102 research outputs found

    Amorphous Calcium Phosphate as Bioactive Filler in Polymeric Dental Composites

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    As biocompatible and osteo-inductive precursor to biological apatite formation, amorphous calcium phosphate (ACP) resorbs at the rate that closely coincides with the rate of new bone formation and is more osteo-conductive than its crystalline counterpart. In addition, in the oral environment, ACP intrinsically provides a protracted supply of the remineralizing calcium and phosphate ions needed for regeneration of mineral lost to tooth decay. These features make ACP composites a strong remineralizing tool at the site of caries attack. Our group has been on the forefront of the research on bioactive, remineralizing, polymeric ACP-based dental materials for over two decades. This entry describes methods for filler, polymer, and composite fabrication and a battery of physicochemical and biological tests involved in evaluation of ACP-based restoratives. Also presented is our most recent design of ACP remineralizing composites with added antimicrobial capability that shows promise for extended dental and, potentially, wider biomedical applications

    Ultrasonography of salivary glands in primary Sjögren's syndrome: A comparison with contrast sialography and scintigraphy

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    Objective. To compare ultrasonography (US) of salivary glands with contrast sialography and scintigraphy, in order to evaluate the diagnostic value of this method in primary SS (pSS). Methods. The diagnostic value of parotid gland US was studied in 77 patients with pSS (male/female ratio 3/74; mean age 54 yrs) and in 79 with sicca symptoms but without SS. The two groups were matched for sex and age. Imaging findings of US were graded using an ultrasonographic score ranging from 0 to 16, which was obtained by the sum of the scores for each parotid and submandibular gland. The sialographic and scintigraphic patterns were classified in four different stages. The area under receiver operating characteristic curve (AUC-ROC) was employed to evaluate the screening methods performance. Results. Of the 77 patients with pSS, 66 had abnormal US findings. Mean US score in pSS patients was 9.0 (range from 3 to 16). Subjects without confirmed pSS had the mean US score 3.9 (range from 0 to 9) (P < 0.0001). Results of sialography showed that 59 pSS patients had abnormal findings at Stage 1 (n = 4), Stage 2 (n = 8), Stage 3 (n = 33) or Stage 4 (n = 14), and 58 patients had abnormal scintigraphic findings at Stage 1 (n = 11), Stage 2 (n = 18), Stage 3 (n = 25) or Stage 4 (n = 4). Through ROC curves US arose as the best performer (AUC = 0.863 +/- 0.030), followed by sialography (AUC = 0.804 +/- 0.035) and by salivary gland scintigraphy (AUC = 0.783 +/- 0.037). The difference between AUC-ROC curve of salivary gland US and scintigraphy was significant (P = 0.034). Setting the cut-off score 6 US resulted in the best ratio of sensitivity (75.3%) to specificity (83.5%), with a likelihood ratio of 4.58. If a threshold 8.0 was applied the test gained specificity, at the cost of a serious loss of sensitivity (sensitivity 54.5%, specificity 97.5%, likelihood ratio 21.5). Conclusions. Salivary gland US is a useful method in visualizing glandular structural changes in patients suspected of having pSS and it may represent a good option as a first-line imaging tool in the diagnostics of the disease

    Detection of Emerging and Re-Emerging Pathogens in Surface Waters Close to an Urban Area

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    Current knowledge about the spread of pathogens in aquatic environments is scarce probably because bacteria, viruses, algae and their toxins tend to occur at low concentrations in water, making them very difficult to measure directly. The purpose of this study was the development and validation of tools to detect pathogens in freshwater systems close to an urban area. In order to evaluate anthropogenic impacts on water microbiological quality, a phylogenetic microarray was developed in the context of the EU project µAQUA to detect simultaneously numerous pathogens and applied to samples from two different locations close to an urban area located upstream and downstream of Rome in the Tiber River. Furthermore, human enteric viruses were also detected. Fifty liters of water were collected and concentrated using a hollow-fiber ultrafiltration approach. The resultant concentrate was further size-fractionated through a series of decreasing pore size filters. RNA was extracted from pooled filters and hybridized to the newly designed microarray to detect pathogenic bacteria, protozoa and toxic cyanobacteria. Diatoms as indicators of the water quality status, were also included in the microarray to evaluate water quality. The microarray results gave positive signals for bacteria, diatoms, cyanobacteria and protozoa. Cross validation of the microarray was performed using standard microbiological methods for the bacteria. The presence of oral-fecal transmitted human enteric-viruses were detected using q-PCR. Significant concentrations of Salmonella, Clostridium, Campylobacter and Staphylococcus as well as Hepatitis E Virus (HEV), noroviruses GI (NoGGI) and GII (NoGII) and human adenovirus 41 (ADV 41) were found in the Mezzocammino site, whereas lower concentrations of other bacteria and only the ADV41 virus was recovered at the Castel Giubileo site. This study revealed that the pollution level in the Tiber River was considerably higher downstream rather than upstream of Rome and the downstream location was contaminated by emerging and re-emerging pathogens

    Lack of WHV integration nearby N-myc2 and in the downstream b3n and win loci in a considerable fraction of liver tumors with activated N-myc2 from naturally infected wild woodchucks

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    In liver tumors induced by chronic WHV infection in the WHV/woodchuck model of HBV infection, activation of genes of the myc family by WHV insertion has been well documented. Several studies have shown that N-myc2 is by far the most frequently involved, and in most cases, its transcriptional activation is due to WHV insertion nearby the gene. N-myc2 has been shown to be also activated by WHV insertion in two downstream loci, b3n and win. Although the extent of insertion in these latter loci in woodchuck tumors has not been investigated, their discovery has led to the notion that therein WHV insertion accounts for N-myc2 activation in the remaining tumors expressing the proto-oncogene in absence of any detectable alteration nearby the gene, a notion remained unproved and not further investigated yet. In the majority of cases, the above observations were derived from tumors developed in colony born laboratory bred woodchucks experimentally infected with standardized viral inocula, mostly of the same lineage. In the present work, we investigated a survey of liver tumors naturally developed in wild woodchucks with naturally acquired chronic WHV infection. Tumors had histological features of well to moderately differentiated HCCs. In most animals, multiple tumor nodules were observed; in the great majority of cases, they were shown to be independent tumors because their WHV integration patterns were not clonally related. 53 independent tumors were investigated for N-myc activation and WHV integration nearby N-myc genes and in the b3n and win loci. Comparison of our results with data from previous studies revealed that, in tumors from naturally infected wild woodchucks, the frequency of WHV integration nearby N-myc2 has a tendency to be lower and, in addition, N-myc2 activation is due to WHV integration nearby the gene significantly less frequently than in tumors from experimentally infected colony born animals (12/28, 43% vs. 15/20, 75%, P = 0.0397). These findings are likely related to the less uniform conditions as to infecting virus and host genetic background in naturally infected wild woodchucks with respect to experimentally infected colony born woodchucks and suggest that viral and/or host factors may influence the site of viral insertion finally detected in overt tumors. In addition, more than one third (11/28, 39%) tumors with activated N-myc2 transcription did not show rearrangement either nearby the gene, or in b3n or in win. These findings challenge the notion that integration in the downstream b3n and win loci is responsible for N-myc2 activation in tumors lacking insertion nearby N-myc2 and suggest that in a considerable fraction of liver tumors, at least from wild woodchucks, N-myc2 activation might be due either to WHV integration in further regions of the N-myc2 chromosomal domain or to other mechanisms related or unrelated to viral insertion
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