Weanling rats were fed diets containing raw lyophylized hand-deboned shank beef (HDS) supplemented with CaCO3, retorted lyophylized mechanically deboned shank beef (MDS), or raw lyophylized MDS. Ca in the latter two diets originated from bone during the mechanical deboning process. Ca absorption, Ca retention, bone weight, and bone breaking strength were similar for comparative dietary levels of Ca regardless of the source. Bone ash and Ca content was significantly higher (P < .05) in the MDS 393 (3.93 g Ca/kg diet) diet and in the retorted MDS 460 diet compared with the HDS 488 diet. Relative biological values for the MDS diets calculated relative to the HDS diets ranged from 102 to 132 when the linear regression of Ca consumed, Ca retained, or dietary Ca level vs bone ash or bone Ca content was obtained. The retorted MDS 460 diet contained the highest Fe level and exhibited a lower percent absorption, terminal hemoglobin level, and liver Fe storage. Humerus F content increased as dietary F (also present from bone) level increased. Dietary F level did not determine humerus breaking strength.

A thesis submitted to the College of Dental Medicine of Nova Southeastern University of the degree of Master of Science in Dentistry. Objectives: To determine the amount of initial fluoride release from four orthodontic bonding systems over a period of four weeks, and then to subject these materials to an external source of fluoride for recharge in order to measure the amount of fluoride re-release over another four-week interval. Additionally the surface morphology of these materials was analyzed under the scanning electron microscope in order to identify microscopic changes in the materials that may have occurred during the experiment. Methods: Four orthodontic adhesives: Fuji Ortho LC (GC America, Alsip, IL), Transbond XT (3M Unitek, Monrovia, CA), Illuminate Light Cure (Ortho Organizers, Carlsbad, CA), and Opal Seal with Opal Bond MV (Ultradent, South Jordan, UT), n=120 (30/material) were tested for fluoride release at 1 hour, 24 hours, 3 days, 1 week, 2 weeks, 3 weeks and 4 weeks. Samples (10/subgroup/material) were then recharged with an external source of fluoride (toothpaste, foam, or varnish), and retested for fluoride re-release at 1 hour, 24 hours, 3 days, 1 week, 2 weeks, 3 weeks and 4 weeks. The scanning electron microscope was utilized in order to assess each material's surface morphology before testing and after completion of the experiment (n=16). Descriptive statistics, means and standard deviations were calculated for all four materials and their subgroups at each time interval. A mixed model two-way ANOVA was run, using a level of significance of 0.05. Bonferroni multiple comparison tests were conducted using if groups were found to be statistically significantly different. To determine significant differences between fluoride release and re-release for each recharge subgroup within each material group, paired t-tests were performed for the time intervals of 24 hours, 2 weeks, and 4 weeks. For the paired t-tests, the level of significance used was 0.02 to allow for Bonferroni correction. Results: During the initial 24 hours the fluoride measurements (in mg/L or ppm) were as follows: Fuji 9.78±0.65, Illuminate 7.83±1.49, Opal 0.05±0.02, and Transbond 0.01±0.0. At the initial four weeks time point, the readings were as follows: Fuji 6.68±0.79, Illuminate 3.82±1.84, Opal 0.06±0.01, and Transbond 0.01±0.01. The greatest fluoride release came from the varnish subgroups from each of the materials at 2 weeks post re-charge: Fuji 9.16±1.53, Illuminate 7.5±3.1 (tied with foam subgroup 7.5±4.4), Opal 5.3±2.45, and Transbond 3.75±1.67. The greatest fluoride measurement for each material at the final week post-recharge was: Fuji varnish subgroup 8.3±3.58, Illuminate foam subgroup 6.5±3.5, Opal varnish subgroup 2.50±1.1, and Transbond varnish subgroup 1.72±1.82. SEM results showed an observable difference between the materials pre-experiment and post-experiment at a magnification of 50X and 500X. The Fuji foam and paste subgroups displayed surface crackling patterns at both magnifications when compared to the control and varnish samples. The Illuminate control, foam, and paste specimens all had a roughened grainy appearance, while the varnish specimen seemed to be smoothed over by the varnish material. The Transbond samples appeared to have observable differences in surface morphology at 50X, but not at 500X. The Opal paste and foam specimens appeared to have a smoother surface than both the control and the varnish samples. Conclusions: There were significant differences in release and re-release of fluoride among all four adhesives at different time intervals over a period of eight weeks. Significant increase in fluoride re-release was seen for all three of the recharge subgroups for both Opal and Transbond at each time interval. A significant increase in fluoride re-release for the Illuminate group was mainly observed at the end of second and fourth week. Though no significant increase in fluoride re-release was observed, Fuji released highest amount of fluoride during release and re-release, at all different time intervals. Fluoride varnish was the superior recharge material, as it provided the greatest fluoride measurements, followed by foam and toothpaste. There were observable changes in the surface morphology of the materials pre-experiment and post-experiment at a magnification of 50X and 500X, which may have an affect on the fluoride releasing capabilities of the materials.

Indiana University-Purdue University Indianapolis (IUPUI) / Dental biofilm is a main contributing factor in the initiation and progression of dental caries. The maturation of dental biofilms is expected to alter the anti-caries efficacy of fluoride compounds. In the first aim, we conducted a series of modeldevelopment experiments to test different variables to standardize a reproducible in-vitro microbial caries model. We evaluated: surface conditioning using saliva; sucrose concentrations and caries lesion severity; growth media conditions and mineral saturation; dental substrate types; pH cycling protocol characteristics. In the second aim, we used the developed model to evaluate the changes in the anti-caries efficacy of three fluoride compounds (Sodium fluoride (NaF); Stannous fluoride (SnF2); Amine fluoride (AmF); and deionized water (DIW- negative control)) at increasing maturation of a microcosm biofilm. We continued the pH cycling protocol for 4 days, 8 days, and 12 days. We tested biofilm cariogenicity and carious lesion severity at each maturation stage. In the third aim, we used the developed model to test the effect of different exposure periods (early vs. late exposure) of the biofilm to three fluoride compounds (NaF, SnF2, AmF, DIW) in comparison to DIW. We also evaluated the recovery of biofilm cariogenicity with each exposure period. We evaluated, for each exposure period and recovery stage, biofilm cariogenicity and carious lesion severity. We analyzed the relationships between different variables (biofilm age, fluoride compound type, exposure period) using ANOVA models. In conclusion: 1. The present model allows testing the effect of biofilm maturation on the anti-caries efficacy of fluoride compounds. 2. Biofilm maturation plays an important role in increasing biofilm tolerance against fluoride treatment; it could also influence the selection of fluoride compounds to achieve optimum cariostatic effect. 3. Exposure period, and type of fluoride compound, both influence the biofilm tolerance to fluoride anti-caries effect; they may also result in a sustainable release of fluoride over time. / 2021-08-21

京都大学 / 0048 / 新制・課程博士 / 博士(地球環境学) / 甲第19419号 / 地環博第145号 / 新制||地環||29(附属図書館) / 32444 / 京都大学大学院地球環境学舎環境マネジメント専攻 / (主査)教授 藤井 滋穂, 教授 高岡 昌輝, 准教授 田中 周平 / 学位規則第4条第1項該当 / Doctor of Global Environmental Studies / Kyoto University / DFAM

No description available.

Aim: The aim of this study was to investigate if there is a beneficial effect on the prevalence of white spot lesions (WSL) in the mandibular and maxillary teeth when the teeth in the maxilla are treated with fluoride varnish compared to a placebo group. The null hypothesis was that there is no difference between the test and placebo group in development of WSL. Material and Method: 182 patients from three clinics in Scania county (Sweden) undergoing treatment with fixed orthodontic appliances were selected to participate, in the end 149 patients were included in the study. The patients were divided into two groups, one receiving a varnish of 7700 ppm fluoride (Fluor Protector S, Ivoclar Vivadent AG, Schaan, Liechtenstein) and one a placebo varnish. Pre- and post-treatment photos were taken and WSL was graded according to Gorelick index by two independent observers.  Results: No significant difference could be seen between the test and placebo group, neither on surface nor individual level. The results were based on both t-test and percentual calculations.  Conclusion: The null hypothesis could be accepted since no significant difference could be seen between the test or placebo group. Due to the loss of a number of patients, mainly because of loss in the original study and new exclusion criteria set by the authors, the results may have been conflicted. More research is therefore needed to draw any conclusions. / Syfte: Syftet med studien var att undersöka om det finns en effekt på förekomsten av white spot lesions (WSL) hos under- och överkäkens tänder när tänderna i överkäken behandlas med fluoridvarnish. Nollhypotesen sattes till att det inte finns någon skillnad mellan test- och placebogruppen i prevalens av WSL. Material och metod: Patienter från tre olika kliniker i Skåne deltog i studien, 149 av 182 deltagare fullföljde studien. Patienterna delades in i två grupper, en som fick ett fluoridvarnish med 7700 ppm fluorid (Fluor Protector S, Ivoclar Vivadent AG, Schaan, Liechtenstein) och en med placebovarnish. Kliniska foton togs innan samt efter behandling med fast apparatur som graderades och bedömdes enligt Gorelick-skalan för WSL av två oberoende observatörer. Resultat: Det fanns ingen signifikant skillnad mellan testgruppen och placebogruppen varken på individ- eller ytnivå. Resultatet baserades på både t-test och procentberäkningar. Slutsats: Nollhypotesen accepterades då ingen signifikant skillnad fanns mellan test- och placebogrupp. På grund av bortfall av patienter, både i originalstudien men även med anledning av exklusionskriterier satta för denna studie, kan resultatet ha påverkats. Mer forskning behövs därför för att dra några slutsatser.

Water pollution represents one of the major concerns of the modern world, after scientific and industrial development that generates hazardous organic and inorganic contaminants. Biochar (BC) has gained tremendous attention in the past decade as a cheap and efficient adsorbent for organic and inorganic contaminants from aqueous solutions. BC is considered to be a low-cost alternative to activated carbon, however, BC typically suffer performance reductions due to their low surface areas and poor mechanical properties. The main objective of this work is to develop novel biochar materials by modifying the biochar surface for the removal of organic and inorganic contaminants from water. In recent years, biochar modifications involving various methods such as, acid/base treatment, impregnation of mineral sorbents, functional groups incorporation, steam activation and magnetic modification have been widely studied. Chapter I summarizes these biochar modification methods. In Chapter II, Chitosan-Modified fast pyrolysis BioChar (CMBC) was used to remove Pb2+ from water. CMBC was made by mixing pine wood biochar with a 2% aqueous acetic acid chitosan (85% deacylated chitin) solution followed by treatment with NaOH. CMBC removed more Pb2+ than non-modified biochar suggesting that modification with chitosan generates amine groups on the biochar surface which enhance Pb2+ adsorption. Chapter III describes the fast nitrate and fluoride adsorption and magnetic separation from water on iron oxide particles dispersed on Douglas Fir biochar. Nitrate and fluoride adsorption occurred by electrostatic attraction over the wide 2 to 10 pH range. In the chapter IV, aniline and nitrobenzene removal from water was studied using magnetized and nonmagnetized Douglas Fir biochar. The adsorption of aniline and nitrobenzene occurred mainly through pi-pi electron interactions over the wide 2 to 12 pH range and H-bonding. The surface morphology, chemistry, and composition of the modified biochars were examined by SEM, SEM-EDX, TEM, PZC, XPS, XRD, FTIR, TGA, DSC, elemental analysis, and surface area measurements.

Amphiphilic block copolymers based on poly(ethylene glycol) (PEG) and poly(vinylidene fluoride) (PVDF) were synthesized by RAFT polymerization. The commercial poly(ethylene glycol) methyl ether (Me-PEG-OH, 20 Kg/mol) and difunctional polyethylene glycol (OH-PEG-OH, 20 Kg/mol) were used to synthesize diblock copolymers (Me-PEG-b-PVDF), and triblock copolymers (PVDF-b-PEG-b-PVDF) respectively. For the synthesis, the esterification reaction followed by the SN2 reaction was employed to make macro CTA (Me-PEG-XA, XA-PEG-XA, XA refers to the xanthate group). The macro CTAs were used further for VDF polymerization in dimethyl carbonate (DMC) inside the autoclave. Different molecular weights of the PVDF block (whether in the diblocks or the tribolcks) were obtained based on changes in the reaction time. The resulting block copolymers were molecularly characterized by FT-IR, 1H,19F-NMR, and SEC. The thermal properties were studied by DSC and TGA. Furthermore, the crystalline phase characterization was investigated by XRD and FT-IR. Being the obtained block copolymers are amphiphilic, their self-assembly was achieved by nanoprecipitation in DMF/water, and they were analyzed by DLS and TEM.

Surface treatment processes of stainless steel, such as pickling, produces acidic waste water consisting of Na⁺, Cl⁻, F⁻, NO⁻3, SO42-, PO43-, Fe3+, Cr6+ and Ni2+. At Sandvik ABs steel works in Sandviken, this waste water is treated and neutralized using slaked lime before being released into the lake Storsjön. The aim of this report was to make a literary review of previous work in using slag as a neutralizing agent for acidic waste water. Furthermore, to see if it’s possible to replace some or all of the slaked lime in the neutralization process with slag and to study what slag that might be suitable to use. Since the waste water contains HF acid, the focus of this report was on different materials used for fluoride adsorptions. The literary study showed that the fluoride adsorption process with BOF slag, quick lime and magnesium oxide as adsorbents were endothermic. Therefore, it benefitted from an increased temperature. Furthermore, the literature study showed that many materials follow a pseudo-second-order kinetic model as well as a Langmuir or Freundlich isotherm for a fluoride adsorption. A previous experiment showed that a mixture of BF slag and slaked lime had the best HF acid neutralization among the tested materials. A fluoride adsorption experiment was made at different temperatures (25 – 55 °C) by using a slag from an aluminium reduced steel melt and a slag from a silicon reduced steel melt from the AOD converter in Sandviken. The silicon reduced steel melt slag showed an increase of fluorides in the solution, due to the presence of calcium fluoride in the slag. This was observed for all temperatures. The aluminium reduced steel melt slag also increased the fluoride content in the solution at 25 and 30 °C. At higher temperatures the fluoride content in the solution decreased with 93.6 to 94.9 %. Na⁺, Cl⁻, F⁻, NO⁻3, SO42-, PO43-, Fe3+, Cr6+, and Ni2+

Thesis advisor: Jia Niu / O-Sulfation is an important chemical code existing widely in nature, participating in a variety of biological activities including immune response, hemostasis, hormone regulation, cell signaling, and viral invasion. The heterogeneous nature, high polarity with negative charge, and the chemical lability of the sulfate modification have created significant challenges in the synthesis and structure-function studies of O-sulfated biomolecules. It is therefore highly desirable to achieve caging and selective release of the O-sulfated biomolecules. Inspired by sulfur (VI) fluoride exchange reaction, our group developed a series of general approaches to caged O-sulfated biomolecules and their selective deprotection. First, an O-sulfation strategy is developed by coupling aromatic fluorosulfate with silylated target molecules. Scalable synthesis was demonstrated on monosaccharides, disaccharides, amino acid, and steroid. Selective hydrolytic and hydrogenolytic removal of the aryl masking groups yielded the corresponding O-sulfated products in excellent yields. Furthermore, a complete knowledge gap was noted in biocompatible caging of sulfate. With the rational design and systematic optimizations, we discovered that fluorosulfotyrosine in peptides and proteins was an ideal precursor for sulfotyrosine (sY), which can be efficiently converted into the anionic active form by hydroxamic acid activators under physiologically relevant conditions. Photocaging the hydroxamic acid activators further allowed for light-controlled activation of functional sulfopeptides. This system featuring fast kinetics, high selectivity, excellent robustness, and on-demand release provides a valuable tool for probing functional roles of sulfation in the peptides and proteins. / Thesis (PhD) — Boston College, 2023. / Submitted to: Boston College. Graduate School of Arts and Sciences. / Discipline: Chemistry.