacteria, fungi, and viruses on and inside hollow dental instruments has been determined before [18]. Cleaning these handpieces with a wipe moistened with ethanol (70%) is insufficient to eradicate microbial contamination [104]. As known from all relevant COVID-19 protocols, it is not only the exterior but also the interior of these instruments that should be cleaned and disinfected properly, because hollow instruments contain contamination of both the patient and the water/air supply [62,101]. Moreover, sufficient guidelines about how to decontaminate handpieces are available [19], but most of the dentists in our study and elsewhere [105,106] are unaware of these guidelines, forgetting, for example, that overnight bacterial accumulation in the handpieces can be significantly reduced by allowing water-cooled handpieces to run and to discharge water into a sink or container for several minutes at the beginning of the clinic day [101]. In the study of Schalli et al. [101], though, the fact that 92.9% of water samples taken after procedures during which no spray water was used showed an increase in protein concentration illustrates that the contamination cannot be due solely to the retraction of spray water and that differences in the maintenance and antiseptic protocols used in different offices and the rotational speed of the handpiece could explain a certain dilution [44,49,103]. Other techniques such as preprocedural mouth rinsing with chlorhexidine [107], essential oil, povidone-iodine or water before ultrasonic scaling could reduce bacterial contamination on aerosol formation and cross-contamination [60]. Finally, researchers seem to agree that the extent of contamination can depend on the person using the instrument, also proven from our data, as well as on the patient [45]. Additional relevant factors include the number of motor stops, the rotational speed of the handpiece (controlled using the foot pedal), the extent of the lesion to be treated and the oral hygiene of the patient. In the study of Schalli et al. [101], it was discussed that six out of seven offices had contaminated spray-water lines even before patients were treated with the handpieces. Only in the case of instruments in the office where thorough decontamination, including disinfection, had been performed was no protein measurable before treatments [101]. An exact documentation of the decontamination procedures and storage conditions, as well as an analysis of the disinfectants and lubricants used, should be assigned for a further update of the procedures [45]. In our study, unfortunately, only 28.2% of the dentists knew the active substance of the antiseptic they were using.
Individual handling of the instruments from assistant personnel or the dentist himself is essential, too, and from our data, dentists studying abroad and those performing general dentistry are more informed on performing four-hand dentistry for a better antimicrobial scene and health for personnel and the patient as also described elsewhere [18]. Further, dentists in our study with some postgraduate education were more likely to have annual maintenance habits for their equipment and unit, have more handpieces and have a contract with a certified disposal company for amalgam removal. Also, it was less likely for them to be responsible for the implementation of the disinfection protocol as they work with an assistant. This is also reported elsewhere, where there are significant differences in the knowledge scores between different groups of dental professionals and between dental specialists and dental assistants, too [99,100,106]. The trend for specialists and more educated dentists is to work on a team basis and run larger clinics with more than one unit, as was the case in our study, too. In such a scenario, assistants can run safe protocols in between appointments, presenting a safer antiseptic profile.
In our study, dentists that had studied abroad supply antiseptic to the handpieces manually and clean the suction with a small amount of fluid and not between appointments, believing falsely that their practices are environmentally friendly. This is attributed to differences in educational approaches in different countries and regions as mentioned elsewhere [108]. In larger dental clinics, though, equipment is newer, the supply of antiseptic to the handpieces is automatic and they have more handpieces, implantology motors and contracts with amalgam disposal companies. Economic reasons for performing cheaper and not environmentally friendly safety protocols in the practice are also reported elsewhere [109]. But the cheap protocol is not scientifically based, nor is it safe. It can even be more expensive even in a short-end period. Patients are well informed after the COVID-19 pandemic on the safety protocols and are willing to support health units that practice these protocols [103,109]. Dentists that do not follow certain antiseptic and equipment maintenance guidelines will disappoint stakeholders sooner than in the past and they will most likely encounter sustainability issues [12].
Thus, the Centers for Disease Control and Prevention [19] recommend that manufacturers should provide dental units with a separate reservoir, typically a container of about 1 L capacity, from which tap water, deionized water and/or distilled water can be fed to the handpiece, which is the case in our study, as 96.1% of participants reported having an antiseptic reservoir embedded in the dental unit compared to 94% in East England reported before [110]. This can also be applied to the use of biocides. In cases where dental units are still fed directly by municipal water, it is even more important to adopt the various systems for preventing microbial contamination, such as, for example, the use of handpieces and turbines fitted with anti-reflux valves or flushing, which should always be carried out for 20–30 s after each patient is treated [35,73]. Of course, flushing with water alone cannot guarantee water quality in the practice as shown in the study of Alkhulaifi et al. [73]. Unfortunately, though, most dentists in our study (71.8%) do not know the active substance of the antiseptic used for the hydraulic parts of the dental unit, a point that needs further attention for continuing education courses in the field. Baudet et al. [111] found that tap water is used in the dental unit by 65% of the dentists, distilled water by 2.3% and filtered water by 19.7% compared to our 89%, 3.6% and 7%, respectively. Additionally, Chate [110] reports that water is tested by 1% of dentists, Baudet [111] reports 2.6%, whereas we found that 21.8% perform water testing compared to 16.8% in the USA [110] and 17% in the EU, reaching as high as 70% in Germany [111]. In our study, it was reported that filters are replaced every 6 months by 18.9% of dentists and every 12 months by 11.1%, and both values are lower than what Baudet has reported [111].
Overall, as already discussed in the guidelines for the prevention and control of legionellosis [11,12,112], in order to reduce microbial contamination and/or the formation of biofilm in dental waterlines, the following recommendations should be implemented: (a) any sections excluded from the flow currents should be eliminated from the network, (b) anti-stagnation devices should be installed to keep the water circulating continuously, particularly during non-working hours, (c) sterile solutions should run through the network, after isolating it from the main water supply, (d) slow dentistry and long appointments on the same patient as well as intervals between patients (as suggested by the COVID-19 pandemic) should be followed, (e) all devices that connect to a waterline and enter patients’ mouths (handpieces, ultrasonic scalers and air/water syringes) should experience sterilization and switched to the hoses after the final system is flushed before use for at least two minutes at the beginning of each working day and for at least 20–30 s before each patient, (f) filters (≤0.2 μm) that can trap microorganisms coming from inside the water supply network should be installed immediately upstream of handpieces, (g) in the case of invasive surgical procedures with implantology motors, only sterile water should be used, and the supply network should also be sterile, and (h) if sterility of the dental unit’s supply network cannot be guaranteed, a bypass system should be created and disposable sterile devices, or sterilizable devices, should be used.
Young dentists should invest in green water strategies, revised protocols and comparative legislation addressing four-handed dentistry even at the beginning of their career. Successful and green water sustainable dental practice can be the scope of not only those managing large clinics but also dentists who are less educated or specialized. The largest impact factor in the dental practice for water sustainability is the human factor, the professionals themselves, their overall education, knowledge on water quality, experience, and willingness to invest in green procedures that may seem or are more expensive [12,113,114,115,116]. Dentists should be dedicated to excellency and constantly invest in revised continuing education on water sustainability and eco-friendly knowledge, financing relevant equipment opportunities and education for themselves and the auxiliary staff. They should also invest in slow dentistry procedures with better time management and revised water maintenance protocols. Professionals should finally decide on withdrawing old equipment not corresponding to green standards with governmental financing as conducted in other fields of green buildings’ philosophy [76].

6. Conclusions

Our findings suggest that authorities should conduct workshops, training sessions and seminars to raise the awareness on water quality and waste in Greek dental practices, especially to general dentists and dentists having studied abroad. Water quality in the dental office is a big issue depending on the unit, the waterline network, the use of filters, the age and type of the equipment, the procedures, materials, and other demographic factors such as gender, age, experience, educational and economic status of the dentist, specialty, and dental practice characteristics.
Limitations of the present study that should be taken into consideration for future coverage include the requirement for a far larger sample in the whole Greek territory, to overlook residence differences (urban vs. non-urban offices) because urbanism seems to affect environmentalism [76]. Also, the present questionnaire should be further enriched with questions based on the socio-environmental and economical capacity of participants to incorporate water sustainability procedures and equipment into their practice, their overall habits on environmentalism and their present culture on green dentistry and water eco-friendly dental practice. Due to the subjective nature of the questionnaire, the study should be repeated after an information-based campaign through the official network of the association to address possible changes in dental practices’ sustainable water eco-culture.

Author Contributions

Conceptualization, M.A., A.I., V.S. and C.K.; methodology, M.A.; software, M.A.; validation, M.A., A.I. and C.K.; formal analysis, M.A.; investigation, M.A., A.I., C.K., I.C., S.C., M.P., I.T. and V.S.; resources, M.A.; data curation, M.A.; writing—original draft preparation, M.A., A.I., C.K., I.C., S.C. and M.P.; writing—review and editing, all; visualization, M.A.; supervision, M.A.; project administration, M.A.; funding acquisition, M.A. All authors have read and agreed to the published version of the manuscript.

Funding

This research is financed by the Specific Account for Grant research of the National and Kapodistrian University of Athens (E.L.K.E). The funding source was not involved in the study.

Institutional Review Board Statement

The study was conducted in accordance with the Declaration of Helsinki and approved by the Scientific Board of the Athens Regional Dental Association (No: 2660/8 December 2022).

Informed Consent Statement

Informed consent was obtained by filling out the questionnaire. The investigation was based on an anonymous online survey with explanations posted in the accompanying email and introduction section of the survey. Submitted responses were considered as obtained informed consent.

Data Availability Statement

Data supporting reported results can be found in Appendix A.

Conflicts of Interest

The authors declare no conflict of interest.

Appendix A. Descriptive Statistics of Dentistry Equipment and Water Quality Practices (n = 206)

Table A1. Descriptive statistics of dentistry equipment and water quality practices (n = 206).
Table A1. Descriptive statistics of dentistry equipment and water quality practices (n = 206).
n%
Equipment How Old0–5 years4320.90%
6–10 years4119.90%
11–20 years8842.70%
21 years and older3416.50%
Has assistantNo10952.90%
Yes9747.10%
Was informed when acquiringNo8038.80%
Yes12661.20%
Interested in learning moreNo4421.40%
Yes16278.60%
Confident about water qualityNo9244.70%
Yes11455.30%
Performs microbiological testNo16178.20%
Yes4521.80%
Continuous water supply system dental unitNo14469.90%
Yes6230.10%
Continuous water supply system cuttersNo13766.50%
Yes6933.50%
Water supply to the dental unitWater from public network13065.00%
Distilled/Deionized water157.50%
Water from a filter device directly connected to the supply5527.50%
Water supply to handpiecesWater from public network12462.30%
Deionized/Distilled water2211.10%
Water from a filter device directly connected to the supply5326.60%
Supply to ultrasonic scalerWater from public network11458.50%
Distilled/Deionized water3115.90%
Water from a filter device directly connected to the supply5025.60%
Has water filterNo9144.20%
Yes11555.80%
Water filter replaced/cleanedNo filter/Don’t want to answer9952.10%
every month52.60%
every 6 months3618.90%
every 12 months2111.10%
every 2 years94.70%
every 5 years +42.10%
whenever there is a problem with the flow168.40%
Knows the active substance of antiseptic
Antiseptic to the incisors (auto)
No14871.80%
Yes5828.20%
No16490.60%
Antiseptic to the incisors (manually)Yes179.40%
No15585.60%
Yes2614.40%
Antiseptic reservoirNo83.90%
Yes19896.10%
Has strong surgical suctionNo115.30%
Yes19594.70%
Small suction between two patients7839.60%
every few appointments (3–4)3718.80%
per day5527.90%
per week2110.70%
never before COVID-1942.00%
never again due to COVID-19 let patients flush21.00%
Surgical suctionbetween two patients189.00%
every few appointments (3–4)2311.50%
per day8944.50%
per week5728.50%
per month63.00%
Never73.50%
Small Suctionbetween two patients9045.50%
every few appointments (3–4)3015.20%
per day5326.80%
per week147.10%
per month52.50%
Never63.00%
Surgical Suctionbetween two patients157.70%
every few appointments (3–4)2412.20%
per day8442.90%
per week5829.60%
per month73.60%
Never84.10%
Dental unit waterlinebetween two patients147.80%
every few appointments (3–4)137.30%
per day5631.30%
per week5430.20%
per month168.90%
Never2614.50%
Disinfecting Surfacesbetween two patients18992.20%
every few appointments (3–4)83.90%
per day73.40%
per week10.50%
Annual maintenanceNo7638.40%
Yes12261.60%
Micromotors15124.80%
26933.50%
32411.70%
42512.10%
5+3718.00%
Airotors12914.10%
26330.60%
32713.10%
42512.10%
5+6230.10%
Handpieces MaintenanceDecontamination12058.30%
Decontamination/Sterilization146.80%
Sterilization3617.50%
Surface cleaning3617.50%
Has implantology motorNo12862.40%
Yes7737.60%
Via suction vs. central drainNo7946.20%
Yes9253.80%
Has amalgam trapNo7035.40%
Yes12864.60%
Has contract with medical waste collection companyNo8241.80%
Yes11458.20%
Has contract for amalgam removalNo14173.40%
Yes5126.60%
Is informed about water quality legislationNo16785.60%
Yes2814.40%
Time spentno time52.40%
up to 2 h per month5727.70%
up to 4 h per month6230.10%
more than 4 h8239.80%
Money spentEUR 0 per month83.90%
less than EUR 25 per month4421.40%
EUR 25–50 per month8943.20%
EUR 51–75 per month3818.40%
more than EUR 75 per month2713.10%
Environmentally friendly practicesa little bit2815.40%
Satisfactorily8546.70%
Enough5027.50%
very much1910.40%
Implementation of disinfection protocol is my responsibilityNo8641.70%
Yes12058.30%
Stricter after COVID-19No9949.30%
Yes10250.70%

References

  1. Department of Health. Environment and Sustainability Health Technical Memorandum 07-04: Water Management and Water Efficiency—Best Practice Advice for the Healthcare Sector. 2013. Available online: http://www.nationalarchives.gov.uk/doc/open-government-licence/ (accessed on 15 March 2023).
  2. Facciolà, A.; Laganà, P.; Caruso, G. The COVID-19 pandemic and its implications on the environment. Environ. Res. 2021, 201, 111648. [Google Scholar] [CrossRef] [PubMed]
  3. Lawler, O.K.; Allan, H.L.; Baxter, P.W.J. The COVID-19 pandemic is intricately linked to biodiversity loss and ecosystem health. Lancet Planet. Health 2021, 5, e840–e850. [Google Scholar] [CrossRef] [PubMed]
  4. Marazziti, D.; Cianconi, P.; Mucci, F.; Foresi, L.; Chiarantini, I.; Della Vecchia, A. Climate change, environment pollution, COVID-19 pandemic and mental health. Sci. Total Environ. 2021, 773, 145182. [Google Scholar] [CrossRef] [PubMed]
  5. Nandi, S.; Sarkis, J.; Hervani, A.A.; Helms, M.M. Redesigning Supply Chains using Blockchain-Enabled Circular Economy and COVID-19 Experiences. Sustain. Prod. Consum. 2021, 27, 10–22. [Google Scholar] [CrossRef]
  6. Εuropean Commision. Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee, and the Committee of the Regions. EU Biodiversity Strategy for 2030. Bringing Nature Back into Our Lives. Brussels. 20 May 2020. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=celex%3A52020DC0380 (accessed on 15 March 2023).
  7. Intergovernmental science-policy Platform for Biodiversity and Ecosystem Services (IPBES). Summary for Policymakers of the Global Assessment Report on Biodiversity and Ecosystem Services of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services; IPBES: Bonn, Germany, 2019; Volume A.2, p. 12-1. [Google Scholar]
  8. European Environmental Bureau. EEB Position for a Revised Urban WasteWater Directive. Available online: https://eeb.org/wp-content/uploads/2021/07/EEB-position-for-a-revised-UWWTD.pdf (accessed on 15 April 2023).
  9. European Parliament. Revision of the Urban Wastewater Treatment Directive. Available online: https://www.europarl.europa.eu/legislative-train/theme-a-european-green-deal/file-revision-of-the-urban-wastewater-treatment-directive-(refit) (accessed on 15 April 2023).
  10. European Green Deal. Available online: https://www.consilium.europa.eu/en/policies/green-deal/#:~:text=The%20European%20Green%20Deal%20is%20a%20package%20of%20policy%20initiatives,a%20modern%20and%20competitive%20economy (accessed on 15 March 2023).
  11. CDC. Reduce Risk from Water. Available online: https://www.cdc.gov/hai/prevent/environment/water.html (accessed on 15 April 2023).
  12. Leach, R. Water Management, and IP Risk. Infect. Cont. Today 2023, 27. Available online: https://www.infectioncontroltoday.com/view/water-management-ip-risk (accessed on 15 April 2023).
  13. Antoniadou, M.; Tzoutzas, I.; Tzermpos, F.; Panis, V.; Maltezou, H.; Tseroni, M.; Madianos, F. Infection control during COVID-19 outbreak in a university dental school. J. Oral Hyg. Health 2020, 8, 4. [Google Scholar]
  14. Rezania, S.; Park, J.; Md Din, M.F. Microplastics pollution in different aquatic environments and biota: A review of recent studies. Mar. Pollut. Bull. 2018, 133, 191–208. [Google Scholar] [CrossRef]
  15. Dulsat-Masvidal, M.; Ciudad, C.; Infante, O.; Mateo, R.; Lacorte, S. Water pollution threats in important bird and biodiversity areas from Spain. J. Hazard Mater. 2023, 448, 130938. [Google Scholar] [CrossRef]
  16. Szymańska, J.; Sitkowska, J. Bacterial contamination of dental unit waterlines. Environ. Monit. Assess 2013, 185, 3603–3611. [Google Scholar] [CrossRef] [Green Version]
  17. Yuan, Q.; Zhang, M.; Zhou, J. To Implement A Clear-Water Supply System for Fine-Sediment Experiment in Laboratories. Water 2019, 11, 2476. [Google Scholar] [CrossRef] [Green Version]
  18. Matys, J.; Grzech-Leśniak, K. Dental Aerosol as a Hazard Risk for Dental Workers. Materials 2020, 13, 5109. [Google Scholar] [CrossRef] [PubMed]
  19. Centers for Disease Control and Prevention. Summary of Infection Prevention Practices in Dental Settings. Basic Expectations for Safe Care. Atlanta, GA: Centers for Disease Control and Prevention, US Dept of Health and Human Services; October 2016. Available online: https://www.cdc.gov/oralhealth/infectioncontrol/pdf/safe-care2.pdf (accessed on 20 March 2023).
  20. Leoni, E.; Dallolio, L.; Stagni, F.; Sanna, T.; D’Alessandro, G.; Piana, G. Impact of a Risk Management Plan on Legionella Contamination of Dental Unit Water. Int. J. Environ. Res. Public Health 2015, 12, 2344–2358. [Google Scholar] [CrossRef] [PubMed]
  21. Dallolio, L.; Scuderi, A.; Rini, M.S.; Valente, S.; Farruggia, P.; Bucci Sabattini, M.A.; Leoni, E. Effect of Different Disinfection Protocols on Microbial and Biofilm Contamination of Dental Unit Waterlines in Community Dental Practices. Int. J. Environ. Res. Public Health 2014, 11, 2064–2076. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  22. Shajahan, I.F.; Kandaswamy, D.; Srikanth, P.; Narayana, L.L.; Selvarajan, R. Dental unit waterlines disinfection using hypochlorous acid-based disinfectant. J. Conserv. Dent. JCD 2016, 19, 347–350. [Google Scholar] [CrossRef]
  23. Ditommaso, S.; Giacomuzzi, M.; Ricciardi, E.; Zotti, C.M. Efficacy of a Low Dose of Hydrogen Peroxide (Peroxy Ag+) for Continuous Treatment of Dental Unit Water Lines: Challenge Test with Legionella pneumophila Serogroup 1 in a Simulated Dental Unit Waterline. Int. J. Environ. Res. Public Health 2016, 13, 745. [Google Scholar] [CrossRef] [Green Version]
  24. Lizzadro, J.; Mazzotta, M.; Girolamini, L.; Dormi, A.; Pellati, T.; Cristino, S. Comparison between Two Types of Dental Unit Waterlines: How Evaluation of Microbiological Contamination Can Support Risk Containment. Int. J. Environ. Res. Public Health 2019, 16, 328. [Google Scholar] [CrossRef] [Green Version]
  25. Cervino, G.; Fiorillo, L.; Laino, L.; Herford, A.S.; Lauritano, F.; Giudice, G.L.; Fama, F.; Santoro, R.; Troiano, G.; Iannello, G. Oral Health Impact Profile in Celiac Patients: Analysis of Recent Findings in a Literature Review. Gastroenterol. Res. Pract. 2018, 2018, 7848735. [Google Scholar] [CrossRef]
  26. Gawish, S.; Abbass, A.; Abaza, A. Occurrence and biofilm forming ability of Pseudomonas aeruginosa in the water output of dental unit waterlines in a dental center in Alexandria, Egypt. Germs 2019, 9, 71–80. [Google Scholar] [CrossRef]
  27. Ajami, B.; Ghazvini, K.; Movahhed, T.; Ariaee, N.; Shakeri, M.T.; Makarem, S. Contamination of a Dental Unit Water Line System by Legionella Pneumophila in the Mashhad School of Dentistry in 2009. Iran Red Crescent. Med. J. 2012, 14, 376–378. [Google Scholar]
  28. Tuvo, B.; Totaro, M.; Cristina, M.L. Prevention and Control of Legionella and Pseudomonas spp. Colonization in Dental Units. Pathogens 2020, 9, 305. [Google Scholar] [CrossRef] [Green Version]
  29. Pouralibaba, F.; Balaei, E.; Kashefimehr, A. Evaluation of Gram-Negative Bacterial Contamination in Dental Unit Water Supplies in a University Clinic in Tabriz, Iran. J. Dent. Res. Dent. Clin. Dent. Prospect 2011, 5, 94–97. [Google Scholar] [CrossRef]
  30. Giacomuzzi, M.; Zotti, C.M.; Ditommaso, S. Colonization of Dental Unit Waterlines by Helicobacter pylori: Risk of Exposure in Dental Practices. Int. J. Environ. Res. Public Health 2019, 16, 2981. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  31. Cicciù, M. Water Contamination Risks at the Dental Clinic. Biology 2020, 9, 43. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  32. Cárdenas, A.M.; Campos-Bijit, V.; Di Francesco, F.; Schwarz, F.; Cafferata, E.A.; Vernal, R. Electrolyzed water for the microbiologic control in the pandemic dental setting: A systematic review. BMC Oral. Health 2022, 22, 579. [Google Scholar] [CrossRef]
  33. Hatzenbuehler, L.A.; Tobin-D’Angelo, M.; Drenzek, C.; Peralta, G.; Cranmer, L.C.; Anderson, E.J.; Milla, S.S.; Abramowicz, S.; Yi, J.; Hilinski, J.; et al. Pediatric dental clinic-associated outbreak of Mycobacterium abscessus infection. J. Pediatr. Infect. Dis. Soc. 2017, 6, e116–e122. [Google Scholar] [CrossRef]
  34. Han, P.; Li, H.; Walsh, L.J.; Ivanovski, S. Splatters and Aerosols Contamination in Dental Aerosol Generating Procedures. Appl. Sci. 2021, 11, 1914. [Google Scholar] [CrossRef]
  35. Spagnolo, A.M.; Sartini, M.; Cristina, M.L. Microbial Contamination of Dental Unit Waterlines and Potential Risk of Infection: A Narrative Review. Pathogens 2020, 13, 651. [Google Scholar] [CrossRef]
  36. Fiorillo, L. Conscious Sedation in Dentistry. Medicina 2019, 55, 778. [Google Scholar] [CrossRef] [Green Version]
  37. Walker, J.T.; Bradshaw, D.J.; Bennett, A.M.; Fulford, M.R.; Martin, M.V.; Marsh, P.D. Microbial Biofilm Formation and Contamination of Dental-Unit Water Systems in General Dental Practice. Appl. Environ. Microbiol. 2000, 66, 3363–3367. [Google Scholar] [CrossRef] [Green Version]
  38. Walker, J.T.; Bradshaw, D.J.; Fulford, M.R.; Marsh, P.D. Microbiological Evaluation of a Range of Disinfectant Products To Control Mixed-Species Biofilm Contamination in a Laboratory Model of a Dental Unit Water System. Appl. Environ. Microbiol. 2003, 69, 3327–3332. [Google Scholar] [CrossRef] [Green Version]
  39. Yabune, T.; Imazato, S.; Ebisu, S. Assessment of Inhibitory Effects of Fluoride-Coated Tubes on Biofilm Formation by Using the In Vitro Dental Unit Waterline Biofilm Model. Appl. Environ. Microbiol. 2008, 74, 5958–5964. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  40. Mills, S.E. The dental unit waterline controversy: Defusing the myths, defining the solutions. J. Am. Dent. Assoc. 2000, 131, 1427–1441. [Google Scholar] [CrossRef] [Green Version]
  41. EU. Directorate-General for Environment. Proposal for Ecodesign for Sustainable Products Regulation. Annexes—Proposal for a Regulation Establishing a Framework for Setting Ecodesign Requirements for Sustainable Products and Repealing Directive 2009/125/EC. Available online: https://environment.ec.europa.eu/publications/proposal-ecodesign-sustainable-products-regulation_en (accessed on 15 March 2023).
  42. Cicciu, M.; Fiorillo, L.; Herford, A.S.; Crimi, S.; Bianchi, A.; D’Amico, C.; Laino, L.; Cervino, G. Bioactive Titanium Surfaces: Interactions of Eukaryotic and Prokaryotic Cells of Nano Devices Applied to Dental Practice. Biomedicines 2019, 7, 12. [Google Scholar] [CrossRef] [Green Version]
  43. Cataldi, M.E.; Al Rakayan, S.; Arcuri, C.; Condò, R. Dental unit wastewater, a current environmental problem: A sistematic review. Oral. Implantol. 2017, 10, 354–359. [Google Scholar] [CrossRef]
  44. Innes, N.; Johnson, I.G.; Al-Yaseen, W.; Harris, R.; Jones, R.; Kc, S.; McGregor, S.; Robertson, M.; Wade, W.G.; Gallagher, J.E. A systematic review of droplet and aerosol generation in dentistry. J. Dent. 2021, 105, 103556. [Google Scholar] [CrossRef] [PubMed]
  45. Sasaki, J.I.; Imazato, S. Autoclave sterilization of dental handpieces: A literature review. J. Prosthodont. Res. 2020, 64, 239–242. [Google Scholar] [CrossRef]
  46. Maltezou, H.; Tseroni, Μ.; Vorou, Ρ.; Koutsolioutsou, A.; Antoniadou, Μ.; Tzoutzas, Ι.; Panis, V.; Tzermpos, F.; Madianos, P. Preparing dental schools to refunction safely during the COVID-19 pandemic: An infection prevention and control perspective. J. Infect. Dev. Ctries. 2021, 15, 22–31. [Google Scholar] [CrossRef] [PubMed]
  47. Senpuku, H.; Fukumoto, M.; Uchiyama, T.; Taguchi, C.; Suzuki, I.; Arikawa, K. Effects of Extraoral Suction on Droplets and Aerosols for Infection Control Practices. Den. J. 2021, 9, 80. [Google Scholar] [CrossRef] [PubMed]
  48. Chen, Z.; Osman, A.I.; Rooney, D.W.; Oh, W.-D.; Yap, P.-S. Remediation of Heavy Metals in Polluted Water by Immobilized Algae: Current Applications and Future Perspectives. Sustainability 2023, 15, 5128. [Google Scholar] [CrossRef]
  49. Engsomboon, N.; Pachimsawat, P.; Thanathornwong, B. Comparative Dissemination of Aerosol and Splatter Using Suction Device during Ultrasonic Scaling: A Pilot Study. Dent. J. 2022, 10, 142. [Google Scholar] [CrossRef]
  50. Li, Y.; Xu, Z.; Ma, H.S.; Hursthouse, A. Removal of Manganese (II) from Acid Mine Wastewater: A Review of the Challenges and Opportunities with Special Emphasis on Mn-Oxidizing Bacteria and Microalgae. Water 2019, 11, 2493. [Google Scholar] [CrossRef] [Green Version]
  51. Engelmann, C.; Schmidt, L.; Werth, C.J.; Walther, M. Quantification of Uncertainties from Image Processing and Analysis in Laboratory-Scale DNAPL Release Studies Evaluated by Reflective Optical Imaging. Water 2019, 11, 2274. [Google Scholar] [CrossRef] [Green Version]
  52. Yoon, H.Y.; Lee, S.Y. Susceptibility of bacteria isolated from dental unit waterlines to disinfecting chemical agents. J. Gen. Appl. Microbiol. 2019, 64, 269–275. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  53. Costa, D.; Girardot, M.; Bertaux, J.; Verdon, J.; Imbert, C. Efficacy of dental unit waterlines disinfectants on a polymicrobial biofilm. Water Res. 2016, 91, 38–44. [Google Scholar] [CrossRef] [PubMed]
  54. Hoogenkamp, M.A.; Brandt, B.W.; Laheij, A.M.G.A.; de Soet, J.J.; Crielaard, W. The microbiological load and microbiome of the Dutch dental unit; ‘please, hold your breath’. Water Res. 2021, 200, 117205. [Google Scholar] [CrossRef]
  55. EYDAP Sustainable Development Report. Sustainable Development EYDAP SA. Athens. 2021. Available online: https://www.eydap.gr/userfiles/Presentations/presentations/EYDAP_CSR_2021_21x29-7CM_F13_WEB/index.html#page=1 (accessed on 15 March 2023).
  56. Gawlik, B.M.; Easton, P.; Koop, S.; Van Leeuwen, K.; Elelman, R. (Eds.) Urban Water Atlas for Europe; European Commission, Publications Office of the European Union: Luxembourg, 2017. [Google Scholar] [CrossRef]
  57. Putnins, E.E.; Di Giovanni, D.; Bhullar, A.S. Dental unit waterline contamination and its possible implications during periodontal surgery. J. Periodontol. 2001, 72, 393–400. [Google Scholar] [CrossRef]
  58. Toomarian, L.; Rikhtegaran, S.; Sadighi, M.; Savadi Oskoee, S.; Alizadeh Oskoee, P. Contamination of Dental Unit Water and Air Outlets Following Use of Clean Head System and Conventional Handpieces. J. Dent. Res. Dent. Clin. Dent. Prospect. 2007, 1, 43–47. [Google Scholar] [CrossRef]
  59. Laino, L.; Cicciù, M.; Fiorillo, L.; Crimi, S.; Bianchi, A.; Amoroso, G.; Monte, I.P.; Herford, A.S.; Cervino, G. Surgical Risk on Patients with Coagulopathies: Guidelines on Hemophiliac Patients for Oro-Maxillofacial Surgery. Int. J. Environ. Res. Public Health 2019, 16, 1386. [Google Scholar] [CrossRef] [Green Version]
  60. Takenaka, S.; Sotozono, M.; Yashiro, A.; Saito, R.; Kornsombut, N.; Naksagoon, T.; Nagata, R.; Ida, T.; Edanami, N.; Noiri, Y. Efficacy of Combining an Extraoral High-Volume Evacuator with Preprocedural Mouth Rinsing in Reducing Aerosol Contamination Produced by Ultrasonic Scaling. Int. J. Environ. Res. Public Health 2022, 19, 6048. [Google Scholar] [CrossRef]
  61. Adedoja, O.S.; Hamam, Y.; Khalaf, B.; Sadiku, R. Development of a Contaminant Distribution Model for Water Supply Systems. Water 2019, 11, 1510. [Google Scholar] [CrossRef] [Green Version]
  62. Acosta-Gio, E.; Bednarsh, H.; Cuny, E.; Eklund, K.; Mills, S.; Risk, D. Sterilization of dental handpieces. Am. J. Infect. Control 2017, 45, 937–938. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  63. Walker, J.T.; Marsh, P.D. Microbial biofilm formation in DUWS and their control using disinfectants. J. Dent. 2007, 35, 721–730. [Google Scholar] [CrossRef] [PubMed]
  64. Offner, D.; Fioretti, F.; Musset, A.-M. Contamination of dental unit waterlines: Assessment of three continuous water disinfection systems. BDJ Open 2016, 2, 1–6. [Google Scholar] [CrossRef] [Green Version]
  65. Pawar, A.; Garg, S.; Mehta, S.; Dang, R. Breaking the Chain of Infection: Dental Unit Water Quality Control. J. Clin. Diagn. Res. 2016, 10, ZC80–ZC84. [Google Scholar] [CrossRef] [PubMed]
  66. Garg, S.K.; Mittal, S.; Kaur, P. Dental unit waterline management: Historical perspectives and current trends. J. Investig. Clin. Dent. 2012, 3, 247–252. [Google Scholar] [CrossRef]
  67. Fujita, M.; Mashima, I.; Nakazawa, F. Monitoring the decontamination efficacy of the novel Poseidon-S disinfectant system in dental unit water lines. J. Microbiol. Immunol. Infect. 2017, 50, 270–276. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  68. Noopan, S.; Unchui, P.; Techotinnakorn, S.; Ampornaramveth, R.S. Plasma Sterilization Effectively Reduces Bacterial Contamination in Dental Unit Waterlines. Int. J. Dent. 2019, 2019, 5720204. [Google Scholar] [CrossRef] [Green Version]
  69. Pantanella, F.; Schippa, S.; Solimini, A.; Rosa, L.; Bettucci, A.; Berlutti, F. Efficacy of acoustic waves in preventing Streptococcus mutans adhesion on dental unit water line. Ann. Ig. 2019, 31, 109–116. [Google Scholar] [CrossRef]
  70. Troiano, G.; Laino, L.; Cicciu, M.; Cervino, G.; Fiorillo, L.; D’Amico, C.; Zhurakivska, K.; Lo Muzio, L. Comparison of Two Routes of Administration of Dexamethasone to Reduce the Postoperative Sequelae after Third Molar Surgery: A Systematic Review and Meta-Analysis. Open. Dent. J. 2018, 12, 181–188. [Google Scholar] [CrossRef] [Green Version]
  71. Kohn, W.G.; Collins, A.S.; Cleveland, J.L.; Harte, J.A.; Eklund, K.J.; Malvitz, D.M. Centers for Disease Control and Prevention (CDC). Guidelines for infection control in dental health-care settings-2003. MMWR Recomm. Rep. 2003, 52, RR-17. [Google Scholar]
  72. American Dental Association ADA Statement on Dental unit waterlines. J. Am. Dent. Assoc. 1996, 127, 185–186. [CrossRef]
  73. Alkhulaifi, M.M.; Alotaibi, D.H.; Alajlan, H.; Binshoail, T. Assessment of nosocomial bacterial contamination in dental unit waterlines: Impact of flushing. Saudi Dent. J. 2020, 32, 68–73. [Google Scholar] [CrossRef] [PubMed]
  74. Fiorillo, L. We Do Not Eat Alone: Formation and Maturation of the Oral Microbiota. Biology 2020, 9, 17. [Google Scholar] [CrossRef] [Green Version]
  75. Antoniadou, M. Quality of Life and Satisfaction from Career and Work–Life Integration of Greek Dentists before and during the COVID-19 Pandemic. Int. J. Environ. Res. Public Health 2022, 19, 9865. [Google Scholar] [CrossRef] [PubMed]
  76. Antoniadou, M.; Chrysochoou, G.; Tzanetopoulos, R.; Riza, E. Green Dental Environmentalism among Students and Dentists in Greece. Sustainability, 2023; under review. [Google Scholar]
  77. Pasquarella, C.; Veronesi, L.; Napoli, C. Microbial environmental contamination in Italian dental clinics: A multicenter study yielding recommendations for standardized sampling methods and threshold values. Sci. Total. Environ. 2012, 420, 289–299. [Google Scholar] [CrossRef] [PubMed]
  78. Zhang, Y.; Ping, Y.; Zhou, R.; Wang, J.; Zhang, G. High throughput sequencing-based analysis of microbial diversity in dental unit waterlines supports the importance of providing safe water for clinical use. J. Infect. Public Health 2018, 11, 357–363. [Google Scholar] [CrossRef] [PubMed]
  79. Water Information System for Europe (WISE). Available online: http://water.europa.eu/ (accessed on 20 March 2023).
  80. European Innovation Partnership on Water. Available online: http://ec.europa.eu/environment/water/innovationpartnership/ (accessed on 15 March 2023).
  81. Tims, M.; Bakker, A.B.; Derks, D. Development and validation of the job crafting scale. J. Vocational. Behav. 2012, 80, 173–186. [Google Scholar] [CrossRef]
  82. Bursac, Z.; Gauss, C.H.; Williams, D.K. Purposeful selection of variables in logistic regression. Source Code. Biol. Med. 2008, 3, 17. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  83. Green, H.; Weller, D.; Johnson, S.; Michalenko, E. Microbial Source-Tracking Reveals Origins of Fecal Contamination in a Recovering Watershed. Water 2019, 11, 2162. [Google Scholar] [CrossRef] [Green Version]
  84. Ayers, K.M.; Thomson, W.M.; Rich, A.M.; Newton, J.T. Gender differences in dentists’ working practices and job satisfaction. J. Dent. 2008, 36, 343–350. [Google Scholar] [CrossRef]
  85. McKay, J.C.; Ahmad, A.; Shaw, J.L.; Rashid, F.; Clancy, A.; David, C. Gender differences and predictors of work hours in a sample of Ontario dentists. J. Can. Dent. Assoc. 2016, 82, 1488–2159. [Google Scholar]
  86. Walker, S. Work pattern differences between male and female orthodontists in Canada. J. Can. Dent. Assoc. 2016, 82, g6. [Google Scholar] [PubMed]
  87. Emrani, R.; Sargeran, K.; Shamshiri, A.R.; Hessari, H. Job satisfaction among dentists according to workplace in Tehran. Front. Dent. 2021, 18, 11. [Google Scholar] [CrossRef] [PubMed]
  88. Surdu, S.; Mertz, E.; Langelier, M.; Moore, J. Dental workforce trends: A national study of gender diversity and practice patterns. Med. Care. Res. Rev. 2021, 78 (Suppl. 1), 30S–39S. [Google Scholar] [CrossRef] [PubMed]
  89. Archer, J. The reality and evolutionary significance of human psychological sex differences. Biology 2019, 94, 1381–1415. [Google Scholar] [CrossRef] [PubMed]
  90. Baptiste, D.; Fecher, A.M.; Dolejs, S.C.; Yoder, J.; Schmidt, C.M.; Couch, M.E. Gender differences in academic surgery, work-life balance, and satisfaction. J. Surg. Res. 2017, 218, 99–107. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  91. Rich-Edwards, J.W.; Kaiser, U.B.; Chen, G.L.; Manson, J.E.; Goldstein, J.M. Sex and gender differences research design for basic, clinical, and population studies: Essentials for investigators. Endocr. Rev. 2018, 39, 424–439. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  92. Shannon, G.; Jansen, M.; Williams, K.; Cáceres, C.; Motta, A.; Odhiambo, A. Gender equality in science, medicine, and global health: Where are we at and why does it matter? Lancet 2019, 393, 560–569. [Google Scholar] [CrossRef] [Green Version]
  93. Nirupama, Y.S.; Boppana, N.K.; Vinnakota, N.R.; Thetakala, R.K.; Kallakuri, P.; Karthik, B.K. Indian women dentists’ perspectives towards balancing professional, personal and social responsibilities. Indian. J. Dent. Res. 2020, 31, 358–362. [Google Scholar] [CrossRef]
  94. Antoniadou, M. Estimation of Factors Affecting Burnout in Greek Dentists before and during the COVID-19 Pandemic. Dent. J. 2022, 10, 108. [Google Scholar] [CrossRef]
  95. Dousin, O.; Collins, N.; Kler, B.K. The experience of work-life balance for women doctors and nurses in Malaysia. Asia. Pac. J. Hum. Resour. 2022, 60, 362–380. [Google Scholar] [CrossRef]
  96. McCarthy, G.M.; MacDonald, J.K. Gender differences in characteristics, infection control practices, knowledge and attitudes related to HIV among Ontario dentists. Commun. Dent. Oral. Epidemiol. 1996, 24, 412–415. [Google Scholar] [CrossRef] [PubMed]
  97. Reza, E.; Sargeran, K.; Hessari, H.; Masoumeh, E. Differences in the work pattern of male and female dentists in Tehran in 2021. Ital. J. Gend. Specif. Med. 2022, 8, 143–146. [Google Scholar] [CrossRef]
  98. Li, J.; de Souza, R.; Esfandiari, S.; Feine, J. Have women broken the glass ceiling in North American dental leadership? J. Adv. Dent. Res. 2019, 30, 78–84. [Google Scholar] [CrossRef] [PubMed]
  99. Shahin, S.Y.; Bugshan, A.S.; Almulhim, K.S.; AlSharief, M.S.; Al-Dulaijan, Y.A.; Siddiqui, I.; Al-Qarni, F.D. Knowledge of dentists, dental auxiliaries, and students regarding the COVID-19 pandemic in Saudi Arabia: A cross-sectional survey. BMC Oral. Health 2020, 20, 363. [Google Scholar] [CrossRef]
  100. Qabool, H.; Sukhia, R.H.; Fida, M. Knowledge and awareness of dental specialists, general dentists and dental assistants regarding SARS-CoV-2. Dent. Med. Probl. 2021, 58, 285–290. [Google Scholar] [CrossRef]
  101. Schalli, M.; Kogler, B.; Miorini, T.; Gehrer, M.; Reinthaler, F.F. High-Speed Dental Instruments: An Investigation of Protein-Contaminated Dental Handpieces with the Bicinchoninic Acid Assay in Dental Offices in Styria, Austria. Int. J. Environ. Res. Public Health 2023, 20, 1670. [Google Scholar] [CrossRef]
  102. Deshpande, A.; Smith, G.W.; Smith, A.J. Biofouling of surgical power tools during routine use. J. Hosp. Infect. 2015, 90, 179–185. [Google Scholar] [CrossRef]
  103. Rosa, V.; Agarwalla, S.V.; Tan, B.L.; Choo, S.Y.; Sim, Y.F.; Boey, F.Y.C.; Anantharaman, S.; Duggal, M.S.; Tan, K.S. Pandemic Preparedness and Response: A Foldable Tent to Safely Remove Contaminated Dental Aerosols—Clinical Study and Patient Experience. Appl. Sci. 2022, 12, 7409. [Google Scholar] [CrossRef]
  104. Pinto, F.M.; Bruna, C.Q.; Camargo, T.C.; Marques, M.; Silva, C.B.; Sasagawa, S.M. The practice of disinfection of high-speed handpieces with 70% w/v alcohol: An evaluation. Am. J. Infect. Control 2017, 45, e19–e22. [Google Scholar] [CrossRef]
  105. Osegueda-Espinosa, A.A.; Sanchez-Perez, L.; Perea-Perez, B.; Labajo-Gonzalez, E.; Acosta-Gio, A.E. Dentists survey adverse events during their clinical training. J. Patient Saf. 2020, 16, e240–e244. [Google Scholar] [CrossRef] [PubMed]
  106. Hbibi, A.; Kasouati, J.; Charof, R.; Chaouir, S.; El Harti, K. Evaluation of the knowledge and attitudes of dental students toward occupational blood exposure accidents at the end of the dental training program. J Int.Soc. Prev. Commun. Dent. 2018, 8, 77–86. [Google Scholar]
  107. Agahi, R.H.; Hashemipour, M.A.; Kalantari, M.; Ayatollah-Mosavi, A.; Aghassi, H.; Nassab, A.H.G. Effect of 0.2% chlorhexidine on microbial and fungal contamination of dental unit waterlines. Dent. Res. 2014, 11, 351–356. [Google Scholar]
  108. Dupont, D.; Adamowicz, W.L.; Krupnick, A. Differences in water consumption choices in Canada: The role of socio-demographics, experiences, and perceptions of health risks. J. Water Health 2010, 8, 671–686. [Google Scholar] [CrossRef] [PubMed]
  109. Banakar, M.; Bagheri Lankarani, K.; Jafarpour, D. COVID-19 transmission risk and protective protocols in dentistry: A systematic review. BMC. Oral. Health 2020, 20, 275. [Google Scholar] [CrossRef] [PubMed]
  110. Chate, R.A. An audit improves the quality of water within the dental unit water lines of general dental practices across the East of England. Br. Dent. J. 2010, 209, E11. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  111. Baudet, A.; Lizon, J.; Martrette, J.M.; Camelot, F.; Florentin, A.; Clément, C. Efficacy of BRS® and Alpron®/Bilpron® Disinfectants for Dental Unit Waterlines: A Six-Year Study. Int. J. Environ. Res. Public Health 2020, 17, 2634. [Google Scholar] [CrossRef] [Green Version]
  112. Italian Health Ministry. Guidelines for Prevention and Control of Legionellosis. Rome, Italy, 2015. Available online: http://www.salute.gov.it/imgs/C_17_pubblicazioni_2362_allegato.pdf (accessed on 15 March 2023).
  113. McManus, K.R.; Fan, P.L. Purchasing, installing and operating dental amalgam separators: Practical issues. J. Am. Dent. Assoc. 2003, 134, 1054–1065. [Google Scholar] [CrossRef] [Green Version]
  114. Spaveras, A.; Antoniadou, M. Awareness of Students and Dentists on Sustainability Issues, Safety of Use and Disposal of Dental Amalgam. Dent. J. 2023, 11, 21. [Google Scholar] [CrossRef]
  115. Oosthuysen, J.; Potgieter, E.; Fossey, A. Compliance with infection prevention and control in oral health-care facilities: A global perspective. Int. Dent. J. 2014, 64, 297–311. [Google Scholar] [CrossRef]
  116. Carraro, E.; Bonetta, S.; Bonetta, S. Hospital Wastewater: Existing Regulations and Current Trends in Management. In Hospital Wastewaters. The Handbook of Environmental Chemistry; Verlicchi, P., Ed.; Springer: Cham, Switzerland, 2017; Volume 60. [Google Scholar] [CrossRef]
Figure 1. Graph showcasing various water treatment methods and arrangements within a dental practice: (i) Self-contained water systems (e.g., independent water tank) that supply the dental unit/s. (ii) Systems in line with one or more dental units within the same dental practice that filter incoming water. (iii) Systems in line with one or more dental units within the same dental practice that treat incoming water to remove or inactivate microorganisms throughout the network. These methods (iiii) can also be used sequentially in line, e.g., tank combined with chemical treatment (periodic or continuous chemical microbicide treatment protocols) and filters.
Figure 1. Graph showcasing various water treatment methods and arrangements within a dental practice: (i) Self-contained water systems (e.g., independent water tank) that supply the dental unit/s. (ii) Systems in line with one or more dental units within the same dental practice that filter incoming water. (iii) Systems in line with one or more dental units within the same dental practice that treat incoming water to remove or inactivate microorganisms throughout the network. These methods (iiii) can also be used sequentially in line, e.g., tank combined with chemical treatment (periodic or continuous chemical microbicide treatment protocols) and filters.
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Figure 2. Systemic schematic presentation of factors affecting water maintenance of a dental unit.
Figure 2. Systemic schematic presentation of factors affecting water maintenance of a dental unit.
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Table 1. Demographics and dental practice characteristics (n = 206).
Table 1. Demographics and dental practice characteristics (n = 206).
n%
GenderMen11756.8%
Women8842.7%
Other10.5%
Family StatusUnmarried4823.3%
Married13967.5%
Other199.2%
Ageup to 30 years157.3%
31–402914.1%
41–506431.1%
51–606029.1%
60+3818.4%
WorkplaceAthens or urban center19092.2%
Province167.8%
Experience0–10 years3215.5%
11–20 years5928.6%
21–30 years5727.7%
30+5828.2%
Family Incomeup to EUR 25,0006933.5%
EUR 25,001–50,0009043.7%
50,001 and above3918.9%
I don’t want to answer83.9%
EducationBasic dental education in Greece8943.2%
Basic dental education abroad3818.4%
Postgraduate education10350.0%
Recognized specialty2110.2%
Clinical activityGeneral dentistry15675.7%
other activities5024.3%
Dental practiceprivate dental practice13666.0%
dental clinic5727.7%
Other136.3%
Table 2. Differences between genders (male vs. female) in dentistry equipment and water quality practices.
Table 2. Differences between genders (male vs. female) in dentistry equipment and water quality practices.
FemaleMaleχ2(p)
n%N%
Interested in learning more7787.50%8471.80%7.35 (0.006)
Continuous water supply system cutters2225.00%4740.20%5.17 (0.023)
Water supply to the dental unitWater from public network6273.80%6758.30%8.90 (0.012)
Distilled/Deionized water89.50%76.10%
Water from a filter device directly connected to the supply1416.70%4135.70%
Water supply to the handpiecesWater from public network5870.70%6656.90%6.72 (0.035)
Deionized/Distilled water1012.20%119.50%
Water from a filter device directly connected to the supply1417.10%3933.60%
Supply to ultrasonic scalerWater from public network5568.80%5951.80%10.31 (0.006)
Distilled/Deionized water1417.50%1614.00%
Water from a filter device directly connected to the supply1113.80%3934.20%
Disinf. Surfacesbetween two patients8597.70%10388.00%12.54 (0.028)
every few appointments 00.00%86.80%
per day11.10%65.10%
per week11.10%00.00%
Annual maintenance5566.30%6657.90%10.10 (0.018)
Has implantology motor2427.60%5244.40%6.07 (0.014)
Table 3. Differences between dentists’ experience (in years) in dentistry equipment and water quality practices.
Table 3. Differences between dentists’ experience (in years) in dentistry equipment and water quality practices.
Experienceχ2(p)
0–10 Years11–20 Years21–30 Years31 Years and Over
n%n%n%N%
Water supply to the dental unitWater from public network2589.30%3663.20%3764.90%3255.20%13.70 (0.033)
Distilled/Deionized water13.60%712.30%47.00%35.20%
Water from filter 27.10%1424.60%1628.10%2339.70%
Water supply to the handpiecesWater from public network2492.30%3762.70%3460.70%2950.00%16.69 (0.010)
Deionized/Distilled water13.80%915.30%610.70%610.30%
Water from filter 13.80%1322.00%1628.60%2339.70%
Supply to ultrasonic scalerWater from public network2180.80%3864.40%3258.20%2341.80%13.63 (0.034)
Distilled/Deionized water311.50%813.60%712.70%1323.60%
Water from filter27.70%1322.00%1629.10%1934.50%
Large amount of water through surgical suction to the dental unitbetween two patients517.20%00.00%23.60%815.10%31.12 (0.008)
every few appointments (3–4)26.90%58.60%1017.90%713.20%
per day931.00%2848.30%2239.30%2547.20%
per week or more1344.80%2543.10%2239.40%1324.60%
Large amount of water to the dental unitbetween two patients416.00%23.80%48.30%47.40%27.69 (0.024)
every few appointments (3–4)14.00%35.80%24.20%713.00%
per day1040.00%1121.20%1327.10%2240.70%
per week or more1040.00%3669.30%2960.40%2139.00%
Micromotors11546.90%1830.50%1221.10%610.30%25.92 (0.011)
2515.60%2237.30%1933.30%2339.70%
339.40%58.50%915.80%712.10%
439.40%813.60%35.30%1119.00%
5+618.80%610.20%1424.60%1119.00%
Airotors11134.40%813.60%58.80%58.60%29.17 (0.004)
21031.30%2033.90%1729.80%1627.60%
313.10%1423.70%58.80%712.10%
439.40%58.50%1119.30%610.30%
5+721.90%1220.30%1933.30%2441.40%
Is informed about water quality legislation827.60%35.40%713.20%1017.50%8.34 (0.039)
Time Spentno time412.50%00.00%11.80%00.00%26.21 (0.002)
up to 2 h per month1340.60%1322.00%1526.30%1627.60%
up to 4 h per month1031.30%2237.30%1424.60%1627.60%
more than 4 h515.60%2440.70%2747.40%2644.80%
Table 4. Differences between dentists’ educational characteristics in dentistry equipment and water quality practices.
Table 4. Differences between dentists’ educational characteristics in dentistry equipment and water quality practices.
Education Abroadχ2(p)Postgraduate Educationχ2(p)Recognized Specialtyχ2(p)
NoYesNoYesNoYes
n%n%n%n%n%n%
Has assistant8349.40%1436.80%ns4135.70%5661.50%13.66 (<0.001)8244.30%1571.40%5.56 (0.018)
Knows the active substance of antiseptic4531.70%1339.40%ns2525.50%3342.90%5.86 (0.016)5535.00%316.70%ns
Antiseptic to the handpieces (auto)159.90%26.70%ns54.90%1215.20%5.54 (0.019)159.20%211.10%ns
Antiseptic to the handpieces (manually)1711.30%930.00%7.15 (0.008)1817.60%810.10%ns2515.30%15.60%ns
Small
Suction
between two patients8050.00%1026.30%13.26 (0.021)4440.70%4651.10%13.04 (0.023)8547.80%525.00%ns
every few appointments2515.60%513.20%1312.00%1718.90%2815.70%210.00%
per day3622.50%1744.70%3835.20%1516.70%4525.30%840.00%
per week or more1911.80%615.8%1312.00%1213.40%2011.20%525.00%
Annual maintenance10364.00%1951.40%ns5853.20%6471.90%7.24 (0.007)11464.00%840.00%4.40 (0.036)
Micromotors13822.60%1334.20%ns3429.60%1718.70%12.72 (0.013)4323.20%838.10%ns
25532.70%1436.80%4135.70%2830.80%6334.10%628.60%
32011.90%410.50%87.00%1617.60%2211.90%29.50%
42213.10%37.90%1714.80%88.80%2413.00%14.80%
5+3319.60%410.50%1513.00%2224.20%3317.80%419.00%
Airotors12112.50%821.10%ns2118.30%88.80%8.94 (0.063)2010.80%942.90%22.76 (<0.001)
24929.20%1436.80%3631.30%2729.70%5429.20%942.90%
32112.50%615.80%1613.90%1112.10%2714.60%00.00%
42112.50%410.50%1613.90%99.90%2513.50%00.00%
5+5633.30%615.80%2622.60%3639.60%5931.90%314.30%
Has amalgam trap10665.80%2259.50%ns7063.60%5865.90%ns12168.00%735.00%8.56 (0.003)
Has contract for amalgam removal4227.30%923.70%ns2220.60%2934.10%4.46 (0.035)4828.10%314.30%ns
Environment-friendly practicesA little2617.20%26.50%10.93 (0.012)1817.10%1013.00%ns2817.10%00.00%ns
Satisfactory7348.30%1238.70%4845.70%3748.10%7646.30%950.00%
Enough4127.20%929.00%3028.60%2026.00%4326.20%738.90%
Very much117.30%825.80%98.60%1013.00%1710.40%211.10%
Implementation of disinfection protocol is my responsibility9958.90%2155.30%ns7666.10%4448.40%6.57(0.010)11160.00%942.90%ns
Table 5. Differences dental office characteristics in dentistry equipment and water quality practices.
Table 5. Differences dental office characteristics in dentistry equipment and water quality practices.
General Dentistryχ2(p)Clinic vs. Private Practiceχ2(p)Family Incomeχ2(p)
NoYesNoYesEUR < 25.000 25.001–50.000 €EUR > 50.000
n%n%n%n%n%n%n%
Equipment age0–5 years1224.00%3119.90%ns3019.90%1323.60%16.12 (0.001)1927.50%1112.20%1057.50%ns
6–10 years1326.00%2817.90%2113.90%2036.40%1217.40%1718.90%1130.30%
11–20 years1734.00%7145.50%7046.40%1832.70%3043.50%4448.90%1130.30%
21 and above816.00%2616.70%3019.90%47.30%811.60%1820.00%715.20%
Has assistant3978.00%5837.20%25.32 (<0.001)5033.10%4785.50%44.26 (<0.001)2231.90%4550.00%2766.70%14.36 (<0.001)
Performs microbiological test1326.00%3220.50%ns3321.90%1221.80%ns1724.60%1314.40%1456.10%7.60 (0.022)
Continuous water supply system to dental unit1530.00%4730.10%ns4127.20%2138.20%ns1623.20%2628.90%1848.50%6.38 (0.041)
Antiseptic to the handpieces (auto)613.60%118.00%ns86.10%918.40%6.36 (0.012)814.00%33.80%616.10%6.21 (0.045)
Antiseptic to the handpieces (manually)24.50%2417.50%4.56 (0.033)1914.40%714.30%ns915.80%1012.50%616.10%ns
Clean suctiotion
Large Small
between two patients2145.70%6945.40%ns6344.10%2749.10%ns2740.30%3946.40%045.50%23.24 (0.010)
every few appointments 36.50%2717.80%2416.80%610.90%1319.40%910.70%118.20%
per day1328.30%4026.30%3826.60%1527.30%1319.40%3035.70%515.20%
per week or more919.5%1610.6%1812.6%712.7%1420.9%67.2%612.1%
between two patients48.50%117.40%11.64 (0.040)85.60%713.00%ns69.10%33.60%86.10%ns
every few appointments 36.40%2114.10%149.90%1018.50%913.60%1214.30%19.10%
per day2451.10%6040.30%6143.00%2342.60%2030.30%3845.20%063.60%
per week or more1634.00%5738.30%5941.50%1425.90%3147.00%3137.00%838.00%
Micromotors1918.00%4226.90%ns4630.50%59.10%31.40 (<0.001)2333.30%2022.20%1518.20%24.39 (0.002)
21938.00%5032.10%5838.40%1120.00%2029.00%3943.30%324.20%
3510.00%1912.20%1610.60%814.50%913.00%1213.30%119.10%
448.00%2113.50%159.90%1018.20%811.60%88.90%415.20%
5+1326.00%2415.40%1610.60%2138.20%913.00%1112.20%033.30%
Airotors11020.00%1912.20%ns2415.90%59.10%22.04 (<0.001)1318.80%1314.40%26.10%ns
21632.00%4730.10%5335.10%1018.20%2333.30%2831.10%130.30%
3612.00%2113.50%2315.20%47.30%913.00%1516.70%143.00%
4510.00%2012.80%1912.60%610.90%913.00%1011.10%615.20%
5+1326.00%4931.40%3221.20%3054.50%1521.70%2426.70%645.50%
Has implantology motor1734.70%6038.50%ns4832.00%2952.70%7.37 (0.007)2841.20%2831.10%045.50%ns
Has amalgam trap2552.10%10368.70%4.38 (0.038)9062.50%3870.40%ns4671.90%5461.40%3862.50%ns
Has contract for amalgam removal1021.70%4128.10%ns3222.70%1937.30%4.07 (0.044)1627.10%2123.90%2034.40%ns
Money Spent<25 EUR/month1122.00%3321.20%3724.50%712.70%2130.40%1820.00%512.10%
25–50 EUR/month1836.00%7145.50%7348.30%1629.10%3043.50%4246.70%830.30%
50–75 EUR/month918.00%2918.60%2415.90%1425.50%1014.50%1415.60%336.40%
>75 EUR/month918.00%1811.50%127.90%1527.30%68.70%1213.30%118.20%
Implementation of disinfection protocol is my responsibility1938.00%10164.70%11.14 (<0.001)10468.90%1629.10%26.24 (<0.001)4971.00%4752.20%054.50%6.26 (0.044)
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Antoniadou, M.; Intzes, A.; Kladouchas, C.; Christou, I.; Chatzigeorgiou, S.; Plexida, M.; Stefanidakis, V.; Tzoutzas, I. Factors Affecting Water Quality and Sustainability in Dental Practices in Greece. Sustainability 2023, 15, 9115. https://doi.org/10.3390/su15119115

AMA Style

Antoniadou M, Intzes A, Kladouchas C, Christou I, Chatzigeorgiou S, Plexida M, Stefanidakis V, Tzoutzas I. Factors Affecting Water Quality and Sustainability in Dental Practices in Greece. Sustainability. 2023; 15(11):9115. https://doi.org/10.3390/su15119115

Chicago/Turabian Style

Antoniadou, Maria, Anestis Intzes, Christos Kladouchas, Iliana Christou, Stavroula Chatzigeorgiou, Martha Plexida, Valantis Stefanidakis, and Ioannis Tzoutzas. 2023. "Factors Affecting Water Quality and Sustainability in Dental Practices in Greece" Sustainability 15, no. 11: 9115. https://doi.org/10.3390/su15119115

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