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1 ring winter/spring) than in the eMed (during summer).
2 s apart from lower prevalence of mice during summer.
3 s and accelerated the sea ice melting in the summer.
4 e community composition during the following summer.
5 temperatures reaching up to 42 degrees C in summer.
6 higher risks were observed in winter than in summer.
7 from the European atmospheric variability in summer.
8 seeds cultivated in winter against those in summer.
9 s long before the Arctic becomes ice-free in summer.
10 t) century shows significant increase during summer.
11 g autumn and winter and is absent during the summer.
12 lead to increased C. finmarchicus biomass in summer.
13 the active North Sea bacterioplankton in the summer.
14 winter and greater host plant desiccation in summer.
15 erally, SHP develops and is diagnosed in the summer.
16 eveloped more petals than those flowering in summer.
17 ugh the differences tended to be less in the summer.
18 with total arsenic or DMA during the spring/summer.
19 heast during the winter and south during the summer.
20 ce of cyanobacterial blooms in the following summer.
21 d the drawdown of [Formula: see text] during summer.
22 nated by limiting silicate concentrations in summer.
23 in the modern environment in both winter and summer.
24 he shoulder seasons and decreases during the summer.
25 and occupied deep pelagic waters during the summer.
26 male weasels then regrow during their second summer.
27 highest during low snowfall winters and cool summers.
28 plant productivity in the increasingly warm summers.
30 arlier after spending a weekend camping in a summer 14 hr 39 min:9 hr 21 min natural light-dark cycle
31 previously shown that exposure to a natural summer 14 hr 40 min:9 hr 20 min light-dark cycle entrain
32 rrelating negatively with temperature in the summer 2 yr before masting, and positively with summer t
33 od sampler at three sites and for 5 weeks in summer 2009 and 5 weeks in winter 2010 in Cleveland, OH.
37 eaths comparable to that observed during the summer 2017 mass mortality event may cause a decline to
39 , 402 kJ kg(-0.75) d(-1)) and the highest in summer (25.87 +/- 3.88 MJ d(-1), 586 kJ kg(-0.75) d(-1))
43 d North American cities, particularly during summer afternoons when NO levels are low and temperature
46 Rice was traditionally grown only during the summer (aman) monsoon in Bangladesh but more than half i
47 more and Chicago are most intense during the summer and at night, with urban-rural aerosol pH differe
48 ty formed cool (spring and winter) and warm (summer and autumn) subgroups, indicating that spatial va
51 or bears that remained on the sea ice during summer and fall, while mean concentrations of the POP ch
53 represented the main OMCOARSE source during summer and its contribution to PM10 was comparable to th
54 hat in the last 60 years both high-frequency summer and spring NAO, and low-frequency winter NAO comp
55 genic (NT - MSOY8200) soybean seeds, sown at summer and winter cultivation periods are investigated u
56 Sampling over three weeks was conducted in summer and winter for each city and covered each system
57 in the resting periods of people between the summer and winter in southern cities is almost twice tha
59 UK diets and earlier studies showed organic summer and winter milk to be significantly lower in iodi
60 es for each year from 2004 to 2009, and mean summer and winter temperatures for each tract in each ye
62 stablishment and GDD, suggesting that longer summers and/or greater heat accumulation might enhance e
63 m brandy according to harvest time as early (summer) and late (autumn) plum varieties; the total corr
64 Diplotaxis tenuifolia were grown in the UK (summer) and subjected to commercial growth, harvesting a
67 reasing precipitation, especially during the summer, and the conversion of forest to cropland, grassl
70 1 degrees ) surface observations of extended summer (April-September) surface ozone (O3), fine partic
72 de, organic and polar fraction yields in the summer are correlated with the coumarin UV-vis absorbanc
73 ial factors but snake assemblages facing dry summers are more affected by spatial processes operating
75 ntly increased compared to a HL diagnosis in summer at higher latitudes (HR = 1.082 [95%-CI: 1.009-1.
76 est growth of A. muricata was in the 2013-14 summer at Lizard Island, which was unusually cool and 0
77 in 34 families from 111 sites that varied in summer average temperature by 1.7-3.4 degrees C within e
79 temperatures, those equivalent to long-term summer averages in their natural habitats ( 29 degrees C
81 ratosphere over the central United States in summer based upon the same reaction network that reduces
85 7%-285% across time, while two larger spring-summer breeders with higher thermal preferences declined
86 nvest substantial resources in boot camp and summer bridge activities in the hopes of better supporti
87 Many PhD programs incorporate boot camps and summer bridge programs to accelerate the development of
88 g total fuel and fine fuel structure) on the summer Burned Area (BA) across all eco-regions in Medite
89 competition for resources in both winter and summer but was less pronounced in recent years, despite
90 inifera species will not be inhibited during summer, but instead the temperature window for their cal
91 a westward shift of anticyclonic airflow in summer, but uncertainty is larger for spring with only h
92 study in a eutrophic subtropical bay during summer by investigating the effect of rising CO2 on a mo
93 olonies of A. muricata during the winter and summer, by partially enclosing each colony in a clear pl
98 bial assembly are stronger under winter than summer conditions and inhibit the recruitment of the cya
100 scillations and the predicted lengthening of summer conditions will have a significant positive impac
102 we attribute this expansion to multi-decadal summer cooling likely driven by volcanic and/or solar fo
104 s C in the field experiment during a typical summer day, indicating a great potential application for
106 rrestrial-aquatic linkages occur during mild summer drought and whether this affects biota across 43
107 show that the detrimental effects of severe summer drought on ecosystem carbon storage can be mitiga
109 gnificant relationship between fire and same-summer droughts in most regions, while antecedent climat
111 n of summertime atmospheric circulation--the summer East Atlantic (SEA) pattern--is predictable from
112 by the implementation of policies to reduce summer electricity consumption in the affected areas, fo
119 how volcanically-induced suppression of Nile summer flooding led to societal unrest in Ptolemaic Egyp
121 , peak algal biomass was generally higher in summers following bankfull, bed-scouring winter floods.
122 ime series, winter influenced the subsequent summer for some nutrient variables and zooplankton bioma
123 ter snow cover and ample water supply during summer from melting snow and ice as well as thawing perm
126 eeply thawed soils exceeded the increases in summer GPP, and thawed tundra was a net annual CO2 sourc
129 ical evidence of molting suggests that after summer had passed, molt began in the adults that had jus
130 f extreme weather in the Northern Hemisphere summer have been shown to be associated with the presenc
131 reas those assemblages in regions with rainy summers have a stronger signature of coarse-scale proces
132 sonal dynamical model forecasts for European summers have very little skill, particularly for rainfal
133 iod cues, patterns of genetic variation, and summer heat waves could limit the capacity of coast Doug
134 erature and water viscosity, winter calm and summer (iceberg and storm) disturbance and resources.
135 rite concentrations can exceed 10 muM during summer in estuarine waters adjacent to Sapelo Island, Ge
138 n bottom waters (hypoxia) forms nearly every summer in the northern Gulf of Mexico because of nutrien
139 ns with distinct climatological regimes: dry summers in the northern-AF and rainy summers in the sout
141 t species in monsoonal wet deposition in the summer Indian subcontinent, Bangladesh, with inorganic a
142 lankton blooms beneath ponded sea ice during summer, indicating that satellite-based Arctic annual pr
143 s suggest lower TC activity despite stronger summer insolation and warmer sea surface temperature in
144 0 yr precession cycle in northern hemisphere summer insolation by an average of 3240 years (-900 to 6
145 glacials occurred when the energy related to summer insolation exceeded a simple threshold, about eve
146 6,000 yBP) characterized by increased boreal summer insolation, a vegetated Sahara, and reduced dust
147 higher, but population growth from spring to summer is lower, after a warm compared with a cold sprin
150 years, those with shorter springs and longer summers, lake trout had reduced access to littoral habit
152 the degree of amplification in inter-annual summer LSWT is variable, and is greater for cold lakes (
153 the observation of an amplified response of summer LSWT to SAT variability using 20 years of satelli
154 CO2 fixation in the above-ground biomass of summer maize (Zea mays L.) under different tillage and r
156 mperatures reached or exceeded the long-term summer maxima, coral growth during summer periods was eq
158 of PV systems over Sydney, Australia reduces summer maximum temperatures by up to 1 degrees C because
159 hat predicts microcystin concentrations from summer mean total nitrogen and total phosphorus concentr
161 When floods ravage Asian monsoon regions in summer, megadroughts often attack extratropical North Am
162 Here I show that these glaciers provide summer meltwater to rivers and aquifers that is sufficie
166 dependent intensifications of the East Asian summer monsoon (EASM) around the O-M boundary and the la
167 The Holocene variability in the East Asian summer monsoon (EASM) based on speleothem delta(18)O rec
168 n variability associated with the East Asian summer monsoon (EASM) has profound societal implications
171 etween the North Atlantic and the East Asian Summer Monsoon regions, probably via the westerlies.
173 es strongly with the weakening of East Asian summer monsoon which is the primary source of moisture a
174 ed in the dry period before the onset of the summer monsoon, suggesting that local land-atmosphere fe
175 os indicate a marked upward trend during the summer months and an increase in the relative risk of th
177 source was also 0.8-6.7 degrees C warmer in summer months than Detroit water and exceeded the minimu
180 ossible at several U.S. locations during the summer months, particularly in southern Florida and Texa
190 ossible that record low precipitation in the summer of 2007 led to the higher major ion and Hg concen
192 visitors (n = 293) were surveyed during the summer of 2015 and asked to choose among images of wildf
196 We repeatedly surveyed lizards in spring and summer of each year at up to 32 sites, and used hierarch
199 wo contrasting phenotypes, termed winter and summer, of four Caribbean reef corals to similar light a
203 tions of the seasonal thermocline during two summer periods in the Medes Islands marine reserve (NW M
204 long-term summer maxima, coral growth during summer periods was equal to, if not lower than, winter p
205 of summer values for chlorophyll a, 15.8% of summer phytoplankton biovolume and 25.3% of summer zoopl
207 -16) following over 100 years of warming and summer precipitation in this polar desert environment pr
211 ls to an uncontaminated mountain site during summer proved to be an effective decontamination procedu
212 denitrification products, especially during summer rainfall events, may lead to underestimation of a
213 ediate application to empirical forecasts of summer rainfall for the United Kingdom, Ireland, and nor
216 tegy; due to the conical shape of mountains, summer range was expected to decline by 17%-86% for 7 of
217 to higher elevation (i.e., "thermoneutral") summer range was unlikely to be a viable behavioral adap
221 casts of UV dosage over the United States in summer require understanding the response of this dynami
226 fying organisms encompassed up to 56% of the summer season, and were accompanied by some of the lowes
229 ged between 7.68 and 9.88 km(2), and for two summer seasons that ranged between 5.51 and 6.24 km(2).
230 olarity (logP approximately 1.9), whereas in summer, smaller (225-330 g/mol) and more polar (logP app
235 more frequently during biological spring and summer; specimens of threatened species collected less f
236 ental exposure to present and predicted mean summer SST of the Mediterranean Sea (25 degrees C, 27 de
238 ethane accumulated in the hypolimnion during summer stratification, and at most 15% of the diffusive
241 mer 2 yr before masting, and positively with summer temperature 1 yr before masting (i.e. 2T model).
245 ng was more sensitive to a given increase in summer temperature at colder than warmer high-latitude l
246 ities of Rangifer populations, and projected summer temperature changes by the NCAR CCSM4.0 general c
248 dest high-temperature tolerance despite high summer temperature extremes, species in mid-latitude ( 2
252 ence between using a macroclimate predictor (summer temperature) and using a mechanistic predictor (p
253 relation to existing combinations of maximum summer temperature, mean annual streamflow, and their in
254 s best explained by spring precipitation and summer temperature, whereas stem growth showed weak and
255 in high-latitude species because it elevates summer temperatures above the upper limit for reproducti
256 y, temperatures >16 degrees C (equivalent to summer temperatures at sites where P. helianthoides were
258 easonal climate trend (e.g., the increase of summer temperatures in Antarctica in the last decades) i
259 ulations in lakes to the effects of elevated summer temperatures in historically acidified ecosystems
260 ed pattern, with negative effects of extreme summer temperatures in hotter areas and positive effects
261 patterns of branching coral growth, and high summer temperatures in the northern GBR may already be c
262 dalea corals from the hot Persian Gulf where summer temperatures reach 36 degrees C were compared wit
263 ing phenology in a given year was delayed if summer temperatures were high the previous year or 2 yea
267 nd observed were significantly larger during summer than other seasons potentially because of higher
268 approximately 2,000 storms, on average, each summer that reach the altitude of rapidly increasing ava
269 n the stratosphere over the United States in summer that resolves spatial and structural variability,
270 te models project ice-free conditions during summer this century under realistic emission scenarios,
272 a simple explanation for not only the spring-summer timing of historical pandemics, but also early in
274 el projects a 0.2-unit drop in pH during the summer upwelling season from 2013 to 2063, which results
275 Redundancy analyses revealed that in the summer, urban and agricultural streams were abundant in
277 o the stratosphere over the United States in summer using the Next-Generation Radar system; (ii) the
278 n expected; mean winter values were 43.2% of summer values for chlorophyll a, 15.8% of summer phytopl
281 ona shrubs in response to recent High Arctic summer warming shows that recent and future warming migh
283 to predictions, such as positive effects of summer water availability in wetter parts of the range a
285 plots driven by increasingly severe postfire summer weather events (number of consecutive days with h
286 skill reflects inherent unpredictability of summer weather or, alternatively, is a consequence of we
289 in contrast, concentrations are high during summer when air is mainly arriving from the oceans but l
290 t, with the largest contributions during the summer when wildfires occur and smaller contributions du
292 assemblages is greater in regions with rainy summers where climatic niche partitioning is more likely
293 lains in spring and in the central plains in summer, whereas current climatological patterns persist
294 dult brown trout attained 100% at the end of summer, while seasonal population decay was higher in YO
295 correlated with the coumarin absorbances in summer, winter and spring whereas mixtures without ethan
296 nge comparing exposure from 48 to 720 hours (summer worker lifespan) for cadmium, as the most time-de
297 hat the survival of family lineages from the summer worker to the spring queen stage in the following
298 Conversely, tropical ectotherms facing dry summers would have fewer opportunities to climatic niche
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