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1 ere determined from the subtropical eucalypt forest fire.
2 d in-situ immediately after a typical boreal forest fire.
3 dissipated due to the influence of a nearby forest fire.
4 tion on the toxicity of particulate ROC from forest fires.
5 and of a similar magnitude as emissions from forest fires.
6 inal Tasmanians, despite episodic widespread forest fires.
7 ge-scale disturbances such as clear cuts and forest fires.
8 Neither were egg Hg trends related to recent forest fires.
9 d drying has led to more severe and frequent forest fires(5-7), which threaten to shift the carbon ba
10 3 PAHs) were determined from the subtropical forest fire (7,000 +/- 170) compared to the tropical sav
11 rallels debates involving abstract models of forest fires, a central metaphor in complex systems theo
13 change has emerged as a driver of increased forest fire activity and should continue to do so while
14 For example, avalanches, earthquakes, and forest fires all propagate in systems organized into a c
16 dium spp, predominantly), impacted or not by forest fires and collected at different times, were stud
17 electric tissues and chemical oscillators to forest fires and competing populations, are nonlinear, s
19 ng) within the Athabasca watershed, however, forest fires and erosion of fossil fuel deposits within
21 further underestimates emissions from Arctic forest fires and inadequately represents long-range poll
26 that has resulted in increased frequency of forest fires and subsequent alteration of watershed carb
27 observed behavior, the forest fire model for forest fires and the sand pile model for landslides.
28 chanism of feedback particularly relevant to forest fires), and it presents evidence that characteris
30 ces of brown carbon include biomass burning, forest fires, and residential burning of biofuels, and a
32 nce Arctic temperatures and the frequency of forest fires are both expected to rise with climate chan
38 ntributed to an additional 4.2 million ha of forest fire area during 1984-2015, nearly doubling the f
40 he western United States (WUS), where annual forest fire area increased by more than 1,100% during 19
43 ring the droughts of 2007 and 2010, regional forest fires burned 12 and 5% of southeastern Amazon for
46 ng of medicinal plants, pasturing cattle and forest fires can induce environmental modifications, esp
49 s often lead to more common and more intense forest fires, causing dramatic changes in the nutrient s
50 es in its watershed during the study period (forest fire; changes in shoreline inundation due to beav
56 Along a transect (10-150-350 m) from the forest fire, concentration decrease for PCBs during flam
59 hifts in ambient temperature, air pollution, forest fires, desert (dust and sand) storms and extreme
63 function of pyrogenic carbon in neutralizing forest fire emissions and call for its consideration in
64 delineation revealed that rapidly increasing forest fire emissions in extratropical pyromes, linked t
66 se results suggest that the impact of boreal forest fire emissions on air quality in the mid-latitude
69 concerning their initiation and propagation, forest fires exhibit power-law frequency-area statistics
70 he influence of NPJ behavior on moisture and forest fire extremes in California before and during the
71 atural petrogenic source (93% petrogenic, 7% forest fire) for alkylated PAHs during the past approxim
77 we focus on the elevational distribution of forest fires in mountainous ecoregions of the western Un
80 collected on unmanned aircraft systems over forest fires in Utah, USA, we determine bacterial emissi
83 sitive to vegetation changes associated with forest fires, increasing by 94% in burned vs. unburned f
84 ombustion, suggests that its use as a unique forest fire indicator may not be suitable in PAD sedimen
85 report measurements and analysis of a boreal forest fire, integrating the effects of greenhouse gases
86 rmer world would likely increase the risk of forest fires, leading to potentially substantial release
87 s in models, our results suggest that boreal forest fires may be more sensitive to future aerosol mit
88 d as analogs for this observed behavior, the forest fire model for forest fires and the sand pile mod
95 e are well documented in North America, with forest fire occurrence and area clearly increasing in re
96 by the carbon dioxide emission increase from forest fires offsetting the decreasing emissions from gr
98 n extreme El Nino (EN) drought and extensive forest fires on plant mortality and carbon loss in undis
100 d PAHs and DBTs were not elevated during the forest fire period, supporting their association with pe
103 ck carbon sediments from Northern Hemisphere forest fires reduced albedo below a critical threshold i
105 en drought and fire regimes in United States forests, fire-related drought metrics and expected chang
106 sults suggest that warming may also increase forest fire severity (the number of trees killed) indepe
107 nic compounds (ROC) in western U.S. wildland forest fire smoke using a combination of observations fr
109 ern migrant tactic emerged following a large forest fire that enhanced forage in an area with lower p
110 ecover from catastrophic disturbances (e.g., forest fires, traffic jams, orphaned children, and refug
111 EF data for many PAHs from the eucalypt forest fire were comparable with those previously report
113 l stacks, vehicles, residential heating, and forest fires, whereas the PAH concentrations at AMS 14 (
114 dies have found that conditions conducive to forest fires, which generate harmful air pollutants and
115 e severe during El Nino events, pan-tropical forest fires will increase as more damaged, less fire-re
116 on prenatal exposure to the 1997 Indonesian forest fires with child nutritional outcomes and find th