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1 ter of restored floodplains along a mid-size river.
2 duction in BC concentrations to the Colorado River.
3 via greater carbon evasion from streams and rivers.
4 ates sulfate that is carried to the ocean by rivers.
5 fate of 216 P. unifilis nests along 88 km of rivers.
6 odplain systems and light-limited whitewater rivers.
7 may impact the chemical pollution burden in rivers.
8 ogical Survey streamgage sites in freshwater rivers.
9 from inland waters to coastal systems making rivers a critical link between terrestrial and ocean car
13 typical seasonal lake linked to the Yangtze River and is significantly affected by water level fluct
14 We found high, but relatively stable Maumee River and lake concentrations of total P (TP) and solubl
16 of the eastern part, delimited by the Tiber River and the Apennine Mountains, manifest a peculiar mi
21 valent freshwater volume stored in lakes and rivers and is universally accessible without pipelines o
22 ll agricultural streams that drain to larger rivers and lakes, despite best management practices inte
25 results indicate that the removal of dams on rivers and their connected reservoirs applies predominan
28 and in three different water matrixes (tap, river, and groundwater), and thereby validated for repea
30 se nitrate delivery to the main stem Yenisei River, and ultimately the Arctic Ocean, in the coming de
31 d the spawning migration as adults return to rivers, and the overall abundance and distribution of se
32 osaic ecosystem populated by groundwater-fed rivers, aquatic plants, angiosperm shrublands, and edibl
34 in North America, and the La Plata and Nile Rivers are found to contribute extensively to virtual wa
36 roplatidae: Keroplatinae), which occur along river banks in the Appalachian Mountains in Eastern Unit
39 ted agriculture in the snow-dependent Yakima River Basin (YRB) in the Pacific Northwest United States
40 arcelona catchment area, including the Besos River basin and the Barcelona coast, and in the Ebro Riv
43 am bromide concentrations in the Monongahela River Basin in the water year (WY) 1998 (during a nation
45 ises the North China Type, the Lower Yangtze River Basin Type, the Southwest Type, the Plateau Type,
46 sses in riparian zones of the Lower Savannah River Basin, followed by cultivated crops and pasture/ha
50 m 33 mesocosm experiments with those from 14 river basins and 22 cross-basin studies in Europe, produ
51 characteristics controls the transition from rivers being 'sinks' to 'sources' of microplastics under
53 ciasis, a macroparasitic disease that causes river blindness in Western Uganda and other regions of A
54 ood fluoroethers released into the Cape Fear River by a fluorochemical manufacturing facility were de
55 epeated landslides dammed the Yigong Tsangpo River ca. 3500 BC, 1300 BC, 1000 BC, 600 BC, and twice m
58 a and Syr Darya, were the center of advanced river civilizations, and a principal hub of the Silk Roa
61 , samples from along straight courses of the river contained fewer microplastics than samples from in
66 flood changes to longitudinal variability in river conveyance, precipitation climatology, flows and s
68 ater is routed through drainage networks and river corridors serve as year-round transmission foci.
70 hat a large fraction of the carbon export to rivers could have been mineralized in inland waters.
72 (RCP4.5) will result in ~80% of the dryland rivers crossing a threshold from one type to another, ma
79 ey manufacturing hubs, including the Yangtze River Delta, Pearl River Delta, and North China Plain.
80 sin and the Barcelona coast, and in the Ebro River Delta, using single particle inductively coupled p
82 et, we show that 339 million people lived on river deltas in 2017 and 89% of those people live in the
84 hat will disproportionately impact people on river deltas, particularly in developing and least-devel
85 orm packages which together demonstrate that river deposition was already well established >3.7 Ga.
87 , was used to train two ML models to predict river depth over the domain for an arbitrary discharge.
88 hemicals which were relatively stable in the rivers, DGT and grab sampling were in good agreement.
89 tors (BCFs) are used together with the daily river dilution patterns to predict internal concentratio
92 anges such as climate warming and increasing river discharge might increase CH(4) emissions and hence
93 en concentration, an indication of increased river discharge, explained the second-most variation in
94 relationship between seasonality, ENSO, and river discharge, with significantly higher values occurr
96 flows of a freshwater apex predator, Ganges River dolphin (GRD, Platanista gangetica gangetica), whi
97 the ecology of a small cetacean, the Ganges River dolphin (Platanista gangetica gangetica, GRD), in
98 nce of natural organic matter (NOM; Suwannee River DOM) and 15 LMM thiols, an internally consistent t
100 ants mainly showed encamped movements at the river during the dry season, when temporary water source
102 matic cases will see currently through-going rivers (e.g. Murrumbidgee, Macintyre) experience step ch
103 le combination of selected habitat features (river, elephant corridor, agricultural field, trees), an
109 ent caused the dramatic decline of the Pearl River estuary coral communities reported from 1980 to 20
110 Yangshan Deep-Water Harbour near the Yangtze River estuary in China and identified more than 4,500 di
111 ncentration, consistent with the rapid Pearl River estuary urbanization as the main cause for this eu
121 fossils found in marginal-marine, storm- and river-flood deposits from the Middle Devonian Naranco Fo
122 an in oligotrophic blackwater and clearwater river-floodplain systems and light-limited whitewater ri
124 linked increasing forest cover with reduced river flow and potentially detrimental effects downstrea
125 uld take into account that changes to annual river flow are likely to persist for up to five decades.
126 iver engineering problems typically requires river flow characterization, including the prediction of
132 Previous reviews have investigated trends in river flow response over time, but the influence of fore
134 ton (PEUK) during spring and after spikes in river flow were also detected, making PEUK periodically
138 Moreover, modeling two- or three-dimensional river flows with high-resolution topographic data for la
139 ean flow conditions in the lower Monongahela River for the WYs of interest, the median-estimated wet
141 ges, (b) investigated the combined impact of river fragmentation and climate change and (c) tested th
145 tion annually and contributes ~17% of global river freshwater input to the oceans; its hydroclimatic
146 investigate the impact of Cl(-) and Suwannee River fulvic acid (SRFA) on Cu(II) reduction and Cu(I) o
147 he Carpathian Mountains and along the Danube River, further confirming these regions as hot spots for
148 ial) would allow similar analyses of dryland rivers globally where hydroclimate is an important drive
149 imate change could affect larval survival in rivers, growth and maturation in lakes, phenology and th
150 Our results indicate that management of river habitats for dragonfly conservation should incorpo
151 ut can rival monsoon-fed discharges in major rivers hundreds to thousands of kilometers downstream.
152 roups were considered simultaneously, run-of-river hydro had moderate overlap (0.56), while shale gas
153 eneration from renewable (wind farms, run-of-river hydro) and non-renewable (shale gas) sources in Br
155 0-2100: compared with 2009-2029, the average river ice duration declines by 16.7 days under Represent
156 rical change and predicted future changes in river ice extent and duration have not yet been quantifi
159 ervations, we show that the global extent of river ice is declining, and we project a mean decrease i
162 e Hells Canyon Complex (HCC) along the Snake River (Idaho-Oregon border, U.S.A.) encompasses three su
163 music festival held adjacent to the Traisen River in Austria increased the river's dissolved organic
166 c sediment from 34 stations along the Thames River in Ontario, Canada, to determine the influence of
167 om the Oyogos Yar coast near the Kondratievo River in the Laptev Sea region, Sakha (Yakutia) Republic
170 vated nitrogen concentrations in streams and rivers in the Chesapeake Bay watershed have adversely af
171 Using data obtained from 78 sites across six rivers in the mainland Japan and the Amami-Oshima Island
173 ded Sediment Concentration (SSC) in channels/rivers include costs and technological gaps but this pap
174 00, simulated Hg concentrations in the Yukon River increase by 14% for the low emissions scenario, bu
175 ng 2,715 kilometres of stream length for 147 rivers indicate that existing records underestimate barr
176 e.g., decreased fluvially transported upland river inputs, and increased tidally induced marine algae
179 he estimated total mass of Hg transported by rivers is substantially less than the estimated tons of
181 predict mean monthly temperature for 465,775 river km in the western U.S., and then applied simple ye
182 Laboratory, Taconic Biosciences, and Charles River Laboratories; and (3) mice subjected to intestinal
186 Titan has a methane cycle with clouds, rain, rivers, lakes, and seas; it is the only world known to p
187 linked hb locus of a jawless vertebrate, the river lamprey (Lampetra fluviatilis), shares a range of
188 Selection at ar in the effluent-dominated River Lee may have resulted from historical contaminatio
191 on nutrient stress, while highlighting that river management requires more bespoke management soluti
193 h simulations are required for comprehensive river modeling, where a system of connected rivers is to
194 rmine the influence of land use, grain size, river morphology, and relative amount of organic debris
196 negatively correlated with distance from the river mouth and cumulative height of trans-river structu
201 of past reported values (e.g., for Suwannee River Natural Organic Matter IHSS isolate: 1.8% vs 0.23-
204 olved organic carbon (DOC) from soils to the river network is an overlooked component of the terrestr
205 global increase in terrestrial DOC inputs to river network of 35 Tg C year(-1) (14%) from 1860 to 201
207 ingly erratic depinning events along smectic river networks correlated over system spanning scales.
212 lacier (Hunza region), dammed the proglacial river of Muchuhar Glacier, which formed an ice-dammed la
213 tified flow-ecology responses in the Karnali River of Nepal during the low-flow season when habitat w
216 iched bacteria from sediments of the Passaic River on two organohalides, trichloroethene (TCE) and 1,
217 ented the importance of tropical mountainous rivers on global silicate weathering and suspended sedim
218 is influenced by Mississippi and Atchafalaya River outflow, remained fairly stable over this time per
219 allenges of monitoring biological threats to rivers over long time periods and across large geographi
221 ations of OPEs in samples from the Mackenzie River plume suggest riverine discharge as an OPE source
223 3.4 +/- 0.2 x 10(-5) mg.mL(-1).min(-1)) and river red gum honeys (E. camaldulensis; 3.2 +/- 0.2 x 10
226 x and composition of carbon (C) from land to rivers represents a critical component of the global C c
227 ensity are agricultural pressure, density of river-road crossings, extent of surface water and elevat
228 scopy structures of Fab in complex with Ross River (RRV), Mayaro, or chikungunya viruses reveal a con
229 /16, indicating drought conditions with less river runoff, rainfall and higher ocean salinities.
230 o the Traisen River in Austria increased the river's dissolved organic carbon (DOC) concentration fro
232 , with ARGs unique to WWTP and WWTP-impacted river samples predominantly belonging to the aminoglycos
238 NOM-amended soil collected from the Savannah River Site (SRS) or unamended vadose zone soil and expos
239 egacy defense nuclear tank waste at Savannah River Site is highly desirable for the purpose of nuclea
241 (GLM) and the associated Saint John/Wolastoq River (SJWR), we studied the spatial (i.e., across the m
243 to 2050, which highlights the importance of river-specific strategies for waterway exploitation worl
245 the contiguous region of Bayelsa, Delta, and Rivers states, or another more restricted, yet unidentif
246 pulations of roach (Rutilus rutilus) inhabit river stretches polluted with estrogenic WwTW effluents.
247 e river mouth and cumulative height of trans-river structures from the river mouth to each site.
248 Expanding our approach to include other river styles (e.g. mixed bedrock-alluvial) would allow s
251 ions into groundwater reaching the Athabasca River system adjacent to the reclaimed pond at Tar Islan
252 uring the rapid expansion of agriculture and river system modification associated with European colon
254 ne boundary, probably via a continuous paleo-river system or along the Tethys coastal line, which are
260 nd monitor ECs at the catchment scale in the River Thames system (U.K.) and explored their sources an
262 ter in major (sub)tropical and high-latitude rivers than in major temperate rivers, with further sign
265 Aral Sea basin in Central Asia and its major rivers, the Amu Darya and Syr Darya, were the center of
267 program that focused on the six major Arctic rivers to establish a contemporary (2012-2017) benchmark
268 ole of land cover change and soil erosion on river transport of Hg in a heavily ASGM-impacted watersh
269 o Basin, an expansive network of streams and rivers transport and cycle terrigenous C sourced from th
270 aration of five specific dominantly alluvial river types and quantification of their present-day catc
271 -replacement, at 11 sites along the Colorado River upstream and downstream of the WWTP and analyzed f
273 icrobial prevalence less well in adults from river villages with more regular access to markets.
274 these declines, we studied mussels in Clinch River, Virginia and Tennessee, USA, where the endemic an
276 east by 500 thousand years ago (ka) the Solo River was diverted into the Kendeng Hills, and that it f
277 6) to 45.1 x 10(6) Ag-NPs/L) in the analyzed rivers was limited to certain hotspots close to wastewat
278 -2) with 2.0 M NaCl as the draw solution and river water (0.017 M) as the feed water at an applied hy
281 f 107 +/- 10% and 96 +/- 8% were obtained in river water for 3 and 5 muM of atrazine, respectively.
282 almost the same sensitivity in the simulated river water samples as in phosphate buffer, reflecting i
283 soil in an infiltration pond recharged with river water using a set of in situ sensors measuring eve
284 ses of collected water samples (groundwater, river water, and seawater) demonstrated the applicabilit
291 ere, we studied DOM dynamics in the Altamaha River watershed in Georgia, USA, a fluvial system where
293 ibited exploratory movements to and from the river, while females showed an increase in the frequency
294 g downstream through a mesh enclosure in the river with and without predator cues present to measure
296 e to changes in the dilution capacity of the river with elevated concentrations under lower flows in
297 e first time the geomorphology of 29 dryland rivers with catchments across a humid to arid gradient c
298 omparing the eroded organic carbon export to rivers with the particulate organic carbon export to oce
299 high-latitude rivers than in major temperate rivers, with further significant differences between bio