ライフサイエンスコーパス: biocide

1 a novel BWMS that employs granular DICD as a biocide.

2 protect cells from the toxic effects of the biocide.

3 (2)), an extremely effective and fast-acting biocide.

4 inical settings in which silver is used as a biocide.

5 and uncharged aqueous ammonia (NH3), a known biocide.

6 he exposed cultures into fresh media lacking biocide.

7 s display resistance to this membrane-active biocide.

8 ammonia relative to other metal(oxides) and biocides.

9 glutaraldehyde- and isothiazolone-based test biocides.

10 onmental stresses and increased tolerance to biocides.

11 e to multidrug resistance to antibiotics and biocides.

12 ave potential applications for this class of biocides.

13 contains growth substrates as well as toxic biocides.

14 l stimuli for ROS release to be effective as biocides.

15 structurally diverse and clinically relevant biocides.

16 s, lozenges, throat and nasal sprays, and as biocides.

17 de more potent than commonly used industrial biocides.

18 on half-lives even for many rapidly degraded biocides.

19 products that contain formaldehyde-releasing biocides.

20 aps that should be considered when selecting biocides: (1) uncharged species will dominate in the aqu

21 fracturing fluids (e.g., quaternary ammonium biocides, 2-butoxyethanol) and downhole transformations

22 amic therapy agents, radiotherapy agents and biocides; (3) metal-containing polymers as biosensors, a

23 ell as other organic solvents and commercial biocides across a large and clinically important concent

24 greatest difference of 75% with and without biocide addition for unamended soil, while the lowest PA

25 uticals, personal care products, pesticides, biocides, additives, corrosion inhibitors, musk fragranc

26 ispersed and contamination of soil with this biocide adversely affects its functional biodiversity, p

27 e that activated PS is an effective chemical biocide against species of marine phytoplankton.

28 d with zerovalent iron (Fe(0)) as a chemical biocide against two taxa of marine phytoplankton grown i

29 of Escherichia coli's populations exposed to biocide and antibiotic combinations lead to more accurat

30 In addition, biocide and heavy metal resistance genes were prevalent,

31 stance to cadmium and arsenic, as well as to biocides and antibiotics.

32 ncrease their susceptibility toward standard biocides and antibiotics.

33 ce interactions, and provide protection from biocides and antimicrobial agents.

34 etabarcoding, to establish correlations with biocides and climate change records.

35 eudomonas aeruginosa to many antibiotics and biocides and hamper research focused on the discovery an

36 AOs among categories of substances, such as biocides and metals, were demonstrated.

37 dings will help guide the appropriate use of biocides and other antimicrobials in food production set

38 The emissions of biocides and their transformation products from building

39 B1 (UB1), exhibiting strong activity against biocides and vancomycin-resistant Staphylococcus aureus

40 Sunlight is a known biocide, and photodriven inactivation is an important av

41 mplex genetic targets, including antibiotic, biocide, and virulence determinants that can be highly t

42 eratures, exposure to chemical additives and biocides, and brine-level salinities.

43 nrelated agents, including fluoroquinolones, biocides, and dyes, resulting in a multidrug resistant (

44 s of fragrances, flame retardants, solvents, biocides, and dyes.

45 adsorbing cellulosic fibers do not leach any biocides, and it is an environmentally sustainable and c

46 lecules associated with medications, outdoor biocides, and microbially derived compounds were distrib

47 ardants, stabilizers, flocculants, pigments, biocides, and preservatives.

48 The rise of biocide- and antibiotic-resistant microbes in hospital s

49 results suggest the necessity of optimizing biocide application at the level of individual shale pla

50 Four months after the initial biocide application, a new outbreak appeared in the form

51 mechanisms, which enable the optimization of biocide application, hold significant implications for g

52 les collected between 2007 and 2008, and the biocides applied were not effective in eliminating this

53 he black stains and the effectiveness of the biocides applied, by using cloning, denaturing gradient

54 We also show that the toxic actions of this biocide are zinc dependent and require the activation of

55 Biocides are added to facade paints and renders to preve

56 Biocides are applied to control biological activity, oft

57 Biocides are common additives in building materials.

58 Chemical biocides are commonly employed to manage problems caused

59 Biocides are critical components of hydraulic fracturing

60 The results show that some biocides are degraded rapidly in soil (e.g., isothiazoli

61 ible for bacterial inactivation with various biocides are fairly well understood, virus inactivation

62 Biocides are included in organic building facade coating

63 Consequently, residues of some biocides are likely to be continuously present due to re

64 Medicines and agricultural biocides are often discovered using large phenotypic scr

65 Treatments with antibiotics or biocides are often ineffective in eradicating biofilms.

66 to soils and be less bioavailable; (2) many biocides are short-lived or degradable through abiotic a

67 Chemical biocides are used for the prevention and control of infe

68 Antimicrobial biocides are widely used in critical human health situat

69 at incorporating PMA into standard DNA-based biocide assessment protocols is both feasible and benefi

70 electrochemically released back as a potent biocide at 1.3 V vs Ag|AgCl, reducing marine growth by 9

71 es C the organisms are damaged: in this case biocides at concentrations 10x lower than in normal appl

72 r of avenues for building powerful selective biocides based on combinations of colloid antibodies and

73 olluted runoff water (up to several mg L(-1) biocides) being infiltrated into the soil surrounding ho

74 nal care products, along with pesticides and biocides can accumulate in ephippia with log BCF values

75 Biocides can also promote the transfer of antimicrobial

76 ously present due to repeated input and most biocides can be considered as "pseudo-persistent"-contam

77 ldehyde, highly toxic compounds, which, as a biocide, can lead to numerous health ailments.

78 bactericidal mechanisms vary among different biocide chemistries.

79 varying in polarity, such as UV blockers and biocide compounds in water, and the data were in good ag

80 Biocide concentrations tend to be higher in the early li

81 analyzed to measure total organic carbon and biocide concentrations using the Total Organic Carbon An

82 6-1.27]), and in samples with lower residual biocide concentrations.

83 ategy for combating marine fouling is to use biocide-containing paints, but environmental concerns an

84 widespread use of antiseptic or disinfectant biocides could contribute to the emergence and spread of

85 makes PS an attractive alternative to other biocides currently in use for ballast water treatments a

86 The LOQ was 10 ng g(-1) for the majority of biocides depending on the matrix.

87 Biocides detected in wristbands included p,p'-dichlorodi

88 based methods that are widely used to assess biocide effectiveness often cannot distinguish between l

89 consider the impact of bacteria that survive biocide exposure in environmental and clinical contexts.

90 ed to have effects on bacterial fitness upon biocide exposure, suggesting that these compounds may ha

91 r persistent compounds; (3) understanding of biocides' fate under downhole conditions (high pressure,

92 In addition to flutamide, the biocides fenitrothion, vinclozolin and linuron significa

93 anic anion, hexafluoroarsenate, an arsenical biocide found recently in wastewater.

94 could also confer resistance by exclusion of biocides from the bacterial community.

95 Rain is mobilizing these biocides from the facades and transports them to the sur

96 to extrude selected antibacterial drugs and biocides from the membrane, lowering their effective con

97 ng electrochemical bubble generation without biocide generation.

98 downhole chemistry of the commonly used HFF biocide glutaraldehyde (GA).

99 nhanced tolerance against the typically used biocide glutaraldehyde and increased susceptibility to t

100 formation was impeded in the presence of the biocide glutaraldehyde and was completely inhibited by s

101 lhexanol) in the absence and presence of the biocide glutaraldehyde were investigated under a range o

102 A mutant was confirmed by treatment with the biocide H(2)O(2) and by microscopic observations.

103 Booster biocides have been widely applied to ships and other sub

104 The membrane-active biocides hindered the propensity to develop bacterial re

105 effectiveness and safety of natural chemical biocide hydrogen peroxide (H(2)O(2)) for brown tide bloo

106 nd increased susceptibility to the oxidative biocide hypochlorite in a native and a model bacteria an

107 Copper, the most widely used biocide in antifouling paints, is at the brink of a tota

108 Terbutryn is a commonly used biocide in construction materials.

109 ted catalysis, leading to the formation of a biocide in situ, which resulted in the growth inhibition

110 Iodine is used as a biocide in spacecraft water.

111 r potential as a tool for not only detecting biocides in biological samples, but also mapping their d

112 h importance for the long-term assessment of biocides in coating materials.

113 method was successfully applied to quantify biocides in dairy products and feed.

114 for quantitative analysis of a wide range of biocides in dairy products and slurry feed.

115 Given that the determination of biocides in food and feed is currently not routinely don

116 increased resistance to a number of cationic biocides in K. pneumoniae and other members of the Enter

117 the potential to reduce/eliminate the use of biocides in MWFs, improves the feasibility of end-of-lif

118 on for reducing/eliminating the use of toxic biocides in MWFs, stimulating a growing interest in the

119 hat SmvA is a major efflux pump for cationic biocides in several bacterial species and that increased

120 d produced water, was exposed to widely used biocides including glutaraldehyde (Glut) and tetrakis(hy

121 es; (2) metal-containing polymeric drugs and biocides, including antimicrobial and antiviral agents,

122 rnative to tributyltin for antifouling paint biocides, inhibits the ubiquitin-proteasome system (UPS)

123 Biocides interact with multiple targets on the bacterial

124 The biocides irgarol and terbutryn enter the wastewater trea

125 none, a widely used industrial and household biocide, is highly toxic to cultured neurons but not to

126 ducts may be higher than those of the parent biocide, knowledge of the emissions of transformation pr

127 Biocides leach from the facade material with driving rai

128 Previous studies have shown that biocides leach out of the material when contacted with r

129 appropriate usage or low concentrations of a biocide may act as a stressor while not killing bacteria

130 There is concern that resistance to topical biocides may be emergeing, although the potential clinic

131 ence Gene Catalog, to include putative acid, biocide, metal, stress resistance genes, in addition to

132 ur results support the concern that residual biocides might promote antibiotic resistance in pathogen

133 The results show that biocides, musk fragrances, and other personal care produ

134 ite overall high stability of QACs and their biocide nature, the ones with perfluoroalkyl chains can

135 Further, these biocides not only inhibited the formation of biofilms bu

136 niae with chlorhexidine and another cationic biocide, octenidine, resulted in increased expression of

137 effects of methylisothiazolinone and related biocides on neurons have not been reported previously.

138 ARGs appear to co-occur with antibacterial biocide or metal resistance genes.

139 y, many pathogens can be combatted only with biocides or environmentally dangerous fumigants.

140 50 parts per thousand sea salts, without any biocides or pond crashes, for over 143 days.

141 tor), tetramethylammonium (clay stabilizer), biocides or strong oxidants.

142 ionary-phase cells were more tolerant to the biocide peracetic acid than were biofilms.

143 in a standard DNA-based workflow to evaluate biocide performance more accurately.

144 fort, we advocate for its adoption in future biocide performance studies, in particular for engineere

145 ocarbons, industrial chemicals, and a set of biocides, pesticides, and pharmacologically active subst

146 signed-bioactive anthropogenic contaminants (biocides, pharmaceuticals) comprised 57% of 406 organics

147 ted DADMAC C8:C8 and C8:C10, two widely used biocides previously unreported in environmental samples.

148 Most biocides primarily target the cytoplasmic membrane and e

149 f AceI, chlorhexidine, an entirely synthetic biocide produced only during the last century.

150 ants are known to be associated with natural biocide production, they have not been evaluated for the

151 fouling coatings, restrictions on the use of biocide-releasing coatings have made the generation of n

152 avy metal resistance (HMR) and disinfectants/biocide resistance (DBR).

153 We also observed multi-metal and multi-biocide resistance across all water types.

154 ormed to characterize antibiotic, metal, and biocide resistance genes.

155 ting the importance of RND efflux systems in biocide resistance in S. marcescens.

156 Biocide resistance mechanisms share many themes with ant

157 Efforts to fundamentally understand biocide resistance mechanisms, which enable the optimiza

158 nt role in the acquisition of antibiotic and biocide resistance, especially through the formation of

159 mediated stress response could contribute to biocide resistance.

160 a mechanistic interpretation of the altered biocide resistance.

161 wn bacteria might develop a biofilm-specific biocide-resistant phenotype.

162 ed with glutaraldehyde, further lowering the biocide's aqueous concentration.

163 Moreover, the biocides showed negligible toxicity against mammalian ce

164 e U.S. concerning persistent polychlorinated biocides, showing a potential path forward to judicious

165 There are concerns that biocide skin and mucous membrane decolonisation, which i

166 like wild-type biofilms are sensitive to the biocide sodium dodecyl sulfate.

167 as during different injection intervals of a biocide (sodium azide) which allowed monitoring biofilm

168 The use of biocides such as glutaraldehyde and quaternary ammonium

169 An ATP-based biocide susceptibility assay for mycobacteria was develo

170 The biocides synthesized via a facile methodology not only d

171 the release of several commonly used organic biocides (terbutryn, Irgarol 1051, diuron, isoproturon,

172 ed that sub-inhibitory concentrations of the biocides that dissipate membrane potential can promote A

173 pounds (QACs) represent widely used cationic biocides that persist in natural environments.

174 oor monuments, largely depends on the use of biocides, that may be dangerous for the users, the envir

175 understanding of the mechanisms of action of biocides, the bacterial resistance mechanisms encompassi

176 fort has gone into the development of potent biocides, the effectiveness of many first-line antibioti

177 ltidrug efflux systems and that this popular biocide therefore readily selects mutants which are cros

178 Adding biocides, though effective in reducing microbial growth,

179 e, engineered systems are often treated with biocides to control microbiologically influenced corrosi

180 We coined the term endocides (endogenous biocides) to describe such metabolites that can poison o

181 there is a biologically driven mechanism to biocide tolerance in produced water.

182 ch facilitates bacterial survival and alters biocide tolerance.

183 e and account for the long-term emissions of biocide transformation products from building facades to

184 Although the emissions of biocide transformation products may be higher than those

185 providing broad resistance to environmental biocides, transporters from the small multidrug resistan

186 erbutryn degradation products in soils below biocide treated facades.

187 his study we report on the efficacy of novel biocide treated filters and their antimicrobial activity

188 Biocide-treated communities, in comparison to untreated

189 ganisms are probably linked to the intensive biocide treatments and to the anthropogenic changes intr

190 he negative effects associated with standard biocide treatments are absent.

191 ds like quaternary ammonium surfactants, the biocide triclocarban, and the tentative identification o

192 d TraDIS-Xpress to identify responses to the biocide triclosan across a range of concentrations.

193 Using the biocide triclosan as a selective agent, several triclosa

194 hat correlates with resistance to the common biocide triclosan in Mycobacterium smegmatis, binding to

195 azaborine class of antibacterial agents, the biocide triclosan, and one of the targets for the front-

196 NR is also the target for the broad-spectrum biocide triclosan.

197 ide range of different concentrations of the biocide Triclosan.

198 t regulation of plant protection product and biocide use.

199 nt study the degradation rates in soil of 11 biocides used for the protection of building materials w

200 review of the potential fate and toxicity of biocides used in hydraulic fracturing operations.

201 ds insight into the potential utility of non-biocide virulence inhibitors in treating skin infections

202 C), in parallel to the application of three biocides, was verified in the laboratory with six epi- a

203 nes are required for A. baumannii fitness in biocides, we confirmed that sub-inhibitory concentration

204 Biocides were applied for three years to control this ou

205 Several biocides were identified as major risk contributors, wit

206 Therefore, biocides were used again in 2008.

207 Microencapsulation of biocides with edible coatings represents a highly target

208 controlling contamination of fish by booster biocides, with low consumption of biodegradable reagents

209 ls including pharmaceuticals, pesticides and biocides; with logK(ow) (logarithmic octanol-water parti