ライフサイエンスコーパス: spill

1 meric substances was observed after this oil spill.

2 several years after the occurrence of an oil spill.

3 re also occasionally reported after the AFFF spill.

4 present in sediment collected 10 months post spill.

5 erations or in the event of an environmental spill.

6 hat bloomed during the Deepwater Horizon oil spill.

7 beaches following the Deepwater Horizon oil spill.

8 ealth effects from the Deepwater Horizon oil spill.

9 he time of study enrollment, 1-3 y after the spill.

10 consistent with the results from the DWH oil spill.

11 disaster led to the largest ever marine oil spill.

12 s formation during the Deepwater Horizon oil spill.

13 , domestic conflict, and exposure to the oil spill.

14 ed from the 2010 Deepwater Horizon (DWH) oil spill.

15 d after the 2010 Deepwater Horizon (DwH) oil spill.

16 tem loss following the Deepwater Horizon oil spill.

17 Gulf of Mexico during the Deepwater Horizon spill.

18 dorous chemicals from an industrial chemical spill.

19 y effects associated with cleaning up an oil spill.

20 aim to find the responsible source(s) of the spill.

21 of crude oil in the environment after an oil spill.

22 her, conceived before and after a nearby oil spill.

23 consequence of biological synthesis and oil spills.

24 heir activities that control the fate of oil spills.

25 ight of a coffee cup can both lead to coffee spills.

26 g models that predict the fate of marine oil spills.

27 urfaces contaminated by uncontrolled patient spills.

28 generated dissolved organic matter from oil spills.

29 mental monitoring and risk assessment of FPW spills.

30 ominates microbial communities following oil spills.

31 en neighboring countries to mitigate any oil spills.

32 s such as wastewater treatment plants or oil spills.

33 Hs) in marine sediments as the result of oil spills.

34 f remediation and managing efforts after oil spills.

35 cts in populations following exposure to oil spills.

36 ment and buildings, and containment of agent spills.

37 in degrading petroleum after accidental oil spills.

38 s of fish are particularly vulnerable to oil spills.

39 ompared to GoM, global data and previous oil spills.

40 d impact of hydrocarbons released during oil spills.

41 soil/sediment following the traditional oil spills.

42 disturbances, especially hurricanes and oil spills.

43 y in the Arctic may increase the risk of oil spills.

44 gainst oil exposure during cleanup of future spills.

45 e microbial communities following marine oil spills.

46 working as a commercial fisherman before the spill (1.38, 1.21-1.57; and 2.01, 1.58-2.55, respectivel

47 This could indicate that spills (1) were small or contained on wellpads, (2) were

48 exico in 2010, one of the largest marine oil spills(1), changed bacterial communities in the water co

49 In 1950, a large oil spill (10 million L) covered the harbor area of Parry So

50 ring and following the Deepwater Horizon oil spill (2010-2013).

51 82.3%), and worked at least 1 day on the oil spill (76.5%).

52 For example, ~1300 spills (76 >= 400 gallons or ~1500 L) were reported from

53 ldwide concern because of the increasing oil spill accidents and industrial oily wastewater generatio

54 Marine pollution caused by frequent oil spill accidents has brought about tremendous damages to

55 thorities in the mitigation of potential oil spill accidents in the Eastern Mediterranean Sea.

56 whether their effect persists over time and spills across context.

57 The Antarctic Circumpolar Current (ACC) spills across the Falkland Plateau into the South Atlant

58 We study how onshore oil spills affect neonatal and infant mortality by combining

59 d (iii) improving the matching of diesel oil spills affected by weathering.

60 Forensic investigations of oil spills aim to find the responsible source(s) of the spil

61 opulations in natural oil ecosystems and oil spills, along with available underlying physicochemical

62 bons released from the Deepwater Horizon oil spill and deposited in marine sediments, this study char

63 We returned six decades after the spill and found that the frequency of deformities had re

64 AF) from slick oil collected during the 2010 spill and gradations of natural sunlight in a fully fact

65 saltmarsh ecosystem from 9 to 48 months post-spill and identify highly oxidized Macondo well oil comp

66 The Deepwater Horizon Oil Spill and physical health among adult women in southern

67 occur during crude oil production as well as spills and cause difficulties to efficient remediation p

68 l reefs, as well as in areas affected by oil spills and dispersants.

69 revenue, and energy, but also concerns over spills and environmental risks.

70 sel (LSMD) is frequently involved in coastal spills and monitoring ecosystem damage, and the effectiv

71 Large oil spills and oily wastewater discharges from ships and ind

72 exposed to contaminants derived from on-site spills and well-bore failures, should they occur.

73 o (collected after the Deepwater Horizon oil spill) and an asphalt volcano sample collected off the c

74 al means by which humans stave off slipping, spilling, and tilting disasters while manipulating objec

75 oastal development, agricultural runoff, oil spills, and fishing.

76 following disasters such as hurricanes, oil spills, and tsunamis, which may lead to increased popula

77 amination impacting shores after a major oil spill; and following the Deepwater Horizon (DWH) acciden

78 nd locations after the Deepwater Horizon oil spill are also shown to contain ketones/aldehydes, and c

79 mmediate effects on an ecosystem from an oil spill are clearly recognizable, however the long-term ch

80 ng-term chronic effects and recovery after a spill are still not well understood.

81 Crude oil spills are a worldwide ocean conservation threat.

82 Marine oil spills are catastrophic events that cause massive damage

83 Oil spills are one of the most dangerous sources of pollutio

84 Oil spills are one of the most serious forms of pollution in

85 d October 2011, disclose that the sinking of spill-associated substances, mediated by marine particle

86 ted HCB would respond in the event of an oil spill at sea.

87 ion rates occurring for ~1-2 years after the spill at sites with the highest amounts of plant stem oi

88 nimas River 13 days after the Gold King Mine spill (August 5, 2015).

89 ty and ease of transportation by eliminating spilling because its high melting temperature means it i

90 lth effects have been reported following oil spills but few studies have identified specific responsi

91 little is known about the degradation of oil spills by solar radiation and the impact of nutrient lim

92 Oil spills can be environmentally devastating and result in

93 Oil spills can have dramatic impacts on the environment.

94 Oil spills can lead to irreversible environmental degradatio

95 disturbances such as sea level rise and oil spills can potentially reduce marsh capacity for N remov

96 Diesel oil spill cases are more challenging, because biomarkers rec

97 ested on samples from a number of diesel oil spill cases, (i) distinguishing chemically similar sourc

98 -accommodated fraction (WAF) of oil from the spill causes developmental toxicity through cardiac defe

99 rt of workers and volunteers involved in oil spill clean-up after the Deepwater Horizon disaster.

100 INTERPRETATION: Oil spill clean-up workers with high amounts of total hydroc

101 ulation, 3D cell culture, micro reactor, oil spill clean-up, and oil/water separation.

102 able in oily wastewater purification and oil spill cleanup.

103 ays for reduced-emission combustion and fuel-spill cleanup.

104 f oil spills on the nitrogen cycle under oil spill conditions, and in improving current bioremediatio

105 on for hazard responses, such as SAR and oil spill containment, and hence have the potential to save

106 The Deepwater Horizon (DWH) oil spill contaminated coastlines from Louisiana to Florida,

107 The Deepwater Horizon (DWH) oil spill contaminated the spawning habitats for numerous co

108 Offshore oil exploration, oil spill contingency planning, and fish larval connectivity

109 rdized regulatory requirements for reporting spills could improve the accuracy and speed of analyses

110 important in the ultimate transformation of spilled crude oil.

111 We assessed spill data from 2005 to 2014 at 31481 UOG wells in Color

112 We designed an interactive spills data visualization tool to illustrate the value o

113 Covering spills decreased disinfection efficacy against E. coli o

114 remediated sites of underground storage tank spills demonstrates that composition of hydrocarbons in

115 The Deepwater Horizon Oil Spill (DHOS) is the largest oil spill in U.S. history, n

116 ed with respect to the Deepwater Horizon oil spill (DHOS).

117 NIFICANCE STATEMENT Clumsy disasters such as spilling, dropping, and crushing during our daily intera

118 ndirect effects of the Deepwater Horizon Oil Spill (DWH) on northern Gulf of Mexico (nGoM) reef fish

119 reline oiling from the Deepwater Horizon oil spill (DWH).

120 s into the marine environment from point oil spills (e.g. Deepwater Horizon).

121 We found 2-16% of wells reported a spill each year.

122 in spills sites up to 4 years following the spill events.

123 rface oil residues from the Exxon Valdez oil spill (EVOS) along the shorelines of Prince William Soun

124 vania to 4.9 m(3) in New Mexico; the largest spills exceeded 100 m(3).

125 Aqueous crude oil spills expose fish to varying concentrations of dissolve

126 The 2010 Deepwater Horizon oil spill exposed the Gulf of Mexico to substantial amounts

127 ned to investigate relationships between oil spill exposures and multiple potential physical and ment

128 s which can promote the understanding of oil spills fate in aquatic ecosystems.

129 Following the Deepwater Horizon (DWH) oil spill, field studies from a few sites suggested that oil

130 g the possible detrimental outcomes of toxic spills, for example oil spills, in relatively simple com

131 d enable us to differentiate the Macondo oil spill from other sources.

132 r facilities, superfund sites, and leaks and spills from industrial and municipal facilities.

133 Typically, the public learns of spills from reports from industry, media, or government

134 e/separation and their use in separating oil spills from water are summarized.

135 stal and offshore waters impacted by the DwH spill further revealed the changing nature of fluorescen

136 hereby describe an unusual case of infected spilled gallstones in the right sub-phrenic space, prosp

137 By conjugating EEDs to a TAT-PTD/CPP spilt-GFP peptide complementation assay, we were able to

138 nse and cleanup of the Deepwater Horizon oil spill (Gulf of Mexico) and heart attack risk among 24,37

139 monstrate that sediments impacted by the DWH spill had returned to near baseline conditions after 2 y

140 accommodated fraction (WAF) of oil from the spill has been shown to cause cardiac toxicity during ea

141 area and timing of the Deepwater Horizon oil spill highlight the need to study oil and hypoxia exposu

142 iment extracts collected over 48 months post-spill highlights the chemical complexity of highly polar

143 igate some of the effects of a potential oil spill, however, the effect of dispersant is ambiguous an

144 jor source of uncertainty related to the oil spill impacts.

145 ations were at prespill conditions after the spill in 2012 and 2013 near the DwH site, the variable a

146 mples from the largest accidental marine oil spill in history.

147 within 16 km of the wellhead during the oil spill in May 2010, which included one typical subsurface

148 U.S. history (The 2010 Deepwater Horizon oil spill in the Gulf of Mexico).

149 Following the Deepwater Horizon oil spill in the Gulf of Mexico, natural marine snow interac

150 a women exposed to the Deepwater Horizon Oil Spill in the WaTCH Study.

151 nology was applied to the largest marine oil spill in U.S. history (The 2010 Deepwater Horizon oil sp

152 Horizon Oil Spill (DHOS) is the largest oil spill in U.S. history, negatively impacting Gulf Coast r

153 Deepwater Horizon was the largest marine oil spill in U.S. waters, oiling large expanses of coastal w

154 Crude 4-methylcyclohexane methanol (4-MCHM) spilled in a river and then contaminated drinking water

155 rrupt disease transmission from uncontrolled spills in Ebola outbreaks.

156 norganic contamination associated with brine spills in North Dakota is remarkably persistent, with el

157 Chemical spills in streams can impact ecosystem or human health.

158 in areas impacted by oil and gas wastewater spills in the Bakken region of North Dakota.

159 This work suggests that oil spills in the Eastern Mediterranean Sea should be mitiga

160 topic tracers that can identify Bakken brine spills in the environment.

161 , the direction of the major axis of the oil spills, in most of the cases examined, is oriented accor

162 al outcomes of toxic spills, for example oil spills, in relatively simple communities such as often f

163 d with DVR estimates and minimized potential spill-in from uptake outside the brain.

164 lement of the concerted effort to respond to spills includes the ability to rapidly classify and char

165 sulting from the Deepwater Horizon (DWH) oil spill, including the use of the oil dispersant COREXIT i

166 itats, and population declines following oil spills, including DWH, have been documented.

167 ude 4-methylcyclohexanemethanol (crude MCHM) spilled into the Elk River, West Virginia.

168 trend for east and northeast movement of oil spills into the Levantine Basin, affecting the coastal a

169 The fingerprinting of the oil spill is based on a trace analysis of petroleum biomarke

170 Engineering bacteria to clean-up oil spills is rapidly advancing but faces regulatory hurdles

171 and PTSD, but after taking into account oil spill job experiences, only the association between the

172 Deep marine oil spills like the Deepwater Horizon (DWH) in the Gulf of M

173 er likely caused primarily by re-emission of spilled liquid hydrocarbons.

174 Nevertheless, during oil spills, low-abundant hydrocarbonoclastic bacteria bloom

175 cyclic aromatic hydrocarbons (PAHs) from oil spills may exert toxicity.

176 THC exposure from oil spills might be similarly associated, but no research ha

177 combining spatial data from the Nigerian Oil Spill Monitor with Demographic and Health Surveys.

178 conventional spectroscopic equipment for oil spill monitoring and fingerprinting in aqueous systems h

179 ed into titanite, both of which occur in the spilled Mount Polley tailings.

180 When oil spills occur in fish spawning habitats, natural resource

181 Seventy-five to 94% of spills occurred within the first three years of well lif

182 griculture, the food industry, cosmetics, or spills of liquids.

183 dings indicate that discharge and accidental spills of OGW to waterways pose risks to both human heal

184 esses change the chemical composition of the spilled oil and make the matching of oil spill samples t

185 hemical forces influencing the weathering of spilled oil have been investigated for decades, the envi

186 The long-term effects of oil spills on freshwater organisms have been little studied.

187 evidence suggesting that the effects of oil spills on neonatal mortality persist for several years a

188 on is paramount in predicting impacts of oil spills on the nitrogen cycle under oil spill conditions,

189 is critical to predicting the effects of oil spills on wild fish populations.

190 r as commonly occurred during a deep-sea oil spill or a natural seep, and enables detailed observatio

191 arge amount of hypersaline wastewater, whose spills or discharges may significantly increase the brom

192 perturbations (e.g., extreme weather, toxic spills or epizootics) severely reduce the abundance of a

193 orescence has to deal with multiple pathways spilling out low-energy long tail, that causes poor reso

194 , surfaces with substantial electron density spill-out give rise to electric fields with a much slowe

195 However, electronic spill-out is limited in F/H-terminated carbon materials.

196 vity overestimation in the object center and spill-out of counts from the object edges-remain of rele

197 uch as nonlocality(11-13) and local-response spill-out(14,15).

198 ntum effects such as nonlocality, electronic spill-out, and Landau damping.

199 to effects such as nonlocality and electron spill-out.

200 was an enlarged volume of interest including spilled-out counts, method 4 was activity concentration

201 in these observations with the Texas A&M Oil spill/Outfall Calculator (TAMOC), which models the press

202 Individual contributions to the public good spill over and benefit members in each group to differen

203 gh people to abandon the tradition, this can spill over and induce others to follow.

204 hat the inhibitory neurotransmitter GABA can spill over between axon terminals to cause excitation of

205 asing evidence that species and interactions spill over between habitats, calling for further study o

206 m zoonoses, where new vector-borne pathogens spill over from wild animals into humans.

207 t (e.g., mosquitoes), pathogen variants will spill over into human communities.

208 constitute reservoirs of infection that can spill over into other species.

209 s the third highly pathogenic coronavirus to spill over into the human population.

210 ted by the involved allergens suggesting the spill over of locally synthesized specific IgE to the ci

211 tivation and lipid oxidation in the lung can spill over systemically, leading to metabolic dysfunctio

212 that GABA release evoked from MNTB axons can spill over to neighboring MNTB axons and cause excitatio

213 disturbance of the innate immune system can "spill over" into autoimmunity in some cases.

214 this lineage infecting poultry in Asia have spilled over into wild birds and spread via bird migrati

215 imentary record suggests that meltwater only spilled over the threshold at the peak of the surge of E

216 to haemosporidian parasites that likely are spilling over from other local bird species.

217 S. commercial swine population, subsequently spilling over into exhibition swine, and caused a majori

218 rvation value, but these benefits may not be spilling over to crops.

219 Meltwater from Etonbreen spills over a threshold to the lake, only when the glaci

220 Humans become infected when NiV spills over from the reservoir species.

221 eedforward glutamatergic transmission, which spills over to allow cross talk between terminals in the

222 These spill-over effects suggest that major payment changes in

223 rvoir hosts is crucial to inform the risk of spill-over events, yet our understanding of these dynami

224 lihood of epidemics occurring as a result of spill-over events.

225 Multiple studies have suggested a "spill-over" effect into other conditions, but the extent

226 Although the oil spill overlapped with a relatively small portion of pred

227 se in the endemic rate of animal-human viral spill-overs in Africa by 2070, given current modes of he

228 en decades of production and hundreds of oil spills per year, there were no comprehensive baselines f

229 ominate the composition of heavily weathered spilled petroleum.

230 method by assessing the short-term risks oil spills pose to polar bears, ringed seals, and walrus in

231 with C. atrox venom will produce fibrinogen spilt products, thereby upregulating fibrinogen levels,

232 ted in this work, capable of classifying oil spills rapidly on-site.

233 Reporting rates varied by state, affecting spill rates and requiring extensive time and effort gett

234 en 2011 and 2013 collected information about spill-related activities, demographics, lifestyle, and h

235 il-August of 2010, the Deepwater Horizon oil spill released approximately 4 million barrels of oil in

236 The Deepwater Horizon oil spill released approximately 4.9 million barrels of crud

237 during the 2010 Deepwater Horizon (DWH) oil spill released numerous pollutants, including combustion

238 ever, their physiological role during an oil spill remains poorly understood.

239 ave important implications for enhancing oil spill remediation efforts in beach sands and coastal sed

240 diation is a low-cost approach for crude oil spill remediation, but it is often limited by electron a

241 g the high efficiency of fire whirls for oil-spill remediation.

242 xtiles, water harvesting, self-cleaning, oil spill removal and microfluidic devices.

243 environment including: immobilisation of oil spills, removal of dyes, extraction of heavy metals or t

244 verse health effects amongst marine life and spill responders in the northern Gulf of Mexico.

245 m lists of individuals who worked on the oil spill response and clean-up or received safety training.

246 Oil spill response and clean-up work was associated with inc

247 ers (hired after completing training for oil spill response and clean-up) and 2225 non-workers (compl

248 mental health of individuals involved in oil spill response and clean-up.

249 of chemical oil dispersants used in the oil spill response and cleanup (OSRC) work following the Dee

250 However, spill response and cleanup techniques (e.g., oil recuper

251 l systems and will have implications for oil-spill response decisions.

252 The 2010 Deepwater Horizon oil spill resulted in 1.6-2.6 x 10(10) grams of petrocarbon

253 The 2010 Deepwater Horizon oil spill resulted in the accidental release of millions bar

254 The Deepwater Horizon (DWH) oil spill resulted in the release of millions of barrels of

255 Oil spills resulting from maritime accidents pose a poorly u

256 ce of spatially explicit season-specific oil spill risk assessment in the Arctic and that environment

257 dy reports key information for improving oil spill risk assessment models and presents a novel approa

258 nd speed of analyses to identify and prevent spill risks and mitigate potential environmental damage.

259 ls, (ii) investigating weathering effects on spill samples to determine type and degree of weathering

260 the spilled oil and make the matching of oil spill samples to potential sources difficult.

261 ence of heavy metals in urban water and mine spill samples, based on the the dynamic transcription pr

262 ity to rapidly classify and characterize oil spill samples, preferably on-site.

263 Model simulations of the spill scenarios showed that addition of chemical dispers

264 population of marine phytoplankton under oil spill-simulated conditions, and compare it to that of th

265 Oil spill simulations for 19 existing offshore wells were ca

266 s is as important as the recovery of the oil spills since the supplies are scarce.

267 Sterilized, impacted, spill-site sediment released minor amounts of cis- and u

268 background waters, and soil and sediment in spill sites had elevated total radium activities ((228)R

269 elevated levels of contaminants observed in spills sites up to 4 years following the spill events.

270 r to that recognized internationally for oil spill source identification, is proposed for use in conj

271 e components that are consistent with an oil-spill source.

272 es, with potential applications for matching spill-source pairs in forensic investigations.

273 Positive matches for spill-source pairs were identified after excluding the s

274 Catastrophic oil spills stimulate these organisms to "bloom" in a reprodu

275 hough the oil persists six decades after the spill, sufficient uncontaminated sediment has covered th

276 and DOC concentrations three years after the spill suggest the potential long-term persistence of the

277 rom sea surface and deep plume waters of the spill that assimilate alkane and polycyclic aromatic hyd

278 We find that nearby oil spills that occur before conception increase neonatal mo

279 and highlight local disturbances (e.g., oil spills) that kill wetland plants as agents that can acce

280 ced two of the largest accidental marine oil spills, the 1979 Ixtoc-1 blowout and the 2010 Deepwater

281 n and the whole-body burden recovery after a spill), then the nonsteady-state formulation should be e

282 enced accelerated erosion as a result of the spill, these habitat impacts would represent additional

283 cid (PFOA)) from the solution state (after a spill) through the gel-state and finally into the true s

284 testing was conducted 2 weeks following the spill to understand resident perceptions, tap water chem

285 ude UV may underestimate the toxicity of oil spills to early lifestage fish species.

286 across scales ranging from local contaminant spills to global fluxes of methane emanating from ecosys

287 iments impacted by the Deepwater Horizon oil spill using a combination of (29)N2 and (30)N2 productio

288 for the analysis and matching of diesel oil spills using two-dimensional gas chromatography-high res

289 Median spill volumes ranged from 0.5 m(3) in Pennsylvania to 4.

290 centrations of dissolved salts (Na, Cl, Br), spill waters also consisted of elevated concentrations o

291 For fingerprinting the oil spill, we constructed diagrams and conducted correlation

292 sediment samples collected within 4 y of the spill, we develop a Macondo oil "fingerprint" and conser

293 bsequent to the 2010 Deepwater Horizon (DWH) spill, we implemented Gulf-wide fish surveys extending o

294 Individuals who worked on the spill were exposed to toxicants and stressors that could

295 Exposure measurements taken during the oil spill were used with questionnaire responses to characte

296 sceptible to evaporation, and photo-oxidized spills were also matched due to the presence of unaffect

297 Across all four states, 50% of spills were related to storage and moving fluids via flo

298 transport of droplets during a deep-sea oil spill with dispersant.

299 nt health impacts of THC exposure during oil spill work, and results support increased protection aga

300 xico) and heart attack risk among 24,375 oil spill workers enrolled in the Gulf Long-Term Follow-up S