ライフサイエンスコーパス: spill

1 re also occasionally reported after the AFFF spill.

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

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

4 hat bloomed during the Deepwater Horizon oil spill.

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

6 tem loss following the Deepwater Horizon oil spill.

7 Gulf of Mexico during the Deepwater Horizon spill.

8 dorous chemicals from an industrial chemical spill.

9 y effects associated with cleaning up an oil spill.

10 shoreline oil persistence after a major oil spill.

11 GOM during July 2012, 2 years after the oil spill.

12 ales collected around the world prior to the spill.

13 h oil from the 2010 BP Deepwater Horizon oil spill.

14 ional coral communities were impacted by the spill.

15 various intervals up to two years after the spill.

16 r) from a site impacted by a recent coal ash spill.

17 agreement with that of SOA formed at DWH oil spill.

18 l communities from the Deepwater Horizon oil spill.

19 Louisiana over the first 18 months after the spill.

20 n alkylated PAHs that can dominate in an oil spill.

21 d with gypsum after the October 2010 red mud spill.

22 of the environmental consequences of the oil spill.

23 itats as seen following the Exxon Valdez oil spill.

24 sediments several miles upstream of the ash spill.

25 is species could be altered following an oil spill.

26 beaches following the Deepwater Horizon oil spill.

27 present in sediment collected 10 months post spill.

28 ealth effects from the Deepwater Horizon oil spill.

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

30 consistent with the results from the DWH oil spill.

31 disaster led to the largest ever marine oil spill.

32 s formation during the Deepwater Horizon oil spill.

33 erations or in the event of an environmental spill.

34 consequence of biological synthesis and 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 emical dispersants for large-scale petroleum spills.

42 ally important in the aftermath of petroleum spills.

43 ncing the fate of crude oil in the sea after spills.

44 major role in the natural attenuation of oil spills.

45 ctures, wastewater discharge, and accidental spills.

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

47 urfaces contaminated by uncontrolled patient spills.

48 mental monitoring and risk assessment of FPW spills.

49 en neighboring countries to mitigate any oil spills.

50 s such as wastewater treatment plants or oil spills.

51 il concentration commonly found after an oil spill (1 muL L(-1)), the heterotrophic dinoflagellates N

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

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

54 consistent results with those at the DWH oil spill: (1) organic compounds of intermediate volatility

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

56 Here we focus on heavy fuel oil that spilled (~200,000 L) from two suspected fuel tanks that

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

58 82.3%), and worked at least 1 day on the oil spill (76.5%).

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

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

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

62 08 Tennessee Valley Authority (TVA) coal ash spill affected waters; (2) CCR effluents from power plan

63 n source and treated waters include chemical spills, algal blooms, and increased salinization, organo

64 appear to have been acutely impacted by the spill, although two of the newly discovered communities

65 vities began in the summer preceding the DWH spill and continued almost two years following the accid

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

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

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

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

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

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

72 Catastrophic oil spills and oil from waste waters such as bilge and frack

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

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

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

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

77 state MPAs where threats from shipping, oil spills, and offshore energy development remain.

78 Crude oil spills are a worldwide ocean conservation threat.

79 ispersant products with applicability to oil spill assessment.

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

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

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

83 nal changes in oil during the first day of a spill at the sea surface.

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

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

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

87 teria operated simultaneously throughout the spill, but their relative importance was controlled by c

88 ocarbons dissolved in water relevant for oil spills by evaluating the "fingerprint" of the volatile o

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

90 dispersed oil concentrations reported during spills, caused a lower initial production of eggs/naupli

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

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

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

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

95 able in oily wastewater purification and oil spill cleanup.

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

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

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

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

100 important in the ultimate transformation of spilled crude oil.

101 nce results assist interpretation of DWH oil spill data and formulating future protocols.

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

103 porating the 49 years (1964-2012) of OCS oil spill data, the EVT is capable of describing the oil spi

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

105 Covering spills decreased disinfection efficacy against E. coli o

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

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

108 The Deepwater Horizon oil spill (DWH) in 2010 in the Gulf of Mexico is the largest

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

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

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

112 formation and oil transport following an oil spill event.

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

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

115 upea pallasi) following the Exxon Valdez oil spill (EVOS) in Prince William Sound, Alaska.

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

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

118 study examines the potential effects of oil spill exposure on coral larvae of the Florida Keys.

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

120 ossible interactive effects of light and oil spill exposures on Calanus population dynamics under fie

121 cted to the immediate wound site rather than spilling extensively into the adjacent tissue as in cont

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

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

124 (ii) the use of homohopanes and TAS for oil spill forensics must account for degradation, and (iii)

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

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

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

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

129 n of Gulf water samples collected during the spill had PAH concentrations exceeding toxicity threshol

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

131 the wellhead apparently not impacted by the spill have been impacted by deep-sea fishing operations.

132 es of Louisiana and Florida after the BP oil spill have shown the presence of electron paramagnetic r

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

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

135 Toxic spills, hypoxia, disease outbreaks and toxin-producing a

136 graded within several years following an oil spill, (ii) the use of homohopanes and TAS for oil spill

137 FS) at the time of the Deepwater Horizon oil spill in 2010 and thereafter.

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

139 Tennessee Valley Authority Kingston coal ash spill in December 2008 deposited approximately 4.1 milli

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

141 rred, releasing more oil than any accidental spill in history.

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

143 The return period of a catastrophic oil spill in OCS areas is estimated to be 165 years, with a

144 months after the Deepwater Horizon (DWH) oil spill in the Gulf of Mexico (GOM).

145 my as evidenced by the Deepwater Horizon oil spill in the Gulf of Mexico in 2010 and the Fukushima nu

146 mpounds over the Deepwater Horizon (DWH) oil spill in the Gulf of Mexico in June 2010 indicated the p

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

148 Mexico is the largest accidental marine oil spill in the history of the petroleum industry.

149 In a simulated marine oil spill in the laboratory, PE-based results were within a

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

151 l ecosystem functioning, we simulated an oil spill in tidal mesocosms consisting of intact sediment c

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

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

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

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

156 rrupt disease transmission from uncontrolled spills in Ebola outbreaks.

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

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 his paper, the EVT is applied to analyze oil spills in the U.S. outer continental shelf (OCS).

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

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

164 ventricle and the atrial cavities displayed spill-in from the myocardium in late frames as compared

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 LN, increases with disease progression, and spills into the circulation in lupus-prone mice.

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

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

171 The Deepwater Horizon oil spill is unparalleled among environmental hydrocarbon re

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

173 ries along the coast might be sources of oil spills/leakages and lead to the formation of TBs.

174 f surface water and shallow groundwater from spills, leaks, and/or the disposal of inadequately treat

175 The Deepwater Horizon oil spill led to the severe contamination of coastal environ

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

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

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

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

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 s than in pristine ones where accidental oil spills occurred.

183 The Deepwater Horizon oil spill of 2010 prompted concern about health risks among

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

185 nsumer products used indoors, and accidental spills of liquids.

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

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

188 ence integrated environmental impact, of the spilled oil in the environment.

189 mited the ability to estimate the impacts of spilled oil on aquatic communities.

190 hance insight into the environmental fate of spilled oil, improved toxicology, molecular modeling of

191 ify that only one tank was the source of the spilled oil: in fact, a single principal component could

192 The spill oiled upper surface water spawning habitats for ma

193 The large-scale chemical spill on January 9, 2014 from coal processing and cleani

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

195 sidual disease and LN involvement (14%), and spill or soilage alone (9%).

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

197 ic routes from the surface (e.g., accidental spills or leaks).

198 Academic advances are now spilling out into the real world, with chefs and food in

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

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

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

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

203 During this time, glutamate release can spill outside the synaptic cleft and possibly stimulate

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

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

206 evaluating the likelihood of African HNVs to spill over into human populations.

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

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

209 Glutamate may spill over to more distant sites at the same synapse, or

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

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

212 longed release of 5-HT during motor activity spills over from its release sites to the AIS of motoneu

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

214 ogs preceded those in lions, suggesting that spill-over from dogs was the main driver of infection in

215 ogical data indicate that humans represent a spill-over host in which infection with M. bovis is not

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

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

218 odels lack adequate representation of energy spilling pathways and stoichiometric constraints on meta

219 apture of oil and gas began 43 days into the spill, petroleum hydrocarbons decreased, the fraction of

220 Selenium (Se) in coal ash spills poses a threat to adjacent ecosystems because of

221 The Deepwater Horizon oil spill produced large subsurface plumes of dispersed oil

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

223 hat crude oil samples collected from the DWH spill prolonged the action potential of isolated cardiom

224 to interact with dispersed crude oil after a spill, protozoan-mediated processes affecting crude oil

225 ne-xylene measurements-both collected during spills, providing oil estimates during wave tank dilutio

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

227 ta, the EVT is capable of describing the oil spills reasonably well.

228 ndicate that exposure of coral larvae to oil spill related contaminants, particularly the dispersant

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

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

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

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

233 ed to develop an inexpensive sorbent for oil spill remediation.

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

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

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

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

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

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

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

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

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

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

244 Oil spill response operations endorse the concept of net env

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

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

247 itigated flow from the wellhead early in the spill resulted in the highest proportions of n-alkanes a

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

249 The oil spill resulting from the explosion of the Deepwater Hori

250 esults of this study are very useful for oil spill risk assessment, contingency planning, and environ

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

252 ue samples from the 2007 M/V Cosco Busan HFO spill (San Francisco, CA).

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

254 eggs and larvae with oil from different oil-spill scenarios, both without and with the dispersant Co

255 Future risk assessments of coal ash spills should consider not only the leaching potential o

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

257 Oil spill simulations for 19 existing offshore wells were ca

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

259 brine treatment sites in Pennsylvania and a spill site in West Virginia show elevated levels of hali

260 t facility in Pennsylvania and an accidental spill site in West Virginia.

261 0(10) m(2) deep-water region surrounding the spill site indicate the deposition of a fossil-carbon co

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

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

264 tion of radium isotopes in some disposal and spill sites.

265 in soil or stream sediments near disposal or spill sites; and (4) the overextraction of water resourc

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

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

268 products were followed for 90 days from the spill start at April first independent of time for spawn

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

270 f Mexico, which when put in context with oil spill studies elsewhere should improve our ability to av

271 Large oil spills, such as the Deepwater Horizon (DWH) disaster tha

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

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

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

275 ston fossil plant and the site of a coal ash spill that occurred in 2008 in Tennessee.

276 ble large-scale response to catastrophic oil spills that can be used when the preferable option of re

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

278 lues have decreased since just after the DWH spill, they remain higher at some stations than typical

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

280 bacteria before, during and after the 83-day spill to determine the microbial response and biodegrada

281 water-accommodated fraction of oil from the spill to mahi-mahi as juveniles, or as embryos/larvae th

282 cted from in situ burn plumes of the DWH oil spill to study the acute effects of exposure to OSPM on

283 e Deepwater Horizon (DWH) Gulf of Mexico oil spill to track the subsea oil plume.

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 diments of the Emory River near the coal ash spill, total mercury concentrations were 3- to 4-times g

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

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

290 oral community significantly impacted by the spill was discovered in late 2010 at 1,370 m depth.

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

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

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

294 ed a more comprehensive understanding of oil spill weathering.

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

296 mory and Clinch River sediments near the ash spill were slightly elevated (up to a factor of 3) at ce

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

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

299 e likelihood that a similar catastrophic oil spill (with a volume over 1 million barrels) will happen

300 lity over an eighteen month period after the spill, with a specific focus on mercury and methylmercur