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1.
The UV sunscreen role commonly ascribed to mycosporine-like amino acids (MAAs) was investigated with an isolate of the terrestrial cyanobacterium Gloeocapsa sp. strain C-90-Cal-G.(2), which accumulates intracellularly an MAA with absorbance maximum at 326 nm but produces no extracellular sunscreen compound (i.e., scytonemin). The intracellular concentrations of MAA achieved were directly related to the intensity of the UV radiation (maximum at 320 nm) received by the cells. However, the presence of high concentrations of MAA was not necessary for the physiological acclimation of the cultures to UV radiation. The measured sunscreen factor due to MAA in single cells was 0.3 (the MAA prevented 3 out of 10 photons from hitting potential cytoplasmic targets). High contents of MAA in the cells correlated with increased resistance to UV radiation. However, when resistance was gauged under conditions of desiccation, with inoperative physiological photoprotective and repair mechanisms, cells with high MAA specific contents were only 20 to 25% more resistant. Although UV radiation centered around both 320 and 365 nm resulted in chlorophyll a photobleaching and photoinhibition of photosynthesis, the difference in sensitivity correlated with MAA accumulation occurred only at 320 nm (absorbed by MAA) and not at 365 nm (not absorbed by MAA). This difference represents the maximal protection ascribable to the presence of MAA for single cells, i.e., if one does not consider the enhancing effects of colony formation on protection by sunscreens.  相似文献   

2.
3.
Seven species of bacterial biothreat agents were tested for susceptibility to UV light (254 nm). All gram-negative organisms tested required <12 mJ/cm2 for a 4-log10 reduction in viability (inactivation). Tailing off of the B. anthracis spore inactivation curves began close to the 2-log10 inactivation point, with a fluence of approximately 40 mJ/cm2, and 3-log10 inactivation still was not achieved with a fluence of 120 mJ/cm2.The security of our nation''s water supply is a concern for water providers and public health officials. Questions have been asked regarding the possibility of our drinking water becoming contaminated with biothreat agents and the efficacy of current disinfection practices for the reduction in viability (inactivation) of biothreat agents (5, 8, 14). The use of UV irradiation as a supplemental water disinfection practice is increasing for several reasons, among them improving control of protozoa, such as Cryptosporidium spp., and decreasing disinfection by-products created by chemical disinfectants (21). This study employed a bench-scale collimated beam test to determine the UV fluence (dose) required to inactivate seven representative bacterial biothreat agents.Seven species, two isolates each, from the Health and Human Services and U.S Dept. of Agriculture lists of select agents (http://www.selectagents.gov/resources/List%20of%20Select%20Agents%20and%20Toxins_111708.pdf) were used in this study: Bacillus anthracis Ames spores, B. anthracis 34F2 (Sterne) spores, Brucella melitensis ATCC 23456, B. melitensis IL195, Brucella suis KS528, B. suis MO562, Burkholderia mallei M9, B. mallei M13, Burkholderia pseudomallei ATCC 11688, B. pseudomallei CA650, Francisella tularensis LVS, F. tularensis NY98, Yersinia pestis A1122, and Y. pestis Harbin. B. anthracis was grown on soil extract-peptone-beef extract agar (SEA) (1) or in Schaeffer''s sporulation medium (SSM) (10) for 7 days, resulting in >99% spores as determined by phase-contrast microscopy. The cells and spores were then washed by centrifugation (8,000 × g), resuspended in ultrapure water, transferred to centrifuge tubes, treated with 50% ethanol for 1 h at room temperature, and washed five times with sterile ultrapure water before being stored in reverse-osmosis water at −70°C. F. tularensis isolates were grown on cysteine heart agar (1) and all other isolates on Trypticase soy agar with 5% sheep blood (TSA II; Becton Dickinson Microbiology Systems, Sparks, MD) for 24 h before testing. B. anthracis spores were adjusted to 107 CFU/ml and other bacterial suspensions to 108 CFU/ml in Butterfield buffer (3 mM KH2PO4, pH 7.2; Becton Dickinson Microbiology Systems), and then isolates were sonicated (40-Hz ultrasonic cleaner; VWR, Suwanee, GA) for 1 min to disperse aggregates. The suspensions were diluted 1:100 in Butterfield buffer for final test concentrations. Five milliliters of each suspension were placed into a small petri dish (50-mm diameter) along with a small sterile stir bar, and the petri dish was placed on a stir plate.UV irradiation was performed by using a collimated beam apparatus (Calgon Carbon, Pittsburgh, PA) equipped with a low-pressure lamp (254 nm) according to the standard method developed by Bolton and Linden (2). The surface of the suspension was placed 5 cm from the end of the collimating tube. The UV intensity was measured with a radiometer at 0.5-cm intervals across the test area and variability compensated for according to the UVCalc software directions (International UV association [http://www.iuva.org]). The fluences (UV doses) were determined using the UVCalc software, and the petri dishes were placed under the beam for at least five time periods to deliver a range of appropriate fluences to the organisms. Each irradiation test was conducted at room temperature (23 ± 2°C) in triplicate and in a random order of fluences. After exposure, 10-fold serial dilutions were performed, and the dilutions were spread plated in triplicate. Plates were placed in a dark incubator within 10 min of plating and incubated at the temperature appropriate for the organism, and the colonies were counted at 24 h and 48 h for B. anthracis and at 3 and 5 days for the remaining organisms. Colonies were counted, and the log10 inactivation at each fluence was determined for each organism. A linear regression of the fluence response data determined the fluence required for 2-, 3-, and 4-log10 inactivation.The UV fluences required for inactivation of each organism are reported in Table Table1.1. Little difference in UV susceptibility was seen between the gram-negative organisms. B. suis KS528 and B. melitensis ATCC 23456 required the greatest UV fluence of the gram-negative organisms for 4-log10 inactivation (10.5 and 10.2 mJ/cm2, respectively), while the two Y. pestis isolates required the lowest UV fluence (4.1 and 4.9 mJ/cm2) for the same 4-log10 inactivation (Table (Table1).1). Generally, the two isolates of each species differed no more than 3 mJ/cm2 in the UV fluence required for 4-log10 inactivation.

TABLE 1.

UV fluence required for given log10 inactivation of each organism
OrganismFluence (mJ/cm2) for log10 inactivation of:
1234
B. anthracis Ames25.3 (5.1)∼40>120 (tailing off)>120 (tailing off)
B. anthracis Sterne23.0 (0.7)∼40>120 (tailing off)>120 (tailing off)
B. suis MO5621.7 (0.0)3.6 (0.1)5.6 (0.2)7.5 (0.3)
B. suis KS5282.7 (0.2)5.3 (0.3)7.9 (0.4)10.5 (0.5)
B. melitensis ATCC 234562.8 (0.2)5.3 (0.2)7.8 (0.3)10.3 (0.5)
B. melitensis IL1953.7 (0.2)5.8 (0.2)7.8 (0.2)9.9 (0.3)
B. pseudomallei ATCC 116881.7 (0.2)3.5 (0.1)5.5 (0.2)7.4 (0.3)
B. pseudomallei CA6501.4 (0.2)2.8 (0.1)4.3 (0.3)5.7 (0.6)
B. mallei M-91.0 (0.3)2.4 (0.2)3.8 (0.2)5.2 (0.3)
B. mallei M-131.2 (0.5)2.7 (0.2)4.1 (0.1)5.5 (0.4)
F. tularensis LVS1.3 (0.0)3.1 (0.0)4.8 (0.0)6.6 (0.1)
F. tularensis NY981.4 (0.1)3.8 (0.0)6.3 (0.1)8.7 (0.2)
Y. pestis A11221.4 (0.5)2.6 (0.5)3.7 (0.6)4.9 (0.6)
Y. pestis Harbin1.3 (0.1)2.2 (0.0)3.2 (0.1)4.1 (0.1)
Bacillus anthracis Sternea27.5∼36∼53d
Bacillus subtilisb28395062
E. colic3.04.86.78.4
Cryptosporidiumc2.55.81222
Giardiac2.15.21122
Virusc58100143186
Open in a separate windowaData from reference 12 (estimated from graph).bData from reference 4.cData from reference 21.d—, 4-log10 inactivation not achieved with a fluence of 60 mJ/cm2.The spores of the two B. anthracis isolates were more resistant to UV than the gram-negative organisms tested but were similar to each other in UV susceptibility (Fig. (Fig.1).1). B. anthracis Sterne and B. anthracis Ames spores were inactivated by 90% (1 log10), with fluences of 23.0 and 25.3 mJ/cm2, respectively. B. anthracis spores produced on SEA and plated after UV exposure on TSA II required more than 40 mJ/cm2 for a 2-log10 inactivation, and further exposure to UV light did not inactivate the sample further (Fig. (Fig.1),1), as seen in the tailing off of the inactivation curve. In order to investigate this tailing off further, B. anthracis spores produced in SSM were also challenged with the same UV fluences and found to require 40 mJ/cm2 for a 2-log10 inactivation as well, but they continued to be inactivated to a slightly greater degree than the spores produced on SEA (Fig. (Fig.1).1). An additional experiment was conducted in which spores produced on SEA were grown on two media (SSM with 1.7% agar and TSA II) after UV exposure, and no difference in recovery was observed (data not shown).Open in a separate windowFIG. 1.UV inactivation curves of B. anthracis spores. B. anthracis Sterne was grown and sporulated on SEA and SSM, and B. anthracis Ames was grown and sporulated on SEA.The inactivation results for Y. pestis, F. tularensis, Brucella spp., and Burkholderia spp. reflect findings similar to those of other waterborne pathogenic organisms, such as Escherichia coli, Shigella sonnei, Yersinia enterocolitica, and Campylobacter jejuni (3, 4). These reported values ranged from 1.8 to 6 mJ/cm2 for a 3-log10 inactivation (Table (Table11).Previous work established that bacterial spores are 10 to 50 times more resistant to UV at 254 nm than vegetative cells (11, 12). The DNA in spores is saturated with α/β-type small acid-soluble proteins during the sporulation process. This bound small acid-soluble protein suppresses the formation of pyrimidine dimers (as seen in vegetative cells) when irradiated with UV and instead promotes formation of a unique spore photoproduct, 5-thyminyl-5,6-dihydrothymine. During germination, light-independent repair occurs by lyase activation of the spore photoproduct and nucleotide excision repair, restoring the two thymines (6, 18, 19). Variations in resistance to UV may be attributed to differences in sporulation conditions, such as the availability of metal ions present during sporulation, or germination conditions (10, 11, 13, 18).The susceptibility of B. anthracis spores grown on SEA in this study can be compared to the results found by Knudson (6), in which a fluence of 120 mJ/cm2 was not sufficient to achieve a 2-log10 reduction. However, Nicholson and Galeano (12) did not observe tailing off of the disinfection curve occurring after a 2-log10 reduction. We therefore produced spores in the same manner as Nicholson and Galeano to determine if the difference in spore preparation could account for the differences in UV susceptibility. Though this study noted a greater susceptibility of SSM-produced spores than SEA-produced spores, we did not see as great a reduction as did Nicholson and Galeano (12) (Fig. (Fig.1).1). Rice and Ewell (15) also reported tailing off of the inactivation curve in a similar study using Bacillus subtilis spores and were unable to determine if the tailing off indicated the presence of a resistant subpopulation of organisms or was an artifact of the testing protocol. Subsequent work by Mamane-Gravetz and Linden (7) demonstrated that the tailing off of UV inactivation curves is a result of the presence of spore aggregates in the suspension, and the degree of aggregation is directly related to the hydrophobicity of the spores. The hydrophobicity of the spores used in this study was tested in the same manner as in the study by Mamane-Gravetz and Linden (7) and found to correlate with the inactivation curves in Fig. Fig.1.1. The SSM-produced spores were less hydrophobic (P = 0.25) at 64.1% (standard deviation [SD], 5.6%) than the SEA-produced spores at 76.2% (SD, 2.8%), whereas the SEA-produced Ames spores were closer (P = 0.03) in hydrophobicity to the SEA-produced Sterne spores at 79.6% (SD, 3.4%). These observations agree with the previous publication (7) in that the more hydrophobic spores tend to aggregate together to a greater extent, shielding a greater number of spores from exposure to UV radiation, thereby creating a more pronounced tailing off of the inactivation curve.Since the finding that UV irradiation can control protozoa much more effectively than chlorine, installation of UV technology in water treatment facilities has been on the rise, with more than 150 treatment plants in North America currently using the technology or planning installations in the near future (22).The latest Environmental Protection Agency surface water treatment rules require drinking water systems to document their ability to provide a 2- or 3-log10 inactivation (for unfiltered systems) of Cryptosporidium (depending upon source water monitoring results and treatment practices in place at the facility), a 3-log10 inactivation of Giardia, and a 4-log10 inactivation of viruses (21). No two treatment facilities are alike, but these requirements can be met by physical removal such as filtration, flocculation, and settling and/or by various disinfection methods such as use of chlorine, monochloramine, chlorine dioxide, ozone, or UV irradiation (20, 21).Should water be contaminated with biothreat agents upstream from a water treatment facility with UV capability, we can expect a facility following Environmental Protection Agency regulations to remove or inactivate 3 log10 Giardia spp. and Cryptosporidium spp. and also to effectively inactivate the gram-negative bacterial biothreat agents Y. pestis, F. tularensis, B. mallei, B. pseudomallei, B. suis, and B. melitensis. If the contaminating agent is B. anthracis in spore form, the facility may not eradicate spores with UV treatment alone, requiring cotreatment with other disinfection methods. However, it is possible that the clumping of spores may increase the efficacy of the facility''s coexisting available treatment, such as flocculation and filtration. Further examination of these practices would be necessary.In the event that a biothreat agent is intentionally released into the distribution system after water treatment, and no disinfectant residual (chlorine or chloramine) is provided by the treatment facility, a point-of-use (POU) or point-of-entry (POE) UV system may prove to be effective. NSF/ANSI standard 55 (9) establishes the requirements for two classes of POU and POE UV systems. The class A systems, designed to disinfect contaminated clear water, are required to deliver a minimum UV fluence of 40 mJ/cm2. The class B systems offer supplemental reduction in pathogens and are required to deliver a UV fluence of 16 mJ/cm2. Both class A and B POU/POE devices would be effective in providing a 4-log10 inactivation of the gram-negative organisms tested. Only the class A device would prove effective against B. anthracis spores prepared in this manner, though only in providing 2-log10 inactivation.These data, along with previous investigations of the efficacy of chlorine and monochloramine against bacterial biothreat agents (16, 17), provide public health officials and water treatment facility operators essential information to better prepare for protecting public health in the event of a water contamination incident.  相似文献   

4.
Abstract

Conjugation of the photosensitive nucleoside ( E )-5-(2-methoxycarbonylethenyl)cytidine to biotin provided a means to attach this analogue to microparticles for dosimetry applications that require uv sensor mobility.  相似文献   

5.
Three strains of Helicobacter pylori were exposed to UV light from a low-pressure source to determine log inactivation versus applied fluence. Results indicate that H. pylori is readily inactivated at UV fluences typically used in water treatment regimens. Greater than 4-log10 inactivation was demonstrated on all three strains at fluences of less than 8 mJ cm−2.  相似文献   

6.
The results of this study confirm that adenoviruses are the most resistant enteric viruses to inactivation by UV light and that adenovirus 40 appears to be the most resistant. The effect of freeze-thawing and storage in water may affect the sensitivity of some adenoviruses to inactivation by UV light.  相似文献   

7.
8.
对采用超声辅助法萃取苦丁茶防晒组分进行了较为系统的研究。选择萃取时间、萃取剂体积分数、萃取温度、样品细度4个主要影响因素,运用多因素多水平可视化设计法安排实验。以防晒光区的紫外吸收面积值作为防晒组分萃取含量的实验评定指标。用自主提出的多因素多水平实验结果可视化分析方法对多维空间实验数据进行分析。得出当ρ(苦丁茶)=0.20 g/L时,最佳工艺范围为萃取时间30~60 min、萃取剂体积分数φ(C2H5OH)为50%~70%、萃取温度50~65℃、萃取样品细度140~160目。  相似文献   

9.
10.
The doses of UV irradiation necessary to inactivate selected enteric viruses on the U.S. Environmental Protection Agency Contaminant Candidate List were determined. Three-log reductions of echovirus 1, echovirus 11, coxsackievirus B3, coxsackievirus B5, poliovirus 1, and human adenovirus type 2 were effected by doses of 25, 20.5, 24.5, 27, 23, and 119 mW/cm2, respectively. Human adenovirus type 2 is the most UV light-resistant enteric virus reported to date.  相似文献   

11.
The epidermal growth factor receptor (EGFR) is a member of the ErbB family of receptor tyrosine kinases. EGFR is activated upon binding to e.g. epidermal growth factor (EGF), leading to cell survival, proliferation and migration. EGFR overactivation is associated with tumor progression. We have previously shown that low dose UVB illumination of cancer cells overexpressing EGFR prior to adding EGF halted the EGFR signaling pathway. We here show that UVB illumination of the extracellular domain of EGFR (sEGFR) induces protein conformational changes, disulphide bridge breakage and formation of tryptophan and tyrosine photoproducts such as dityrosine, N-formylkynurenine and kynurenine. Fluorescence spectroscopy, circular dichroism and thermal studies confirm the occurrence of conformational changes. An immunoassay has confirmed that UVB light induces structural changes in the EGF binding site. A monoclonal antibody which competes with EGF for binding sEGFR was used. We report clear evidence that UVB light induces structural changes in EGFR that impairs the correct binding of an EGFR specific antibody that competes with EGF for binding EGFR, confirming that the 3D structure of the EGFR binding domain suffered conformational changes upon UV illumination. The irradiance used is in the same order of magnitude as the integrated intensity in the solar UVB range. The new photonic technology disables a key receptor and is most likely applicable to the treatment of various types of cancer, alone or in combination with other therapies.  相似文献   

12.
13.
14.
High-energy wavelengths in the ultraviolet-B (UVB, 280-315 nm) and the UVA (315-400-nm) portion of the spectrum are harmful to terrestrial and aquatic organisms. Interestingly, UVA is also involved in the repair of UV induced damage. Organisms living in shallow coral reef environments possess UV absorbing compounds, such as mycosporine-like amino acids, to protect them from UV radiation. While it has been demonstrated that exposure to UV (280-400 nm) affects the UV absorbance of fish mucus, whether the effects of UV exposure vary between UVB and UVA wavelengths is not known. Therefore, we investigated whether the UVB, UVA, or photosynthetically active radiation (PAR, 400-700 nm) portions of the spectrum affected the UV absorbance of epithelial mucus and Fulton’s body condition index of the cleaner fish Labroides dimidiatus. We also compared field-measured UV absorbance with laboratory based high-performance liquid chromatography measurements of mycosporine-like amino acid concentrations. After 1 week, we found that the UV absorbance of epithelial mucus was higher in the UVB+UVA+PAR treatment compared with the UVA+PAR and PAR only treatments; after 2 and 3 weeks, however, differences between treatments were not detected. After 3 weeks, Fulton’s body condition index was lower for fish in the UVB+UVA+PAR compared with PAR and UVA+PAR treatments; furthermore, all experimentally treated fish had a lower Fulton’s body condition index than did freshly caught fish. Finally, we found a decrease with depth in the UV absorbance of mucus of wild-caught fish. This study suggests that the increase in UV absorbance of fish mucus in response to increased overall UV levels is a function of the UVB portion of the spectrum. This has important implications for the ability of cleaner fish and other fishes to adjust their mucus UV protection in response to variations in environmental UV exposure.  相似文献   

15.
The UV inactivation of RNA-directed DNA polymerase activity of Rauscher leukemia virus was shown to be due to damage to the protein. The UV dose resulting in 37% survival of viral polymerase activity at 254 nm was 2.4 × 104 to 3.1 × 104 ergs/mm2. The inactivation rate of p30, a major internal viral protein, was much slower.  相似文献   

16.
Contamination of platelet units by bacteria has long been acknowledged as a significant transfusion risk due to their post-donation storage conditions. Products are routinely stored at 22 °C on an agitating shaker, a condition that can promote bacterial growth. Although the total number of bacteria believed to be introduced into a platelet product is extremely low, these bacteria can multiply to a very high titer prior to transfusion, potentially resulting in serious adverse events. The aim of this study was to evaluate a riboflavin based pathogen reduction process against a panel of bacteria that have been identified as common contaminants of platelet products. This panel included the following organisms: S. epidermidis, S. aureus, S. mitis, S. pyogenes, S. marcescens, Y. enterocolitica, B. neotomae, B. cereus, E. coli, P. aeruginosa and K. pneumoniae. Each platelet unit was inoculated with a high bacterial load and samples were removed both before and after treatment. A colony forming assay, using an end point dilution scheme, was used to determine the pre-treatment and post-treatment bacterial titers. Log reduction was calculated by subtracting the post-treatment titer from the pre-treatment titer. The following log reductions were observed: S. epidermidis 4.7 log (99.998%), S. aureus 4.8 log (99.998%), S. mitis 3.7 log (99.98%), S. pyogenes 2.6 log (99.7%), S. marcescens 4.0 log (99.99%), Y. enterocolitica 3.3 log (99.95%), B. neotomae 5.4 log (99.9996%), B. cereus 2.6 log (99.7%), E. coli ≥5.4 log (99.9996%), P. aeruginosa 4.7 log (99.998%) and K. pneumoniae 2.8 log (99.8%). The results from this study suggest the process could help to lower the risk of severe adverse transfusion events associated with bacterial contamination.  相似文献   

17.
Nile tilapia fish were individually reared under similar light levels for 8 weeks under five colored light spectra (maximum wavelength absorbance): white (full light spectrum), blue (∼452 nm), green (∼516 nm), yellow (∼520 nm) or red (∼628 nm). The effects of light on feeding, latency to begin feeding, growth and feed conversion were measured during the last 4 weeks of the study (i.e., after acclimation). We found that red light stimulates feeding, as in humans, most likely by affecting central control centers, but the extra feeding is not converted into growth.  相似文献   

18.
Russian Journal of Genetics - Experimental curves of the dependence of survival and delayed colony formation on UV light (254 nm) fluence for two wild-type strains of diploid yeast Saccharomyces...  相似文献   

19.
Fruit and vegetable growers continually battle plant diseases and food safety concerns. Surface water is commonly used in the production of fruits and vegetables and can harbor both human- and plant-pathogenic microorganisms that can contaminate crops when used for irrigation or other agricultural purposes. Treatment methods for surface water are currently limited, and there is a need for suitable treatment options. A liquid-processing unit that uses UV light for the decontamination of turbid juices was analyzed for its efficacy in the treatment of surface waters contaminated with bacterial or oomycete pathogens, i.e., Escherichia coli, Salmonella enterica, Listeria monocytogenes, Clavibacter michiganensis subsp. michiganensis, Pseudomonas syringae pv. tomato, and Phytophthora capsici. Five-strain cocktails of each pathogen, containing approximately 108 or 109 CFU/liter for bacteria or 104 or 105 zoospores/liter for Ph. capsici, were inoculated into aliquots of two turbid surface water irrigation sources and processed with the UV unit. Pathogens were enumerated before and after treatment. In general, as the turbidity of the water source increased, the effectiveness of the UV treatment decreased, but in all cases, 99.9% or higher inactivation was achieved. Log reductions ranged from 10.0 to 6.1 and from 5.0 to 4.2 for bacterial pathogens and Ph. capsici, respectively.  相似文献   

20.

Background

0.5% to 10% of clean surgeries result in surgical-site infections, and attempts to reduce this rate have had limited success. Germicidal UV lamps, with a broad wavelength spectrum from 200 to 400 nm are an effective bactericidal option against drug-resistant and drug-sensitive bacteria, but represent a health hazard to patient and staff. By contrast, because of its limited penetration, ∼200 nm far-UVC light is predicted to be effective in killing bacteria, but without the human health hazards to skin and eyes associated with conventional germicidal UV exposure.

Aims

The aim of this work was to test the biophysically-based hypothesis that ∼200 nm UV light is significantly cytotoxic to bacteria, but minimally cytotoxic or mutagenic to human cells either isolated or within tissues.

Methods

A Kr-Br excimer lamp was used, which produces 207-nm UV light, with a filter to remove higher-wavelength components. Comparisons were made with results from a conventional broad spectrum 254-nm UV germicidal lamp. First, cell inactivation vs. UV fluence data were generated for methicillin-resistant S. aureus (MRSA) bacteria and also for normal human fibroblasts. Second, yields of the main UV-associated pre-mutagenic DNA lesions (cyclobutane pyrimidine dimers and 6-4 photoproducts) were measured, for both UV radiations incident on 3-D human skin tissue.

Results

We found that 207-nm UV light kills MRSA efficiently but, unlike conventional germicidal UV lamps, produces little cell killing in human cells. In a 3-D human skin model, 207-nm UV light produced almost no pre-mutagenic UV-associated DNA lesions, in contrast to significant yields induced by a conventional germicidal UV lamp.

Conclusions

As predicted based on biophysical considerations, 207-nm light kills bacteria efficiently but does not appear to be significantly cytotoxic or mutagenic to human cells. Used appropriately, 207-nm light may have the potential for safely and inexpensively reducing surgical-site infection rates, including those of drug-resistant origin.  相似文献   

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