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1 Methane (CH(4)) is a potent greenhouse gas.
2 atmosphere is a major source of this potent greenhouse gas.
3 s to produce nitrous oxide (N(2)O), a potent greenhouse gas.
4 y component of natural gas (NG), is a potent greenhouse gas.
5 emissions of nitrous oxide (N(2)O), a potent greenhouse gas.
6 to mitigating emissions of methane, a potent greenhouse gas.
7 trification, nitrous oxide, is a significant greenhouse gas.
8 Microbial activity mediates the fluxes of greenhouse gases.
9 Light-duty vehicles emit ~20% of net US greenhouse gases.
10 ditions, increasing emissions of aerosol and greenhouse gases.
11 able syngas and simultaneously mitigate both greenhouse gases.
12 missions and, often, accompanying removal of greenhouse gases.
13 eduction of soil fertility and production of greenhouse gases.
14 olume and high concentrations of atmospheric greenhouse gases.
15 ed organic matter (DOM) in surface waters to greenhouse gases.
16 arms in response to rising concentrations of greenhouse gases.
19 onse to increased anthropogenic emissions of greenhouse gases(11), and is projected to warm further.
22 be measured by monitoring changing fluxes of greenhouse gases, adaptation is more complicated to meas
24 obically treated effluent, which is a potent greenhouse gas and is easily stripped out in the aeratio
29 acial-interglacial variations in atmospheric greenhouse gases and Antarctic climate were reduced in t
30 ion of the emission trading system (ETS) for greenhouse gases and Euro-4 standards for new vehicles e
31 2009 Endangerment Finding for six well-mixed greenhouse gases and find that this new evidence lends i
34 source of nitrous oxide (N(2) O), a powerful greenhouse gas, and increasing SOC may influence N(2) O
36 steel sector emits 25% of global industrial greenhouse gases, and the U.S. is the world's second-lar
37 ouse gases in the atmosphere increase; (iii) greenhouse gases are a worldwide public bad with emissio
38 algae in BC cycling, and the degree to which greenhouse gases are released following disturbance of B
41 t of their impacts on nitrogen leaching, net greenhouse gas balances (NGHGB) and crop productivity.
45 nge (including production and consumption of greenhouse gases) but also how they will be affected by
47 l fuels produces emissions of the long-lived greenhouse gas carbon dioxide and of short-lived polluta
48 o produce valuable fuels and chemicals using greenhouse gas carbon dioxide as the carbon feedstock.
51 ectrosynthesis is presented to transform the greenhouse gas CO(2) into an unusually thin walled, smal
52 f renewable fuels from abundant water or the greenhouse gas CO(2) is a major step toward creating sus
55 region by 2080-2099 for low, medium and high greenhouse gas concentration trajectories (Representativ
56 responding to low (RCP2.6) and high (RCP8.5) greenhouse gas concentration trajectories(6), predict ma
58 esponse to astronomical forcing depending on greenhouse gas concentrations and polar ice sheet volume
60 g increases in chemodiversity could increase greenhouse gas concentrations in lake sediments by an av
61 skewed towards lower values (under very high greenhouse gas concentrations, the most likely value is
63 ineering assume that warming owing to rising greenhouse-gas concentrations can be compensated by arti
64 Despite the observed monotonic increase in greenhouse-gas concentrations, global mean temperature d
65 arth exerts a fundamental influence upon the greenhouse gas content of the atmosphere, and hence glob
67 evaluate impacts of solar geoengineering and greenhouse gas-driven climate change on equal terms, we
73 is is a promising method because of its zero greenhouse gas emission and its compatibility with all t
74 tion, soil physical-chemical parameters, and greenhouse gas emission are measured and the economic an
75 t low-grade heat recovery can help to reduce greenhouse gas emission as over 70% of primary energy in
82 rently exceeds forest gain, leading to a net greenhouse gas emission that exacerbates global climate
83 is a key technological approach to reducing greenhouse gas emission while we transition to carbon-fr
84 h system models considering their effects on greenhouse gas emission, biogeochemical processes, and b
88 d the energy return on investment (EROI) and greenhouse gas emissions (GHGs) by 20% and 16%, respecti
90 fficient, and effective solutions to cut net greenhouse gas emissions and adapt to climate change.
91 ain global warming, we must strongly curtail greenhouse gas emissions and capture excess atmospheric
92 s, world economies are seeking to reduce the greenhouse gas emissions and local air pollution from tr
95 important seasonal process and shows spring greenhouse gas emissions are largely due to production f
96 y below 1.5 degrees C, drastic reductions of greenhouse gas emissions are mandatory but not sufficien
98 onalized urban food systems by examining the greenhouse gas emissions associated with food transport.
100 analysis determined the potential to reduce greenhouse gas emissions by 50 to 271% relative to petro
101 o adoption would further limit water use and greenhouse gas emissions by preventing sugarcane expansi
103 ve no means to reconstruct the pacing of LIP greenhouse gas emissions for comparison with climate rec
106 , PRELIM provided results for energy use and greenhouse gas emissions from petroleum refineries with
107 e could mitigate environmental pollution and greenhouse gas emissions from the agricultural sector.
108 -based regulatory program designed to reduce greenhouse gas emissions from the electric power sector
110 d in the climate system due to anthropogenic greenhouse gas emissions has been taken up by the oceans
111 elihood of current Chinese policies reducing greenhouse gas emissions in accordance with China's Pari
112 Protection Agency maintains an inventory of greenhouse gas emissions in accordance with the Intergov
113 ing how such complex land use change affects greenhouse gas emissions is essential for modelling clim
115 ineering, motivated by concern that reducing greenhouse gas emissions may be insufficient to avoid si
116 ience has outlined targets for reductions of greenhouse gas emissions necessary to provide a substant
117 tilizer value, 79 (45-113) TJ of energy, and greenhouse gas emissions of 6.8 (3.4-10.1) MMT CO(2) equ
118 picture of the consequences of anthropogenic greenhouse gas emissions on future sea-level rise and it
119 more realistic assessment of the life cycle greenhouse gas emissions outcomes, using a case study of
122 ied and largely associated with volcanogenic greenhouse gas emissions released by large igneous provi
124 Hg from thawing permafrost for low and high greenhouse gas emissions scenarios using a mechanistic m
126 role in determining the near-term allowable greenhouse gas emissions that will limit future warming
129 ond method that combines temporally resolved greenhouse gas emissions with techno-economic analysis.
130 ssions (which account for ~10% of total U.S. greenhouse gas emissions) and corresponds to an emission
131 al system and led to reductions of 29-47% in greenhouse gas emissions, 26-41% in energy consumption,
132 most efforts have been directed to reducing greenhouse gas emissions, complementary strategies are n
133 cores, and BMI; 2) environmental indicators (greenhouse gas emissions, cumulative energy demand, and
134 from additional change due to anthropogenic greenhouse gas emissions, including the 4 per mille init
135 icted rates of warming arising from moderate greenhouse gas emissions, inhibitory effects of climate
136 ation would push back the timeline to reduce greenhouse gas emissions, largely undermining the Paris
137 yntheses link earthworm activities to higher greenhouse gas emissions, less soil biodiversity, and in
140 00 years at present, but, without mitigating greenhouse gas emissions, this can decrease to 3.5 years
142 ny mining operations could offset net mining greenhouse gas emissions, while simultaneously giving va
166 saline aquifers is needed to mitigate global greenhouse gas emissions; monitoring the mechanical inte
170 he century (1900-1949), however, a signal of greenhouse-gas-forced change is robustly detectable.
171 er significantly from an expected pattern of greenhouse gas forcing around mid-century (1950-1975), c
172 ern Hemisphere in response to insolation and greenhouse gas forcing is thought to have caused groundi
174 is a key process determining the release of greenhouse gases from surface waters and a fundamental c
178 an help achieve emission reductions for both greenhouse gas (GHG) and air toxics from O&G production
179 udy fills the information gap, analyzing the greenhouse gas (GHG) and criteria air pollutant (CAP) em
180 endent in each other's water and energy use, greenhouse gas (GHG) and PM(2.5) emissions, and labor an
182 ing technologies are important components of greenhouse gas (GHG) emission reduction strategies for l
183 data from 2014, we investigate U.S. refinery greenhouse gas (GHG) emissions (CO(2), CH(4), and N(2)O)
184 effectively moved the mean of the life cycle greenhouse gas (GHG) emissions 38% higher while maintain
187 erstand aquaculture's contribution to global greenhouse gas (GHG) emissions and how it can be mitigat
189 Agriculture is a major contributor to global greenhouse gas (GHG) emissions and must feature in effor
190 roduction (i.e., protein and iron), minimize greenhouse gas (GHG) emissions and resource use (i.e., w
192 e, and it is critical to understand how soil greenhouse gas (GHG) emissions and uptake will respond t
193 a factor of 12.7-29.5 under a high-intensity greenhouse gas (GHG) emissions and urban development pat
194 of these alternative cements result in lower greenhouse gas (GHG) emissions as well as other indicato
195 nied by environmental burdens, including the greenhouse gas (GHG) emissions associated with fertilize
197 , nitrogen fertilizer (Nr) and water use and greenhouse gas (GHG) emissions exist, and could improve
199 agrass restoration projects and help reverse greenhouse gas (GHG) emissions from global seagrass loss
200 is an effective way to reduce the life cycle greenhouse gas (GHG) emissions from light-duty vehicles.
201 an Africa and estimates changes in preretail greenhouse gas (GHG) emissions if the cold chain develop
203 rgets on both direct and indirect (upstream) greenhouse gas (GHG) emissions in order to reconcile tra
204 ntial energy use accounts for roughly 20% of greenhouse gas (GHG) emissions in the United States.
208 renewable energy, some projects produce high greenhouse gas (GHG) emissions per unit electricity gene
210 al Corporate Average Fuel Economy (CAFE) and greenhouse gas (GHG) emissions standards and the Zero Em
211 cate that China's non-carbon dioxide (CO(2)) greenhouse gas (GHG) emissions will increase rapidly fro
212 To reduce oil consumption and resulting greenhouse gas (GHG) emissions, carbon dioxide can be ca
213 h Columbia (BC), Canada using three metrics: greenhouse gas (GHG) emissions, electricity cost, and ov
214 periment to estimate fossil energy (FE) use, greenhouse gas (GHG) emissions, PM(2.5)-related emission
224 he magnitudes, patterns and drivers of these greenhouse gas (GHG) fluxes remain poorly understood.
225 voked to explain non-normal distributions of greenhouse gas (GHG) fluxes, also known as hot spots and
226 soil profile, SI could potentially increase greenhouse gas (GHG) fluxes, particularly N(2)O through
228 tic model to quantify the variability in the greenhouse gas (GHG) footprints of product distribution
229 tly by natural decadal variability, but that greenhouse gas (GHG) forcing erodes the pattern and degr
230 Few studies have evaluated the life cycle greenhouse gas (GHG) impacts associated with India's pow
231 ted wood products (HWPs) can affect national greenhouse gas (GHG) inventories, in which the productio
235 ery systems is the most efficient method for greenhouse gas (GHG) mitigation, and its total GHG mitig
236 forest to drainage-based agriculture alters greenhouse gas (GHG) production, but the magnitude of th
237 able Fuel Standard (RFS) program specifies a greenhouse gas (GHG) reduction threshold for cellulosic
239 thropogenic aerosols, volcanic aerosols, and greenhouse gases (GHG)-relative to each other and to int
240 paper, we compared the well-to-wheels (WTW) greenhouse gases (GHGs) and criteria air pollutant emiss
242 nic matter and stimulate the release of soil greenhouse gases (GHGs), but to what extent soil release
243 Increased concentrations of atmospheric greenhouse gases have led to a global mean surface tempe
244 el warming projections, forced by increasing greenhouse gases, have a large inter-model spread in bot
245 umptions concerning the radiative forcing of greenhouse gases, ice sheets and mineral dust aerosols,
246 their chemical structure makes them possible greenhouse gases if their atmospheric lifetimes are long
247 the production or consumption of this potent greenhouse gas in methanogenic and methanotrophic archae
250 g in any one year increases as the levels of greenhouse gases in the atmosphere increase; (iii) green
251 Ruminants contribute to the emissions of greenhouse gases, in particular methane, due to the micr
253 erved increase in VPD cannot be explained by greenhouse-gas-induced (GHG) radiative warming alone.
254 rogram to an assessment of the U.S. Regional Greenhouse Gas Initiative (RGGI), the United States' fir
257 ent to the 2006 IPCC Guidelines for National Greenhouse Gas Inventories, we incorporate DeltaAGB data
258 tory and the Environmental Protection Agency Greenhouse Gas Inventory (GHGI) with regional airborne e
260 S. Environmental Protection Agency's current greenhouse gas inventory estimate for pipeline mains in
263 f methane (CH(4)), the second most important greenhouse gas, is currently increasing by ~10 million t
264 half the present value, and warming by other greenhouse gases like methane was not a major factor, th
265 preparing reference materials of high impact greenhouse gases, limiting progress toward coherent and
270 r biodiversity protection and land use-based greenhouse gas mitigation call for increases in the effe
272 l life cycle assessment of the potential for greenhouse gas mitigation, including additional effects
273 r enzyme nitrous oxide reductase reduces the greenhouse gas N(2)O to uncritical N(2) as the final ste
276 e conversion of the environmentally critical greenhouse gas nitrous oxide (N(2)O) to dinitrogen (N(2)
278 ons from landfilling, but emissions of other greenhouse gases, odorous/toxic species, and reactive co
279 adly assumed that hydropower facilities emit greenhouse gases on par with wind, there is mounting evi
280 of the North Atlantic, caused by increasing greenhouse gases over the 21st century, climate projecti
286 assessment methodology ignores the impact of greenhouse gases relative to when they are emitted.
288 ccumulate C, have a net positive atmospheric greenhouse gas removal effect, and support shoreline acc
289 degrees C, most scenario projections rely on greenhouse gas removal technologies (GGRTs); one such GG
290 than emission factors utilized by the EPA's greenhouse gas reporting program (GHGRP) but less than e
294 ity of the integration of a dense network of greenhouse gas sensors with a science-driven building an
295 olysis offers an attractive route to upgrade greenhouse gases such as carbon dioxide (CO(2)) to valua
297 t a method for leveraging the social cost of greenhouse gases to account for the temporal impacts of
300 able dry reforming catalysts from two potent greenhouse gases which could be of great interest for ma