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  • 1
    facet.materialart.
    Unknown
    PANGAEA
    In:  Supplement to: Paton-Walsh, Clare; Guérette, Elise-Andrée; Kubistin, Dagmar; Humphries, Ruhi S; Wilson, Stephen R; Dominick, Doreena; Galbally, Ian; Buchholz, Rebecca R; Bhujel, Mahendra; Chambers, Scott D; Cheng, Min; Cope, Martin; Davy, Perry; Emmerson, Kathryn M; Griffith, David W T; Griffiths, Alan D; Keywood, Melita D; Lawson, Sarah; Molloy, Suzie; Rea, Geraldine; Selleck, Paul; Shi, Xue; Simmons, Jack B; Velazco, Voltaire (2017): The MUMBA Campaign: Measurements of Urban, Marine and Biogenic Air. Earth System Science Data, 9(1), 349-362, https://doi.org/10.5194/essd-9-349-2017
    Publication Date: 2023-01-13
    Description: The Measurements of Urban, Marine and Biogenic Air (MUMBA) campaign took place in Wollongong, New South Wales (a small coastal city approximately 80 km south of Sydney, Australia), from 21st December 2012 to 15th February 2013. Instruments were deployed during MUMBA to measure the gaseous and aerosol composition of the atmosphere with the aim of providing a detailed characterisation of the complex environment of the ocean/forest/urban interface that could be used to test the skill of atmospheric models. Gases measured included ozone, oxides of nitrogen, carbon monoxide, carbon dioxide, methane and many of the most abundant volatile organic compounds. Aerosol characterisation included total particle counts above 3 nm, total cloud condensation nuclei counts; mass concentration of PM2.5, number concentration size distribution, aerosol chemical analyses and elemental analysis. Meteorological measurements and LIDAR measurements were also performed. The campaign captured varied meteorological conditions, including two extreme heat events, providing a potentially valuable test for models of future air quality in a warmer climate. There was also an episode when the site sampled clean marine air for many hours, providing a useful additional measure of background concentrations of these trace gases within this poorly sampled region of the globe. Here we present the observations recorded at the MUMBA site during the campaign, as well as radon and air quality data from nearby sites. These records can be used for testing chemical transport models.
    Type: Dataset
    Format: application/zip, 17 datasets
    Location Call Number Expected Availability
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  • 2
    Publication Date: 2023-01-13
    Description: Location Spectrometer: Roof of 2 storey building at 2 Percy St, Auburn NSW 2144 Australia, -33.85472, 151.0373, 20.6 m rooftop above sea level, height rooftop above street level = 6.72 m; height measurement path above rooftop= 1.2 m Location Reflectors: Roof of 3 story building, Cumberland City Council, Auburn Office, at 1 Susan St Auburn 2144, Australia, -33.85311, 151.0335, 40.8 m rooftop above sea level, height roof top above street = 12.8 m, height mid-mirrors above rooftop = 2.4 m, Distance between Spectrometer and reflectors = 395.8 m one-way (instrument to reflector) + 1 m Return Measurement path = 792.6 m (including 1 m internal reflectance) Measurement Path Slope: = 5.3 Degrees; Difference in altitude = 20.9 m Measurement Path Bearing: 296.0278 degrees Gas Species Reported (units): Carbon Monoxide (CO, ppbv) Carbon Dioxide (CO2, ppmv) Nitrous Oxide (N2O, ppbv), Ammonia (NH3, ppbv), Methane (CH4, ppbv). Instrument description: The open path FTIR system is based on an FTIR spectrometer (Matrix-M IR cube, Bruker Optik, Ettlingen, Germany) which provides modulated infrared radiation with 1 cm-1 resolution from a globar source in a nominally parallel 25 mm diameter output beam. The beam passes through a beamsplitter (ZnSe window, 50 x 3 mm) to the secondary mirror of an on-axis beam expander which expands the beam diameter to 250 mm and reduces the divergence by a factor of 10. The beam expander was constructed from a modified 10 inch Schmidt-Cassegrain telescope (Model LX200R, Meade Instrument Corp., California, USA) by removing the standard Schmidt correction plate and secondary mirror and replacing it with a convex mirror of effective focal length 50mm. The beam expander is focussed by shifting the secondary mirror along the optic axis so that its focus is coincident with that of the primary mirror. An optically black mask ~ 5 mm in diameter at the centre of the secondary mirror blocks the back reflection of radiation to the detector from the centre of the mirror. The expanded beam follows an open path to 3 x 300 mm diameter retroreflector arrays (PLX Industries, New York, USA) located ~500 m distant from the spectrometer. The retroreflector returns the beam back on itself through the beam expander to the beamsplitter. The reflected beam from the beamsplitter is focussed by a 29 mm focal length 90 degrees off-axis paraboloidal mirror to a cooled MCT detector (Infrared Associates Inc., Florida, USA). The detector is cooled to liquid nitrogen temperature by a Stirling cycle mechanical refrigerator (RicorK508), removing the need for a liquid nitrogen supply in field applications. The FTIR spectrometer, beamsplitter, beam expander and detector are mounted on a single 100 mm optical rail to allow simple and robust alignment. The optical rail is mounted to a heavy duty tripod (Gibralter model 4-60450-OA, Quickset International Inc., Illinois, USA ) with a computer controlled Automated Instrument Mount (AIM Colterlec, Unanderra, Australia) to the allow accurate and stable alignment of the beam between spectrometer and retroreflector. The reported precision of the instrument is: NH3 1 ppb, N2O 0.6 ppb, CO2 0.5 ppm, CH4 2 ppb, CO 1 ppb. Data Collection Rate: average 5 min, timestamped at start of data collection period. Spectral Analysis: MALT (Griffith, D.W.T., Synthetic calibration and quantitative analysis of gas phase infrared spectra, Applied Spectroscopy, 50 (1), 59-70, 1996) with spectral parameters from HITRAN08 database (www.hitram.com). Spectral Micro Windows: CO2, N2O, CO and H2O 2150-2280 cm-1 CH4, H2O 3001-3140 cm-1 NH3, H2O 900-945 and 955-995 cm-1 Data QA: Data were removed when the maximum spectral intensity in the 2300 cm-1 spectral region was reduced to 〈 40% of the typical maximum value. Reduction in spectral intensity was typically due to rain, dew or dust on the telescope or retro-reflector surfaces. Calibration and Validation: Data (CO, CO2, CH4 and N2O) were compared with concurrent data from the Spectronus in-situ FTIR spectrometer. The regression results used to correct the OP-FTIR data (data collected at wind speed 〈 1 ms-1 were removed from the regression). Interruptions and Issues: Instrument Failure: UoW OP-FTIR OP3 failed with laser failure on 28 May 2017 14:15 and was replaced by OP5 on 31 May 2017 14:14; Optics on OP-FTIR updated on 16 June 2017 10:35. Instrument shut down when air temperature exceeded 42 C to protect instrument against over-heating.
    Keywords: Air chemistry observatory; Ammonia; Auburn_PercySt; Australia; Carbon dioxide; Carbon monoxide; DATE/TIME; HEIGHT above ground; Methane; Nitrous oxide; SPUSO
    Type: Dataset
    Format: text/tab-separated-values, 302239 data points
    Location Call Number Expected Availability
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  • 3
    Publication Date: 2023-01-13
    Description: It is recognised that Western Sydney experiences poorer air quality compared to the eastern suburbs due to the topography of the Sydney basin resulting in pollution produced in eastern Sydney being transported by the easterly sea breeze to Western Sydney, where it pools against the mountain range. As part of the Western Air-Shed and Particulate Study for Western Sydney (WASPSS), targeted air quality measurement campaigns were conducted in Western Sydney with the aim to identify hot spots for poor air quality and understand the variability in air quality in western Sydney, in particular how well the existing air quality monitoring network represents the air quality where people live. The measurement campaigns were operated in collaboration with the Office of Environment and Heritage (OEH), supplementing the information available from the ongoing OEH measurement network. The Auburn Air Quality measurement site was established on the roof a 2 story building at 2 Percy St, on the edge of the Auburn CBD in Western Sydney, and operated between 25 May 2016 and 9 September 2017. The site is adjacent to major rail line, used for heavy diesel freight, and major road networks. To the east is light industry, to the north and west is the Auburn CBD, with residential areas to the west. The site included a portable air monitoring station (OEH), containing instrumentation comparable to the OEH monitoring stations, an extended open path Fourier transform infrared (OP-FTIR) spectrometer, measuring atmospheric CO2, CO, N2O, CH4 and NH3 and an open path ultra-violet visible (UV-visible) Differential Optical Absorption Spectrometer (DOAS) measuring O3, SO2, NO2, HCHO & HONO. The two open path instruments operated with parallel measurement paths of ~ 400m, with the measurement paths terminated by mirror arrays located on the roof of a 3 story building within the Auburn CBD, on a small hill above the Percy St building. The open path FTIR and DOAS operated from October 2016 to March 2017, and May 2017 to September 2017. In August 2017 an in-situ FTIR tracer gas analyser (CO, CO2, N2O, CH4 and 13C in CO2) was installed with an air intake adjacent to the OEH monitoring station intake, and operated until September 2017. Meteorological data supplied by a 3D sonic anemometer from July 2017 to September 2017 complimented the weather station data from the portable monitoring station. Location: Roof of 2 storey building at 2 Percy St, Auburn NSW 2144, Australia, -33.85472, 151.0374; Height: roof top above sea level 20.6 m; height rooftop above street level 6.72m Site operational Dates: 28-October-2016 13:00 to 18-September-2017 13:00 Time zone: Australian Eastern Standard Time, UTC+10 hours
    Type: Dataset
    Format: application/zip, 5 datasets
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  • 4
    Publication Date: 2023-06-10
    Description: Measurements of volatile organic compounds (VOCs) were collected using an Ionicon 4000 Proton Transfer Reaction Time of Flight Mass Spectrometer (PTR-ToF-MS). Measurements were taken at Cataract Scout Park, Appin, N.S.W. (34°14'42.29S 150°49'24.97E) from an inlet 10 m above ground level as part of the Characterizing Organics and Aerosol Loading over Australia (COALA-2020) campaign. The campaign ran from mid-January to mid-March, 2020, with the instrument running from early February. Data presented here corresponds to data used in paper by Mouat et al. (2021a) which spans from 2-6 Feb. 2020. These species are in addition to directly calibrated species archived by Mouat et al. (2021b) in a seperate PANGAEA record. Sample air was drawn down a 20 m PTFE inlet line with a bypass pump (flow rate 1.5 – 3 Lmin-1). Concentrations for compounds presented in this dataset were calculated using methodology proposed in Sekimoto et al. (2017).
    Keywords: 1-Butene; 2-(3H)Furanone + cis-2-butenediol; 2-Furanmethanol; 2-Furfural; 2-Hydroxy-3-methyl-2-cyclopenten-1-one; 5-Methyl furfural + catechol; Acetic acid; Appin, Australia; Australia; Benzaldehyde; Biogenic VOC; biomass burning; C3-Furan; Calculated, according to Sekimoto et al. (2017); Cataract_scout_park; Characterizing Organics and Aerosol Loading over Australia; COALA; COALA-2020; Creosol; Cyclopentanone + HCO1; DATE/TIME; Formamide; Formic acid; Furan; Guaiacol; Hydrocarbons, assorted; Maleic anhydride; Methyl acetate; Methylglyoxal; Methyl methacrylate; Methyl propanoate; MULT; Multiple investigations; Nitromethane; Phenol; Propene; PTR-ToF-MS; Styrene; volatile organic compounds
    Type: Dataset
    Format: text/tab-separated-values, 26975 data points
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  • 5
    Publication Date: 2023-07-18
    Description: Measurements of volatile organic compounds (VOCs) were collected using an Ionicon 4000 Proton Transfer Reaction Time of Flight Mass Spectrometer (PTR-ToF-MS). Measurements were taken at Cataract Scout Park, Appin, N.S.W. (34°14'42.29"S 150°49'24.97"E) from an inlet 10 m above ground level as part of the Characterizing Organics and Aerosol Loading over Australia (COALA-2020) campaign. The campaign ran from mid-January to mid-March, 2020, with the instrument running from early February. Sample air was drawn down a 20 m PTFE inlet line with a bypass pump (flow rate 1.5 - 3 L min-1). Calibration occurred in situ using standard cylinders for the compounds reported below. Calibration uncertainty is ±20%. Additional compounds may be available on request. Measurements were processed using the Ionicon PTR-MS Viewer software. Measurements from February 2 - February 7 have been corrected to account for an identified inlet leak. A flat subtraction was applied, and resulting compound offsets are provided in the parameter comments. Data from February 7 – February 16 have been removed due to identified leak requiring greater corrections.
    Keywords: Acetaldehyde; Acetone; Acetonitrile; Appin, Australia; Australia; Benzene; Biogenic VOC; biomass burning; Butan-2-one; Cataract_scout_park; Characterizing Organics and Aerosol Loading over Australia; COALA; COALA-2020; DATE/TIME; HEIGHT above ground; Isoprene; Methacrolein + methyl vinyl ketone; Methanol; Monoterpenes; MULT; Multiple investigations; Precision; Prop-2-enal; Proton Transfer Reaction Time of Flight Mass Spectrometer, Ionicon 4000; PTR-ToF-MS, Ionicon 4000; Sum C8H10; Sum C9H12; Toluene; volatile organic compounds
    Type: Dataset
    Format: text/tab-separated-values, 885045 data points
    Location Call Number Expected Availability
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  • 6
    Publication Date: 2023-07-11
    Description: Measurements of wind speed and direction were captured using a three-dimensional sonic anemometer (Windmaster Pro, Gill Instruments Limited, Hampshire, UK). Measurements were taken at Cataract Scout Park, Appin, N.S.W. (34°14'42.29"S 150°49'24.97"E) from a mast 10 m above ground level as part of the Characterizing Organics and Aerosol Loading over Australia (COALA-2020) campaign. Data processing was handled by the EddyPro® 7 software (LI-COR Biosciences, Lincoln, NE, USA). Measurements were taken at 1-minute time resolution and averaged to thirty-minute means, as reported here. Mean wind speed and direction are the only parameters reported here as the authors are concerned the adjacent tree canopy has significantly impacted the flux measurements. For further details please contact the authors. Wind speed and direction measurements were also taken at an adjacent air quality monitoring station installed for the campaign. These data are also available in this depository, listed under "Air quality pollutants measurements at Cataract Scout Park, Australia, taken during the COALA-2020 campaign."
    Keywords: 3D sonic anemometer (Gill Windmaster Pro, Hampshire, UK); anemometer; Appin, Australia; biomass burning; Cataract_scout_park; Characterizing Organics and Aerosol Loading over Australia; COALA; COALA-2020; DATE/TIME; HEIGHT above ground; MULT; Multiple investigations; Wind direction; wind speed; Wind speed; Wind speed, maximum
    Type: Dataset
    Format: text/tab-separated-values, 8289 data points
    Location Call Number Expected Availability
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  • 7
    Publication Date: 2023-07-11
    Description: Measurements of air quality pollutant concentration were collected using a New South Wales Department of Planning, Industry, and Environment Air Quality Monitoring Station (AQMS). Measured variables included relative humidity, ambient temperature, wind speed and direction, particulate matter less than 2.5 µm in diameter (PM2.5), particulate matter less than 10 µm in diameter (PM10), ozone, nitric oxide (NO), nitrous oxide (NO2), oxides of nitrogen (NOx), sulfur dioxide (SO2) and visibility by nephelometer. The station used was identical to those used in the DPIE air quality monitoring network around N.S.W. Details of the instrumentation used can be found here: https://www.environment.nsw.gov.au/topics/air/air-quality-basics/sampling-air-pollution. Measurements were taken at Cataract Scout Park, Appin, N.S.W. (34°14'42.29"S 150°49'24.97"E) as part of the Characterising Organics and Aerosol Loading over Australia (COALA-2020) campaign. Measurements are available from late December, 2019 to mid-March, 2020. Reported measurements are at 1-minute time resolution. Data have been filtered for flagged, outlying and negative values. All gaseous measurements were corrected using overnight zero and span measurements. Ozone was corrected overnight using only zero measurements. It must be noted that the sulfur dioxide record contains some data gaps.
    Keywords: aerosol; air quality; Air Quality Monitoring Station (AQMS), New South Wales Department of Planning, Industry, and Environment; Appin, Australia; AQMS; Atmospheric chemistry; biomass burning; Cataract_scout_park; Characterizing Organics and Aerosol Loading over Australia; COALA; COALA-2020; DATE/TIME; HEIGHT above ground; Humidity, relative; MULT; Multiple investigations; Nitric oxide; Nitrogen dioxide; Nitrogen oxide; NOx; O3; Ozone; Particulate matter, 〈 10 µm; Particulate matter, 〈 2.5 µm; Sulfur dioxide; Temperature, air; Visibility, NEPH; Wind direction; Wind direction, standard deviation; Wind speed
    Type: Dataset
    Format: text/tab-separated-values, 1576953 data points
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  • 8
    facet.materialart.
    Unknown
    PANGAEA
    In:  Supplement to: Buchholz, Rebecca R; Paton-Walsh, Clare; Griffith, David W T; Kubistin, Dagmar; Caldow, Christopher; Fisher, Jenny A; Deutscher, Nicholas M; Kettlewell, Graham; Riggenbach, Martin; Macatangay, Ronald; Krummel, Paul B; Langenfelds, Ray L (2016): Source and meteorological influences on air quality (CO, CH4 & CO2) at a Southern Hemisphere urban site. Atmospheric Environment, 126, 274-289, https://doi.org/10.1016/j.atmosenv.2015.11.041
    Publication Date: 2023-09-02
    Description: Wollongong, Australia is an urban site at the intersection of anthropogenic, biomass burning, biogenic and marine sources of atmospheric trace gases. The location offers a valuable opportunity to study drivers of atmospheric composition in the Southern Hemisphere. Here, a record of surface carbon monoxide (CO), methane (CH4) and carbon dioxide (CO2) was measured with an in situ Fourier transform infrared trace gas analyser between April 2011 and August 2014. Clean air was found to arrive at Wollongong in approximately 10% of air masses. Biomass burning influence was evident in the average annual cycle of clean air CO during austral spring. A significant negative short-term trend was found in clean air CO (-1.5 nmol/mol/a), driven by a reduction in northern Australian biomass burning. Significant short-term positive trends in clean air CH4 (5.4 nmol/mol/a) and CO2 (1.9 µmol/mol/a) were consistent with the long-term global average trends. Polluted Wollongong air was investigated using wind-direction/wind-speed clustering, which revealed major influence from local urban and industrial sources from the south. High values of CH4, with anthropogenic DCH4/DCO2 enhancement ratio signatures, originated from the northwest, in the direction of local coal mining. A pollution climatology was developed for the region using back trajectory analysis and DO3/DCO enhancement ratios. Ozone production environments in austral spring and summer were associated with anticyclonic meteorology on the east coast of Australia, while ozone depletion environments in autumn and winter were associated with continental transport, or fast moving trajectories from southern latitudes. This implies the need to consider meteorological conditions when developing policies for controlling air quality.
    Keywords: Australia; Carbon dioxide; Carbon monoxide; DATE/TIME; Fourier transform infrared spectroscopy (FTIR); FTIR/atmospheric composition observation & Weather station/meteorological observation (WST); FTIR-WST; HEIGHT above ground; Humidity, relative; Methane; Pressure, atmospheric; Temperature, air; Wind direction; Wind speed; Wollongong_UOW
    Type: Dataset
    Format: text/tab-separated-values, 1031888 data points
    Location Call Number Expected Availability
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  • 9
    Publication Date: 2023-07-11
    Description: Measurements of radon-222 (222Rn) concentration were collected using a 1500 L dual-flow loop radon detector, designed and built by the Australian Nuclear Science and Technology Organisation (ANSTO; Lucas Heights, NSW, Australia) (Chambers et al., 2011; Whittlestone and Zahorowski, 1998). Sampling occurred at 65-75 L min^-1. Calibration occurred during the campaign from a Pylon (Ottawa, ON, Canada) source. Measurements were taken at Cataract Scout Park, Appin, N.S.W. (34°14'42.29"S 150°49'24.97"E) from an inlet 3.94 m above ground level as part of the Characterizing Organics and Aerosol Loading over Australia (COALA-2020) campaign. The campaign ran from mid-January to mid-March, 2020. Reported measurements are at 30-minute time resolution. Concentrations have not been corrected for the response time of the detector but can be on the request of users. See Griffiths et al. (2016) for details.
    Keywords: aerosol; Appin, Australia; boundary layer; Cataract_scout_park; Characterizing Organics and Aerosol Loading over Australia; COALA; COALA-2020; DATE/TIME; Dual-flow loop radon detector, Australian Nuclear Science and Technology Organisation (ANSTO), Australia; HEIGHT above ground; MULT; Multiple investigations; radon; Radon-222 activity; Radon-222 activity uncertainty fraction; stability; tracer
    Type: Dataset
    Format: text/tab-separated-values, 5928 data points
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  • 10
    Publication Date: 2023-07-11
    Description: Measurements of aerosol size distribution between 14 and 661 nm diameter were measured using a TSI Scanning Mobility Particle Sizer (consisting of 3080 DMA, 3772 CPC and x-ray aerosol neutraliser, TSI Incorporated, Shoreview, MN, USA). Measurements were taken at Cataract Scout Park, Appin, N.S.W. (34°14'42.29"S 150°49'24.97"E) from an inlet 5.13 m above ground level as part of the Characterising Organics and Aerosol Loading over Australia (COALA-2020) campaign. Zero and flow checks logged have been removed from the published measurements, presented at 1-minute temporal resolution. 1-minute data are spline interpolations of the 5-minute scan measurements output by the instrument. Measurements span from January 29 2020 until March 15 2020. Please note that the instrument was run with leaky impactor until February 18 2020. Measurements in this period should be treated with caution. Measurements made during February 18-20 were disrupted due to impactor testing and have been removed. Following February 20, measurements were made without an impactor. Measurements were not made between February 25 and February 29.
    Keywords: aerosol; Aerosol size distribution; Appin, Australia; biomass burning; Cataract_scout_park; Characterizing Organics and Aerosol Loading over Australia; COALA; COALA-2020; DATE/TIME; HEIGHT above ground; Log-normal particle size distribution, normalized concentration at particle diameter 101.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 105.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 109.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 113.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 117.6 nm; Log-normal particle size distribution, normalized concentration at particle diameter 121.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 126.3 nm; Log-normal particle size distribution, normalized concentration at particle diameter 131 nm; Log-normal particle size distribution, normalized concentration at particle diameter 135.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 14.6 nm; Log-normal particle size distribution, normalized concentration at particle diameter 140.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 145.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 15.1 nm; Log-normal particle size distribution, normalized concentration at particle diameter 15.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 151.2 nm; Log-normal particle size distribution, normalized concentration at particle diameter 156.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 16.3 nm; Log-normal particle size distribution, normalized concentration at particle diameter 16.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 162.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 168.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 17.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 174.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 18.1 nm; Log-normal particle size distribution, normalized concentration at particle diameter 18.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 181.1 nm; Log-normal particle size distribution, normalized concentration at particle diameter 187.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 19.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 194.6 nm; Log-normal particle size distribution, normalized concentration at particle diameter 20.2 nm; Log-normal particle size distribution, normalized concentration at particle diameter 20.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 201.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 209.1 nm; Log-normal particle size distribution, normalized concentration at particle diameter 21.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 216.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 22.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 224.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 23.3 nm; Log-normal particle size distribution, normalized concentration at particle diameter 232.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 24.1 nm; Log-normal particle size distribution, normalized concentration at particle diameter 241.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 25.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 250.3 nm; Log-normal particle size distribution, normalized concentration at particle diameter 259.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 25 nm; Log-normal particle size distribution, normalized concentration at particle diameter 26.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 269 nm; Log-normal particle size distribution, normalized concentration at particle diameter 27.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 278.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 28.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 289 nm; Log-normal particle size distribution, normalized concentration at particle diameter 299.6 nm; Log-normal particle size distribution, normalized concentration at particle diameter 30 nm; Log-normal particle size distribution, normalized concentration at particle diameter 31.1 nm; Log-normal particle size distribution, normalized concentration at particle diameter 310.6 nm; Log-normal particle size distribution, normalized concentration at particle diameter 32.2 nm; Log-normal particle size distribution, normalized concentration at particle diameter 322 nm; Log-normal particle size distribution, normalized concentration at particle diameter 33.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 333.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 34.6 nm; Log-normal particle size distribution, normalized concentration at particle diameter 346 nm; Log-normal particle size distribution, normalized concentration at particle diameter 35.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 358.7 nm; Log-normal particle size distribution, normalized concentration at particle diameter 37.2 nm; Log-normal particle size distribution, normalized concentration at particle diameter 371.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 38.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 385.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 40 nm; Log-normal particle size distribution, normalized concentration at particle diameter 41.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 414.2 nm; Log-normal particle size distribution, normalized concentration at particle diameter 42.9 nm; Log-normal particle size distribution, normalized concentration at particle diameter 429.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 44.5 nm; Log-normal particle size distribution, normalized concentration at particle diameter 445.1 nm; Log-normal particle size distribution, normalized concentration at particle diameter 46.1 nm; Log-normal particle size distribution, normalized concentration at particle diameter 461.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 47.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 478.3 nm; Log-normal particle size distribution, normalized concentration at particle diameter 49.6 nm; Log-normal particle size distribution, normalized concentration at particle diameter 495.8 nm; Log-normal particle size distribution, normalized concentration at particle diameter 51.4 nm; Log-normal particle size distribution, normalized concentration at particle diameter 514 nm; Log-normal particle size distribution, normalized concentration at particle diameter 53.3 nm; Log-normal particle size distribution, normalized
    Type: Dataset
    Format: text/tab-separated-values, 5717224 data points
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