ライフサイエンスコーパス: disinfectant

1 least studied, especially in the presence of disinfectant.

2 on systems where chloramines are used as the disinfectant.

3 ance of both biofilm and detached biofilm to disinfectant.

4 the widespread use of aqueous chlorine as a disinfectant.

5 lowest oxidant exposure associated with each disinfectant.

6 , and the bronchoscope was never immersed in disinfectant.

7 route may be impaired differently by a given disinfectant.

8 om reaction with chlorine, a common chemical disinfectant.

9 m hypochlorite (NaOCl), a potent but caustic disinfectant.

10 free chlorine to chloramines as a secondary disinfectant.

11 ely help predict virus susceptibility to the disinfectant.

12 w lumens was compared against the commercial disinfectant.

13 ance to chlorine, the most efficient in-line disinfectant.

14 in systems using free chlorine as a residual disinfectant.

15 monium from urine for use as a fertilizer or disinfectant.

16 Proteins are important targets of chemical disinfectants.

17 ir virulence and efficacy as therapeutics or disinfectants.

18 olutions resulted in 100% mortality, for all disinfectants.

19 active ingredient in several EPA registered disinfectants.

20 tion by predator organisms, antibiotics, and disinfectants.

21 its intrinsic resistance to antibiotics and disinfectants.

22 line glutaraldehyde, and other commonly used disinfectants.

23 extensive decontamination using nonspecific disinfectants.

24 vated by alcohol- and aldehyde-based surface disinfectants.

25 oramine, chlorine dioxide, and copper-silver disinfectants.

26 especially for workers repeatedly exposed to disinfectants.

27 consumer and industrial products, including disinfectants.

28 consumer and industrial products, including disinfectants.

29 en species (ROS) production upon exposure to disinfectants.

30 activity of 16 clinically relevant drugs and disinfectants.

31 disinfectants, especially with more reactive disinfectants.

32 ne, along with pools treated with these same disinfectants.

33 nificant cross-resistance to genome-damaging disinfectants.

34 that they can be inactivated by other common disinfectants.

35 from deleterious external attacks including disinfectants.

36 ) and a DWDS in Norway with minimal residual disinfectant (0.08 +/- 0.01 mg L(-1)).

37 In tests with the two bactericidal disinfectants, 22 of 1,639 cultures (1.3%) in the chlori

38 An understanding of disinfectant action and microbial resistance to treatmen

39 e parameters, was first applied to bacterial disinfectant action and then was successfully used to mo

40 mg/L) and produced up to a 0.8 log reduction disinfectant activity.

41 ever, BAC filtration or addition of residual disinfectants alone tended to increase these indicators.

42 guanide or hexamethylene components of other disinfectants (ALX, PHMB) can be detected by SPT, PHMB I

43 Hydrogen peroxide (H2O2) is an important disinfectant and bleach and is currently manufactured fr

44 water utilities using chlorine as a primary disinfectant and chloramines for maintenance of a distri

45 ch bleach was used); UV (quaternary ammonium disinfectant and disinfecting ultraviolet [UV-C] light e

46 Watson model with first-order dependences on disinfectant and infective phage concentrations.

47 Ozone is a commonly applied disinfectant and oxidant in drinking water and has more

48 s, either for micropollutant control or as a disinfectant and preoxidant in certain reuse processes.

49 It is used in water supply treatment as a disinfectant and slime preventive and has an advantage o

50 eatment plants using chlorine as an upstream disinfectant and the extent and rate at which those chan

51 the specific biomolecules reacting with the disinfectant and the mechanism of disinfection remains e

52 the organism and aid development of improved disinfectant and therapeutic agents.

53 As silver is often used as a disinfectant and treatment for burn wounds, we present h

54 Disinfectant and water age were both observed to be stro

55 ese clinical features, as they resist common disinfectants and antibiotic treatment.

56 There are numerous disinfectants and antiseptics for treating materials in

57 termining virus infectious doses, evaluating disinfectants and antivirals, and developing vaccines.

58 This EPS strongly protects cells against disinfectants and desiccation, indicating its potential

59 Overall, brief exposure to broad-spectrum disinfectants and direct steam could be used to limit D.

60 me plasmid underscore the potential roles of disinfectants and heavy metals in the coselection of ARG

61 breaks, its resistance to antimicrobials and disinfectants and its persistence on human skin and in t

62 ucts (DBPs) that form from reactions between disinfectants and nitrogen-containing precursors, the la

63 e environmental hazards such as antibiotics, disinfectants and oxidative stress agents by modulating

64 Disinfectants and skin application processes were standa

65 than the samples treated with chlorine-based disinfectants and was not significantly different compar

66 two quaternary ammonium compound (QAC)-based disinfectants, and 1.4% hydrogen peroxide.

67 ch avoids primary chemical-based coagulants, disinfectants, and advanced oxidation processes.

68 unusually robust resistance to antibiotics, disinfectants, and desiccation.

69 factors such as high temperature, radiation, disinfectants, and drying.

70 eposits protect the associated bacteria from disinfectants, and due to their mobility, the associated

71 interactions among water quality parameters, disinfectants, and iodine sources, compounded by the dif

72 ysts in the environment or after exposure to disinfectants, and therefore their potential infectivity

73 Antibiotic-, disinfectant-, and heavy-metal-resistant genes on the sa

74 dose; resistance to heat, drying, and common disinfectants; and lack of prophylactic therapies.

75 ture research should investigate long-acting disinfectants, antimicrobial surfaces, and more effectiv

76 is evolving, future research with additional disinfectants, application methods, and environmental co

77 ibuted to improving our understanding of how disinfectants, applied to control biofouling of reverse

78 (DBPs) can form from these contaminants when disinfectants are applied during or after reuse treatmen

79 In-building disinfectants are commonly applied to control the growth

80 None of the common disinfectants are effective in killing the parasite beca

81 ort the recommendations to use alcohol-based disinfectants as prevention measures or in outbreak situ

82 cyanuric acid (TCICA)-a common swimming pool disinfectant-as opposed to previously employed reagents

83 , bleach, and ammonia; minimizing the use of disinfectants; avoidance of mixing products; use of resp

84 Mask wearing and bleach disinfectants became commonplace during the COVID-19 pan

85 peroxide, formaldehyde, and the iodine-based disinfectant Betadine; (iii) the absence of DPA increase

86 ance (AMR), heavy metal resistance (HMR) and disinfectants/biocide resistance (DBR).

87 s exist that widespread use of antiseptic or disinfectant biocides could contribute to the emergence

88 and matching isolates were recovered from a disinfectant bottle and nearby sink.

89 ability of drinking water without a residual disinfectant, but the conventional microbiological cultu

90 raviolet (UV) light is being considered as a disinfectant by the water industry because it appears to

91 loramines are the second most used secondary disinfectant by United States water utilities.

92 ions of dibromoacetonitrile (DBAN), a common disinfectant by-product found in many water supply syste

93 is likely due to not only the consumption of disinfectants by the biofilm and the reduced disinfectan

94 s, including preservatives, antioxidants and disinfectants, by evaluating the performance of differen

95 everal constituents including alkalinity and disinfectant byproducts served as indicators of municipa

96 red water chemistry (metals, alkalinity, and disinfectant byproducts) and microbiology (total cell co

97 Disinfectants can cause tonometer tips to swell and crac

98 eter prisms in eye care and to highlight how disinfectants can damage tonometer tips and cause subseq

99 Various primary disinfectants can deactivate NDMA precursors prior to ch

100 Environmental stressors such as heat and disinfectants can inactivate virus particles and prevent

101 emic; however, the extensive use of chemical disinfectants can threaten human health and ecosystems.

102 (PbO(2)) scales destabilized as a result of disinfectant change.

103 resenting distribution networks experiencing disinfectant changeover from free chlorine to monochlora

104 Intensive monitoring following the disinfectant changeover may be required to determine the

105 Effects of disinfectant (chloramines, chlorine), water age (2.3 day

106 lication to pool water, they can (1) release disinfectant chlorine or (2) stabilize the free availabl

107 xidation of the corrosion scales by residual disinfectant chlorine released Cr(VI) and exhibited a th

108 Ms), and nitrosamines (NAs) from the popular disinfectants chlorine, chloramine, and ozone.

109 Cs could serve as a water recovery system, a disinfectant/cleaner generator that limits undesired bio

110 Disinfectant combinations should be optimized to reduce

111 Utilities are exploring new disinfectant combinations to reduce the formation of reg

112 iclosan (TCS), employed as an antiseptic and disinfectant, comes into direct contact with humans thro

113 rapid and facile fabrication of enzyme-based disinfectant composite coatings with high activity and s

114 Disinfectant concentration had the strongest effect on b

115 iments was clearly shaped by BAC filtration, disinfectant conditions, and water age.

116 Peracetic acid (PAA) is a disinfectant considered for use in ballast water treatme

117 Bromine is a versatile disinfectant consisting of different chemical forms with

118 ng system materials and two commonly applied disinfectants, copper and chloramines, on water chemistr

119 Implementation of copper as a disinfectant could help reduce OPs, but a mechanistic un

120 ther adding phosphate prior to switching the disinfectant could mitigate lead release.

121 Kinetic models for disinfectant decay and disinfection byproduct (DBP) form

122 Disinfectant decay was noted with water age, particularl

123 agnant water, where the relationship between disinfectant decay, microbial growth, and water age is p

124 Because ClO(2) exhibits lower disinfectant demand than chlorine, substantially lower c

125 DUWL disinfectants designed for continuous presence in irriga

126 After these results, the disinfectant dosage was increased to between 6 and 10 mg

127 Furthermore, choice of disinfectant, dose, and predisinfection treatment at the

128 conditions including different pH levels and disinfectant doses that are typical of drinking water di

129 cast iron corrosion in contact with residual disinfectants, drinking water distribution systems have

130 n animal bioassay, we compared the TSE agent disinfectant efficacy of a commercially available produc

131 For both disinfectants, electrochemical measurements supported a

132 Chemical disinfectants employed in water and wastewater treatment

133 lt of particular concern was the tendency of disinfectants, especially monochloramine, to enrich ARGs

134 viruses in the environment and resistance to disinfectants, especially with more reactive disinfectan

135 r strategies: reference (quaternary ammonium disinfectant except for C difficile, for which bleach wa

136 ditions, biofilms were prepared under either disinfectant exposure (predisinfected biofilms) or disin

137 After three months of the disinfectant exposure process, the disinfected biofilms

138 biofilm thickness within the first month of disinfectant exposure was presumably due to the consumpt

139 torage tanks may protect microorganisms from disinfectant exposure, causing the degradation of water

140 However, by the second to third month during disinfectant exposure, the biofilm mean stiffness showed

141 After the first month of disinfectant exposure, the mean stiffness of monochloram

142 mum, suggesting that the biofilms adapted to disinfectant exposure.

143 Thus, understanding how long-term residual disinfectants exposure affects biofilm mechanical and st

144 organic pollutants such as dyes, pesticides, disinfectants, food additives and antibiotics, along wit

145 Ozone, a known disinfectant for aqueous solutions, is known to promote

146 that natural sunlight may be effective as a disinfectant for contaminated nonporous materials.

147 luated extensively as an alternative halogen disinfectant for inactivation of Cryptosporidium parvum

148 Peracetic acid (PAA) is an emerging disinfectant for municipal wastewater treatment owing to

149 ption of antisense gene silencing as a novel disinfectant for prokaryotic organisms is hindered by po

150 hich has led to consideration of alternative disinfectants for their control.

151 ectant exposure (predisinfected biofilms) or disinfectant-free (untreated biofilms) conditions, respe

152 ts two case studies in which a change in the disinfectant from free chlorine to chloramine caused an

153 nt of their scales, a change in the residual disinfectant from free chlorine to monochloramine can de

154 r(-)-containing source waters when switching disinfectant from free chlorine to monochloramine.

155 No inhibition by antibacterial agents or disinfectants from the hospital was observed in the MBR.

156 lution of chromosomal AMR to triclosan (TCS) disinfectant has correlated effects on modulating bacter

157 n proposed, but dental unit waterline (DUWL) disinfectants have received little attention; specifical

158 In simulated clinical procedures, the disinfectant ICX reduced bacteriophage detection substan

159 For all disinfectants, immersion in 1% solutions caused 100% mor

160 indings suggest that unrestricted use of TCS disinfectant imposes a dual impact on bacterial antibiot

161 which was found to be an effective TSE agent disinfectant in a previous study.

162 rhexidine is widely used as an antiseptic or disinfectant in both hospital and community settings.

163 ient of household bleach, is the most common disinfectant in medical, industrial, and domestic use an

164 Dosed cupric ions acted as a disinfectant in stratified stagnant pipes, inhibiting cu

165 tone, and mucin) was combined with 50 muL of disinfectant in suspension for 0.5, 1, 5, or 10 min at 2

166 Chlorine is widely used as a disinfectant in the water industry, and the residual fre

167 ative role of exposure to surgical smoke and disinfectants in the observed association.

168 oom for significant improvement in anti-MRSA disinfectants, including the compounds themselves and th

169 the JSRV vector was inactivated by standard disinfectants, indicating that JSRV vectors pose no unus

170 ttracted considerable attention for use as a disinfectant ingredient for various applications over th

171 courage that the future development of novel disinfectants instead focus on five specific design elem

172 chloramines are commonly used drinking water disinfectants intended to safeguard public health and cu

173 wback associated with the use of chlorine as disinfectant is its potential to react with precursor su

174 n iron corrosion scales by chlorine residual disinfectant is the dominant reaction to form carcinogen

175 tems, often achieved through the addition of disinfectants, is essential to limiting waterborne illne

176 ct of a potential biological implant surface disinfectant, leukocyte- and platelet-rich fibrin (L-PRF

177 overed from the spa, despite apparently high disinfectant levels.

178 rventions to improve water flow and increase disinfectant levels.

179 Common water disinfectants like chlorine have been reported to select

180 a complex system of reactions that leads to disinfectant loss and DBP formation.

181 Cleaning sprays, bleach, ammonia, disinfectants, mixing products, and specific job tasks h

182 a steady state and enables in vitro tests of disinfectant mouthwashes in simulated clinical use.

183 used water with monochloramine as a residual disinfectant (odds ratio 10.2 [95% CI 1.4-460]).

184 compared with the most commonly used peracid disinfectant of municipal wastewater, peracetic acid (PA

185 owever, the side effects of the use of these disinfectants often result in the generation of toxic re

186 ast 1 worker admitted sometimes spraying the disinfectant on the ear studs before piercing.

187 The effect of DUWL disinfectants on total aerosol concentration was assesse

188 dy aims to 1) investigate the effect of DUWL disinfectants on viral dispersion in dental bioaerosols

189 , a widely used class of quaternary ammonium disinfectants, on microbial community structure and anti

190 about the efficacy of laundry detergents and disinfectants or the reduction of risk achieved by washi

191 d compounds including antibiotics, household disinfectants, organic solvents and other toxic chemical

192 were reduced by 4 log(10) (99.99%) for both disinfectants over the duration of the experiments.

193 endoscopic test pieces with plasma activated disinfectant (PAD) resulted in a 7.30 log(10) reduction

194 disinfectants by the biofilm and the reduced disinfectant penetration into the biofilm but also the c

195 However, microbial activity and disinfectant penetration within water storage sediment r

196 PS components with monochloramine influenced disinfectant penetration, biofilm inactivation, as well

197 sis of acetate esters to generate the potent disinfectant, peracetic acid (PAA).

198 d homo- and heterocyclic aromatics including disinfectants, pesticides and pharmaceuticals raise conc

199 Interactive effects of disinfectant, pipe material, and water age on both bacte

200 ibutions from the wells and without residual disinfectant present in these systems, any increase in v

201 Combined coagulation-disinfectant products had the highest LRV performance fo

202 arious agricultural, hospital and veterinary disinfectant products.

203 To improve the understanding of disinfectant-protein reactions, this study characterized

204 tein reactions, this study characterized the disinfectant:protein molar ratios at which 50% degradati

205 ams (blaZ), aminoglycosides (aacA-aphD), and disinfectants (qacC).

206 increased human exposure to the widely used disinfectants quaternary ammonium compounds (QACs).

207 This targeting concurs with its high disinfectant rate constants and supports its hypothesize

208 targeting of amino acids is driven by their disinfectant rate constants rather than their geometrica

209 However, disinfectants react with organic matter and other consti

210 mplars of halogenated byproducts formed from disinfectant reactions with biomolecules within produce.

211 2 carbon aliphatic halogenated byproducts of disinfectant reactions with organic matter [disinfection

212 nd biofilm on the aged resin likely prompted disinfectant reactivity and inhibited BTEX diffusion int

213 DUWL disinfectants reduced bacteriophage viability, and inter

214 Disinfectants represent a crucial tool in killing infect

215 ion of distribution system conditions with a disinfectant residual of 1 mgC2 L(-1) showed complete co

216 r simulated drinking water flow containing a disinfectant residual was examined.

217 This study highlights the interaction among disinfectant residual, biofilms, and L. pneumophila, whi

218 ical or hydraulic pipe integrity and lack of disinfectant residual.

219 apparent at water ages corresponding to low disinfectant residual.

220 ration + chlorination, chloramination, or no disinfectant residual.

221 ration + chlorination, chloramination, or no disinfectant residual.

222 eria if chloramines are applied as secondary disinfectant residual.

223 vermiformis and the depletion of chloramine disinfectant residuals by nitrifying bacteria, leading t

224 te as an electron donor to quench chloramine disinfectant residuals in municipal wastewater effluents

225 ibution systems because they persist despite disinfectant residuals.

226 OPPPs share the common characteristics of disinfectant resistance and growth in biofilms in water

227 The higher disinfectant resistance of L. pneumophila released from

228 infectious forms of Lp also exhibit enhanced disinfectant resistance.

229 te intracellular growth to accurately assess disinfectant resistance.

230 and increase bacterial cell vulnerability to disinfectants, resulting in greater membrane damage and

231 Ozone, a strong oxidant and disinfectant, seems ideal to cope with future challenges

232 h the monkeypox virus (MPXV) by applying six disinfectant solutions (and three controls) on six surfa

233 and cysticidal efficacy of four multipurpose disinfectant solutions (MPDSs) and a one-step hydrogen p

234 tion of H(2)O(2) in real samples (commercial disinfectant solutions and tap water samples).

235 ersion and spray treatments of 1%, 2% and 4% disinfectant solutions were examined for applications of

236 anic matter suspended in water that consumes disinfectants) sourced from operational drinking water d

237 in influent were those used most commonly in disinfectants, specifically benzylalkyldimethylammonium

238 by weight) in hard water, and a ready-to-use disinfectant spray with 58% ethanol (EDS), were tested a

239 ons for the testing and use of alcohol-based disinfectant sprays and printing inks.

240 del, we included the use of cleaning sprays, disinfectant sprays, and nonspray disinfection methods,

241 ing agents (cleaning products/detergents and disinfectants) starting before conception, in the 2-year

242 yproducts (DBPs) formed from the reaction of disinfectants such as chlorine and monochloramine with o

243 g from free chlorine to alternative chemical disinfectants such as monochloramine may result in the f

244 ly lowered their susceptibility threshold to disinfectants such as ozone, chloramine B, and free chlo

245 osure to PAD in comparison to the commercial disinfectant, suggesting the developed approach is no mo

246 /L to more than 150 mug/L as a result of the disinfectant switch when phosphate was not present.

247 Chlorhexidine (CHX) is a widely utilized disinfectant that can cause IgE-mediated urticaria/anaph

248 tudy show that monochloramine is a promising disinfectant that can prevent Legionella contamination o

249 Chlorocyanurates are chlorine-based disinfectants that have been used for drinking water in

250 ld be employed to devise methods of applying disinfectants that minimize byproduct formation while ac

251 onella nutrient, while also directly causing disinfectant to decay more rapidly.

252 is increasingly being used as an alternative disinfectant to free chlorine to maintain a residual in

253 Performic acid (PFA) is an emerging disinfectant to inactivate bacterial and viral microorga

254 For experiments with water flow containing a disinfectant to release the biofilm-associated L. pneumo

255 ochloramine (MCA) is a widely used secondary disinfectant to suppress microbial growth in drinking wa

256 e(VI)O(4)(2), Fe(VI)) is an emerging oxidant/disinfectant to treat a wide range of contaminants and m

257 eness of three commonly used, broad-spectrum disinfectants to cause mortality of D. villosus: Virasur

258 ritate the cornea, harbor microbes, or allow disinfectants to enter the interior of the tonometer tip

259 n with smaller dosages of secondary chemical disinfectants to minimize microbial regrowth in distribu

260 hlorides (BACs)-an active ingredient of many disinfectants-to benzyldimethyl amine (BDMA) was identif

261 , predictive models might be used to monitor disinfectant tolerance in food production and might supp

262 Overall, disinfectant towelette efficacy is dependent upon produc

263 Overall, the HP-based disinfectant towelette was significantly more fungicidal

264 y more fungicidal than the QAC-alcohol-based disinfectant towelette.

265 ernary ammonium chloride (QAC)-alcohol-based disinfectant towelettes irrespective of tested contact t

266 , we tested the efficacies of EPA-registered disinfectant towelettes products that are increasingly u

267 Hydrogen peroxide (HP)-based disinfectant towelettes were more efficacious against C.

268 ly lead to the development of more effective disinfectant treatments.

269 The effects of pH, disinfectant type (free chlorine and monochloramine), an

270 uential in chloraminated systems and primary disinfectant type (HOCl vs O(3)) in chlorinated systems.

271 Disinfectant type and dose was observed to have the stro

272 Results varied by disinfectant type and surface type.

273 d dissolved organic carbon (DOC) and primary disinfectant type were the two most important contributo

274 to examine the influence of pipe materials, disinfectant type, and water age on occurrence and persi

275 e appeared to display a distinct response to disinfectant type, pipe materials, water age, and their

276 and transform, shaped by factors such as the disinfectant type, water chemistry, biofilms, and pipe m

277 MS2 and hNoV GII in PB at CT values for both disinfectants up to 450 mg-min/L.

278 Due to the COVID-19 pandemic, disinfectant use has increased, purportedly increasing l

279 Polyhexamethylene biguanide (PHMB) is a disinfectant used in swimming pools and hot tubs.

280 ed interest in L. monocytogenes tolerance to disinfectants used in the food industry.

281 diction of L. monocytogenes tolerance to QAC disinfectants used in the food industry.

282 sing results for predicting tolerance to QAC disinfectants using WGS and machine learning.

283 The sensitivity of enteroviruses to disinfectants varies among genetically similar variants

284 of 0.2% chlorine peroxide as a bactericidal disinfectant was compared to that of 10% providone iodin

285 We found handling disinfectants was the most significant risk factor for m

286 th chlorine, a common drinking-water oxidant/disinfectant, was investigated.

287 Disinfectant washing and freezing are among the most use

288 water containing free chlorine as a residual disinfectant were more likely to have a reported outbrea

289 bly, neither contact lens care solutions nor disinfectants were associated with corneal staining.

290 s surfaces, and >=99.40% for wood, QAC-based disinfectants were efficacious on nonporous surfaces (>=

291 Disinfectants were wiped on carriers in triplicate, with

292 insecticide-treated bednets, soap, and water disinfectant) were marketed in 30 intervention villages

293 inhaled agents, including surgical smoke and disinfectants, which are associated with adverse respira

294 Surface cleaning using commercial disinfectants, which has recently increased during the c

295 nts with IgE-mediated CHX allergy with other disinfectants, which share structural similarities with

296 ater treatment from the reaction of chemical disinfectants with natural organic matter (NOM), anthrop

297 t and an active ingredient of EPA-registered disinfectants with wide human exposure in various agricu

298 er assay were completely inactivated by each disinfectant within 1-5 min contact time.

299 viruses become inactivated by drinking water disinfectants would facilitate the development of sensor

300 ruses can exhibit resistance to common water disinfectants, yet the mechanisms that allow them to tol