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1 rease the occurrence and magnitude of pulsed biogeochemical activity, affecting carbon (C) and nitrog
2 mixing zones (hyporheic zones) have enhanced biogeochemical activity, but assembly processes governin
3                         Here we use detailed biogeochemical analyses to track past penguin colony cha
4 activities for which sufficient knowledge on biogeochemical and biophysical effects exists but robust
5 dance of deciduous hardwoods, with potential biogeochemical and biophysical feedbacks to regional and
6  common land management activities for their biogeochemical and biophysical impacts, the level of pro
7                              As life spread, biogeochemical and climate changes cyclically increased
8 ydrological regimes, sediment transport, and biogeochemical and contaminant fluxes from rivers to oce
9 ansitional habitats characterized by complex biogeochemical and ecological gradients that result in s
10 standing of supraglacial DOM cycling and the biogeochemical and ecological impacts of DOM export to d
11 y, the study also illustrates how integrated biogeochemical and economic assessments of multidimensio
12  does not imply the absence of hydrological, biogeochemical, and biological exchanges with nearby and
13 ity-level metabolic reconstruction, and soil biogeochemical assessment to understand the principles g
14 lages from layers beneath the chemocline had biogeochemical associations that differed from those in
15  partially explained the variability in many biogeochemical attributes such as C:N ratio and %TOC.
16                       We found that the soil biogeochemical background corresponding to P inherited f
17 we experimentally characterize the principal biogeochemical barrier to SCN(-) biodegradation for an a
18 sions from streams are important to regional biogeochemical budgets.
19 ay help to explain discrepancies in deep-sea biogeochemical budgets.
20 s precluded a unified view of Southern Ocean biogeochemical change.
21                              We investigated biogeochemical changes along a chronosequence of hydrolo
22 vironmental impacts of this process, yet the biogeochemical changes induced in the deep subsurface ar
23 ween catchments and lakes but at the cost of biogeochemical changes that release stored contaminants.
24  present in each lake, reflecting the unique biogeochemical characteristics of these environments.
25     Iron oxides are important structural and biogeochemical components of soils that can be strongly
26 ults from this 3-year study demonstrate that biogeochemical conditions present during reductive treat
27 0)Sr behavior and stability under a range of biogeochemical conditions stimulated by electron donor a
28                    Although hydrological and biogeochemical connectivity is often episodic or slow (e
29   A key factor in determining ecological and biogeochemical consequences of turbulent stirring is the
30 has significant ecological, biophysical, and biogeochemical consequences.
31 ass and they have significant ecological and biogeochemical consequences.
32                         Due to their complex biogeochemical controls and high spatial and temporal va
33 ) mining and processing, we investigated the biogeochemical controls of U bioavailability in the mode
34 The complex interactions of hydrodynamic and biogeochemical controls on emissions of this important g
35                     To better understand the biogeochemical controls on PBDEs, 12 PBDE congeners were
36 jor iron source and emphasizing iron's tight biogeochemical coupling to major nutrients, a more compl
37                                  The complex biogeochemical cycle of Hg makes identifying primary sou
38 seawater analysis will shed new light on the biogeochemical cycle of marine arsenic.
39            Human activities have altered the biogeochemical cycle of mercury (Hg) since precolonial t
40 nium (Se) emissions play a major role in the biogeochemical cycle of this essential micronutrient.
41 provide a quantitative summary of the global biogeochemical cycle of vanadium (V), including both hum
42                                   The sulfur biogeochemical cycle plays a key role in regulating Eart
43 hylation is an important component of the As biogeochemical cycle that can influence As toxicity and
44  is a central process in the organoarsenical biogeochemical cycle.
45 ment effectively removing Hg from the active biogeochemical cycle; this results in a 27% lower presen
46 isms that play a major role in food webs and biogeochemical cycles (1) .
47 stand the impact of microbial communities on biogeochemical cycles and (2) reframe current theory and
48 yanobacteria are an integral part of Earth's biogeochemical cycles and a promising resource for the s
49 and minerals plays a critical role in global biogeochemical cycles and climate evolution.
50 information on function of marine food webs, biogeochemical cycles and copepod health.
51 he rise of pelagic calcifiers - have changed biogeochemical cycles and ecosystem dynamics.
52 tary Cu isotope compositions in the study of biogeochemical cycles and oceanic redox balance in the p
53 ir of genetic diversity with great impact on biogeochemical cycles and organismal health.
54  this framework for the evolution of Earth's biogeochemical cycles and the rise of atmospheric oxygen
55 treams harbor diverse microorganisms driving biogeochemical cycles and, consequently, influencing eco
56 icroorganisms that drive the pelagic ocean's biogeochemical cycles are currently facing an unpreceden
57                  Carbon (C) and silicon (Si) biogeochemical cycles are important factors in the regul
58  in the Mediterranean abyssal ecosystems and biogeochemical cycles are to be expected.
59 er in sediments is an important component of biogeochemical cycles because marine sediments are criti
60 ox evolution is informed by our knowledge of biogeochemical cycles catalysed by extant biota.
61 otentially important implications for global biogeochemical cycles especially in view of the recent a
62 s the potential to foundationally impact all biogeochemical cycles in the environment.
63 mitation, with broad implications for global biogeochemical cycles in the future ocean.
64 nformation on potential microbially mediated biogeochemical cycles in tundra ecosystems.
65 pproaches to quantifying and predicting soil biogeochemical cycles mostly consider microbial biomass
66 f hydroxyaluminosilicates is integral to the biogeochemical cycles of aluminium and silicon.
67 o characterize the stoichiometry between the biogeochemical cycles of C and Si.
68  have shown that global changes decouple the biogeochemical cycles of carbon (C), nitrogen (N), and p
69 l and longstanding role it has played in the biogeochemical cycles of Earth over billions of years.
70 d have large effects on the trophic webs and biogeochemical cycles of estuaries and coastal areas by
71 een invoked as a key mechanism governing the biogeochemical cycles of forest ecosystems.
72 understanding of the interaction between the biogeochemical cycles of iron and methane.
73 ways and thus provides new insights into the biogeochemical cycles of nitrogen and other elements in
74 gs highlight crucial links between Tc and Fe biogeochemical cycles that have significant implications
75                  Microbial communities drive biogeochemical cycles through networks of metabolite exc
76 l implications of these top-down changes for biogeochemical cycles via consumer-mediated nutrient dyn
77  the USA, impacts to drinking water quality, biogeochemical cycles, and aquatic ecosystems are estima
78 roles in the regulation of marine food webs, biogeochemical cycles, and Earth's climate.
79 lobal climate resonate in plankton dynamics, biogeochemical cycles, and marine food webs.
80 t directly probes governing processes in CO2 biogeochemical cycles, Delta(17)O (=ln(1 + delta(17)O) -
81            Archaea are major contributors to biogeochemical cycles, possess unique metabolic capabili
82 re frequent floodplain fires, and changes to biogeochemical cycles, transport of organic and inorgani
83 are complex but are important for downstream biogeochemical cycles.
84 ials that contribute significantly to global biogeochemical cycles.
85 ate organic matter degradation and influence biogeochemical cycles.
86 e the degree to which microbes regulate soil biogeochemical cycles.
87 tical to evaluating their influences on soil biogeochemical cycles.
88 n drivers of the sulfur, nitrogen and carbon biogeochemical cycles.
89 hat drive transformations central to Earth's biogeochemical cycles.
90 t fuel marine food webs and influence global biogeochemical cycles.
91 y contributes to long-term changes in global biogeochemical cycles.
92  to the impacts on air quality, climate, and biogeochemical cycles.
93 inked to the coevolution of life and Earth's biogeochemical cycles.
94 a major role in both terrestrial and oceanic biogeochemical cycles.
95 o the role of freshwaters in global C and Si biogeochemical cycles.
96 mentally stable and can participate in local biogeochemical cycles.
97 rine food webs and the functioning of global biogeochemical cycles.
98  processes, such as primary productivity and biogeochemical cycles.
99 ely to play a different role in ocean global biogeochemical cycles.
100 hich may have broad effects on food webs and biogeochemical cycles.
101 ke ecosystems and play central roles in lake biogeochemical cycles.
102 ole(s) of pyrogenic organic matter (PyOM) in biogeochemical cycles.
103 DOS removal and active involvement in marine biogeochemical cycles.
104 role in climate regulation and global sulfur biogeochemical cycles.
105 ected for, altering linkages among the major biogeochemical cycles.
106 plankton assemblages and its role in aquatic biogeochemical cycles.
107 king it an integral component of the ocean's biogeochemical cycles.
108 t interactions and physiology as controls on biogeochemical cycles.
109 mal vent microbial communities in deep ocean biogeochemical cycles.
110 of sediment bioturbation - a key mediator of biogeochemical cycling - to determine whether post-extin
111 lobal ocean volume, plays important roles in biogeochemical cycling [2], and holds potentially huge f
112  speciation and carbon isotope data suggests biogeochemical cycling across a dynamic redox boundary,
113 s of host diversity, population dynamics and biogeochemical cycling and contribute to the daily flux
114 ury, our findings document the potential for biogeochemical cycling and multi-trophic interactions al
115  globally and advancing our understanding of biogeochemical cycling and other ecosystem processes.
116 fungi, which are critical for plant fitness, biogeochemical cycling and other processes.
117 r each, we discuss the role of microbiota in biogeochemical cycling and outline ecological and hydrol
118 bility, were clear drivers of differences in biogeochemical cycling and resulted in substantially dif
119 ty drives changes in microbial diversity and biogeochemical cycling between the aerobic surface layer
120 vel Nitrospirae bacteria might contribute to biogeochemical cycling in natural habitats.
121 nked roles of the most abundant organisms in biogeochemical cycling in the aquifer sediment.
122 ystem dynamics, ecological interactions, and biogeochemical cycling of both cellular and acellular co
123 ctions propel the engine that results in the biogeochemical cycling of individual elements, and they
124 ine to more crystalline forms, affecting the biogeochemical cycling of iron and the behavior of any s
125  detailing of the historical controls on the biogeochemical cycling of silicic acid [Si(OH)4] on the
126 of these clades appear to participate in the biogeochemical cycling of sulfur and nitrogen, filling p
127 sms provides important information about the biogeochemical cycling of the element and transfer throu
128 tant roles in the environment, especially in biogeochemical cycling of toxic elements in aquatic syst
129                         Ocean microbes drive biogeochemical cycling on a global scale.
130 es may play previously unrecognized roles in biogeochemical cycling through mechanisms that include e
131 scale is essential to better understand it's biogeochemical cycling to improve Se transfer into diets
132 e, we use models for erosion, weathering and biogeochemical cycling to show that this can be explaine
133 They also make major contributions to global biogeochemical cycling, and ameliorate atmospheric accum
134 like conductivity of the pili, their role in biogeochemical cycling, and applications in bioenergy an
135 ciation in relation to Fe and C dynamics and biogeochemical cycling, and the mechanisms responsible f
136 ing pressures on phytoplankton and hence for biogeochemical cycling, higher trophic levels and biodiv
137 ms play key roles in ecosystem processes and biogeochemical cycling, however, the relationship betwee
138 ence ecosystems, sea ice, species diversity, biogeochemical cycling, seafloor methane stability, deep
139 of organisms includes an additional class of biogeochemical cycling, this being the flow and transfor
140 bining these effects in a model of long-term biogeochemical cycling, we reproduce a sustained +2 per
141 o the microbial loop, aquatic food webs, and biogeochemical cycling.
142 ated by the effect of microbial processes on biogeochemical cycling.
143 eby highlighting the complexities of arsenic biogeochemical cycling.
144 OTUs to hypotheses about processes governing biogeochemical cycling.
145 r might affect sediment-water dSi fluxes and biogeochemical cycling.
146 remediation products and understanding of Se biogeochemical cycling.
147 ons for contaminant remediation and nutrient biogeochemical cycling.
148 ophytes) contributes significantly to global biogeochemical cycling.
149 local oxygenic photosynthesis on Pacific AMZ biogeochemical cycling.
150 lves and are critical contributors to marine biogeochemical cycling.
151 oubtedly impact the understanding of mercury biogeochemical cycling; however, there is a lack of cons
152 ltaneously consider interacting climatic and biogeochemical drivers when assessing forest responses t
153 ms, yet our understanding of these microbial-biogeochemical-ecological interactions is limited by a l
154                                  We used the biogeochemical ecosystem model N14CP, which considers in
155 evidence for a long-held hypothesis that the biogeochemical effect of urban aerosol or haze pollution
156  spur the development of a new generation of biogeochemical electron flux models that focus on the ba
157 rbation is localized due to distinct physico-biogeochemical environments and relatively long time sca
158 rating dinoflagellate molecular, fossil, and biogeochemical evidence, we propose a revised model for
159 ion zones, we find elevated biomass within a biogeochemical facies that occurred at the transition be
160 pling the spatial distribution of subsurface biogeochemical facies with biomass-facies relationships
161                  Here, we characterize three biogeochemical facies-oxidized, reduced, and transition-
162 buted carbonate microbialites and associated biogeochemical facies.
163  the transition between oxidized and reduced biogeochemical facies.
164 umulated U(IV) speciation, and to define the biogeochemical factors controlling its reactivity.
165     Reactions mediated by PCM can impact the biogeochemical fate of pollutants and lead to useful str
166 ach in 2011, however, incorporating sediment biogeochemical feedbacks is required to reproduce the ob
167 t, ecosystem functioning and climate through biogeochemical feedbacks, but their response to contempo
168                                        These biogeochemical findings suggest that the relatively grea
169 -driven glacial/interglacial oscillations in biogeochemical fluxes at and near the ocean margins, wit
170 STEs) are of major importance for land-ocean biogeochemical fluxes.
171                                    While the biogeochemical forces influencing the weathering of spil
172 trogen pool is crucial for understanding its biogeochemical function and reactivity in the environmen
173 key, but understudied, component of riverine biogeochemical function.
174 ing by matching taxa to known taxon-specific biogeochemical functions.
175 odel, suggesting that these groups performed biogeochemical functions.
176 aces (SWIs) are often characterized by steep biogeochemical gradients determining the fate of inorgan
177 ific organisms, drove community assembly and biogeochemical gradients in the model ocean.
178 terial adaptations to the extreme and unique biogeochemical gradients of ice-covered lakes in the McM
179 , up-to-date and comprehensive collection of biogeochemical groundwater monitoring data.
180 ations to microbial metabolism, resulting in biogeochemical hotspots and moments.
181     Consistent with previous observations of biogeochemical hotspots at environmental transition zone
182 bacteria, fungi, and detrital matter) act as biogeochemical hotspots by controlling important fluxes
183  and rivers or lakes have been identified as biogeochemical hotspots with steep redox gradients.
184 underlying mechanisms that make PPR wetlands biogeochemical hotspots, which ultimately leads to their
185 ll critical gaps in our understanding of the biogeochemical impact of viruses in the ocean.
186 s in marine ecosystems, but their integrated biogeochemical impacts remain unclear.
187 s into the m5C methylation landscape and its biogeochemical implications in an important marine N2 -f
188 ing (BONCAT) - for studying the activity and biogeochemical influence of marine viruses.
189 inimicrobia metabolism is sparse, making the biogeochemical influence of this group challenging to pr
190 il to account for the complex ecological and biogeochemical interactions that govern reefs.
191  acetate and soluble Mn(3+) represents a new biogeochemical link between carbon and manganese cycles.
192                                Understanding biogeochemical mechanisms affecting decomposition in pea
193 ng conditions in natural waters by combining biogeochemical microcosm experiments and X-ray absorptio
194 ated soil exposed to sea and river waters in biogeochemical microcosm reactors across field-validated
195                  We developed a mercury (Hg) biogeochemical model for the Baltic Sea and used it to i
196 lace our phosphorus record in a quantitative biogeochemical model framework and find that a combinati
197                    By integrating a detailed biogeochemical model that projects future ecological rec
198                  In this study, we applied a biogeochemical model that simulates dissolved oxygen con
199 dividual-based model coupled to an ice-ocean-biogeochemical model was utilized to simulate temperatur
200 omic and metaproteomic sequence data, into a biogeochemical model, as shown here, enables holistic in
201 utions of metabolic processes predicted by a biogeochemical model, suggesting that these groups perfo
202                        Using a process-based biogeochemical model, we predicted that low levels of Nd
203                                              Biogeochemical modeling shows a 3.2-fold increase in the
204 major lineages currently underrepresented in biogeochemical models and identifies radiations that are
205 ncorporating historical climate effects into biogeochemical models simulating future global change sc
206                                              Biogeochemical models that incorporate nitrogen (N) limi
207                                     However, biogeochemical models that simulate simultaneous competi
208 full calibration (stage 5), 24 process-based biogeochemical models were assessed individually or as a
209 ect that merging such an approach with hydro-biogeochemical models will provide important constraints
210 urrent paradigm, widely incorporated in soil biogeochemical models, is that microbial methanogenesis
211  the application of a series of quantitative biogeochemical models, we find that large spatiotemporal
212 s in drylands are higher than predictions by biogeochemical models, which are traditionally based on
213               Phytoplankton (eutrophication, biogeochemical) models are important tools for ecosystem
214 teractions between microbial communities and biogeochemical oxidation-reduction reactions.
215 e (here, > 35 degrees ) forests is a central biogeochemical paradox.
216 S SSU rRNA genes, average 10,000 reads), and biogeochemical parameters are monitored by quantifying 5
217               Guidelines based on measurable biogeochemical parameters have been proposed, but contem
218                   Microorganisms control key biogeochemical pathways, thus changes in microbial diver
219 phosphorus in their rhizosphere via multiple biogeochemical pathways.
220                               Differences in biogeochemical potential between two production well com
221 coupling between underlying hydrological and biogeochemical process dynamics.
222                The model reproduces measured biogeochemical process rates as well as DNA, mRNA, and p
223 however, that the groups associated with one biogeochemical process, sulfate reduction, contained onl
224  The mixed-layer pump is a physically-driven biogeochemical process7-11 that could further contribute
225 hermally altered DOM (TA-DOM) are altered by biogeochemical processes (e.g., transformed by growing a
226 itat in modulating the relationships between biogeochemical processes and Hg bioaccumulation.
227 drive fundamental submicron- to global-scale biogeochemical processes and influence carbon-climate fe
228 t remains uncertain, however, to what extent biogeochemical processes can suppress global GPP growth.
229 the negative impacts of aridity on important biogeochemical processes controlling carbon (C), nitroge
230 better understand the relationship of tau to biogeochemical processes in a dynamic estuarine system,
231 igation of a large panel of hydrological and biogeochemical processes in aquatic systems.
232 ention ponds) has the potential to influence biogeochemical processes in downstream water bodies beca
233 ng the complex linkages among time-dependent biogeochemical processes in hydrodynamically complex env
234 e occurrence and timing of physiological and biogeochemical processes in natural populations.
235 oves our ability to represent ecological and biogeochemical processes in oligotrophic oceans.
236 ool in order to improve our understanding of biogeochemical processes in soil-plant systems.
237 nutrients to alpine watersheds and influence biogeochemical processes in these remote settings.
238 ionation patterns provide information on the biogeochemical processes in these systems.
239 nt and play an important role in a number of biogeochemical processes including microbial activity, s
240 nction, but linking community composition to biogeochemical processes is challenging because of high
241 interactions, is related to variation in key biogeochemical processes like soil carbon formation.
242 olubility of jarosite at near-neutral pH and biogeochemical processes occurring downstream could affe
243 activities and climate change can affect the biogeochemical processes of natural wetland methanogenes
244 t loads are consistent with hydrological and biogeochemical processes such as denitrification.
245          Understanding linked hydrologic and biogeochemical processes such as nitrate loading to agri
246 ed effects of cumulative nutrient inputs and biogeochemical processes that occur in freshwater under
247 table isotopes to examine the ecological and biogeochemical processes underlying THg bioaccumulation
248  changes in winter range occupancy may shape biogeochemical processes via shifts in microbial communi
249 our entire planet and have a crucial role in biogeochemical processes, agriculture, biotechnology, an
250            Despite being key contributors to biogeochemical processes, archaea are frequently outnumb
251 perature, an important driver of terrestrial biogeochemical processes, depends strongly on soil albed
252 the hydrologic regime are expected to impact biogeochemical processes, including contaminant mobility
253 sent an integrated signal from anthropogenic/biogeochemical processes, including fossil fuel burning,
254  that affect plant growth and influence many biogeochemical processes, the impact of future changes i
255 ties are the key drivers of many terrestrial biogeochemical processes.
256 tand can provide integrative proxies for key biogeochemical processes.
257 s importance in pollutant redox dynamics and biogeochemical processes.
258 ultiscale modeling of hyporheic exchange and biogeochemical processes.
259 operate in microbial communities to regulate biogeochemical processes.
260 rming may ultimately lead to changes in soil biogeochemical processes.
261 xample of how biological diel rhythms affect biogeochemical processes.
262 atchment hydrology or habitats, and internal biogeochemical processes.
263 differences that could differentially impact biogeochemical processes.
264 wetland sediments that affect ecological and biogeochemical processes.
265  impacts on litter decomposition and further biogeochemical processes.
266 s between microbial iron reduction and other biogeochemical processes.
267 sions have been reported to influence global biogeochemical processes; however, in the literature the
268 chnique for the investigation of very subtle biogeochemical processing of bulk DOM.
269 pportunities for elucidating the origins and biogeochemical properties of FDOM.
270 dertaken in conjunction with analysis of key biogeochemical properties of two mats (smooth and pustul
271 ain size distribution is a good predictor of biogeochemical properties, and that subsets of the overa
272 ng and water sources, explicitly calculating biogeochemical rates, and exploring the complex linkages
273  correlated with interstation variability in biogeochemical rates; however, bioturbation potential ex
274 methane emissions to the atmosphere, but the biogeochemical reactions driving such fluxes are less we
275   Microorganisms catalyze carbon cycling and biogeochemical reactions in the deep subsurface and thus
276  groups and have a 1.5 V potential range for biogeochemical reactions that invoke electron transfer p
277 of many contaminants through a wide range of biogeochemical reactions.
278 l variably saturated flow and multicomponent biogeochemical reactive transport modeling, based on pub
279 uable tool for the field characterization of biogeochemical reactivity, aquifer transport properties,
280 indicated the urban aquifer also serves as a biogeochemical reactor.
281 uctive Cr(VI) immobilization under different biogeochemical regimes were tested for their susceptibil
282                        We also show that the biogeochemical response of the aquifer system has not mo
283 tion to address the nature and timing of the biogeochemical response to oxygenation directly.
284  autotrophically with iron, indicating a new biogeochemical role for this ubiquitous microorganism.
285 studied extensively due to their significant biogeochemical roles in the marine ecosystem.
286                            To understand the biogeochemical roles of microorganisms in the environmen
287                                  Despite the biogeochemical significance of the interactions between
288 ct interspecies electron transfer (DIET) has biogeochemical significance, and practical applications
289 nterpretation of paleo-proxy data as well as biogeochemical simulations, we show that a sea level fal
290                             In balance, most biogeochemical studies that aim at molecularly fingerpri
291 tocks and turnover times we developed a soil biogeochemical testbed that forces three different soil
292 tanding, evaluation, and improvement of soil biogeochemical theory and models at regional to global s
293 rk elucidates spatio-temporal aspects of the biogeochemical transformation of copper mobilized from m
294 (California, USA) to identify Hg sources and biogeochemical transformations downstream of a historica
295 y, the role of the genus in soil ecology and biogeochemical transformations is of agricultural and en
296 re to establish the sequence of physical and biogeochemical transitions and lags during the vernal wi
297      Peatlands frequently serve as efficient biogeochemical traps for U.
298 udies, wherever an improved understanding of biogeochemical turnover processes is necessary.
299 versity in relation to spatial, temporal and biogeochemical variation, within and across lakes locate
300 the SBB we hypothesize a dynamic and annular biogeochemical zonation by which the bacteria capitalize

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