ライフサイエンスコーパス: remediation

1 desirable properties for in situ groundwater remediation.

2 uction materials and crude oil, and in water remediation.

3 isms have been widely applied in heavy metal remediation.

4 mmendations for surveillance modalities, and remediation.

5 pollutants and lead to useful strategies for remediation.

6 mercury capture and therefore environmental remediation.

7 on processes (AOPs) applied in soil or water remediation.

8 lysis but also in other fields such as water remediation.

9 rget for KRAS-associated lung adenocarcinoma remediation.

10 impaired, unless the OSPW has received some remediation.

11 on programs were more likely to use resident remediation.

12 ategy for low permeability contaminated soil remediation.

13 d by natural leachate and acid mine drainage remediation.

14 r value commodity chemicals or environmental remediation.

15 high efficiency of fire whirls for oil-spill remediation.

16 s, robust shock absorbers, and environmental remediation.

17 of solar energy conversion and environmental remediation.

18 dioactive waste management and environmental remediation.

19 olecular gels as materials for environmental remediation.

20 e, methane production) during full-scale RDX remediation.

21 that neutralize pollutants for environmental remediation.

22 fuels and commercial products to hydrocarbon remediation.

23 grafts which is followed by its photothermal remediation.

24 echnology for nonaqueous-phase liquid (NAPL) remediation.

25 eing increasingly utilized for environmental remediation.

26 mistry, gas valorization, and greenhouse gas remediation.

27 als placed in the subsurface for contaminant remediation.

28 tential applications including environmental remediation.

29 in biomedical engineering and environmental remediation.

30 ZVI) is a promising material for groundwater remediation.

31 ed process intensification for environmental remediation.

32 ation, wastewater treatment, and contaminant remediation.

33 erstand in situ technologies for groundwater remediation.

34 D-impacted stream over the first 6 months of remediation.

35 than high-attrition programs to use resident remediation (21.0% vs 6.8%; P < .001).

36 that bauxite could be an affordable fluoride-remediation adsorbent with the potential to improve acce

37 nZVI) has shown potential to be an effective remediation agent for uranium-contaminated subsurface en

38 output hold potential for evaluating UV as a remediation alternative in areas such as wastewater trea

39 of its promising application in groundwater remediation, although its synthesis is still a challenge

40 facilitate strategies for simultaneous soil remediation and agricultural production, but a thorough

41 tself key to develop the most efficient soil remediation and agricultural techniques, and better pred

42 ural chars and human-made chars used in soil remediation and agriculture.

43 important electrochemical pathway for water remediation and arsenic detection.

44 tions of micro/nanomachines in environmental remediation and beyond.

45 This paper discusses challenges in remediation and bioavailability assessments of Pb in urb

46 nvironment due to their use in environmental remediation and biomedical applications, potentially har

47 r mining safety, mine water utilization, and remediation and control of water environment is achieved

48 ion and storage, chemosensing, environmental remediation and energy storage.

49 The cognitive remediation and healthy-behaviors training groups did no

50 or the investigation of CO(2) storage, water remediation and hydrocarbon recovery processes.

51 es used as engineered geomedia for quinolone remediation and in developing transport models of antibi

52 Therefore, it is essential to explore how remediation and initial plant establishment can alter mi

53 ly understood, limiting the effectiveness of remediation and managing efforts after oil spills.

54 , logistic, and security challenges required remediation and medical protocols within the context of

55 omaterials' beneficial role in environmental remediation and membranes for water filtration, includin

56 application in next-generation environmental remediation and mercury sensing.

57 emistry, which is important to environmental remediation and microbial fuel cell development.

58 h has important implications for contaminant remediation and nutrient biogeochemical cycling.

59 at application potentials such as wastewater remediation and power generation.

60 ly investigated and applied in environmental remediation and protection, and in energy conversion and

61 al biogeochemistry of cobalt and in relevant remediation and resource recovery processes, are poorly

62 aterials is important for both environmental remediation and resource recycling.

63 s work, a novel study for acid mine drainage remediation and reutilization by means of a forward osmo

64 ul material applications, including advanced remediation and sensing technologies.

65 ontrolled trial of guanfacine plus cognitive remediation and social skills training (15 guanfacine, 1

66 ion on combined therapies, such as cognitive remediation and social skills training, have not been st

67 enhanced carbon fixation, and environmental remediation and to understand plant-microbiome interacti

68 as lignin biomass, providing opportunity for remediation and valorization of these materials.

69 the potential to develop strategies for mine remediation and waste stabilization by accelerating the

70 , including energy generation, environmental remediation, and antimicrobial treatment.

71 r batteries, water splitting), environmental remediation, and chemical production.

72 ied safety threats should be prioritized for remediation, and clinician behaviors that contribute to

73 ensor development, separation, environmental remediation, and drug delivery.

74 energy conversion and storage, environmental remediation, and important chemical production and indus

75 ncluding therapeutic delivery, environmental remediation, and nanoscale manufacturing.

76 in the fields of biomedicine, environmental remediation, and on-the-fly chemistry.

77 targeted cargo/drug delivery, environmental remediation, and other potential applications of micro/n

78 t implications for risk exposure assessment, remediation, and resource recovery of U and V in locatio

79 ncluding nanomaterial synthesis, heavy metal remediation, and the prevention of weathering.

80 osphorus cycling, metal homeostasis, organic remediation, antibiotic resistance and secondary metabol

81 ay be genetically tailored for environmental remediation applications or bioenergy production.

82 onomical material for multiple environmental remediation applications.

83 lly for water purification and environmental remediation applications.

84 In situ chemical oxidation (ISCO) is a remediation approach that is often used to remediate soi

85 al reduction (ISCR) has been proposed as one remediation approach, but the quantification of pollutan

86 nated with uranium can be used as an in situ remediation approach.

87 fate analyses and the development of in situ remediation approaches for treating impacted aquifers.

88 s at explosive-contaminated sites will allow remediation approaches that simultaneously target both c

89 issue for retrospective risk assessment and remediation approaches.

90 as in air/water treatments for environmental remediation are reviewed.

91 eochemical tracers for understanding in situ remediation becomes important in situations where down-g

92 croalgae are good candidates for toxic metal remediation biotechnologies.

93 roduction tools or as a high-rate, real-time remediation biotechnology.

94 mation is helpful not only for environmental remediation but also for the doping design of iron oxide

95 uld provide an opportunity for environmental remediation, but detailed catalytic mechanisms for these

96 n is a low-cost approach for crude oil spill remediation, but it is often limited by electron accepto

97 y of emerging technologies for environmental remediation by comparing nanotechnology and synthetic bi

98 tially opening new research lines focused on remediation by natural attenuation processes or engineer

99 s for groundwater management and contaminant remediation by providing microbially mediated buffering

100 on and free radicals and have potential soil remediation capabilities.

101 tal and industrial applications such as soil remediation, CO2 sequestration, and enhanced oil recover

102 active transport in relevance to groundwater remediation, CO2 sequestration, and enhanced oil recover

103 ns, basaluminite standards, and samples from remediation columns using synchrotron-based techniques a

104 2-DCA remains a challenging compound for the remediation community.

105 Technetium (Tc) remains a priority remediation concern due to persistent challenges, includ

106 two-in-one strategy to address environmental remediation concerns and chemical resource demands.

107 This approach to remediation could prime indigenous bacteria for degradin

108 growth in homes, assist with inspection and remediation decisions, and potentially lead to reduced e

109 application of microorganisms to heavy metal remediation depends on their resistance to toxic metals.

110 fferent remediation scenarios and to improve remediation design to maximize benefits while minimizing

111 ay minerals are widely used in environmental remediation due to their low-cost, adequate availability

112 to evaluate ecosystem service provision and remediation effectiveness in watersheds under future cli

113 emistry, metal transformation processes, and remediation effectiveness under exceptionally low-flow c

114 nowledge, this is the first investigation of remediation effects on AMD INPs and the first use of spI

115 inic accessible therapy may assist cognitive remediation effort for people with schizophrenia.

116 l impact the long-term sustainability of the remediation effort.

117 maceutical contamination concerns as well as remediation efforts emphasizing adsorption.

118 dlife that has been a focus of environmental remediation efforts for decades.

119 portant implications for enhancing oil spill remediation efforts in beach sands and coastal sediments

120 ary production in most lakes, protective and remediation efforts often seek to reduce P input.

121 ing the use of the oil dispersant COREXIT in remediation efforts, to determine whether obesogens were

122 mponent in nuclear fuel processing and waste remediation efforts.

123 ials used in water treatment and groundwater remediation-especially micro- and nanosized zerovalent i

124 nanoflowers may hold great promises in water remediation field and beyond.

125 osis, and adsorption has been used for their remediation from aqueous systems.

126 one dyes in the effluents and ways for their remediation from dyehouse effluents, focusing on enzymat

127 Pharmacological augmentation of cognitive remediation has been attempted, but the effects of augme

128 nt iron (nano-ZVI) particles for groundwater remediation has spurred research into the influence of t

129 The microbial remediation, however, can be a complex process since mic

130 AMD-generated INP behavior before and during remediation in a hydrologically dynamic alpine stream.

131 For successful remediation in coastal areas, permanent binding of mobil

132 nd has significant implications for chromium remediation in contaminated environments.

133 ocyanate (SCN(-)) is a contaminant requiring remediation in gold mine tailings and wastewaters global

134 ctive barrier (PRB) systems for arsenic (As) remediation in the presence or absence of microbial sulf

135 Cognitive remediation is an efficacious treatment for schizophreni

136 Phosphate remediation is important for preventing eutrophication i

137 G-ZVI is a common remediation material in permeable reactive barriers (PRB

138 n soil can play an important role in natural remediation mechanisms of carbamates.

139 we report the design and demonstration of a remediation method based on a concept of asymmetrical al

140 Adsorption remediation methods are easily integrated with wastewate

141 The performance limitations of existing remediation methods motivate efforts to develop effectiv

142 Moreover, surfactant remediation methods must be carefully analyzed in the la

143 Current nanomaterial and dispersant remediation methods neglect to investigate their adverse

144 nology and synthetic biology to conventional remediation methods.

145 iked sediments and soils (e.g., when judging remediation necessity or interpreting results of toxicit

146 The selective remediation of (99) TcO(4) (-) in the presence of a larg

147 stant to traditional groundwater treatments, remediation of 1,4-dioxane is often limited to costly ex

148 hus, a paradoxical outcome of the successful remediation of acid deposition is a globally widespread

149 prediction and, potentially, prevention and remediation of AMD.

150 been considered as effective phases for the remediation of aquatic environments, to remove anionic c

151 ides basic knowledge for risk assessment and remediation of both extractable and nonextractable DDT-r

152 ization of cement manufacturing will require remediation of both the CO(2) emissions due to the decom

153 ial of being applied to paddy fields for the remediation of Cd(II) pollution so as to reduce the risk

154 tion (ISCO) treatment aimed predominantly at remediation of chlorinated volatile organic compounds (c

155 biology as the optimal level of analysis for remediation of clinical relapse.

156 ved colloidal stability and transport during remediation of contaminated aquifers.

157 ir practical utility for water treatment and remediation of contaminated groundwater.

158 l and engineered systems, such as during the remediation of contaminated sites and in water treatment

159 m of environmental applications ranging from remediation of contaminated sites to biotechnology.

160 ron (nZVI) is an emerging technology for the remediation of contaminated sites.

161 This discovery will contribute toward the remediation of contaminated sites.

162 deal of effort has been made to address the remediation of contaminated soil/sediment following the

163 ty heating (ERH), to activate PS, to achieve remediation of contaminated, low permeability soil.

164 eresting as a smart system for detection and remediation of diverse pesticides and other contaminants

165 ot-gun proteomic technology to study the bio-remediation of environmental hazards by white-rot fungus

166 g increasing attention as a strategy for the remediation of environmental pollutants.

167 ish new methods for early identification and remediation of gait deficits.

168 These results indicate that in situ remediation of groundwater by phosphate addition provide

169 Remediation of groundwater impacted by per- and polyfluo

170 articles have excellent capacity for in situ remediation of groundwater resources contaminated by a r

171 drug design considerations and environmental remediation of halogenated contaminants.

172 demands in production of valuable chemicals, remediation of hydrocarbon pollutants and energy sustain

173 Remediation of industrial wastewater is important for pr

174 eration, likely undergirded by environmental remediation of marginal lands in the city.

175 paminergic medication and, thus, concomitant remediation of medication-induced impairment in decision

176 al model it enables validation and potential remediation of metalloprotein models, improving structur

177 Microbial remediation of metals can alleviate the concerns of meta

178 anthropogenic pollutants, research into the remediation of microplastics is lacking.

179 llulose-based systems applied to the passive remediation of mining-influenced waters.

180 ging from selective hydrocarbon oxidation to remediation of NO x pollutants.

181 ance of this process for the attenuation and remediation of NTO.

182 of fundamental importance for the effective remediation of nuclear waste.

183 ifers, fuel cells, oil recovery, and for the remediation of oil contaminated soils.

184 ronmental implications for future studies on remediation of other halogenated persistent aromatic pol

185 ngle source may have delayed recognition and remediation of other significant sources of L. pneumophi

186 s an inexpensive and effective technique for remediation of Pb-contaminated homes.

187 Ti(III)-citrate for potential use in in situ remediation of perfluorooctanesulfonate (PFOS) found tha

188 ersulfate is a promising oxidant for in situ remediation of perfluorooctanoic acid (PFOA), yet a comp

189 ell free reagent for long term environmental remediation of pesticide/chemical warfare contaminated a

190 tion and contrasting results obtained on the remediation of petroleum, this review is an attempt to f

191 ankton biodiversity could play a role in the remediation of pollutant loads in aquatic ecosystems.

192 proteins, reduction of protein synthesis and remediation of proteostasis.

193 al biological treatment systems designed for remediation of selenium-contaminated waters were shown t

194 the production of aromatic wines and in the remediation of smoke-tainted wines.

195 ide range of applications, including in situ remediation of soil and groundwater.

196 s spp.) is a tree species considered for the remediation of soil contaminated by metals, including zi

197 ckage, peddy, to identify and facilitate the remediation of such errors via interactive visualization

198 The remediation of the contaminated stable lead to a 2-3 fol

199 FOS and PFOA to meet health advisory levels, remediation of the wider range of PFASs in AFFF will pro

200 iven supramolecular chemistry, for efficient remediation of trace heavy metal ions from water.

201 The selective capture and remediation of trivalent arsenic (As(III)) is a central

202 r waste temporal evolution and the reductive remediation of uranium contamination.

203 sulfide mackinawite, play a key role in the remediation of uranium from groundwater systems.

204 icrobes for in situ SCN(-) biodegradation, a remediation option that is less costly than engineered a

205 s that may be used to assess the progress of remediation or natural attenuation of pollution and that

206 Remediation or transmutation of spent nuclear fuel obtai

207 plant tissues did not correlate with overall remediation performance for monocultures or mixtures, as

208 Cognitive remediation plus social skills training may be an approp

209 Both guanfacine and cognitive remediation plus social skills training were well tolera

210 ulate matter is critical to making efficient remediation policies to minimize the regional and global

211 ed in reactive iron barriers for groundwater remediation positively interacted with enrichment cultur

212 ese AC-clay granules (ACC-G) were tested for remediation potential (PCB-bioaccumulation reduction) an

213 ge Chironomus riparius was used to study the remediation potential and secondary effects of activated

214 have adverse effects on organisms, but their remediation potential is superior to coarser, granular A

215 s show that ACC-G has a significantly higher remediation potential than GAC, allowing for reductions

216 s spills and cause difficulties to efficient remediation practice.

217 is vital to the successful development of a remediation procedure.

218 then essential either to develop sustainable remediation procedures as well as for use in paleotracer

219 , our findings suggest that the proposed AMD remediation process can represent a modest but suitable

220 ve techniques are desired for monitoring the remediation process of contaminated soils.

221 As a remediation process, ACP removal of antibiotics in compl

222 eservoir-souring generation, prevention, and remediation processes, allowing us to incorporate insigh

223 g the novel technologies considered in water remediation processes, metal-organic frameworks (MOFs) a

224 ities on the transformation of chromium (Cr) remediation products has generally been overlooked.

225 ial reaction kinetics and pathways of Cr(VI) remediation products in the presence of microbial activi

226 ates can promote the release of Cr(III) from remediation products via both ligand complexation and in

227 (III)-Fe(III)-(oxy)hydroxides, common Cr(VI) remediation products, with a range of compositions in th

228 This is the first full-scale marine remediation project using a geo-engineering method that

229 d in establishing monitoring, treatment, and remediation protocols for HF-FPW.

230 c and sediment matrices; however, its use in remediation purposes has drawn some concern due to possi

231 m generated to concentrate the compounds for remediation purposes.

232 APS) fractionation, we found that active BES remediation resulted in 50% more polar, oxygen-containin

233 r determine trade-offs involved in different remediation scenarios and to improve remediation design

234 Three remediation scenarios were evaluated: No Action (NA), So

235 rhamnolipid for surfactant-enhanced aquifer remediation (SEAR), which may overcome the drawbacks of

236 energy storage and conversion, environmental remediation, sensing, ionotronics, and biotechnology.

237 nd pH 10.1) were chosen to be relevant to Mn remediation sites.

238 Participants treated with cognitive remediation, social skills training, and guanfacine demo

239 , compared with those treated with cognitive remediation, social skills training, and placebo.

240 Self-sustaining treatment for active remediation (STAR) is an emerging, smoldering-based tech

241 e of considerable interest for designing new remediation strategies and better understanding the geoc

242 To improve remediation strategies for multiple contaminants in redo

243 land degradation and for planning effective remediation strategies in face of future climatic uncert

244 search is essential for developing effective remediation strategies that are consistent with internat

245 This study provides valuable insight into remediation strategies that include persulfate as an oxi

246 n, with important consequences for potential remediation strategies.

247 and As mobilization for risk assessment and remediation strategies.

248 We have established a new soil remediation strategy using nanoscale zero-valent iron (n

249 ehalococcoides mccartyi is a frequently used remediation strategy, the effects of AFFF and PFASs on T

250 be irreversibly bound to humin in soils as a remediation strategy, which can be enhanced by adding so

251 n help parents and educators select the best remediation strategy.

252 us-bound material could serve as a plausible remediation strategy.

253 aring solids is potentially a very effective remediation strategy.

254 f residual U(VI) at ISR mines is a potential remediation strategy.

255 sis (CSIA) is a valuable tool in contaminant remediation studies.

256 Traditional AMD passive remediation systems are based on the reaction of AMD wit

257 o activate persulfate, the operation of ISCO remediation systems is hampered by an inadequate underst

258 In fact, in passive remediation systems, which are implemented to minimize t

259 of REE recovery from waste generated in AMD remediation systems.

260 to study the behavior of REY in AMD passive-remediation systems.

261 ur ecosystem, which lacks efficient and safe remediation tactics both on macro and nanoscales.

262 I and NZVI coupled with AC EMF as a combined remediation technique for increasing the rate and comple

263 evelopment of the first large-scale sediment remediation technique for microplastics to address the g

264 ng has significant potential as an effective remediation technique for PFAS-impacted soils and PFAS-l

265 ndwork for developing an alternative in situ remediation technique for rapidly decontaminating soils

266 Phytoremediation is a potentially low cost remediation technique that could be applied to soil cont

267 anced extraction (SEE) is an in situ thermal remediation technique used to remove and recover polycyc

268 Here, we used a novel remediation technique, brief periods of auditory stimulu

269 The limitations of current oil remediation techniques have inspired researchers to stud

270 e essential to adequately evaluate potential remediation techniques such as sedimentation and (air) f

271 ealth in mind, novel dismantling methods and remediation technologies and intervention practices are

272 r, there is a need to develop cost-effective remediation technologies for their removal from wastewat

273 lem, whereas field applicability of existing remediation technologies has encountered numerous obstac

274 terionic, and nonionic species, although few remediation technologies have been evaluated to assess t

275 Despite advances in physicochemical remediation technologies, in situ bioremediation treatme

276 has tremendous potential as a transformative remediation technology for persistent organic pollutants

277 tal study offers an option for a novel water remediation technology, comprising first a zeolite-based

278 for the application of nanomaterials in soil remediation that could simultaneously enable safe crop p

279 8-week training using computerized cognitive remediation therapy (CCRT) would modify resting brain fu

280 Cognitive remediation therapy has demonstrated efficacy for improv

281 s small sample study, computerized cognitive remediation therapy is shown to enhance mPFC/ACC activit

282 s commonly used treatments such as cognitive remediation therapy.

283 approach to evaluate the success of in situ remediation through abiotic contaminant reduction.

284 ubstantially improve the predictions of soil remediation time, long-range transport, and food chain t

285 aim was to implement emergency environmental remediation to abate exposures to 17,000 lead poisoned v

286 Environmental remediation to address childhood lead poisoning epidemic

287 Remediation to alter physiochemical properties of soil-b

288 ng public health related to water, food, and remediation, to name a few areas.

289 ed gap detection and may have potential as a remediation tool for general auditory processing deficit

290 are the two dominant approaches to cognitive remediation (training of executive skills and training o

291 domly assigned to the experimental attention remediation treatment or the active control group.

292 Our laboratory-based approach for soil Pb remediation uses addition of iron (Fe) sulfate and appli

293 Remediation was conducted over 4 years in three phases,

294 ical tracers for the analysis of groundwater remediation was examined in several example permeable re

295 as one of the most promising methods for HMX remediation, was performed by computational study at PCM

296 ed to identify where more or less postmining remediation will be necessary.

297 aminated sediments is an in-situ approach to remediation with great potential.

298 Although in situ remediation with phosphate amendments is a viable option

299 We also showed that fluoride remediation with the best-performing Guinea bauxite was

300 ing advanced treatment methods for effective remediation, with hydrated electrons shown to be able to