ライフサイエンスコーパス: remediation

1 nd environmental science (e.g., purification/remediation).

2 of organic pollutants in water and oil-spill remediation).

3 of solar energy conversion and environmental remediation.

4 dioactive waste management and environmental remediation.

5 olecular gels as materials for environmental remediation.

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

7 that neutralize pollutants for environmental remediation.

8 fuels and commercial products to hydrocarbon remediation.

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

10 e range of tools available for environmental remediation.

11 heating and cooling with UTES and a need for remediation.

12 valuate potential ongoing impacts, and guide remediation.

13 d an in situ amendment for contaminated site remediation.

14 rspecies dynamics needed for successful site remediation.

15 ation mechanism and promising strategy for U remediation.

16 petroleum hydrocarbons for enhancing in situ remediation.

17 ns from contaminated water for environmental remediation.

18 g-term stability of reduced Tc in subsurface remediation.

19 respond to the bioelectrochemically enhanced remediation.

20 mercury capture and therefore environmental remediation.

21 s to pollution and the efficacy of pollution remediation.

22 ng neural changes associated with behavioral remediation.

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

24 develop an inexpensive sorbent for oil spill remediation.

25 hen biosolids are used for contaminated site remediation.

26 s a promising technique for in situ sediment remediation.

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

28 rget for KRAS-associated lung adenocarcinoma remediation.

29 impaired, unless the OSPW has received some remediation.

30 on programs were more likely to use resident remediation.

31 pollutants and lead to useful strategies for remediation.

32 ategy for low permeability contaminated soil remediation.

33 d by natural leachate and acid mine drainage remediation.

34 r value commodity chemicals or environmental remediation.

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

36 s, robust shock absorbers, and environmental remediation.

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

38 Functional remediation, a novel group intervention, showed efficacy

39 sought to assess the efficacy of functional remediation, a novel intervention program, on functional

40 r establishing "Environmental assessment and remediation: a practice parameter." This is a complete a

41 odulate their energy consumption and organic remediation ability.

42 a homogeneous oxidation film and rapid film remediation ability.

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

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

45 make Pd-NZVI an effective in situ subsurface remediation agent, these particles need to migrate throu

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

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

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

49 les, encapsulated chemicals, or bacteria for remediation and agriculture applications.

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

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

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

53 ce from prion disease, Mte might be used for remediation and decontamination protocols.

54 ively engaged in the deposition, annotation, remediation and dissemination of macromolecular structur

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

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

57 e a variety of applications in environmental remediation and materials science.

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

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

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

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

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

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

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

65 alysts show great potential in environmental remediation and water splitting using either artificial

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

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

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

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

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

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

72 onomical material for multiple environmental remediation applications.

73 metal-binding proteins for biotechnology and remediation applications.

74 ) have been thoroughly studied for potential remediation applications.

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

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

77 es for in situ monitoring of the efficacy of remediation approaches based on alkaline hydrolysis.

78 issue for retrospective risk assessment and remediation approaches.

79 es must be held in comparison to traditional remediation approaches.

80 Existing methods for perchlorate remediation are hampered by the common co-occurrence of

81 thods to prioritize homes for monitoring and remediation are needed, because measuring indoor air qua

82 spread environmental carcinogens, methods of remediation are still limited.

83 ues impacting the effectiveness of cognitive remediation at improving psychosocial outcomes.

84 croalgae are good candidates for toxic metal remediation biotechnologies.

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

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

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

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

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

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

91 studies to determine whether prevention and remediation can improve long-term outcomes.

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

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

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

95 2-DCA remains a challenging compound for the remediation community.

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

97 nique statements according to importance and remediation difficulty.

98 rials for environmental sensing, imaging and remediation due to their unique size, physicochemical an

99 of plants and have been shown to enhance the remediation efficiency of plants, but little information

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

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

102 lly based exposure monitoring and evaluating remediation efforts occurring throughout the Great Lakes

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

104 xicological findings for risk assessment and remediation efforts.

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

106 -scale contamination incident and subsequent remediation events.

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

108 cognition significantly reduced the need for remediation for misdiagnosing optic disc edema during en

109 r CBT, social skills training, and cognitive remediation for overall symptoms were not robust after s

110 nological production of fuels, environmental remediation, functional foods and nutraceuticals.

111 neuroplasticity-based computerized cognitive remediation-geriatric depression treatment (nCCR-GD) to

112 The full remediation group also exhibited stronger negative iFC b

113 dditionally, relative to both TDC and the no remediation group, the remediation groups exhibited stro

114 o both TDC and the no remediation group, the remediation groups exhibited stronger iFC between L.FFG

115 The use of shellfish for coastal nitrogen remediation has been proposed, but formal incorporation

116 n to oil sands process-affected water (OSPW) remediation has been studied to treat fresh OSPW retaine

117 f existing cleanup techniques for benign oil remediation has inspired a recent scientific impetus to

118 valent iron (mZVI) particles for groundwater remediation has received much interest in recent years.

119 humidity has returned to baseline levels and remediation has removed any visible evidence of flood da

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

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

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

123 ossible to predict effectiveness of sediment remediation in reducing PCB uptake in fish.

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

125 , and Enhanced Oil Recovery to environmental remediation in the vadose zone.

126 for transformation of PFAA precursors during remediation included elevated ratios of perfluorohexanes

127 gly evident in the subsurface, likely due to remediation-induced conditions.

128 reviewed literature indicates that cognitive remediation is most likely to impact functional outcome

129 e imaged drug-induced hepatotoxicity and its remediation longitudinally in mice after systemic challe

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

131 providing a new strategy for designer water remediation materials.

132 etwork These results suggest that behavioral remediation may be associated with compensatory changes

133 Cognitive remediation may include a focus on neurocognition and/or

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

135 Due to the highly selective chelators, this remediation method could be both simple and versatile wh

136 as to develop a biogenic nanopalladium-based remediation method for reducing chlorinated hydrocarbons

137 e, then this experiment provides a potential remediation method for small lakes confronted with MeHg

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

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

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

141 nology and synthetic biology to conventional remediation methods.

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

143 ergetic byproduct can be produced during the remediation of a significant inorganic pollutant.

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

145 is shown to be a potential material for the remediation of aqueous radionuclide in groundwater.

146 makes newberyite an attractive material for remediation of arsenic contamination in aqueous environm

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

148 to scan social stimuli and contribute to the remediation of clinical symptoms related to interpersona

149 ecipitation is potentially important for the remediation of contaminants, such as during mineral trap

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

151 fluorinated carboxylates and sulfonates upon remediation of contaminated groundwater or aquifer solid

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

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

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

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

156 ndicator bacteria hamper risk assessment and remediation of contamination sources.

157 anisms make S. vulgaris suitable for in situ remediation of Cr polluted soils.

158 ic barrier packed-bed plasma reactor for the remediation of dichloromethane (CH2Cl2, DCM).

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

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

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

162 ilar size in SCZ and HCS and did not reflect remediation of functions disproportionately impaired in

163 ht into a potential solution for the in situ remediation of groundwater (129)I.

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

165 to facilitate more efficient and lower-cost remediation of hazardous waste sites.

166 ng sealing of improperly abandoned wells and remediation of hydraulic fracturing during shale gas ext

167 Remediation of hydrocarbon contaminated soils can be per

168 Remediation of industrial wastewater is important for pr

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

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

171 sorbents as potential in situ amendments for remediation of mercury and methylmercury (MeHg), using a

172 Microbial remediation of metals can alleviate the concerns of meta

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

174 mistic molecular dynamics simulations on the remediation of naphthalene by polyamidoamine (PAMAM) den

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

176 upgrading to chemicals and the environmental remediation of NO(x)).

177 ical transformation related to environmental remediation of NOx and mammalian blood flow.

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

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

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

181 , thereby providing a unique tool for timely remediation of P deficiency in agriculture.

182 Thus, NP-SLBs may be an effective method for remediation of PAHs, where the lipids provide both the m

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

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

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

186 ng radiation (IR) after radiation accidents, remediation of radioactive-contaminated areas, space tra

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

188 hesis of these peptides hold promise for the remediation of soils and groundwaters contaminated with

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

190 Microbes are the main vehicle for remediation of such sediments, and new discoveries, such

191 e we investigate an alternative strategy for remediation of Tc-contaminated groundwater whereby seque

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

193 be an effective management practice for both remediation of the high NORM in the Marcellus HFFF waste

194 Our assumption is that remediation of these deficits may modulate the underlyin

195 that may provide an alternative strategy for remediation of U contamination.

196 e subsurface is a promising strategy for the remediation of uranium-contaminated sites.

197 ckinawite as a potential reactive medium for remediation of uranium-contaminated water.

198 r nitrogen removal, as required for complete remediation of wastewater.

199 However, the impact of cognitive remediation on functional outcomes is more variable.

200 egulator concerns and in steering subsequent remediation operations.

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

202 ts, emphasizing the need for additional pool remediation options following fecal incidents.

203 There are few available in situ remediation options for Hg contaminated sediments, short

204 a critical role in determining the need for remediation or assessing the effectiveness of risk mitig

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 ediation but also significantly shortens the remediation period and produces sustainable electricity.

208 of aquifer parameters when designing in situ remediation plans.

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

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

211 s spills and cause difficulties to efficient remediation practice.

212 vironments is of interest to researchers and remediation practitioners alike.

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

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

215 at other tailings deposits to accelerate the remediation process and achieve similar results in a sho

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

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

218 meters, it has been possible to optimize the remediation process.

219 use for monitoring natural or technological remediation processes at field sites.

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

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

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

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

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

225 Cognitive remediation programs that do not solely rely on drill an

226 easily improved in current social cognitive remediation programs.

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

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

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

230 o develop new technologies for environmental remediation purposes.

231 vide a more accurate mechanism of predicting remediation rates.

232 ortant for successful implementation of this remediation scheme.

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

234 metC, merB), carbon metabolism, and organic remediation showed a higher abundance in highly contamin

235 urrently produced by activated carbon at RDX remediation sites can be minimized, decreasing the carbo

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

237 can exceed Maryland arsenic soil background remediation standards.

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

239 aker in all dyslexia groups, irrespective of remediation status/literacy competence, suggesting that

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

241 Remediation strategies and natural attenuation in anaero

242 sulfidogenesis and should be considered when remediation strategies are implemented in sulfate-bearin

243 To improve remediation strategies for multiple contaminants in redo

244 , challenges remain in developing engineered remediation strategies for pesticide-contaminated enviro

245 Consequently, remediation strategies for radioactively contaminated sy

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

247 Microbial-based remediation strategies will benefit from an ecological u

248 roleum carbon has important implications for remediation strategies, since it implies that organic co

249 rrently without cost-effective and efficient remediation strategies.

250 n, with important consequences for potential remediation strategies.

251 rous media flow cells to examine a potential remediation strategy employing coprecipitation of stront

252 a suggest that standard ISCO is not a viable remediation strategy for PFAA decomposition, substantial

253 exposure, flushing may not be an appropriate remediation strategy for Type II exposure.

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

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

256 aring solids is potentially a very effective remediation strategy.

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

258 al is not justified as a microbial pollution remediation strategy.

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

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

261 biological activity to that end is a salient remediation strategy; however, the stability of these ma

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

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

264 are needed to optimize nano-composite water remediation systems to subsequently achieve commercial m

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

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

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

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

269 ration of the hypolimnium has been used as a remediation technique in eutrophic water bodies but seve

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

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

272 Current oil remediation techniques are inefficient and may have dele

273 mechanisms of plants and microorganisms, As remediation techniques, and reduced environmental system

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

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

276 selection and performance of uraninite-based remediation technologies over multiyear periods.

277 ation for development of alternative in situ remediation technologies to degrade environmental contam

278 for more efficient and cost effective water remediation technologies will also rise.

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

280 catalysis, drug delivery, and environmental remediation technologies.

281 enomics assay can serve as a useful tool for remediation technology efficacy assessment and provide g

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

283 8-week training using computerized cognitive remediation therapy (CCRT) would modify resting brain fu

284 n brain functioning detected after cognitive remediation therapy in schizophrenia patients might be b

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

286 es in schizophrenia patients after cognitive remediation therapy using a whole-brain approach that co

287 on such as pharmacological agents, cognitive remediation therapy, and repetitive transcranial magneti

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

289 Environmental remediation to address childhood lead poisoning epidemic

290 multaneously randomized to receive cognitive remediation to improve cognitive functioning or healthy-

291 whether summer jobs, which shift focus from remediation to prevention, can reduce crime.

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

293 injectable vs oral risperidone and cognitive remediation vs healthy-behaviors training.

294 Remediation was conducted over 4 years in three phases,

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 eployment of unoxidized nZVI for groundwater remediation will likely be difficult.

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 Ultimate remediation would necessitate reprogramming these signal