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1 black carbon (BC), a climate forcer and air pollutant.
2 a and other developing countries as a global pollutant.
3 of its carcinogenic potential and as climate pollutant.
4 n specific soil constituents and the organic pollutant.
5 represent a spatial proxy of other relevant pollutants.
6 tions of OP(DTT) while controlling for other pollutants.
7 he importance of reducing emissions of other pollutants.
8 ant in controlling the fate of cotransported pollutants.
9 ion reaction and photodegradation of organic pollutants.
10 es for both source sectors and all precursor pollutants.
11 es on emissions of regulated and unregulated pollutants.
12 entrations of fungal spores, pollen, and air pollutants.
13 large multiwell pads, release hazardous air pollutants.
14 m (VI) cations and organic dyes are the main pollutants.
15 genous additives, and adsorbed environmental pollutants.
16 in the lung to remove inhaled pathogens and pollutants.
17 exposed to multiple exogenous environmental pollutants.
18 hydrocarbon oxidation to remediation of NO x pollutants.
19 p,p -DDE) and polychlorinated biphenyl (PCB) pollutants.
20 iations (p < 0.05) were observed for several pollutants.
21 s, which are known targets for environmental pollutants.
22 resolution were estimated for 11 ambient air pollutants.
23 concerns regarding exposure to hazardous air pollutants.
24 as to the abatement of certain environmental pollutants.
25 trategy for the remediation of environmental pollutants.
26 d usage, and climate and health-relevant air pollutants.
27 sed to inhaled microorganisms, allergens and pollutants.
28 reservoir for the accumulation of lipophilic pollutants.
29 n is susceptible to lipophilic environmental pollutants.
30 modify susceptibility to the effects of air pollutants.
31 s that act to capture and transform incoming pollutants.
32 ry's constant, H2, for more than 700 organic pollutants.
33 ssion to account for colinearity between air pollutants.
34 ocarbon fuels and for degradation of various pollutants.
36 oxic equivalent (TEQ) loading of dioxin-like pollutants (400 pg TEQ m(-2) y(-1)) compared to Marseill
41 organic dyes is a simple and rapid method in pollutant analyses and is limited because of quenching c
44 regarded as the leading airborne biological pollutant and the chief cause of pollen allergy worldwid
46 d, having constant exposure to environmental pollutants and allergenic pollens and having a unique co
47 es broad responses to numerous environmental pollutants and cellular metabolites, modulating diverse
48 energy security and reduce emissions of air pollutants and CO2 from coal use, China is attempting to
49 risks per interquartile-range increment for pollutants and high exposure (>/=75th percentile) for ai
50 by PCM can impact the biogeochemical fate of pollutants and lead to useful strategies for remediation
52 s: devices that can be used in detections of pollutants and other treating compounds/analytes (drugs)
53 aging, but no direct link between indoor air pollutants and skin aging manifestations has ever been s
55 ecies to improve photodegradation of organic pollutants and the beneficial use of air pollutants for
56 milarities in chemical structure with legacy pollutants and their potential toxicity have caused incr
58 ist meteorological conditions in winter, air pollutants and water vapour accumulate in a shallow plan
63 rst, followed by petroleum-derived exogenous pollutants, and finally by higher MW polymeric plant mat
66 to neurologists and exposure to selected air pollutants, and restricting to never movers and urban dw
67 t (SP) lever to mitigate short-lived climate pollutants, and the carbon extraction and sequestration
69 ewater containing both inorganic and organic pollutants are generated every day, leading to significa
70 c framework materials that can capture those pollutants are highly desirable but scarcely reported.
73 verage agronomic and economic impacts of the pollutant as well as to breed crops for O3 tolerance.
75 hydrocarbons (PAHs) are common environmental pollutants associated with adverse human health effects
76 we determined whether the common lipophilic pollutants benzo[a]pyrene and diesel exhaust particles i
82 ever, model performance varies widely across pollutant categories and quantifiably definitive perform
84 , and cationic sorbents able to trap several pollutants classes like pharmaceuticals, pesticides, PAH
85 New data suggest that diet, hyperlipidemia, pollutants, commensal microbes, and pathogenic infection
86 ethylene (TCE) is a widespread environmental pollutant common in groundwater plumes associated with i
88 rovides daily spatial field estimates of air pollutant concentrations and uncertainties that are cons
93 high-income countries, which have much lower pollutant concentrations than low-income and middle-inco
95 models tested associations of within-subject pollutant concentrations with FEV1 and forced vital capa
96 age to DNA from the metabolites of drugs and pollutants constitutes a major human toxicity pathway kn
98 l-fired power plants and industry is a major pollutant contributing to their air quality problems.
100 ne systems, one potential mechanism by which pollutants could increase infection risk is by influenci
101 arts per billion (ppb) for ozone using a two-pollutant Cox proportional-hazards model that controlled
102 sure individuals have had to common chemical pollutants critically requires the ability to detect tho
103 ions about how to incorporate time trends in pollutant data, and the most relevant window of exposure
105 bioaugmentation involves the inoculation of pollutant-degrading bacteria to accelerate pollutant deg
106 ion strategies by enhancing the transport of pollutant-degrading bacteria to the source of contaminat
107 Our results suggest that, by mobilizing pollutant-degrading bacteria, zoospores can act as ecolo
109 alysis, corrosion protection, degradation of pollutants, disinfection of bacteria and material synthe
114 O&G activities, production volumes, and air pollutant emission rates from two Colorado basins to cre
117 elopment programs, often lack historical air pollutant emissions data, which can pose challenges for
118 of federal air regulations and quantify air pollutant emissions for two feasibility-level biorefiner
119 ns between spatial and temporal variation in pollutant emissions from livestock farms and lung functi
121 acts of declining transportation-related air pollutant emissions on disparities in exposure have not
122 The effects of international trade on air pollutant emissions, air quality and health have been in
123 er cent (411,100 deaths) were related to air pollutants emitted in a region of the world other than t
125 onmental health, environmental exposures and pollutants, epidemiology, public health, and bioinformat
131 h, we assessed long-term traffic-related air pollutant exposures (represented by nitrogen dioxide; NO
132 interactions with important implications for pollutant fate and transport, sensing applications, and
134 ozone is considered the most detrimental air pollutant for vegetation at the global scale, with negat
135 nic pollutants and the beneficial use of air pollutants for the removal of water pollutants since sul
138 on results suggest contribution to secondary pollutants from multiple sources even where primary poll
139 ld's population and emit large quantities of pollutants from sources such as fossil fuel combustion a
140 ds are engineered to accumulate sediment and pollutants from stormwater and provide environmental val
142 h materials can therefore remediate unwanted pollutants from the environment including: immobilisatio
144 missions and real-time optical properties of pollutants from traditional and alternative cookstoves i
145 d adsorbent materials used to remove organic pollutants from water but they have several deficiencies
147 s to detect toxic, explosive, flammable, and pollutant gases is still a challenging research topic.
148 ent to a highway was primarily influenced by pollutants generated by mobile sources (GOM = nitrogen a
149 al coexposures including traffic-related air pollutants, greenness, and neighborhood walkability.
150 te annual concentrations of 40 hazardous air pollutants (HAPs) across the continental United States (
151 n in outdoor air among the 187 hazardous air pollutants (HAPs) identified by the U.S. Environmental P
152 gnin, a predominant industrial byproduct and pollutant, has been recognized today as a rich reservoir
153 graphical location, as well as environmental pollutants have been shown to modulate autoimmune diseas
154 cal studies are effective for characterizing pollutant impacts on biota in a controlled, simplified e
155 iesel cars are more polluting depends on the pollutant in question, i.e. that diesel cars are not nec
157 the measurements of persistent environmental pollutants in blood; significant Kendall tau correlation
158 triggered cytotoxic effects of a cocktail of pollutants in Caco-2 cells and increase their tumorigeni
165 rcury ion (Hg(2+)) is one of the most common pollutants in water with high toxicity and significant b
166 naphthalene (NA), a ubiquitous environmental pollutant, in human respiratory tract is a subject of in
168 The transient concentration of the other air pollutants, including PM2.5, PM10, and O3, did not signi
169 nts from multiple sources even where primary pollutants indicate the presence of a single source.
170 ncome, or prenatal exposure to hazardous air pollutants, indicating that spatial variation is not att
173 mogeneous catalysts that convert CS2 and COS pollutants into environmentally benign products is impor
175 icated bacteria specialized in degrading the pollutant is suggested as a green and economically sound
178 udies that increased exposure to ambient air pollutants is associated with olfactory dysfunction.
179 essment of environmental biodegradability of pollutants is limited by the use of low throughput syste
181 ocarbons (PAHs) are widespread environmental pollutants, known human lung carcinogens, and potent mam
184 are typically considered in predicting fish pollutant load, and thus recommendations of consumption,
187 volvement in detoxification of environmental pollutants may impede its physiological role, resulting
197 ed with respiratory symptoms based on single-pollutant models, with the largest associations seen for
203 ncentrations of a transportation-related air pollutant, nitrogen dioxide (NO2), in the United States.
207 our understanding of the chronic effects of pollutants on ecosystems in an environmentally realistic
208 imental studies, but the actual impact of OC pollutants on European marine top predators remains unkn
209 se consequences of environmental and dietary pollutants on intestinal barrier integrity/function with
211 Additionally, new UFG records of industrial pollutants parallel changes documented in ice cores from
213 suggest that early exposures to criteria air pollutants, particularly from transport emissions, and h
214 ort and fate of sediment, carbon, nutrients, pollutants, pathogens and manufactured nanoparticles fro
216 he desorption kinetics of typical wastewater pollutants (phenanthrene, tonalide, and benzophenone) at
217 liberation of persistent lipophilic organic pollutants (PLOPs) into blood from their storage in iner
218 tants for six families of persistent organic pollutants: polychlorinated benzenes, polychlorinated bi
220 clusion of BDE-209 in the persistent organic pollutant (POP) convention as well as the need for strat
221 passive sampling (EPS) of persistent organic pollutants (POP) in fish tissue has been hitherto limite
222 ured concentrations of 18 persistent organic pollutants (POPs) and 9 toxic elements in blood, as well
224 table isotope analysis of persistent organic pollutants (POPs) has the potential to characterize sour
227 stimate concentrations of persistent organic pollutants (POPs), and evaluate risk factors associated
228 d analyzed samples for 50 persistent organic pollutants (POPs), including 21 PCB congeners, 8 PBDE co
229 of various industrial-use Persistent Organic Pollutants (POPs), such as polychlorinated biphenyls (PC
230 ging water quantity; however, runoff carries pollutants, posing risks to the local environment and pu
231 aneous photocatalytic degradation of organic pollutants present in the separated water from the oil w
232 great potential for treatment assessment and pollutant prioritization within regulatory applications,
235 nsively studied because of its importance in pollutant redox dynamics and biogeochemical processes.
236 have been associated with combustion-related pollutants, relationships with PM10-2.5 remain unknown.
237 under field conditions (infinite bath), the pollutant release controlled by intraparticle diffusion
238 sion rates reported to the Canadian National Pollutant Release Inventory (NPRI) using accepted estima
239 ective risk reduction strategies for aquatic pollutants requires a comprehensive understanding of tox
240 removal of fecal indicator bacteria (FIB, a pollutant responsible for runoff-associated inland and c
241 eople are directly exposed to high levels of pollutants resulting from deforestation and agricultural
245 hip between the amount of persistent organic pollutants sequestered by passive air sampling devices a
247 e of air pollutants for the removal of water pollutants since sulfite is a waste from flue gas desulf
249 achieve zero net emissions of CO2, the super pollutant (SP) lever to mitigate short-lived climate pol
250 tissues; their associations with atmospheric pollutant species (PM, NOx, trace elements, PAHs); the p
251 Our findings reinforce the importance of pollutant-specific, location-specific, and source-specif
255 dence has associated obesity with persistent pollutants such as the pesticide DDT and its metabolite
256 urther enhanced on exposure to environmental pollutants, such as diesel exhaust particles (DEPs).
261 (TNT) is a significant, global environmental pollutant that is both toxic and recalcitrant to degrada
262 onsiderable amount of wastewater, a powerful pollutant that is currently discarded but could be consi
264 Nitroaromatic compounds are groundwater pollutants that can be degraded through reactions with F
265 Azaarenes are N-heterocyclic polyaromatic pollutants that co-occur with polycyclic aromatic hydroc
268 pounds (SVOCs), an important class of indoor pollutants that may have significant adverse effects on
271 T cell activation is inhibited by lipophilic pollutants through profound interference with gene expre
272 ck carbon (BC) and loss of methane and other pollutants to the atmosphere, impacting climate and air
273 tion, is important for urban ventilation and pollutant transport between adjacent cities when the bac
277 e detection of several important halogenated pollutants under laboratory conditions, e.g., 1,2-dichlo
278 ey have several deficiencies, including slow pollutant uptake (of the order of hours) and poor remova
279 c associations between breast cancer and air pollutants using Cox regression models, adjusting for ma
280 evaluated for both chromium (VI) and organic pollutants (using methyl blue (MB) as an example) remova
281 ding aeroallergens, stinging insects, fungi, pollutants, viral respiratory tract infections, climate
284 obutanoic acid or metformin, but other novel pollutants were also identified, as for example di-o-tol
285 ion, exposures to both primary and secondary pollutants were associated with an increase in PTB.
287 for coexposure to noise, traffic-related air pollutants were not associated with the incidence of dia
289 h endosulfan and TCDD are persistent organic pollutants which elicit cytotoxic effects by inducing re
290 and -furans (PCDD/Fs) are persistent organic pollutants whose main removal process in the environment
293 DLCs) are highly toxic and persistent global pollutants with extremely large differences in sensitivi
295 sights into the association of pathogens and pollutants with SPM and their impact on aquatic life.
298 range in optimized model performance across pollutants, with SO2 predicted most poorly due to limita
299 PMOCs may have not been recognized as water pollutants yet, due to the lack of analytical methods ca
300 ons and as a potentially toxic environmental pollutant, yet the current knowledge on V speciation in
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