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1 in systems using free chlorine as a residual disinfectant.
2 ance of both biofilm and detached biofilm to disinfectant.
3  the widespread use of aqueous chlorine as a disinfectant.
4 lowest oxidant exposure associated with each disinfectant.
5 monium from urine for use as a fertilizer or disinfectant.
6 , and the bronchoscope was never immersed in disinfectant.
7 least studied, especially in the presence of disinfectant.
8 on systems where chloramines are used as the disinfectant.
9  active ingredient in several EPA registered disinfectants.
10 tion by predator organisms, antibiotics, and disinfectants.
11  its intrinsic resistance to antibiotics and disinfectants.
12 line glutaraldehyde, and other commonly used disinfectants.
13 disinfectants, especially with more reactive disinfectants.
14 ne, along with pools treated with these same disinfectants.
15 nificant cross-resistance to genome-damaging disinfectants.
16 that they can be inactivated by other common disinfectants.
17  from deleterious external attacks including disinfectants.
18   Proteins are important targets of chemical disinfectants.
19 ir virulence and efficacy as therapeutics or disinfectants.
20           In tests with the two bactericidal disinfectants, 22 of 1,639 cultures (1.3%) in the chlori
21                          An understanding of disinfectant action and microbial resistance to treatmen
22 e parameters, was first applied to bacterial disinfectant action and then was successfully used to mo
23     Hydrogen peroxide (H2O2) is an important disinfectant and bleach and is currently manufactured fr
24  water utilities using chlorine as a primary disinfectant and chloramines for maintenance of a distri
25 ch bleach was used); UV (quaternary ammonium disinfectant and disinfecting ultraviolet [UV-C] light e
26 Watson model with first-order dependences on disinfectant and infective phage concentrations.
27    It is used in water supply treatment as a disinfectant and slime preventive and has an advantage o
28 eatment plants using chlorine as an upstream disinfectant and the extent and rate at which those chan
29  the specific biomolecules reacting with the disinfectant and the mechanism of disinfection remains e
30 the organism and aid development of improved disinfectant and therapeutic agents.
31                 As silver is often used as a disinfectant and treatment for burn wounds, we present h
32                                              Disinfectant and water age were both observed to be stro
33 ese clinical features, as they resist common disinfectants and antibiotic treatment.
34                           There are numerous disinfectants and antiseptics for treating materials in
35     This EPS strongly protects cells against disinfectants and desiccation, indicating its potential
36 ucts (DBPs) that form from reactions between disinfectants and nitrogen-containing precursors, the la
37 e environmental hazards such as antibiotics, disinfectants and oxidative stress agents by modulating
38 than the samples treated with chlorine-based disinfectants and was not significantly different compar
39  unusually robust resistance to antibiotics, disinfectants, and desiccation.
40 factors such as high temperature, radiation, disinfectants, and drying.
41 eposits protect the associated bacteria from disinfectants, and due to their mobility, the associated
42 ysts in the environment or after exposure to disinfectants, and therefore their potential infectivity
43 ibuted to improving our understanding of how disinfectants, applied to control biofouling of reverse
44                           None of the common disinfectants are effective in killing the parasite beca
45 , bleach, and ammonia; minimizing the use of disinfectants; avoidance of mixing products; use of resp
46 peroxide, formaldehyde, and the iodine-based disinfectant Betadine; (iii) the absence of DPA increase
47  and matching isolates were recovered from a disinfectant bottle and nearby sink.
48 raviolet (UV) light is being considered as a disinfectant by the water industry because it appears to
49 loramines are the second most used secondary disinfectant by United States water utilities.
50 ions of dibromoacetonitrile (DBAN), a common disinfectant by-product found in many water supply syste
51 is likely due to not only the consumption of disinfectants by the biofilm and the reduced disinfectan
52 s, including preservatives, antioxidants and disinfectants, by evaluating the performance of differen
53                                              Disinfectants can cause tonometer tips to swell and crac
54 eter prisms in eye care and to highlight how disinfectants can damage tonometer tips and cause subseq
55                              Various primary disinfectants can deactivate NDMA precursors prior to ch
56 resenting distribution networks experiencing disinfectant changeover from free chlorine to monochlora
57           Intensive monitoring following the disinfectant changeover may be required to determine the
58                                   Effects of disinfectant (chloramines, chlorine), water age (2.3 day
59 lication to pool water, they can (1) release disinfectant chlorine or (2) stabilize the free availabl
60 Cs could serve as a water recovery system, a disinfectant/cleaner generator that limits undesired bio
61                                              Disinfectant combinations should be optimized to reduce
62                  Utilities are exploring new disinfectant combinations to reduce the formation of reg
63                                              Disinfectant concentration had the strongest effect on b
64                    Peracetic acid (PAA) is a disinfectant considered for use in ballast water treatme
65 ng system materials and two commonly applied disinfectants, copper and chloramines, on water chemistr
66                                              Disinfectant decay was noted with water age, particularl
67 agnant water, where the relationship between disinfectant decay, microbial growth, and water age is p
68                     After these results, the disinfectant dosage was increased to between 6 and 10 mg
69                       Furthermore, choice of disinfectant, dose, and predisinfection treatment at the
70 conditions including different pH levels and disinfectant doses that are typical of drinking water di
71 n animal bioassay, we compared the TSE agent disinfectant efficacy of a commercially available produc
72                                     For both disinfectants, electrochemical measurements supported a
73 viruses in the environment and resistance to disinfectants, especially with more reactive disinfectan
74 r strategies: reference (quaternary ammonium disinfectant except for C difficile, for which bleach wa
75 ditions, biofilms were prepared under either disinfectant exposure (predisinfected biofilms) or disin
76                    After three months of the disinfectant exposure process, the disinfected biofilms
77  biofilm thickness within the first month of disinfectant exposure was presumably due to the consumpt
78 However, by the second to third month during disinfectant exposure, the biofilm mean stiffness showed
79                     After the first month of disinfectant exposure, the mean stiffness of monochloram
80 mum, suggesting that the biofilms adapted to disinfectant exposure.
81   Thus, understanding how long-term residual disinfectants exposure affects biofilm mechanical and st
82 ption of antisense gene silencing as a novel disinfectant for prokaryotic organisms is hindered by po
83 ectant exposure (predisinfected biofilms) or disinfectant-free (untreated biofilms) conditions, respe
84 r(-)-containing source waters when switching disinfectant from free chlorine to monochloramine.
85     No inhibition by antibacterial agents or disinfectants from the hospital was observed in the MBR.
86 which was found to be an effective TSE agent disinfectant in a previous study.
87 rhexidine is widely used as an antiseptic or disinfectant in both hospital and community settings.
88 ient of household bleach, is the most common disinfectant in medical, industrial, and domestic use an
89                 Dosed cupric ions acted as a disinfectant in stratified stagnant pipes, inhibiting cu
90                 Chlorine is widely used as a disinfectant in the water industry, and the residual fre
91  the JSRV vector was inactivated by standard disinfectants, indicating that JSRV vectors pose no unus
92 tems, often achieved through the addition of disinfectants, is essential to limiting waterborne illne
93 overed from the spa, despite apparently high disinfectant levels.
94 rventions to improve water flow and increase disinfectant levels.
95                                 Common water disinfectants like chlorine have been reported to select
96            Cleaning sprays, bleach, ammonia, disinfectants, mixing products, and specific job tasks h
97 a steady state and enables in vitro tests of disinfectant mouthwashes in simulated clinical use.
98 used water with monochloramine as a residual disinfectant (odds ratio 10.2 [95% CI 1.4-460]).
99 ast 1 worker admitted sometimes spraying the disinfectant on the ear studs before piercing.
100 , a widely used class of quaternary ammonium disinfectants, on microbial community structure and anti
101 d compounds including antibiotics, household disinfectants, organic solvents and other toxic chemical
102 disinfectants by the biofilm and the reduced disinfectant penetration into the biofilm but also the c
103 PS components with monochloramine influenced disinfectant penetration, biofilm inactivation, as well
104 d homo- and heterocyclic aromatics including disinfectants, pesticides and pharmaceuticals raise conc
105                       Interactive effects of disinfectant, pipe material, and water age on both bacte
106 ibutions from the wells and without residual disinfectant present in these systems, any increase in v
107 arious agricultural, hospital and veterinary disinfectant products.
108              To improve the understanding of disinfectant-protein reactions, this study characterized
109 tein reactions, this study characterized the disinfectant:protein molar ratios at which 50% degradati
110 ams (blaZ), aminoglycosides (aacA-aphD), and disinfectants (qacC).
111         This targeting concurs with its high disinfectant rate constants and supports its hypothesize
112  targeting of amino acids is driven by their disinfectant rate constants rather than their geometrica
113 ion of distribution system conditions with a disinfectant residual of 1 mgC2 L(-1) showed complete co
114 r simulated drinking water flow containing a disinfectant residual was examined.
115  This study highlights the interaction among disinfectant residual, biofilms, and L. pneumophila, whi
116  apparent at water ages corresponding to low disinfectant residual.
117 eria if chloramines are applied as secondary disinfectant residual.
118 ical or hydraulic pipe integrity and lack of disinfectant residual.
119  vermiformis and the depletion of chloramine disinfectant residuals by nitrifying bacteria, leading t
120    OPPPs share the common characteristics of disinfectant resistance and growth in biofilms in water
121                                   The higher disinfectant resistance of L. pneumophila released from
122                  Ozone, a strong oxidant and disinfectant, seems ideal to cope with future challenges
123 and cysticidal efficacy of four multipurpose disinfectant solutions (MPDSs) and a one-step hydrogen p
124 anic matter suspended in water that consumes disinfectants) sourced from operational drinking water d
125 yproducts (DBPs) formed from the reaction of disinfectants such as chlorine and monochloramine with o
126 tudy show that monochloramine is a promising disinfectant that can prevent Legionella contamination o
127 ld be employed to devise methods of applying disinfectants that minimize byproduct formation while ac
128 onella nutrient, while also directly causing disinfectant to decay more rapidly.
129 is increasingly being used as an alternative disinfectant to free chlorine to maintain a residual in
130 For experiments with water flow containing a disinfectant to release the biofilm-associated L. pneumo
131 ritate the cornea, harbor microbes, or allow disinfectants to enter the interior of the tonometer tip
132 hlorides (BACs)-an active ingredient of many disinfectants-to benzyldimethyl amine (BDMA) was identif
133 ly lead to the development of more effective disinfectant treatments.
134                           The effects of pH, disinfectant type (free chlorine and monochloramine), an
135                                              Disinfectant type and dose was observed to have the stro
136  to examine the influence of pipe materials, disinfectant type, and water age on occurrence and persi
137 e appeared to display a distinct response to disinfectant type, pipe materials, water age, and their
138 MS2 and hNoV GII in PB at CT values for both disinfectants up to 450 mg-min/L.
139      Polyhexamethylene biguanide (PHMB) is a disinfectant used in swimming pools and hot tubs.
140  of 0.2% chlorine peroxide as a bactericidal disinfectant was compared to that of 10% providone iodin
141 th chlorine, a common drinking-water oxidant/disinfectant, was investigated.
142 water containing free chlorine as a residual disinfectant were more likely to have a reported outbrea
143 bly, neither contact lens care solutions nor disinfectants were associated with corneal staining.
144 insecticide-treated bednets, soap, and water disinfectant) were marketed in 30 intervention villages
145 t and an active ingredient of EPA-registered disinfectants with wide human exposure in various agricu
146 viruses become inactivated by drinking water disinfectants would facilitate the development of sensor
147 ruses can exhibit resistance to common water disinfectants, yet the mechanisms that allow them to tol

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