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3 results for “chemical ionization mass spectrometry”

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zenodo36/100

Online Aerosol Chemical Characterization by Extractive Electrospray Ionization − Ultrahigh-Resolution Mass Spectrometry (EESI-Orbitrap)

<p>These datasets are the raw data presented in the presented work of &quot;Online Aerosol Chemical Characterization by Extractive Electrospray Ionization &minus; Ultrahigh-Resolution Mass Spectrometry (EESI-Orbitrap)&quot; in <em>Environmental Science &amp; Technology Journal</em>, doi:10.1021/acs.est.9b07090.</p> <p>Abstract:&nbsp;Current mass spectrometry techniques for the online&nbsp;measurement of organic aerosol (OA) composition are subjected to either&nbsp;thermal/ionization-induced artifacts or limited mass resolving power,&nbsp;hindering accurate molecular characterization. Here, we combined the soft&nbsp;ionization capability of extractive electrospray ionization (EESI) and the&nbsp;ultrahigh mass resolution of Orbitrap for real-time, near-molecular&nbsp;characterization of OAs. Detection limits as low as tens of ng m<sup>&minus;3</sup> with&nbsp;linearity up to hundreds of &mu;g m<sup>&minus;3</sup> at 0.2 Hz time resolution were&nbsp;observed for single- and mixed-component calibrations. The performance of the EESI-Orbitrap system was further evaluated with laboratory-generated secondary OAs (SOAs) and filter extracts of ambient particulate&nbsp;matter. The high mass accuracy and resolution (140 000 at <em>m/z</em> 200) of&nbsp;the EESI-Orbitrap system enable unambiguous identification of the&nbsp;aerosol components&rsquo; molecular composition and allow a clear separation&nbsp;between adjacent peaks, which would be significantly overlapping if a medium-resolution (20 000) mass analyzer was used.&nbsp;Furthermore, the tandem mass spectrometry (MS<sup>2</sup>) capability provides valuable insights into the compound structure. For instance,&nbsp;the MS<sup>2</sup> analysis of ambient OA samples and lab-generated biogenic SOAs points to specific SOA precursors in ambient air among a&nbsp;range of possible isomers based on fingerprint fragment ions. Overall, this newly developed and characterized EESI-Orbitrap system&nbsp;will advance our understanding of the formation and evolution of atmospheric aerosols.</p> <p>Structure of the datasets: The raw data are separated into individual file of&nbsp;excel format for the figures. Simulation data from Figure 4 can be generated using the matlab code named <em>Figure4PeakSimulation.m.</em>&nbsp;</p>

opencc-by-4.0Mar 2020View details →
zenodo36/100

Highly time-resolved chemical speciation and source apportionment of organic aerosol components in Delhi, India, using extractive electrospray ionization mass spectrometry

<p>In recent years, the Indian capital city of Delhi has been impacted by very high levels of air pollution,<br> especially during winters. Comprehensive knowledge of the composition and sources of the organic aerosol<br> (OA), which constitutes a substantial fraction of total particulate mass (PM) in Delhi, is central to formulating<br> effective public health policies. Previous source apportionment studies in Delhi identified key sources of primary<br> OA (POA) and showed that secondary OA (SOA) played a major role but were unable to resolve specific SOA<br> sources. We address the latter through the first field deployment of an extractive electrospray ionization timeof-<br> flight mass spectrometer (EESI-TOF) in Delhi, together with a high-resolution aerosol mass spectrometer<br> (AMS). Measurements were conducted during the winter of 2018/19, and positive matrix factorization (PMF)<br> was used separately on AMS and EESI-TOF datasets to apportion the sources of OA. AMS PMF analysis yielded<br> three primary and two secondary factors which were attributed to hydrocarbon-like OA (HOA), biomass burning<br> OA (BBOA-1 and BBOA-2), more oxidized oxygenated OA (MO-OOA), and less oxidized oxygenated OA (LOOOA).<br> On average, 40%of the total OA mass was apportioned to the secondary factors. The SOA contribution to<br> total OA mass varied greatly between the daytime (76.8 %, 10:00&ndash;16:00 local time (LT)) and nighttime (31.0 %,<br> 21:00&ndash;04:00 LT). The higher chemical resolution of EESI-TOF data allowed identification of individual SOA<br> sources. The EESI-TOF PMF analysis in total yielded six factors, two of which were primary factors (primary<br> biomass burning and cooking-related OA). The remaining four factors were predominantly of secondary origin:<br> aromatic SOA, biogenic SOA, aged biomass burning SOA, and mixed urban SOA. Due to the uncertainties in<br> the EESI-TOF ion sensitivities, mass concentrations of EESI-TOF SOA-dominated factors were related to the<br> total AMS SOA (i.e. MO-OOA C LO-OOA) by multiple linear regression (MLR). Aromatic SOA was the major<br> SOA component during the daytime, with a 55.2% contribution to total SOA mass (42.4% contribution to total<br> OA). Its contribution to total SOA, however, decreased to 25.4% (7.9% of total OA) during the nighttime. This<br> factor was attributed to the oxidation of light aromatic compounds emitted mostly from traffic. Biogenic SOA<br> accounted for 18.4% of total SOA mass (14.2% of total OA) during the daytime and 36.1% of total SOA mass<br> (11.2% of total OA) during the nighttime. Aged biomass burning and mixed urban SOA accounted for 15.2%<br> and 11.0% of total SOA mass (11.7% and 8.5% of total OA mass), respectively, during the daytime and 15.4%<br> and 22.9% of total SOA mass (4.8% and 7.1% of total OA mass), respectively, during the nighttime. A simple<br> dilution&ndash;partitioning model was applied on all EESI-TOF factors to estimate the fraction of observed daytime<br> concentrations resulting from local photochemical production (SOA) or emissions (POA). Aromatic SOA, aged<br> biomass burning, and mixed urban SOA were all found to be dominated by local photochemical production,<br> likely from the oxidation of locally emitted volatile organic compounds (VOCs). In contrast, biogenic SOA was<br> related to the oxidation of diffuse regional emissions of isoprene and monoterpenes. The findings of this study<br> show that in Delhi, the nighttime high concentrations are caused by POA emissions led by traffic and biomass<br> burning and the daytime OA is dominated by SOA, with aromatic SOA accounting for the largest fraction.<br> Because aromatic SOA is possibly more toxic than biogenic SOA and primary OA, its dominance during the<br> daytime suggests an increased OA toxicity and health-related consequences for the general public.</p> <p>This repository has excel file corresponding to each figures presented in main text published version.</p>

opencc-by-4.0May 2022View details →
zenodo28/100

Organic pesticide database with 716 molecules analyzed with chemical ionization mass spectrometry. Reagent ions: bromide, protonated acetone, hydronium ion, dioxide.

<p>The dataset joins the measurements output of&nbsp;two standard mixtures from GALAB Laboratories, containing 404 and 312 pesticides. The measurements were conducted at Karsa Oy with a thermal desorption multi-scheme chemical ionization inlet operating at atmospheric pressure, coupled to a linear trap quadrupole orbitrap mass spectrometer.</p> <p>The dataset contains:</p> <ul> <li>name of the compound</li> <li>CAS identifier</li> <li>SMILES</li> <li>signal of the compound with a sample analyzed at a specific concentration and with a specific ionization method.</li> </ul> <p>Reagent ions:</p> <ul> <li>bromide</li> <li>protonated acetone</li> <li>hydronium ion</li> <li>dioxide</li> </ul> <p>Sample concentrations:</p> <ul> <li>10 pg/&micro;l</li> <li>20 pg/&micro;l</li> <li>100 pg/&micro;l</li> <li>1 ng/&micro;l</li> <li>2,5 ng/&micro;l</li> </ul> <p>&nbsp;</p> <p>The dataset has been analysed in the publications:</p> <ul> <li>Bortolussi, F., Sandstr&ouml;m, H., Partovi, F., Mikkil&auml;, J., Rinke, P., and Rissanen, M.: Technical note: Towards atmospheric compound identification in chemical ionization mass spectrometry with pesticide standards and machine learning, Atmos. Chem. Phys., 25, 685&ndash;704, https://doi.org/10.5194/acp-25-685-2025, 2025.</li> </ul>

opencc-by-4.0Jun 2024View details →

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