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1 ed to us identified 22 patients with 'visual snow'.
2 produces memory for a nonstudied word (e.g., snow).
3 turn are strongly influenced by rainfall and snow.
4 nts and geochemical analytes measured in the snow.
5 gnificantly influence Hg(0) flux from Arctic snow.
6 the atmosphere and co-precipitated with the snow.
7 w much Hg is transported with melting Arctic snow.
8 ients had first degree relatives with visual snow.
9 he production of nitrite and nitrous acid in snow.
10 dissolved organic matter (DOM) in Antarctic snow.
11 f consideration of the vertical structure of snow.
12 ertime temperature can modify this effect of snow.
13 n the oceanic water column, sea ice or polar snow.
14 f four cities that are exposed to wintertime snow.
15 atologic knowledge in the cities impacted by snow.
16 sectioned peat cores (4 sites, n = 161), and snow (7 sites, n = 19) from ombrotrophic bogs in the AOS
17 summation operatorPFAS) in freshly deposited snow (760-3600 pg L(-1)) were 1 order of magnitude highe
20 fate and dynamics and reveals the effect of snow accumulation and melt processes on the fate of semi
24 rdwood forest to determine how reductions in snow accumulation, expected with climate change, directl
27 ce mixing model showed that DOC deposited in snow across the Icefield reflects fossil fuel combustion
29 % and 90-100% in medium- (MS) and high- (HS) snow additions relative to Ambient, contributing to incr
30 e combined with UV irradiation intensity and snow age on Hg(0) flux from Arctic snow and (2) elucidat
31 amber, snow temperature, UV irradiation, and snow age were found to significantly influence Hg(0) flu
32 We estimated that the overall decrease in snow albedo by red pigmented snow algal blooms over the
34 strate a relationship between tree cover and snow-albedo feedback that may be used to accurately cons
36 all decrease in snow albedo by red pigmented snow algal blooms over the course of one melt season can
38 nsity and snow age on Hg(0) flux from Arctic snow and (2) elucidate the effect of temperature on snow
40 ower elevation plots, which accumulated less snow and experienced more soil temperature variability d
42 y show that the production of metabolites in snow and ice algae is driven mainly by nitrogen and less
43 abitats on glacial surfaces are dominated by snow and ice algae, which are the critical players and t
44 mple water supply during summer from melting snow and ice as well as thawing permafrost, contrasting
45 Black carbon (BC) in haze and deposited on snow and ice can have strong effects on the radiative ba
47 ng is expected to reduce northern hemisphere snow and ice cover, continued increase in atmospheric gr
50 soluble chemical species that are trapped in snow and ice offer the possibility to investigate past c
51 in the photochemical processes that occur in snow and ice, and DOM could be a significant, but to dat
54 Enhanced concentrations were observed in snow and meltpond samples, implying atmospheric depositi
55 ow depths, and collected over 100 samples of snow and meltwater for chemical analysis in 2008 and 200
56 om the Central Arctic Ocean and shelf water, snow and meltwater samples were collected in 2012; 13 PF
57 ative experiment with additions of rainfall, snow and N was conducted to test their effects on ECE in
58 t limited water resources (such as dew, fog, snow and rain), yet the mechanisms for water collection
60 ere detected at large distances (>100 km) in snow and surface lake sediments, suggesting that the imp
61 en support by diffusion from the surrounding snow and the clearance of CO2 by diffusion and absorptio
62 lifornia, water storage deforms the crust as snow and water accumulates during the wet winter months.
63 active environment and chemical processes in snow, and a lack of consideration of the vertical struct
64 dry world, even a small amount of rain, fog, snow, and even atmospheric humidity can be adequate for
65 e influenced Hg photoreduction kinetics when snow approached the melting point (>-2 degrees C), where
69 nd their masking effect of highly reflective snow, available energy is lower in wetlands, especially
70 Breathing under snow, e.g. while buried by a snow avalanche, is possible in the presence of an air po
71 8 (95% CI, 1.50-5.94; P = .002), presence of snow banking had an adjusted HR of 3.71 (95% CI, 1.18-11
72 whole-community microbial DNA from Antarctic snow, brine, sea ice and sea water to elucidate potentia
73 C7-14 perfluoroalkyl carboxylates (PFCAs) in snow but limited to the transited areas of the research
75 warm spells in winter with rainfall (rain-on-snow) can cause 'icing', restricting access to forage, r
76 event involving the genetic admixture of the snow-capped (Lepidothrix nattereri) and opal-crowned (Le
77 Crown patches are highly reflective white (snow-capped manakin) or iridescent whitish-blue to pink
78 of over snow vehicles (OSV), including five snow coaches and one snowmobile, were measured on a desi
79 eposition, surface snow, streams from melted snow, coastal seawater, and plankton samples were collec
81 However, the factors that generate the TP snow cover (TPSC) anomalies at the intraseasonal time-sc
82 at High Arctic sites with sufficient winter snow cover and ample water supply during summer from mel
83 and attributing the phenological changes in snow cover are essential for meteorological, hydrologica
86 a possible influence of decrease in seasonal snow cover duration, which could have exposed larger bas
93 the growing season as a result of decreased snow cover will not necessarily result in greater tundra
94 ), known as the third pole of the Earth, has snow cover with intraseasonal to decadal variability tha
95 gional abrupt changes in the ocean, sea ice, snow cover, permafrost, and terrestrial biosphere that a
100 s except for strong wintertime dependence on snow covered conditions and corresponding variation in a
101 emisphere live in regions that are regularly snow covered in winter, there is little hydro-climatolog
102 s controlled largely by the contrast between snow-covered and snow-free albedo (Deltaalpha), which in
103 and tree cover differ substantially between snow-covered and snow-free periods, and among plant func
105 ct on the composition of the atmosphere over snow-covered areas as well as on the composition of the
113 ms ordered hexagonally symmetric structures (snow crystals) in its solid state, however not as liquid
114 n freshly deposited snow relative to surface snow (CSD/CSnow), snowmelt (CSD/CSM), and seawater (CSD/
116 e observations with climate reanalysis data, snow data assimilation model output, and satellite spect
118 se in CO2 were mainly associated with higher snow densities and led to premature interruption due to
120 ing into snow with an artificial air pocket, snow density had a direct influence on ventilation, oxyg
124 input of PFAS to Maritime Antarctica, fresh snow deposition, surface snow, streams from melted snow,
126 ce (Normalized Difference Vegetation Index), snow depth and temperature, and the best fit model inclu
127 ly observed responses of plants to increased snow depth at the same experimental site, the ECM fungal
128 ance, but at this intermediate canopy level, snow depth had negative effects on winter survival of se
130 canopy closure, prescribed fire, and winter snow depth on demographic transitions of each species.
131 Here, we focus on the effects of increased snow depth, and as a consequence, increased winter soil
132 gs as a function of both winter coldness and snow depth, both of which are expected to decline with c
133 explanations, including forest disturbance, snow depth, or permafrost melting, could not explain pat
139 lvic and humic acids and an authentic Arctic snow DOM sample isolated by solid phase extraction, indi
143 s data from 2001 to 2014 points out that the snow end date (De) advanced by 5.11 (+/-2.20) days in no
147 tmospheric conditions lead to greater winter snow fall, changes in the ECM fungal community will like
152 ation and was likely conducive to marine oil snow formation, analysis of the MiSeq-derived 16S rRNA d
154 ely by the contrast between snow-covered and snow-free albedo (Deltaalpha), which influences predicti
155 iffer substantially between snow-covered and snow-free periods, and among plant functional type.
157 s particularly strong towards the end of the snow-free season, and it has intensified in recent years
160 igin and nature of glacier DOC, we collected snow from 10 locations along a transect across the Junea
163 ions and case studies (influenza A in lesser snow geese and Yersinia pestis in coyotes), we argue tha
164 g these actions, the increasing abundance of snow geese has since induced a state of satiation in har
165 dance and destructive foraging behaviours of snow geese have created a trophic cascade that reduces (
168 With the aim of controlling overabundant snow geese, the Conservation Order amendment to the Inte
171 red growth trajectories of Canada and lesser snow goose goslings raised on grass-based diets that dif
174 able to support Canada goslings better than snow goslings which require higher-quality forage to sur
175 5 change in emissivity due to mineralogy and snow grain size can cause a 1.8-2.0 W m(-2) difference i
177 in snowpack; however, DOM photochemistry in snow/ice has received little attention in the literature
178 ts further imply that local accumulations of snow/ice within gullies were much more voluminous than c
181 inside the snowpack, producing rigorous lava-snow interaction via meltwater percolation down into the
186 he same heterocyclic aromatics identified in snow, lake sediments, and air were observed in extracts
187 central Greenland was extracted from recent snow layers at NorthGRIP (75.1 degrees N, 042.3 degrees
189 must have accreted material from beyond the 'snow line', which is the distance from the Sun at which
195 ur results imply that highly dynamical water snow-lines must be considered when developing models of
197 ied, emerging drivers of disturbance such as snow loss and subsequent mortality are much less documen
205 ctic and the reduction in albedo accelerates snow melt and increases the time and area of exposed bar
206 if decreased water availability from earlier snow melt and warmer summer temperatures lead to earlier
207 climate change is expected to cause earlier snow melt but may not change the last frost-free day of
213 e salinity, indicating a source from ice and snow melting and consistent with snow depositional input
217 n this study, the structure and diversity of snow microbial assemblages from two regions of the weste
220 plored the formation mechanism of marine oil snow (MOS) and the associated transport of oil hydrocarb
221 Furthermore, the formation of marine oil snow (MOS) in oil-amended incubations was consistent wit
223 able isotope ratio (delta(15)N) in Greenland snow nitrate and in North American remote lake sediments
232 using two methods: in 2011-2013 by altering snow pack (snow-removal vs. control treatments), and in
233 particularly sensitive to changes in winter snow pack accumulation and winter soil temperature varia
235 to the higher temperatures, earlier loss of snow packs, longer growing seasons, and associated water
236 ing the definition of "dragon kings." Marine snow particles overwhelmingly contributed to the total p
238 rements of sulfate aerosols extracted from a snow pit at the South Pole (1984-2001) showed the highes
243 corresponded to lower DOC concentrations in snow (R(2) = 0.31) and a decrease in percent humic-like
244 er phenology led to contrasting anomalies of snow radiative forcing, which is dominated by De and acc
245 mean winter temperatures is at or above the snow-rain threshold (>0 degrees C mean winter temperatur
246 ean winter temperatures are currently at the snow-rain threshold and have been warming for approximat
249 The probabilistic projections show that the snow-rain transition zone will shift to the north under
250 ed distributions of snow frequency show that snow-rain transition zones are mainly zonally distribute
251 e system through atmospheric temperature and snow recharge, which are known exhibit stochastic variab
253 ix Greenland shallow firn cores from the dry snow region confirms that the most recent prior widespre
254 albedo below a critical threshold in the dry snow region, and caused the melting events in both 1889
255 ual PFAS concentrations in freshly deposited snow relative to surface snow (CSD/CSnow), snowmelt (CSD
256 g the first and second growing seasons after snow removal (P = 0.023 for 2009 and P = 0.005 for 2010)
259 ntal treatments, extended growing season via snow removal and extended growing season combined with s
263 the prediction that plants exposed to early snow removal would resemble individuals from lower eleva
265 lowering occurred approx. 10 days earlier in snow-removal than control plots during all years of snow
266 methods: in 2011-2013 by altering snow pack (snow-removal vs. control treatments), and in 2013 by ind
269 s and measurements of CH4 trapped in ice and snow reveal a meteoric rise in concentration during much
271 ride at trace levels in more than 450 recent snow samples collected during the 1998-1999 Internationa
272 CBs are in agreement with data from seasonal snow samples in the Alps, but are a factor of 100 higher
273 Despite this, the chemical composition of snow samples was consistent with a marine contribution,
275 idence indicating the presence of marine oil snow sedimentation and flocculent accumulation (MOSSFA).
277 e, USA, that concurrently monitored climate, snow, soils, and streams over a three-year period and su
278 e Antarctica, fresh snow deposition, surface snow, streams from melted snow, coastal seawater, and pl
279 et survey (n = 275) of self-assessed 'visual snow' subjects done by Eye On Vision Foundation was anal
283 ult from observed and predicted increases in snow thickness, active layer depth, and soil temperature
284 s imply that large mass transfers of Hg from snow to air may take place during the Arctic snowmelt pe
285 the climate warms, a transition from winter snow to rain in high latitudes will cause significant ch
287 panish broom (Spartium junceum), in the rain-snow transition zone of the Sierra Nevada of California.
290 f mast seeding using four 40-yr Chionochloa (snow tussock) datasets; and comparing the performance of
291 s of MeHg production in snowpacks and melted snow using mercury stable isotope tracer experiments, as
293 use, and tailpipe exhaust emissions of over snow vehicles (OSV), including five snow coaches and one
294 al covariates, history of work over water or snow was associated with increased odds of XFS (OR, 3.86
296 recipitation-evapotranspiration index, April snow water equivalent, and water year streamflow from a
299 cation in plankton to a thin layer of marine snow widely observed in stratified systems that concentr
300 port that in healthy subjects breathing into snow with an artificial air pocket, snow density had a d
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