ABSTRACT
Abstract The desire of individuals to have whiter teeth increases the interest in tooth whitening products. Our aim was to in vitro study the whitening effect of hydrogen peroxide, blue covarine and active charcoal containing whitening toothpastes on human teeth. A total of 40 extracted human incisor teeth were used in the study. To measure the whitening effect of toothpastes, the teeth were divided into four subgroups and placed in the phantom tooth jaw model. Then, daily brushing was done with an electric toothbrush. The colors of the teeth were measured initially using the spectrophotometer (single point and bleached shade mode) and at the end of 7th, 14th and 28th days. Whitening effectiveness of toothpastes were studied according to CIEDE2000 formula (ΔE00) and shade guide units (SGU). One- way analysis of variance (ANOVA) and Tukey test were used in the statistical analysis of the data. (p0.05). Blue covarine containing toothpaste had statistically the lowest whitening effect (p<0.05). All toothpastes showed a whitening effect on the teeth after 7 days of use. Activated charcoal containing toothpaste showed more whitening effect after 28 days of use than hydrogen peroxide, blue covarine and traditional toothpaste.
Resumen El deseo de los individuos de tener unos dientes más blancos aumenta el interés por los productos de blanqueamiento dental. Nuestro objetivo fue estudiar el efecto blanqueador de las pastas dentales blanqueadoras que contienen peróxido de hidrógeno, covarina azul y carbón activo en dientes humanos in vitro. En el estudio se utilizaron un total de 40 dientes incisivos humanos extraídos. Para medir el efecto blanqueador de los dentífricos, los dientes se dividieron en cuatro subgrupos y se colocaron en el modelo de diente fantasma en mandíbula. A continuación, se realizó un cepillado diario con un cepillo eléctrico. El color de los dientes se midió inicialmente con un espectrofotómetro (modo de punto único y tono blanqueado) y al final de los días 7, 14 y 28. Se estudió la eficacia blanqueadora de los dentífricos según la fórmula CIEDE2000 (ΔE00) y las unidades de guía de color (SGU). En el análisis estadístico de los datos se utilizó el análisis de varianza de una vía (ANOVA) y la prueba de Tukey. (p0,05). El dentífrico que contiene covarina azul tuvo estadísticamente el menor efecto blanqueador (p<0,05). Todos los dentífricos mostraron un efecto blanqueador en los dientes después de 7 días de uso. Los dentífricos con carbón activado mostraron un mayor efecto blanqueador tras 28 días de uso que el peróxido de hidrógeno, la covarina azul y el dentífrico tradicional.
Subject(s)
Tooth Bleaching , Dentifrices , Hydrogen Peroxide/analysisABSTRACT
Objective@#To investigate the effects of two different sorbents(Carbon perfusion apparatus and Resin perfusion apparatus)in Double plasma molecular absorb syetem for liver failure treatment.@*Methods@#A total of 152 cases with liver failure who were admitted to The Sixth People's Hospital of Zhengzhou, from June 2016 to May 2018 were selected and divided into DPMARS Carbon group (77 cases) and Resin group (75 cases). The two groups were observed in terms of liver function, prothrombin activity(PTA),Plasma albumin ,tumor necrosis factor alpha and interleukin-6 were detected and compared between the two groups before and after treatment.@*Results@#①The clinical symptoms improved in different degree in two groups, the recovery rate of Carbon cans Carbon perfusion apparatus group and Resin group separately were89.6% (69/77)、90.7% (68/75)(χ2 = 0.048, P = 0.975), there were no statistical differences. There were no statistical differences between the two groups in untoward reactions(χ2 = 0.235, P = 0.995), ②Compared with before treatment, TBil(t = 3.735, 3.728; P = 0.000, 0.000)、ALT(t = 5.117, 5.203; P = 0.000, 0.000)、TNF-α (t = 3.158, 3.094; P = 0.000, 0.002)、IL-6(t = 3.647, 3.559; P = 0.002, 0.003)decreased and ALB (t = 2.300, 3.065; P = 0.024, 0.003) increased significantly after treatment in both groups, and there were statistical differences. There were no signifiant differences in the changes in ALB(t = 0.316, 0.209; P = 0.657, 0.720) and PTA(t = 0.810, 0.843; P = 0.429, 0.516). ③After treatment, there were no signifiant differences in the changes in TBil、ALT、ALB、PTA、TNF-α、IL-6(t = 0.377、0.904、-1.133、-1.552、0.841、0.401; P = 0.952、0.283、0.826、0.094、0.154、0.457).@*Conclusion@#Double plasma molecular absorb syetem is effective in treating liver failure. Carbon perfusion apparatus or Resin perfusion apparatus can be combined with Specific bilirubin adsorption column for DPMARS in clinical treatment,and their effects are similar.
ABSTRACT
Objectives: Radon (222Rn) is a noble gas and a component of water in many hot spring spas. The Hot Springs Law and the Guideline of Analytical Methods of Mineral Springs (revised edition) of Japan classify springs containing 74 Bq/kg or more of radon as “hot springs” and those with radon levels exceeding 111 Bq/kg as “medical springs”, also called “radioactive springs”. Komono Town, one of the foremost spa and health resort destinations in Mie Prefecture, is the site of many radioactive springs. For the purpose of regional vitalization of this area through radioactive springs, it is necessary to confirm the safety and effectiveness of their use. To evaluate the exposure dose due to radioactive spring usage, it is important to measure radon concentration in air, especially in high-humidity air such as in bathing rooms. Methods: The concentration of radon in air was analyzed using an activated charcoal detector (PICO-RAD; AccuStar Labs) with a desiccant (Drierite; 8-mesh anhydrous calcium sulfate; W.A. Hammond Drierite Company, Ltd.) and a liquid scintillation counter (LSC LB-5; Hitachi Aloka Medical, Ltd.). A DPO (2,5-diphenyloxazole) + POPOP (1,4-bis- (5-phenyl-2-oxazolyl)-benzene) toluene solution (Wako Pure Chemical Industries, Ltd.) was used as a liquid scintillator. Activated charcoal detectors were set up in and around the radioactive spring facilities. Results and Discussion: In a radioactive spring facility, radon concentration in air in the bathing room and changing room were relatively high at about 50 Bq/m3. In the corridor on all floors and at the entrance, these values were approximately 10-30 Bq/m3, indicating that radon in hot spring water diffuses into the air and spreads within the facility. Outdoors, radon concentration was 12.5 Bq/m3 at a campsite near the discharge point of the radioactive spring. Exposure dose is calculated under the assumption of a two-day stay, during which the visitor will use the bath for several hours. The results obtained show that the exposure dose at the hot spring facility is lower than the exposure dose from daily environmental radiation or medical devices. These conclusions are considered sufficient to confirm the safety of the hot spring facility.
ABSTRACT
<b>Objectives:</b> Radon (<sup>222</sup>Rn) is a noble gas and a component of water in many hot spring spas. The Hot Springs Law and the Guideline of Analytical Methods of Mineral Springs (revised edition) of Japan classify springs containing 74 Bq/kg or more of radon as “hot springs” and those with radon levels exceeding 111 Bq/kg as “medical springs”, also called “radioactive springs”. Komono Town, one of the foremost spa and health resort destinations in Mie Prefecture, is the site of many radioactive springs. For the purpose of regional vitalization of this area through radioactive springs, it is necessary to confirm the safety and effectiveness of their use. To evaluate the exposure dose due to radioactive spring usage, it is important to measure radon concentration in air, especially in high-humidity air such as in bathing rooms.<BR><b>Methods:</b> The concentration of radon in air was analyzed using an activated charcoal detector (PICO-RAD; AccuStar Labs) with a desiccant (Drierite; 8-mesh anhydrous calcium sulfate; W.A. Hammond Drierite Company, Ltd.) and a liquid scintillation counter (LSC LB-5; Hitachi Aloka Medical, Ltd.). A DPO (2,5-diphenyloxazole) + POPOP (1,4-bis- (5-phenyl-2-oxazolyl)-benzene) toluene solution (Wako Pure Chemical Industries, Ltd.) was used as a liquid scintillator. Activated charcoal detectors were set up in and around the radioactive spring facilities. <BR><b>Results and Discussion:</b> In a radioactive spring facility, radon concentration in air in the bathing room and changing room were relatively high at about 50 Bq/m<sup>3</sup>. In the corridor on all floors and at the entrance, these values were approximately 10-30 Bq/m<sup>3</sup>, indicating that radon in hot spring water diffuses into the air and spreads within the facility. Outdoors, radon concentration was 12.5 Bq/m<sup>3</sup> at a campsite near the discharge point of the radioactive spring.<BR> Exposure dose is calculated under the assumption of a two-day stay, during which the visitor will use the bath for several hours. The results obtained show that the exposure dose at the hot spring facility is lower than the exposure dose from daily environmental radiation or medical devices. These conclusions are considered sufficient to confirm the safety of the hot spring facility.