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81.
M. L. Ng  J. A. Hargreaves 《CMAJ》1984,130(7):851-853
To investigate the present status of nutrition education for dentists and physicians in Canada, we conducted a survey of the nutrition education programs in 10 Canadian dental and 16 medical schools in the academic year 1982-83. Seven of the dental schools and seven of the medical schools had a separate course in nutrition. The average duration of these courses was 22 hours for the dental schools and 26 hours for the medical schools. Nutrition education was integrated with another discipline in 4 of the dental schools and 11 of the medical schools. The average duration of this type of instruction was 14 hours for the dental schools and 18 hours for the medical schools. Six of the dental schools and eight of the medical schools employed a nutritionist/dietitian to provide instruction in nutrition. We recommend that courses in basic and applied clinical nutrition be incorporated throughout the curricula of Canadian dental and medical schools, and that personnel trained in clinical nutrition be employed to provide instruction in this area.  相似文献   
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OBJECTIVE: To assess the attendance, outcome, compliance with treatment, and response to interferon alfa in patients with chronic hepatitis C who attended during 1995 and were treated according to a biopsy based algorithm. DESIGN: Retrospective audit of all patients with chronic hepatitis C attending outpatient clinics over one year. SETTING: The liver unit at a London teaching hospital. SUBJECTS: 255 patients with chronic hepatitis C. MAIN OUTCOME MEASURES: Patient survival, attendance, and compliance with diagnostic and therapeutic regimens. Response to interferon alfa treatment, based on loss of viraemia three months after cessation of treatment. RESULTS: A large proportion of patients (39%) with newly diagnosed chronic hepatitis C infection do not want to undergo further investigation. Of those patients who do attend for further treatment, a large proportion with severe hepatic fibrosis (42%) do not want to undergo currently available treatment. The response rate to interferon (21%) in treated patients was similar to that previously reported in a trial setting. There was no significant difference in response rates in patients with or without severe fibrosis not amounting to cirrhosis. In patients with cirrhosis there was a high incidence of hepatocellular carcinoma (18%) over a follow up period of 20 months. CONCLUSION: Current strategies aimed at investigating and treating patients with chronic hepatitis C are not acceptable to a large proportion of patients. Many patients with cirrhosis related to hepatitis C infection develop hepatic neoplasms, and management strategies to deal with this problem are urgently required.  相似文献   
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Prophages are encoded in most genomes of sequenced Clostridium difficile strains. They are key components of the mobile genetic elements and, as such, are likely to influence the biology of their host strains. The majority of these phages are not amenable to propagation, and therefore the development of a molecular marker is a useful tool with which to establish the extent and diversity of C. difficile prophage carriage within clinical strains. To design markers, several candidate genes were analyzed including structural and holin genes. The holin gene is the only gene present in all sequenced phage genomes, conserved at both terminals, with a variable mid-section. This allowed us to design two sets of degenerate PCR primers specific to C. difficile myoviruses and siphoviruses. Subsequent PCR analysis of 16 clinical C. difficile ribotypes showed that 15 of them are myovirus positive, and 2 of them are also siphovirus positive. Antibiotic induction and transmission electron microscope analysis confirmed the molecular prediction of myoviruses and/or siphovirus presence. Phylogenetic analysis of the holin sequences identified three groups of C. difficile phages, two within the myoviruses and a divergent siphovirus group. The marker also produced tight groups within temperate phages that infect other taxa, including Clostridium perfringens, Clostridium botulinum, and Bacillus spp., which suggests the potential application of the holin gene to study prophage carriage in other bacteria. This study reveals the high incidence of prophage carriage in clinically relevant strains of C. difficile and correlates the molecular data to the morphological observation.  相似文献   
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This study compared virulence and antibiotic resistance traits in clinical and environmental Enterococcus faecalis and Enterococcus faecium isolates. E. faecalis isolates harboured a broader spectrum of virulence determinants compared to E. faecium isolates. The virulence traits Cyl-A, Cyl-B, Cyl-M, gel-E, esp and acm were tested and environmental isolates predominantly harboured gel-E (80% of E. faecalis and 31.9% of E. faecium) whereas esp was more prevalent in clinical isolates (67.8% of E. faecalis and 70.4% of E. faecium). E. faecalis and E. faecium isolated from water had different antibiotic resistance patterns compared to those isolated from clinical samples. Linezolid resistance was not observed in any isolates tested and vancomycin resistance was observed only in clinical isolates. Resistance to other antibiotics (tetracycline, gentamicin, ciprofloxacin and ampicillin) was detected in both clinical and water isolates. Clinical isolates were more resistant to all the antibiotics tested compared to water isolates. Multi-drug resistance was more prevalent in clinical isolates (71.2% of E. faecalis and 70.3% of E. faecium) compared to water isolates (only 5.7% E. faecium). tet L and tet M genes were predominantly identified in tetracycline-resistant isolates. All water and clinical isolates resistant to ciprofloxacin and ampicillin contained mutations in the gyrA, parC and pbp5 genes. A significant correlation was found between the presence of virulence determinants and antibiotic resistance in all the isolates tested in this study (p<0.05). The presence of antibiotic resistant enterococci, together with associated virulence traits, in surface recreational water could be a public health risk.  相似文献   
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Cryptosporidium parvum oocysts accumulate on biofilm surfaces. The percentage of oocysts attached to biofilms remained nearly constant while oocysts were supplied to the system but decreased to a new steady-state level once oocysts were removed from the feed. More oocysts attached to summer biofilm cultures than winter biofilm cultures.Cryptosporidium causes a potentially life-threatening gastrointestinal disease. Because conventional water treatment may not effectively target Cryptosporidium, source water monitoring and protection are important to avoid infection outbreaks.Biofilms can accumulate pathogens at densities that are much higher than water column densities, with the potential for pathogen release long after entrapment (5, 13, 15, 19). Biofilms have been identified as a drinking water contamination source (7), causing infections for which the source cannot be identified (4, 6).Several previous studies examined pathogen transport in biofilms using Cryptosporidium parvum oocysts (2, 6, 15, 16) or beads as pathogen surrogates (3, 5, 11, 12). The former studies did not use natural microbial assemblages (2, 16) or quantify oocyst attachment or sloughing (6, 15). The current study provides novel information about C. parvum oocyst attachment to environmental biofilms, including a mass balance analysis to identify the daily number of oocysts that (i) remained in the flowing water or were sloughed from the biofilm and (ii) were attached to the biofilm. We imaged biofilms using scanning confocal laser microscopy, as used in other studies (9, 17, 20, 21), to identify spatial patterns of oocyst attachment.Biofilms were scraped from rocks found in Monocacy Creek (Bethlehem, PA) into 1 liter of creek water in January 2007 (winter biofilm culture) and July 2008 (summer biofilm culture). The biofilm suspension was vacuum filtered through a 6-μm cellulose filter. The filtrate was centrifuged (1,754 × g for 15 min), and the resulting biofilm pellet was resuspended in 1 ml of raw creek water. The cell concentration was quantified by DAPI (4′,6-diamidino-2-phenylindole) staining (14). Cells were split into aliquots (5 × 106 cells each) and stored at −80°C in cryovials containing 30% glycerol.Single-channel flow chambers (length by width by height, 24 mm by 8 mm by 4 mm) with glass coverslips (Stovall Life Science, Inc., Greensboro, NC) were inoculated with 5 × 106 biofilm cells for 24 h before the flow was started. Filter-sterilized creek water was used as the flow medium. A 12-channel peristaltic pump (Ismatec, Glattbrugg, Switzerland) maintained a constant flow of 0.2 mm/s (1).For biofilm imaging, the following two setups were used: (i) 1 × 104 C. parvum oocysts (Iowa isolate; Waterborne, Inc., New Orleans, LA) (all oocysts were used within 3 weeks of shedding) in the influent each day for 3 days and (ii) 3 × 104 C. parvum oocysts added to the influent for the last 24 h of a 3-day flow experiment. Biofilms were imaged with a Zeiss LSM 510 META laser scanning microscope, using an argon laser (458-nm, 477-nm, 488-nm, and 514-nm excitation wavelengths) and a HeNe1 laser (543-nm excitation wavelength). Biofilms were fixed with methanol, blocked using a 1:10 dilution of fetal bovine serum, and stained with 20 μM SYTO 9 (Invitrogen, Molecular Probes, Eugene, OR) (16). C. parvum oocysts in the biofilm were stained with a Cy3-conjugated monoclonal antibody solution specific for Cryptosporidium (Waterborne, Inc.) (16).For the mass balance analysis, C. parvum oocysts (1 × 104 per day for 3 days) were added to 500 ml constantly stirred influent water to keep oocysts in suspension. Influent water was replaced each day. Experiments to quantify sloughing included 2 or 5 additional days with oocyst-free feed water, for a total of 5 or 8 days. Biofilms used for the 3- and 5-day experiments were grown with the winter biofilm culture; biofilms used for the 8-day experiments were grown with the summer biofilm culture.After each 24-hour period, the remaining influent and effluent waters were processed by membrane filtration (MF) and immunomagnetic separation (IMS) to recover the oocysts. On the last day of each experiment, biofilms were scraped from the flow chambers, resuspended in sterile creek water, and also processed by MF and IMS. MF was performed according to the method of Oda et al. (10), using the 3-μm filter only. IMS was performed on the filtrate using the Aureon IMS kit (ImmTech, Inc., New Windsor, MD), and oocysts were dissociated from the magnetic beads with 0.05 M HCl. IMS products were counted by hemocytometry and corrected for MF and IMS processing losses. An average IMS recovery of 65% ± 4.2% standard error (SE) (determined by four trials using 1 × 104 oocysts in deionized water) was used. MF recoveries were consistent within each day but varied between days. Therefore, an MF recovery control was performed each day using 1 × 104 oocysts in 1 liter deionized water to obtain a daily MF correction factor.The mass balance analysis demonstrated that these methods were effective for tracking oocysts throughout the flow system for the experiment''s duration, accounting for all the oocysts within 8% (Table (Table1).1). In a control flow chamber with no biofilm growth (i.e., a clean glass surface), oocyst loss within the system was 1% or less, indicating that very few oocysts attached to any abiotic surface within the flow system. Laboratory biofilms composed of natural microbial assemblages were successfully created, although grazing impacts that would affect biofilm dynamics in the environment were eliminated. The thicknesses of laboratory biofilms (average thickness, 39.6 μm; SD, 4.7 μm; n = 16) were not statistically different (P of 0.17 by independent t test) than those of natural biofilms in Monocacy Creek (average thickness, 35.8 μm; SD, 10.2 μm; n = 36).

TABLE 1.

Mass balance analysis of biofilms grown for 3, 5, and 8 days, with 3-day oocyst dosinga
Biofilm growthNo. of oocysts ± % SE
% of oocysts ± % SE
Avg biofilm thickness ± SE (μm)
InfluentEffluentBiofilmbIn biofilm at end of oocyst dosing (day 3)In biofilm at end of experimentcAccounted for in system
Day 3 (n = 3)1.5 × 104 ± 1.88.6 × 103 ± 9.36.4 × 103 ± 7.143 ± 5.643 ± 5.6100 ± 1.931 ± 6.1
Day 5 (n = 2)1.9 × 104 ± 2.41.8 × 104 ± 3.53.2 × 103 ± 5.340 ± 4.54.8 ± 2.1108 ± 1.037 ± 3.8
Day 8 (n = 2)2.0 × 104 ± 3.11.5 × 104 ± 2.97.6 × 103 ± 1.864 ± 5.028 ± 0.2107 ± 0.942 ± 3.6
Open in a separate windowaData from two or three replicate experiments are presented.bData determined from direct hemacytometer counts of scraped biofilm at the end of the experiment.cCalculated from influent and effluent data [(influent − effluent)/influent].Oocyst attachment location within the biofilm is important for transport dynamics. Oocyst attachment at the biofilm surface may be followed by (i) no transport into the biofilm depth, (ii) burial by biofilm overgrowth, or (iii) transport into the biofilm depth through water channels. In these experiments, oocysts attached to the biofilm surface and were not observed to move to depths or be buried by biofilm overgrowth (Fig. (Fig.1).1). In the 28 biofilms examined, no difference in oocyst attachment location was seen whether oocysts were present in the flow for the entire study duration (n = 14) or whether oocysts were added to the flow on the last study day (n = 14).Open in a separate windowFIG. 1.Top-down projection (A) and cross-sectional view (B) of a summer biofilm culture, with C. parvum oocysts attached at the biofilm surface. Biofilm cells are stained green with SYTO 9; oocysts are stained red with Cy3. The white line in panel A indicates the location of the cross section shown in panel B. Direction of water flow is from right to left. The biofilm is approximately 24-μm thick; oocysts are located 16 μm above the biofilm base.Previous studies (11, 12) also reported that particle attachment and detachment occurred at the biofilm surface. The inner biofilm was denser, with less pore space, while the biofilm surface had more water channels, providing more surface area for particle attachment. The mean pore size in a variety of biofilms was reported as 1.7 to 2.7 μm at the water surface and 0.3 to 0.4 μm at the substrate surface (11), which would restrict larger particle movement, including oocysts (4 to 7 μm).Oocysts became attached to biofilms and rapidly reached a steady state (Fig. (Fig.2),2), as seen in other studies (5, 6). The percentage of oocysts attached to the biofilm remained nearly constant while oocysts were supplied to the system. Once the oocyst supply was removed, the percentage of oocysts in the biofilm decreased to a new steady state. For winter biofilm cultures, the cumulative percentage of oocysts attached to the biofilm at day 3 (i.e., the end of the dosing period; average, 40.0%; SD, 25%; n = 2) was statistically higher (P of 0.003 by independent t test) than the cumulative percentage of oocysts attached to the biofilm at day 5 (average, 4.8%; SD, 1.4%; n = 2). For the summer biofilm cultures, the cumulative percentage of oocysts attached to the biofilm at day 3 (average, 63.7%; SD, 4.5%; n = 2) was also statistically higher (P of 0.01) than the cumulative percentage of oocysts attached to the biofilm at day 5 (average, 33.5%; SD, 1.1%; n = 2). The oocysts that remained in the biofilm at day 5 likely attached to more-stable or sheltered portions of the biofilm that did not slough.Open in a separate windowFIG. 2.Cumulative percentage of oocysts (±SE; n = 2) associated with the biofilm. The cumulative number of oocysts in the biofilm each day was calculated by adding the daily differences between the number of oocysts in the effluent and influent. This number was converted to a percentage by dividing by the cumulative number of influent oocysts. The biofilm accumulation on the last day was determined from the oocysts collected and counted directly from the biofilm, which agreed with the number calculated using the above-described method. Time zero indicates when the flow began; biofilm growth began 24 h earlier by seeding with microbial concentrate at zero flow. The solid black line on the x axis indicates the period of oocyst addition to the inflow. Error bars are smaller than symbols where not visible.The cumulative percentage of oocysts attached to summer biofilm cultures was statistically higher (P of 0.02 and 0.002 at days 3 and 5, respectively, by independent t test) than the cumulative percentage of oocysts attached to the winter biofilm cultures (Fig. (Fig.2).2). In addition, the thickness of summer biofilm cultures (average thickness, 42.1 μm; SD, 4.2 μm; n = 8) was statistically higher (P of 0.03 by independent t test) than that of winter biofilm cultures (average, 37.0 μm; SD, 3.9 μm; n = 8). However, it is unlikely that biofilm thickness explains the increased oocyst attachment to summer biofilm cultures, because all oocysts were observed to attach at the biofilm surface and no oocysts were ever observed within biofilm depths. These observations are in agreement with those of other studies (3, 8, 16) and suggest that other biofilm characteristics (e.g., surface roughness or pore size) may (i) be more important than biofilm thickness for oocyst attachment and (ii) vary with seasonal differences in water chemistry or microbial community caused by water quality differences, such as temperature, pH, or dissolved organic carbon (16).Biofilms are significant reservoirs for oocysts compared to abiotic surfaces (5, 12, 15, 16). Oocysts that remain in the biofilm have important public health implications because they may persist in the biofilm and eventually be released, resulting in potential human exposure.These results confirm that C. parvum oocysts quickly attach to natural microbial biofilms and can be released into the flowing water over time. Oocyst attachment and release dynamics are important for assessing and potentially reducing the risk of human exposure and infection. Although this study used natural stream biofilms, these transport dynamics have important implications for the drinking water industry. Biofilms in the raw water source, represented here by stream biofilms, are linked to drinking water intakes, where any disturbance event can affect water quality. For this reason, a better understanding of the environmental transport of oocysts is important for tracking oocyst contamination, which ultimately affects the drinking water industry. Further investigation is necessary to understand the differences between the summer and winter biofilm cultures as well as the pathogen reservoir that forms in the biofilm.  相似文献   
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