戻る
「早戻しボタン」を押すと検索画面に戻ります。 [閉じる]

コーパス検索結果 (1語後でソート)

通し番号をクリックするとPubMedの該当ページを表示します
1 onitrobenzene (3,4-DCNB) is an environmental pollutant.
2  industry and it is a powerful environmental pollutant.
3 r at least 36-130 vehicles, depending on the pollutant.
4 ly used organic solvent but is also a potent pollutant.
5 and highlights the pervasive nature of these pollutants.
6 tralize and decompose chemical and bacterial pollutants.
7 sessment of toxic potencies of environmental pollutants.
8 ntally co-contaminated with diverse chemical pollutants.
9 te of decline is slow in comparison to other pollutants.
10 llergen molecules may be related to specific pollutants.
11 T measurement of a range of emerging organic pollutants.
12 ght about increases in organic and inorganic pollutants.
13 ncentrations of aerosols, as well as gaseous pollutants.
14 oming a challenge due to novel anthropogenic pollutants.
15  distinct spatial patterns relative to other pollutants.
16 been tested using acute exposure to singular pollutants.
17 des, alpha-halocarbonyl, and alpha-haloallyl pollutants.
18  similar after adjustment for PM and gaseous pollutants.
19 er sources and wastewater for pharmaceutical pollutants.
20 nants, such as metals and persistent organic pollutants.
21 ecomposition of both dissolved and suspended pollutants.
22 ated groundwater containing unsafe levels of pollutants.
23 erventions to mitigate the impact of sensory pollutants.
24 ies for controlling small amounts of organic pollutants.
25 ed by many bacteria to degrade environmental pollutants.
26 e analytical tool for the detection of water pollutants.
27 the toxic effects of individual and combined pollutants.
28 hether plastic debris is the source of these pollutants.
29 r accumulation of both inorganic and organic pollutants.
30 creening studies for potential environmental pollutants.
31 mportant surface for reaction with gas-phase pollutants.
32 tions and infer the potential sources of the pollutants.
33 amages from carbon dioxide (CO(2)) and other pollutants.
34 y the metabolic byproducts of vinyl chloride pollutants.
35 chemical toxins including persistent organic pollutants.
36 ry exposure to total mercury (THg) and other pollutants.
37 rganic (18 trace elements) and organic trace pollutants (200 micropollutants) with high-throughput qu
38  the association between weather/climate and pollutant accumulation in Arctic food webs and the criti
39 ecies and local-scale studies, whether these pollutants affect fitness is less clear, as is how and w
40 hlight the utility of QMRA that incorporates pollutant age and mixture scenarios, the potential advan
41  and underscore the need to consider sensory pollutants alongside traditional dimensions of the envir
42                                       Single-pollutant analyses were followed by multipollutant analy
43                                In the single-pollutant analyses, higher concentrations of several air
44 ochemical/optical dual detection for on-site pollutant analysis, ie.
45 ong-term exposure to a common pharmaceutical pollutant and acute temperature stress alter fundamental
46    Mercury (Hg) is a pervasive environmental pollutant and contaminant of concern for both people and
47                  We investigated both single-pollutant and multipollutant models accounting for coexp
48             Spatial comparison showed higher pollutant and toxicity levels in the samples from northe
49      The association between mixtures of air pollutants and birthweight z-scores (standardized for ge
50 ces (PFAS) are widespread persistent organic pollutants and endocrine disruptors.
51 luable chemicals, remediation of hydrocarbon pollutants and energy sustainability.
52 c hydrocarbons (PAHs) are common atmospheric pollutants and known to cause adverse health effects.
53 lear on how PM(2.5) interacts with other air pollutants and meteorological factors at different tempo
54 y primarily through the biotransformation of pollutants and nutrients rather than by altering the mic
55  detoxification pathways in cells exposed to pollutants and other small molecules.
56 hane and propane are significant atmospheric pollutants and precursors of tropospheric ozone, while t
57 t for tightly controlling the release of air pollutants and preventing more serious diseases.
58  typically reduce emissions for specific air pollutants and sectors to maintain pollutant concentrati
59                    The adsorption of organic pollutants and trace metals is also confined to this out
60 ke exposures, occupational and environmental pollutants, and asthma).
61 lications in sensing, degradation of organic pollutants, and in therapeutic roles.
62        Microplastics are widespread emerging pollutants, and investigations are underway to determine
63 ethod is time consuming, easily disturbed by pollutants, and limited to the analysis of a pure bacter
64 costs, health damages caused by criteria air pollutants, and methane leakage from the natural gas inf
65 euticals, household chemicals, environmental pollutants, and microbiota derivatives, comprising more
66  time series data of PM(2.5), five other air pollutants, and six meteorological factors, as well as t
67 netics, polygenic risk scores, environmental pollutants, and somatic mutations are discussed.
68 tress, chemotherapeutic drugs, environmental pollutants, and sun exposure.
69 ons, highlighting the spatial variability of pollutant anomalies attributable to complex NO(x) chemis
70            A growing number of environmental pollutants are known to adversely affect the thyroid hor
71 lebees can tolerate and identify which scent-pollutants are problematic.
72                       Six "target" oxo-anion pollutants (arsenate, arsenite, selenate, selenite, chro
73 on between 1- and 3-y running means of these pollutants, as well as 23-y running means of NO2 and NOx
74 onitoring of primary and secondary gas-phase pollutants, as well as other atmospheric conditions, was
75                                      For all pollutants, associations in Model 2 were robust to furth
76 timate concentrations of traffic-related air pollutants based on nitrogen oxides (NOx) at participant
77 rom the gas phase to the liquid phase, where pollutant biodegradation occurs.
78 ctionally), including indoor and outdoor air pollutants, built environment, green spaces, tobacco smo
79               The reduction of environmental pollutants by Fe(2+) bound to iron oxides is an importan
80 loamy) of the soil, and the concentration of pollutants can affect the infrared absorbance.
81                             Heavy metal (HM) pollutants can cause serious phytotoxicity or oxidative
82 guidelines, combined with the knowledge that pollutants can interact with human skin, it is now of ev
83 s (CO(2), CH(4), and N(2)O) and criteria air pollutant (CAP) emissions (VOC, CO, NO (x), SO(2), PM(10
84 ng the greenhouse gas (GHG) and criteria air pollutant (CAP) emissions associated with hydrogen produ
85                                         Many pollutants cause endocrine disruption in aquatic organis
86                    Atmospheric transport and pollutant chemistry of primary particulate matter, sulfu
87 ith higher BMI, and levels of organochlorine pollutants, cobalt, and molybdenum were associated with
88 valent group of regulated persistent organic pollutants, commonly couple chemical and stable isotope
89 t when there is a great deal of variation in pollutant concentrations among sites/individual birds.
90 e fundamental in understanding hazardous air pollutant concentrations and ozone formation.
91 o estimate associations between ln-FeNO with pollutant concentrations at individual 1-h lags (up to 2
92           Associations of annual average air pollutant concentrations at participants' residences wit
93 cific air pollutants and sectors to maintain pollutant concentrations below standards.
94 ecies variabilities, incoherently documented pollutant concentrations, and/or bio-physicochemical sed
95 ant questions about how responses to sensory pollutants counteract or exacerbate responses to other a
96                               Organochlorine pollutant data sets spanning 40 years, which is rare for
97 e processes frequently contribute to organic pollutant degradation in natural and engineered systems,
98 tics of radical-mediated oxidation reactions-pollutant degradation in particular.
99  the fatty acids or persistent environmental pollutants drive the association.
100 alyses, higher concentrations of several air pollutants during pregnancy or childhood were associated
101 anking the hazard potential of environmental pollutants (e.g., bisphenols, polycyclic aromatic hydroc
102 el covariates, including traffic-related air pollutants [e.g., ultrafine particles (UFPs) and nitroge
103 ies in California were conducted to quantify pollutant emission rates across the AD-composting proces
104  and (4) they feed on prey located closer to pollutant emission sources/transport pathways.
105  has continuously increased resource use and pollutant emissions far more rapidly than these have bee
106 lth risk by reducing "business as usual" air pollutant emissions from economic activities.
107 ased on social costs of carbon and other air pollutant emissions highlights the importance of ground-
108 TW) greenhouse gases (GHGs) and criteria air pollutant emissions of MHD BEVs with their conventional
109  the same period, we estimated reductions in pollutant emissions of more than a third in comparison w
110 sources, leading to larger declines in major pollutant emissions, but very limited co-benefits in red
111  address air pollution have reduced criteria pollutant emissions, improved regional air quality, and
112 ass utilization with high efficiency and low pollutant emissions.
113 ocarbons (PAHs) are potentially carcinogenic pollutants emitted by diesel engines, both in the gas ph
114 zidine alkaloids (PAs) are found to be toxic pollutants emitted into the environment by numerous plan
115 osure of the intrinsic micropores toward the pollutant environment, thereby, improving the performanc
116 ssessed for the so-called persistent organic pollutants, especially organochlorine pesticides (OCPs)
117 oncentrations of all gaseous and particulate pollutants (except PM(2.5)) were 1.1- to 4.8-fold higher
118 enome-wide association studies (EWAS) on air pollutants exist, and none have been done on transportat
119                                              Pollutant exposure during offspring production in arctic
120         Long-term low- to moderate-level air pollutant exposure is associated with a greater risk of
121 n greater importance that the effects of air pollutant exposure on human skin be investigated.
122 cial, ethnic, and economic inequality in air pollutant exposure.
123  We reported that maternal PFBS, an emerging pollutant, exposure is positively associated with preecl
124 els rely to predict the environmental (micro)pollutant fate.
125 ions between short-term exposure to main air pollutants (fine particulate matter [PM2.5] and ozone) a
126  of short-term exposure to major ambient air pollutants-fine particles (PM(2.5)), inhalable particles
127 gstanding debate in geochemical research and pollutant forensics because its historical record differ
128 per day and $116 million per day during peak pollutant formation periods in summer and winter, respec
129 ess in the removal of the toxic chromium(VI) pollutant from aqueous solutions.
130 d in the production of water-soluble organic pollutants from asphalt.
131  are usually inefficient at removing organic pollutants from sewage or so-called grey water.
132   Exposure in pregnancy and childhood to air pollutants from tailpipe and non-tailpipe emissions were
133 ecause of their bioaccumulation potential of pollutants from their hosts.
134 nd efficient uptake of organic and inorganic pollutants from water (>95% removal within 30 s).
135 ern societies, biodegradation of hydrophobic pollutants generated by industry is important for enviro
136 ever, there are many gas-phase hazardous air pollutants (HAPs) identified by the Environmental Protec
137 class of persistent and highly toxic organic pollutants, have been posing a great threat to human hea
138                               The individual pollutant identified with the largest amount of associat
139 ly explain how and why anthropogenic sensory pollutants impact organisms.
140 ve and quantitative detection of multiplexed pollutant in real-time.
141                       Temporal monitoring of pollutants in aquatic systems impacted by human activiti
142 ntal data aimed at the determination of four pollutants in environmental water samples.
143 ll greatly benefit the evaluation of unknown pollutants in future environmental studies.
144 monitor the spatiotemporal variations of air pollutants in large scales, but it has been challenging
145 ies, which impedes monitoring of trace-level pollutants in many resource-limited environments.
146  on assessing the urban landscape effects of pollutants in megacities, little is known about their as
147 s their effects on the fate and transport of pollutants in natural and engineered water systems.
148 s Sea as a proxy for a West-East gradient of pollutants in polar bear prey.
149 is critical to predicting the persistence of pollutants in sunlit surface waters.
150  role in the transport and transformation of pollutants in the aquatic environment.
151 nases involved in bioremediation of aromatic pollutants in the environment.
152 ring of polyfluorinated substances and other pollutants in the field.
153 t a wide range of contaminants and microbial pollutants in wastewater.
154 s such as disease diagnosis and detection of pollutants in water and food.
155 ain consider the possibility of neutralizing pollutants in water by means of radiolysis, which has al
156 f sustainable methods for the degradation of pollutants in water is an ongoing critical challenge.
157 active intermediates (PPRIs) that react with pollutants in water.
158 etermination of pesticides and other organic pollutants in whole water is not matched by the field sa
159 d for the extraction or trapping of chemical pollutants, in immunoassays, and for the design of senso
160                     Concentrations of 17 air pollutants including nitrogen oxides (NOX), particulate
161 hexane), as well as chlorinated and aromatic pollutants, including vinyl chloride, 1,2-dichloroethane
162                                  Particulate pollutants-including particulate matter with an aerodyna
163            Nonextractable residues (NER) are pollutants incorporated into the matrix of natural solid
164 atmosphere, where continental and marine air pollutants interact and atmospheric oxidative capacity m
165 ic debris can be a major pathway of chemical pollutants into seabirds.
166                               WTPs discharge pollutants into the aquatic environment, they also produ
167 seudo-second-order rate constant for the BPA pollutant is 182.3 g mg(-1) min(-1), which is the highes
168     The identity of an unknown environmental pollutant is reflected by the mass and dissociation chem
169 ectro-Fenton (EF) treatment of organic water pollutants is discussed.
170 ilability for the reduction of anthropogenic pollutants is often limited by competition with other el
171                         Sequestration of air pollutants is one of the main ecosystem services that ur
172 ocumenting the ecological effects of sensory pollutants is weakened by sparse knowledge of the mechan
173 ssments of heating sources and environmental pollutants, is needed.
174 (2.5) are driven by local emissions and both pollutants largely behave as passive tracers at time sca
175                                              Pollutant levels in polar regions are gaining progressiv
176                                              Pollutant levels were measured in harp seals from the Gr
177 ges that may explain the difference in their pollutant levels.
178 t diabetes alters pulmonary responses to air pollutants like ozone (O3).
179            We find responses to both sensory pollutants linked to the functional traits and habitat a
180 ed to uninfected fish, irrespective of their pollutant load.
181 xhibited no significant differences in their pollutant load.
182 mes because of the increase in the tributary pollutant loads attributed to electrical conductivity (E
183      We showed that pelagic bears had higher pollutant loads than coastal bears because (1) they feed
184               These ubiquitous environmental pollutants may derive from the incomplete combustion and
185 s of chemical pollutants (persistent organic pollutants, metals, phthalates, phenols, and pesticides)
186                As a ubiquitous environmental pollutant, methylmercury (MeHg) induces toxic effects in
187 ogenous allergens, microbial substances, and pollutants might occur, rendering individuals prone to d
188 e to the median level of exposure to the air pollutant mixture could occur.
189 -based" approach to characterize complex air pollutant mixtures was applied in the Oil Sands region o
190 d to identify the characteristics of primary pollutant mixtures, which were related to hydrocarbon em
191               Subgroup, sensitivity, and two-pollutant model analyses highlighted the robustness of t
192                                In the single-pollutant model of particle radioactivity, each interqua
193                                In the single-pollutant model of PM(2.5), each interquartile range inc
194 oactivity (2 single-pollutant models and a 2-pollutant model) before the event was examined using tim
195                                     In the 2-pollutant model, for the same averaging window of 21 day
196 of the digestive system on the same day in 2-pollutant models (adjusting for ozone).
197 PM(2.5) and particle radioactivity (2 single-pollutant models and a 2-pollutant model) before the eve
198  effects of a certain particle metric in two-pollutant models by adjusting for copollutants, includin
199                           In adjusted single-pollutant models, (1) TT(4) was inversely associated wit
200                                    In single-pollutant models, each interquartile-range increase in U
201 ed with same-day PM2.5 in both single- and 2-pollutant models, including diabetes mellitus, anemia, i
202                                In the single-pollutant models, the effect estimates of all included a
203 important to note that several environmental pollutants modulated the transcriptional activity of tes
204            The fastest- and slowest-reacting pollutants (morphine and methamphetamine, respectively)
205 o mitigate the adverse health impacts of air pollutants must include the reduction of emissions throu
206 etection and identification of environmental pollutants need more attention.
207                     Models included regional pollutants (nitrogen dioxide [NO(2)] or particulate matt
208 tality was significantly associated with all pollutants: NO2, 1.108 (1.038, 1.182; p < 0.001); PM10,
209 ersistent ammonium compound as typical water pollutant, not only with a cw laser but also with an LED
210 ith 1,2,3-trichloropropane, a haloalkane and pollutant of drinking water, and find these and other si
211             Nitrous oxide (N(2) O) is an air pollutant of major environmental concern, with agricultu
212 (PFAS) are an ensemble of persistent organic pollutants of global interest because of their associati
213 ects of prenatal exposure to mixtures of air pollutants of particulate matter (PM), PM(2.5), PM(10),
214 llows the preconcentration of thermodesorbed pollutants on a polymer thin film and then, their quanti
215 novel approach to study sublethal effects of pollutants on fish larvae in situ.
216 i, two efficient phytoremediators of organic pollutants, on polluted substrate resulted in a mean dec
217 ing mechanisms through which mixtures of air pollutants operate, the causality of air pollution-assoc
218 al barrier function, which allows allergens, pollutants, or microbes to enter the tissue and activate
219 tspots of conservation concern where sensory pollutants overlap in space and time with an organism's
220                Inhalation of the ambient air pollutant ozone causes lung inflammation and can suppres
221 ring shows promise for understanding spatial pollutant patterns, yet it is unclear whether uncertaint
222 average change in the log-concentration of a pollutant per trophic level) have been extensively asses
223 treatment, also transports the environmental pollutant perchlorate (stoichiometry 1Na(+):1ClO(4)(-)),
224  tobacco smoking, and biomarkers of chemical pollutants (persistent organic pollutants, metals, phtha
225  to pharmaceuticals and most likely to other pollutants, placing these ecologically important systems
226 mate change and reduce exposure to toxic air pollutants, policy assessments have considered few if an
227                           Several ubiquitous pollutants (polychlorinated biphenyls (PCBs), organochlo
228         The occurrence of persistent organic pollutants (POPs) in the Arctic has been of constant con
229 e Stockholm Convention on Persistent Organic Pollutants (POPs) was established to generate long-term
230 tants (so-called "legacy" persistent organic pollutants (POPs)) and a synthetic mixture of POPs, usin
231 ave focused on legacy persistent chlorinated pollutants (POPs), while the effects of poly- and perflu
232 e of routes, such as some persistent organic pollutants (POPs).
233 ar those of anthropogenic-persistent organic pollutants (POPs).
234 oid-disrupting effects of persistent organic pollutants (POPs).
235  highly contaminated with persistent organic pollutants (POPs).
236                               We monitor air pollutants pre- and post-renovation and quantify efficie
237 .001], respectively) when highest and lowest pollutant quintiles were compared; however, neonatal mor
238                                 Most organic pollutants reached higher levels in parasites than in ch
239 the composition and fate of the thousands of pollutants reaching the marine environment though wastew
240 educed number of targeted persistent organic pollutants, reaching open waters mainly via atmospheric
241                     Recently, we showed that pollutant reduction rates depend on the thermodynamic dr
242  high water-conservation, energy-saving, and pollutant-reduction goals for the petrochemical industry
243 s for water-conservation, energy-saving, and pollutant-reduction.
244 tion has important applications ranging from pollutant removal and nonreactive carriers, to other ind
245                                              Pollutant removal due to floodplain restoration was grea
246 curring oxo-anions, overestimating realistic pollutant removal potentials, and overlooking the need t
247 global concern regarding these anthropogenic pollutants, research into the remediation of microplasti
248 asurements such that the rate of change of a pollutant's concentrations at any time can be compared t
249                We highlighted differences in pollutant sequestration between urban areas and between
250  mug m(-3) following the short-lived climate pollutant (SLCP) mitigation emission pathway.
251 THRB), when exposed to 14 persistent organic pollutants (so-called "legacy" persistent organic pollut
252 d applied to other nanoparticles for diverse pollutant sorption applications.
253 ty benchmarks and that runoff may be a major pollutant source to urban surface waters.
254 op contamination was found to have different pollutant sources and release histories, even though bot
255 at damage lives and property can also impact pollutant sources and trigger poor water quality.
256 tion depends on facilitated diffusion of the pollutant substrates into the cell, mediated by speciali
257     The atmospheric concentration of several pollutants such as carbon dioxide (CO(2)), tropospheric
258         Therefore, exposure to environmental pollutants such as endocrine-disrupting chemicals (EDCs)
259 characterizing the transformation of organic pollutants such as HCHs in the complex soil-plant system
260 ce ambient concentrations of health-damaging pollutants such as ozone and fine particulate matter (PM
261 ic, make a large contribution to harmful air pollutants such as ozone and fine particulate matter (PM
262 nuously for months and release hazardous air pollutants such as particulate matter and volatile organ
263                    With the potential of air pollutants such as particulate matter to not only modula
264                  Transportation Lden and air pollutants tendentially associated with decreased and in
265  in which the mineralisation of the aromatic pollutant tetralin has been completely characterized at
266 on rates 2-4 times greater, depending on the pollutant, than other segments.
267    Malachite green is a common environmental pollutant that poses a great threat to non-target organi
268 stances (PFAS) are widespread and persistent pollutants that have been shown to have hepatotoxic effe
269 siloxanes (VMS) are ubiquitous anthropogenic pollutants that have recently come under scrutiny for th
270 (i.e., arsenic) and PFOA were the top ranked pollutants that have the potential to cause increased ri
271 iesel exhaust particles (DEPs) are major air pollutants that lead to numerous human disorders, especi
272                    This is especially so for pollutants that persist in the environment and can reach
273                            Emissions of most pollutants that result in fine particulate matter (PM(2.
274 cessary for allergens and particulate matter pollutants to promote airway inflammation.
275 ides is an important process that determines pollutant toxicities and mobilities.
276           Interspecies variation in maternal pollutant transfer may lead to negative effects scaling
277 ediation approach, but the quantification of pollutant transformation is complicated by the perturbat
278 or terrestrial sediment, organic carbon, and pollutant transport to the deep sea.
279 ty measured by the decay kinetics of a model pollutant trichloronitromethane.
280 tions of black carbon (BC) and other primary pollutants vary on small spatial scales (<100m).
281 mplarily, as proof of concept, one nontarget pollutant was identified as N-methylpyrrolidone.
282             Using ozone as a model gas-phase pollutant, we show that titanium-containing minerals oth
283 ing between water, energy, and environmental pollutant (WEE) subsystems, elements (different types of
284 ize was determined, and spatial gradients in pollutants were explored using latitude and longitude ce
285             Both particulate and gaseous air pollutants were positively associated with prevalent and
286  PM2.5, and PM2.5abs) and gaseous (NOx, NO2) pollutants were positively associated with prevalent DSP
287     In conclusion, concentrations of all air pollutants were significantly elevated in passenger cars
288  vascular risk factors and levels of outdoor pollutants were treated as covariates.
289 ght z-scores and exposure to mixtures of air pollutants, where up to -0.21 or approximately a 96 g de
290        Arsenic is a highly toxic heavy-metal pollutant which poses a significant health risk to human
291  pets, molds, etc), tobacco smoke, and other pollutants, which have an impact on respiratory health.
292 ould prime indigenous bacteria for degrading pollutants while providing minimal ecosystem disturbance
293 vironmentally harmful and ubiquitous aquatic pollutant with extensive production and application.
294 ontrast, trophic dilution was documented for pollutants with a high metabolic conversion rate, such a
295 acterization of abiotic reactions of organic pollutants with oxidants such as ozone or hydroxyl radic
296       We aimed to assess associations of air pollutants with prevalent and incident DSPN in a populat
297 perfluoroalkyl ether carboxylic acid (PFECA) pollutants with ultraviolet-generated hydrated electrons
298 ls, the effect estimates of all included air pollutants, with the exception of O(3), were significant
299      FeNO was positively associated with all pollutants, with the strongest associations for an inter
300                 Microplastics are ubiquitous pollutants within the marine environment, predominantly

 
Page Top