source influences on the aerosol size distribution and ccn activity … · source influences on the...
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Source influences on the aerosol size distribution and CCN activity at the Resolute Bay Ground site S. Sharma1, W.R. Leaitch1, R. Staebler1, A. Aliabadi1, F. Kolonjari1, Wanmin Gong1, J. A. Ogren2, D. Veber1 1 Science and Technology Branch, Environment Canada; 2 NOAA/ ESRL, Boulder, CO, USA
Upper Weather Station at Resolute Bay 1. Abstract: Aerosol measurements at the Canadian Aerosol Baseline Measurement station at Resolute Bay, NU began in May 2013. The on-going measurements are particle light absorption, particle light, particle light scattering, particle size distribution, SO2, O3, NOx and PM2.5. Additional measurements of Cloud Condensation Nucleus (CCN) number concentrations were also made during the July 2014 NETCARE campaign and observed growth that may enhance their CCN activity at supersaturations (SS) between 0.,4% and 1%. Two different source influences are presented in this poster : clean air for possible new particle formation (NPF) on July 9 and 2) wildfires influence on July 14 to 16 and July 25 to 27. GEM-MACH model results are also discussed.
2. Method: Aerosol sample was pulled through a ¾” Stainless Steele tubing at 27 slpm through a 1 um size cut URG cyclone. Particle light absorption and light scattering were measured by Continuous Light Absorption Photometer (CLAP, NOAA/ESRL) and 3563, 3-wavelength Nephelometer (TSI Inc.). Particle size distribution measurements were made by 3034 Scanning Mobility Particle Sizer (SMPS, TSI Inc.) between 10 and 500 nm particles and CCN measurements were made by model 200 (DMT). 7-d back-trajectories were computed by using Hy-Split at three different heights. GEM-MACH Arctic 15 km; Emissions: Anthropogenic, fires, marine/shipping.
3. Results and discussion cm-3
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Events 1 and 4: Figures 1 and 2 show total particles concentrations in >20nm, >50 nm and >100 nm. NPF is evident where >20 nm particle concentrations are much higher than the other two modes which suggests a low condensation sink. July 9 NPF episode was also observed on a larger spatial scale via POLAR 6. Much higher >100nm particles present during fire event. Figures 3, 4, 5 and 6 show low anthropogenic influence with low SO2 and NOx levels and aged airmass with lower NOx levels also during wildfires events. Presence of higher light absorption and scattering measurements during fire event which is not present during NPF event. GEM-MACH model predicts all events. For events with fire influence, model predicted higher primary organic as major component of PM2.5. Emissions from bird colony are missing in the model and thus model underestimates the NPF event 1. Ammonia from the bird colonies with SO2 from biogenic emissions is speculated to give rise to small particles. Figures 7 and 8 show total SMPS and CCN concentrations at 0.4% SS (started July 19) and 1% SS. July 9 event shows CCN concentrations much higher than total SMPS particle. Wild fire event shows that at both saturation levels particles approximately 50% of particles have ability to be CCN.
July 26
July 25
7-d back-trajectories suggest airmass influence from coastline of Greenland and Ellesmere for ammonia emissions from bird colonies (Croft et al., 2015)
July8
July9
July8 July8
July9
July26
July26 July26
July25
July25
Event 1 – Possible New particle formation NPF (July 9-10)
Event 4 – Wildfires influence (July 25-26)
7-d back-trajectories support influence of Canadian wildfires at the Resolute Bay site on July 25 and 26 event.
4. Conclusion: 1. CCN activity appears to be higher for the event that may be NPF and lower under the wild fire influence. 2. Model predicted organics as major contributor of PM2.5 from fires and ammonia from bird colonies possible an important ingredient in small particle formation during NPF events.
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Figure 1: Particle Size distribution for July 2014
Figure 6
Figure 7: SMPS and CCN concentrations during event 1
Figure 8: SMPS and CCN concentrations during event 4.
Figure2: Particle # concentrations > 20, 50 and 100 nm
Figure 3:NOx and SO2 levels
Figure 4: PM2.5, light scattering and absorption
Figure 5: Comparison of PM2.5 model vs measurements
Figure 6: Model predictions for aerosol composition