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Expanding Single Particle Mass Spectrometer Analyses for the Identification of Microbe Signatures in Sea Spray Aerosols Camille M Sultana, Hashim Al-Mashat, and Kimberly Ann Prather Anal. Chem., Just Accepted Manuscript • DOI: 10.1021/acs.analchem.7b00933 • Publication Date (Web): 28 Aug 2017 Downloaded from http://pubs.acs.org on September 4, 2017
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Analytical Chemistry
Expanding Single Particle Mass Spectrometer Analyses for the Identification of Microbe Signatures in Sea Spray Aerosols Camille M. Sultana1, Hashim Al-Mashat1, Kimberly A. Prather1,2,* 1
Department of Chemistry and Biochemistry, University of California, San Diego, La
Jolla, CA 92093-0314; 2
Scripps Institution of Oceanography, University of California, San Diego, La Jolla, CA
92093; 1
ABSTRACT: Ocean-derived microbes in sea spray aerosols (SSA) have the potential to
2
influence climate and weather by acting as ice nucleating particles in clouds. Single
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particle mass spectrometers (SPMS), which generate in situ single particle composition
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data, are excellent tools for characterizing aerosols under changing environmental
5
conditions as they can provide high temporal resolution and require no sample
6
preparation. While SPMS have proven capable of detecting microbes, these instruments
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have never been utilized to definitively identify aerosolized microbes in ambient sea
8
spray aerosols. In this study, an aerosol time-of-flight mass spectrometer was used to
9
analyze laboratory generated SSA produced from natural seawater in a marine aerosol
10
reference tank. We present the first description of a population of biological SSA mass
11
spectra (BioSS), which closely match the ion signatures observed in previous terrestrial
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microbe studies. The fraction of BioSS dramatically increased in the largest supermicron
13
particles, consistent with field and laboratory measurements of microbes ejected by
14
bubble bursting, further supporting the assignment of BioSS mass spectra as microbes.
15
Finally, as supported by analysis of inorganic ion signals, we propose that dry BioSS
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particles have heterogeneous structures, with microbes adhered to sodium chloride
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nodules surrounded by magnesium-enriched coatings. Consistent with this structure,
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chlorine-containing ion markers were ubiquitous in BioSS spectra and identified as
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possible tracers for distinguishing recently aerosolized marine from terrestrial microbes.
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(INTRODUCTION START)
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Microbial cells ejected in sea spray aerosols (SSA) by bubble bursting at the
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ocean surface1–7 are of interest because of their potential to act as ice nucleating particles
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(INP)8–13 within clouds. However, common offline methods used to detect and enumerate
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aerosolized microbial cells have poor temporal resolution and often require a significant
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investment of time in sample collection, preparation, and analysis. Therefore these
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traditional offline techniques are not well suited to monitoring microbes in the
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atmosphere. To capture changes in aerosol composition, ground-based and aircraft
28
studies require high temporal resolution measurements on the order of seconds to minutes.
29
In addition, knowledge of the surface composition of individual particles is critical for
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understanding their ice nucleating capabilities.14–16 However, with bulk collection
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methods commonly employed for offline microbial analyses, such as impingers or filters,
32
information on the chemical morphology of microbe-containing particles is not
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maintained.
34
Single particle mass spectrometers (SPMSs) have been shown to be able to detect
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aerosolized microorganisms, providing real-time, single particle, size resolved, chemical
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composition data without requiring any sample preparation.17–19 SPMS studies of isolated
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aerosolized standards of microbes and plant detritus all report similar mass spectra (MS)
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indicative of cellular material, rich in potassium, phosphate, and a number of organic
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nitrogen ion markers.17–21 However, MS with such cellular signatures have only been
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identified in one study of an ambient aerosol population22 and a small number of studies
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of insoluble residues in precipitation and cloud water samples,22–25 which have been
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attributed to terrestrial microbial sources. Identifying MS generated from microbe-
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containing particles within an SSA population is analytically challenging as ion markers
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often considered characteristic of cellular single particle MS are also generated by
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chemical species dissolved in seawater. This study uses isolated SSA to identify a narrow
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set of likely single particle biological mass spectra (BioSS) that can be used in future
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attribution studies of microbes or microbe fragments in the atmosphere.
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Isolated SSA was produced from natural seawater in a marine aerosol reference
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tank (MART) and analyzed with aerosol time-of-flight mass spectrometry (ATOFMS). In
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this study, identified BioSS signatures are consistent with phosphate- and potassium-rich
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MS reported in previous SPMS studies of terrestrial microbes. We also show the first
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application of data analyses utilizing particle size and ion signal dependence on total ion
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intensity and laser pulse energy to further confirm BioSS mass spectra as microbe-
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comtaining SSA particles. In addition, using this information, details on the structure of
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BioSS particles are proposed and studied as a function of changing seawater chemical
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and biological composition.
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EXPERIMENTAL SECTION
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MART Induced Phytoplankton Bloom and SSA Generation
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60 L of coastal Pacific seawater was collected from the ocean surface at Scripps Pier (La Jolla, CA; 32°51´56.8"N: 117° 15´38.48"W; 275 m offshore) on 9/10/13 18:00.
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The ocean seawater chlorophyll-a concentration, water temperature, and salinity were 2.9
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mg/m3, 19.9 °C, and 33.5 PSU at the time of collection. The seawater was added to a 100
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L MART system without treatment or filtering and allowed to equilibrate to room
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temperature. Details of particle generation and phytoplankton bloom initiation have been
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discussed extensively previously, however a brief summary is given here.26 Beginning on
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9/11/2013, SSA particles were generated in the MART using the pulsed plunging
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waterfall technique described in detail previously, with a 4 second waterfall duty cycle.
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After initial generation of SSA particles from the untreated seawater, a diatom growth
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medium commonly known as Guillard’s f medium (ProLine Aquatic Ecosystems) (Table
71
S-1) was added to promote phytoplankton growth, and then SSA particles were again
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generated. Phytoplankton growth was also stimulated by high definition fluorescent tubes
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(5700 K, Full Spectrum Solutions, Model #205457) mounted to the MART and operated
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continuously throughout the experiment. After 9/11/2013, SSA particles were not
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produced until 9/16/2013 as the MART water recirculation system has been found to
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inhibit phytoplankton growth during early periods of a phytoplankton bloom. Once a
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threshold chlorophyll-a concentration was reached, SSA particles were generated and
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sampled daily. Silica gel diffusion dryers were utilized to reduce the relative humidity of
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the sampled air to ~15%.
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Measurement of Bulk Seawater Biological Activity
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Bulk seawater was collected daily from the MART. In vivo measurements of
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chlorophyll-a fluorescence were made immediately after collection using a custom built,
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portable fluorometer calibrated using chlorophyll-a from Anacystis nidulans (Sigma
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Aldrich, C6144) in acetone. Water for DOC analysis was filtered (0.7 µm Whatman GF/F,
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Z242489) into cleaned and combusted 40 mL glass vials and then immediately acidified
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with two drops of trace metal-free 12N HCl to an approximate pH of 2. Samples were
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stored protected from light at room temperature until analysis using the high-temperature
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combustion method (Shimadzu Instruments). Heterotrophic bacteria were enumerated via
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flow cytometry (Beckman-Coulter Altra) stained with Hoechst 34442 (1 µg/ml, final
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concentration) (Method S-1).
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Measurement of SSA Composition via ATOFMS
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ATOFMS was utilized to measure in real time the size-resolved chemical
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compositions of dried individual SSA particles with vacuum aerodynamic diameters (dva)
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between 0.5 – 4.5 µm. Detailed descriptions of ATOFMS have been published previously
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and only a brief discussion is given here. Aerosol particles are drawn into the instrument
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through a converging nozzle inlet and accelerated to their size-dependent terminal
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velocities. Aerosol particles transit two continuous wave laser beams (532 nm) and the
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calculated particle velocity is converted to vacuum aerodynamic diameter. A Q-switched
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Nd:YAG laser pulse (266 nm wavelength, 8 ns, 700 µm spot size,) desorbs and ionizes
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each particle’s chemical components which are then detected by a dual-polarity reflectron
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time-of-flight mass spectrometer. A laser pulse energy (LPE) of 1.1-1.3 mJ was utilized
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every day of SSA sampling. In addition on specific days throughout the bloom the energy
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of the laser pulse energy was varied between 0.2-1.2 mJ.
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Summary of Single Particle Data Analyses
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A total of 453,217 mass spectra were collected over the course of the experiment.
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All ATOFMS single particle data were imported into MATLAB and analyzed using a
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Flexible Analysis Toolkit for the Exploration of SPMS data (FATES).27 Peak
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assignments were made referencing the current literature and correspond to the most
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likely ion produced at a specific mass-to-charge ratio (m/z). No clustering algorithms
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were used to group data, rather the data set was visually explored at the single particle
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mass spectral level utilizing guiFATES, a user-guided visual analytical graphical user
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interface within FATES. Utilizing this tool, a set of MS was identified with signatures
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similar to previous detailed descriptions of terrestrial bacterial SPMS mass spectra.19,28–32
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Based on the characteristics of these initially identified MS, a decision tree was
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developed (Figure S-1) to objectively discriminate a narrow set of ion signatures
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generated by likely microbe or microbe-fragment containing particles (BioSS) from the
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greater SSA population. Markers for potassium (39K+), phosphate (63PO2-, 79PO3-),
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organic nitrogen (74N(CH3)4+, 146C5H8NO4-, -66), and organic (m/z -40, -41) species, all
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detected previously in cellular SPMS ion signatures, were utilized to select for BioSS
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mass spectra. Thresholds for the maximum relative signals from inorganic salt species
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common in seawater, such as magnesium, calcium, sodium, and iron, were set for the
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BioSS class (Figure S-1). The addition of the diatom growth medium immediately
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increased the relative signal from potassium, phosphate, iron, and calcium ion markers,
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but did not discernably influence the relative signals from the organic and organic
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nitrogen ion markers utilized in the discrimination of BioSS (Figures S-2, S3). The
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number fractions of BioSS was 0.014±0.03 and 0.011±0.03 (standard error calculated
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assuming a binomial distribution) before and after the growth medium addition,
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respectively. Thus, the BioSS class as defined successfully discriminated against
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potassium and phosphate-rich MS generated directly by the addition of growth medium.
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Total positive ion intensity represents the sum of all positive ion signals for a
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single mass spectrum from 0 to 300 m/z, and is reported on an arbitrary scale of 0 to 100.
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To generate relative ion values, positive and negative MS were normalized separately by
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either the total positive or total negative ion intensity, respectively. Relative ion signals
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that were utilized to bin MS are listed in Table S-2.
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RESULTS and DISCUSSION
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Description of SSA Microbial Mass Spectra (BioSS)
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Using the criteria described in the last section and Figure S-1, MS likely produced
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by microbial, microbe-containing, or microbe-fragment containing SSA particles (BioSS)
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were identified within the SSA population based upon close similarity to previous
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descriptions of cellular spectra generated from SPMS studies of nebulized terrestrial
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bacteria.19,28–32 For simplicity, throughout this work “microbe-containing particle” is
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utilized to refer to particles with both intact cells or cell fragments. The term “marine
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microbes” encompasses a diverse range of species including viruses, heterotrophic
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bacteria, cyanobacteria, and eukaryotes. While strong potassium and phosphate ion
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signals are ubiquitous in microbial SPMS mass spectra, it is important to note that the
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complete ion signatures for terrestrial and marine microbial SPMS mass spectra exhibit
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wide variations.17–19,32 As such, it is likely that some ion signatures generated from
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ejected marine microbes may fall outside the BioSS class as defined in this study.
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Over the course of the experiment, only ~2% of all SSA mass spectra were
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classified as BioSS, reaching a maximum of ~14% on 9/17/2013 and then falling and
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remaining below 1% after 9/22/2013. All BioSS identified had significant signals from
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phosphate (63PO2-,79PO3-, 97H2PO4-) and potassium (39,41K+). Most also had 42CNO-, 26CN-,
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and
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important to note that in this work, BioSS is treated as a single particle type generated by
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a population of microbe-containing particles. However a great deal of variation between
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the MS exists. Two characteristic MS illustrating the range of BioSS signatures are
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shown in Figure 1. These should not be considered representative of distinct particle
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types but rather the two extremes of a continuum of BioSS mass spectra (Figure S-4). A
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detailed list of common ion markers is provided in Table S-3. To help eliminate noise,
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these MS are made up of an average of 28 (Figure 1a) and 64 (Figure 1b) single particle
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mass spectra.
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35,37
Cl- ion markers with a range in signal responses from additional ions. It is
In Figure 1a, the BioSS signature is characterized by intense signals from
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129,131,133
MgCl3- and relatively large organic nitrogen markers (90C4N3-, 107C4N4H3-,
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117
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which in prior studies have been assigned to the ionization of amino acids.19,28,29
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Additional signal from ion markers -66 and -71 are present which have been noted in
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single cell SPMS studies, but not specifically assigned.21,28,29,31 In some cases, BioSS
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were identified with a positive ion mass spectrum, very similar to Figure 1a but lacking
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negative ion signal. The BioSS signature in Figure 1b is characterized by relatively more
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intense signals from 42CNO-, 26CN- and ion markers -40, -41, -64, and -65 in the negative
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mass spectrum but with diminished signals from -129,131,133MgCl3-, 97H2PO4-, and most
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other positive and negative organic ion markers detailed in Figure 1a. Single particle
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mass spectra similar to Figure 1b consistently generate a set of well-correlated (Figure S-
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5) low intensity positive ion markers (104, 120, 141, 157, 175, 197, 213, 224, 275) some
C5N4H-, 146C5H8NO4-, 59N(CH3)3+, 74N(CH3)4+) in both the positive and negative MS
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of which have been assigned (104K2CN+,120K2CNO+) or noted (157, 175, 213) previously.
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28,29,32–34
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detritus35 lack signals from chlorine ions or chlorine-containing ion clusters except when
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cultured in salt rich media or aerosolized from a salt solution.17,18 Almost all BioSS
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identified in this study contained signal from 35,37Cl- and many also had signals from
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chlorine-containing ion clusters such as 129,131,133MgCl3-, 223,225,227,229Mg2Cl5-, 81,83Na2Cl+,
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and 113,115K2Cl+. This suggests that signals from chlorine-containing ions could be unique
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markers used to distinguish ocean-derived from terrestrial microbial spectra in marine
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influenced air masses. However, atmospheric processing of sea spray aerosols can lead to
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chloride depletion within the particle,36,37 so these ion markers may potentially only be
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generated by freshly produced microbe-containing SSA particles.
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BioSS and Particle Size Dependence
All previously reported SPMS analyses of standards of microbial cells and plant
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The number fraction of BioSS categorized particles relative to all MS generating
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particles increased with size, growing over an order of magnitude from 0.2% (0.5-1 µm)
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to 12% (4-4.5 µm) over the size range of the ATOFMS (Figure S-6). This is consistent
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with field measurements which have detected bacteria predominantly in large
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supermicron SSA particles.38 The authors know of no quantitative comparisons of
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bacterial ejection rates from water into droplets within the size range of the ATOFMS.
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However, published bacterial enrichment factors plummet exponentially from 50 to 20
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µm in wet droplets generated by bubble bursting.7,6 It is hypothesized that with
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continuing decreasing droplet size microbes will continue to be less effectively
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transferred into the aerosol phase due to the physical mechanism of SSA production.5
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For comparison, the size dependent number fraction was also calculated for all
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remaining particles, excluding BioSS, with at least 0.05 or 0.1 relative ion signals from
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both potassium (39K+) and phosphate (79PO3-+63PO2-), referred to as KPhos5 or KPhos10
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classes, respectively. These are similar phosphate and potassium thresholds that are
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utilized in combination with an array of organic nitrogen markers to define BioSS (Figure
203
S-1). Representative MS for all non-BioSS classes are provided in Figure S-7 and S-8.
204
KPhos5 and KPhos10 made up 16% and 5% of all SSA mass spectra, and the number
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fraction for these potassium and phosphate-rich particles remains flat over the instrument
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size range (Figure S-6). The number fraction for KPhos5 mass spectra with also 0.05
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relative ion signal from the sum of 26CN- and 42CNO-, markers for organic nitrogen that
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have been previously utilized to classify biological particles,23,24,39 also did not increase
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with size. While common in BioSS mass spectra, 26CN- and 42CNO- ion markers were not
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utilized to define this class. Because these non-BioSS classes do not display any size
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dependence, it suggests the chemical components generating the phosphate, potassium,
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and organic nitrogen ion signals were transferred as dissolved species from the seawater
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into the aerosol phase rather than associated with cells or particulates.
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The number fraction for KPhos10 mass spectra with at least 0.1 relative ion signal
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from the sum of organic nitrogen ion markers, 26CN- and 42CNO-, did increase with size
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from 0.5 to 3 µm, though this class only made up ~0.1% of all SSA mass spectra. These
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MS are potentially microbial, however most were excluded from BioSS because their
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iron or calcium signal exceeded the maximum thresholds (Figure S-1) implemented to
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eliminate the influence of the diatom growth medium addition. As discussed in the
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following section, the overall BioSS ion signatures are highly dependent on the total
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positive ion intensity (TPII). For this reason, applying a simple threshold, which appears
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to discriminate effectively against the majority of generic SSA mass spectra, does not
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effectively capture the BioSS class. For BioSS with relatively high TPII (>40), 70% of
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the MS had potassium (39K+), organic nitrogen (26CN-+42CNO-), and phosphate (63PO2-
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+79PO3-) relative ion signals all greater than 0.1. However, only 30% of BioSS with
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relatively low TPII met these thresholds. This is the first utilization of particle size in
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SPMS analysis to distinguish between SSA-containing particulates versus dissolved ions.
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The novel results stemming from this approach highlight the importance of careful data
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treatment when trying to identify cellular spectra within a SSA or marine aerosol
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population. Even relatively strong signals from ion markers such as
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and
232
markers are extremely common in SSA populations (Figure S-9).
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Dependence of SSA BioSS Signatures on Total Ion Intensity and Laser Pulse Energy
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SPMS studies of well-characterized and chemically and morphologically uniform
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aerosol particles have illustrated how differences in laser fluence yield variations in mass
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spectral signatures due to changes in both the ionization processes and the degree of
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particle desorption.40–43 For particles with similar composition, the total ion intensities of
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MS generally increase when particles encounter higher laser fluence.40,42 However,
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analyses utilizing total ion signal or variable laser pulse energies have never been
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leveraged previously to help discriminate or confirm a distinct particle type within a
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larger chemically complex aerosol population. Due to the nominally Gaussian beam
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profile and hot spots in the desorption/ionization laser utilized in this study,17,42 the laser
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fluence that each particle experiences upon ionization is variable even when the total
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pulse energy is relatively constant.
39
K+,
PO3-,
79
26
CN-
42
CNO- cannot be used solely as indicating a microbial ion signature, as these ion
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All BioSS identified for the entire experiment, generated at 1.22+-0.04 mJ laser
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pulse energy, were grouped by TPII. Subsequently, the distributions of relative ion
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signals for a variety of m/z (Table S-2) were calculated for all BioSS within these TPII
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bins (Figure 2 and Figure S-10). While this analysis utilizes TPII as a proxy for laser
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fluence, this assumption was further confirmed by directly varying the laser pulse energy
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from 0.2 to 1.2 mJ on September 17th. BioSS were binned based upon relative signals
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from the ions previously described. The results for the lowest (0.21+-0.03) and highest
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(1.28+-0.06) laser pulse energies are shown in Figure 3 and for all laser pulse energies in
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Figure S-11. Except for m/z -90, the distribution of all relative ion signals examined for
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the low and high pulse energies mimics the distribution for the low and high ion
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intensities respectively. This supports the use of total positive ion signal as a proxy for
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laser fluence for BioSS.
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BioSS with low (0-5) TPII or generated utilizing using low laser pulse energy
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more frequently have high relative ion signals from m/z +74 (74N(CH3)4+), -90 (90C4N3-),
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and -146 (146C5H8NO4-) compared to BioSS with high (35-100) TPII (Figure 2a-c) or
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generated with high pulse energy (Figure 3a-c). The opposite trend is observed for the
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sum of m/z -26 and -42 (26CN-, 42CNO-), -66, and the sum of +104 and +120 (104K2CN+,
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120
263
total ion intensity compared to low total ion intensity (Figure 2d-f and Figure 3d-f). It is
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likely that trends in these ion markers, indicative of amino acids, with respect to laser
265
fluence are simply a result in changes in the fragmentation of the molecules, rather than
266
illustrative of differences in the chemical species desorbed from the particle.31,44 The
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trends in most of the relative ion signals described here (m/z +74, -26, -42, -66, -90, -146)
K2CNO+) for which large relative ion signals are more common for BioSS with high
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can be directly compared to and are entirely consistent with prior reports on the influence
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of laser fluence on bacterial cell single particle mass spectra and further confirm BioSS as
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indeed generated from microbial containing particles.30,31
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Utilizing BioSS Signatures and Total Ion Intensity to Probe the Structure of
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Microbe-Containing SSA Particles
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BioSS mass spectral signals due to -Mg negative ion clusters (129,131,133MgCl3,
-
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223,225,227,229
Mg2Cl5), -Cl (35,37Cl-), and +Na (23Na+,46Na2, 81,83Na2Cl+, 139,141,143Na2Cl+) ion
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markers also had a strong dependence on total positive ion intensity and laser pulse
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energy. BioSS with low TPII more frequently had high (>0.15) relative signal from -Mg
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negative ion clusters. In contrast, at very high TPII (>75) the number fraction of +Na and
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-Cl-rich (>0.15) MS making up BioSS increased dramatically (Figure 4a). While
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chlorine-containing ion markers (35,37Cl-, 129,131,133MgCl3, -223,225,227,229Mg2Cl5, 81,83Na2Cl+)
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have never been noted in microbial or biological SPMS mass spectra, except when
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cultured in salt rich media, they are common in SSA mass spectra.26,45,46 This suggests
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that these inorganic ion signals largely originate from chemical species present in the
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microbe-containing SSA particle but are not the ion signature generated by the microbial
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cell. It has been frequently noted that the laser pulse energies commonly utilized in
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SPMS result in incomplete desorption of supermicron particles.43,47–51 The BioSS total
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ion intensity distribution is similar across the ATOFMS size range (0.5-4.5 µm) and only
287
shifts slightly to higher values with increasing size (Figure 4b). Assuming spherical
288
particles and complete particle desorption and ionization, the total ion intensity should
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have a third order dependence on diameter, which would result in a 700-fold increase in
290
ion yield from 0.5 to 4.5 µm (dva). The minimal increase in ion yield with particle
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diameter suggests that desorption of biological SSA particles is not complete over the
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range of laser fluences used in this study.
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Coupling the trends in total ion intensity and -Mg, -Cl, and +Na ion signals
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allows us to offer a conceptual picture of the structure of BioSS SSA particles. First, it is
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well documented that dried seawater and model salt solution droplets exhibit a chemical
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spatial heterogeneity with a core rich in sodium chloride while the outer layer is enriched
297
in organics and all minor inorganic components.52–58 Microbes are likely ejected in
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droplets of seawater, that upon drying will chemically segregate in the same manner with
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microbes adhered to sodium chloride rich nodes, surrounded by a magnesium-rich
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coating. Theoretical studies of laser desorption/ionization processes indicate that
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desorption propagates from the surface of the laser illuminated particle face.59,60
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Therefore if desorption of the microbe-containing SSA particle is incomplete, the
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orientation of the particle within the laser beam will affect the mass spectrum generated.
304
The laser beam could hypothetically illuminate the microbe face of the particle and
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generate little to no signal from sodium chloride in the shadow of the microbe. BioSS
306
would only have relatively more intense signal from sodium chloride when much more
307
complete desorption and ionization of the total particle occurs generating higher ion
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yields. In addition when very low degrees of desorption and ionization occurs, the mass
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spectrum could be rich in signal from the magnesium abundant coating relative to signal
310
associated with ionization of the microbial cell. This is in good agreement with previous
311
studies of supermicron SSA particles; low laser pulse energies generate low intensity MS
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with high magnesium signal relative to sodium due to the enrichment of magnesium at
313
the particle surface and concentration of sodium within the core.61,62
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While there is strong evidence that BioSS identified in this study are generated by
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microbe-containing SSA particles, it is apparent that the BioSS mass spectral class
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represents a continuum which at the extremes is increasingly similar to either very lightly
317
are strongly desorbed typical SSA particles composed largely of sea salts and dissolved
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organic species. For this study, explicit limitations (Figure S-1) on contributions from
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typical sea salt species such as sodium and magnesium were subjectively chosen for the
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BioSS class. Future studies will focus on refining the structural paradigm above to more
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conclusively understand variability of the inorganic composition and resultant ion signals
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for marine microbes.32,63–65 However, the model presented here is the first to illustrate
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that many microbe-containing SSA particles may generate MS with little to no microbial
324
ion signatures. Therefore, the number fraction of BioSS likely represents a lower bound
325
for the total number of microbe-containing SSA particles.
326
Influence of Seawater Chemistry on BioSS signatures
327
The fraction of BioSS was determined over the course of the phytoplankton
328
bloom and found to reach a maximum (~14%) close to the first peak in both the
329
heterotrophic bacteria and chlorophyll-a and before the rise in total organic carbon in
330
seawater (Figure 5). Previous studies of SSA particles generated during phytoplankton
331
blooms show that as the bloom progresses and the dissolved organic carbon content
332
increases in seawater, dry supermicron SSA particles show increasingly thick organic and
333
magnesium-rich coatings surrounding sodium chloride cores.26,46 More detailed
334
descriptions on the influence of induced phytoplankton blooms on the chemistry of the
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broader SSA population can be found in previous publications.26,66–69 ATOFMS data in
336
this study indicate that the magnesium-rich coatings, proposed in the previous section to
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coat the biological SSA particles, also increased in thickness over the course of the
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phytoplankton bloom. As already noted, BioSS with high -Mg (129,131,133MgCl3,
339
223,225,227,229
340
the phytoplankton bloom progressed the fraction of -Mg-rich (>0.15) BioSS increased.
341
Also for each day, BioSS mass spectra were grouped by TPII and the number fraction of
342
-Mg-rich BioSS, within each TPII range, was calculated and normalized by the maximum
343
-Mg-rich number fraction each day. This distribution for -Mg-rich BioSS shifted to higher
344
TPII values over the course of the experiment (Figure 5). Higher total positive ion
345
intensities of -Mg-rich BioSS suggest that more of the magnesium-rich coating had to be
346
desorbed and ionized before reaching the microbial cell. This also suggests that very
347
thick organic and magnesium coatings of dry microbe-containing SSA particles could
348
possibly prevent the generation of recognizable BioSS signatures. This consideration is
349
more critical in the examination of dense laboratory generated phytoplankton blooms
350
where the dissolved organic carbon content of the seawater is much higher than
351
commonly found in the natural marine environment.
-
Mg2Cl5) relative signal generally had relatively low total ion intensities. As
352 353
CONCLUSION
354
Identification and quantification of microbes originating from seawater will allow
355
future studies to better understand their role as ice nuclei within clouds. However, while
356
it has been shown that microbes are ejected in sea spray aerosols,1–7 MS with
357
characteristic microbial signatures have never been uniquely identified within SPMS SSA
358
datasets. This is the first report to distinguish BioSS, likely microbe MS, from the
359
abundant SSA mass spectra with significant potassium and phosphate ion signals likely
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resultant from dissolved chemical species. Reported in this study is an array of
361
identifying size and mass spectral characteristics for SSA BioSS that will support the
362
identification of microbe and microbe fragment-containing SSA particles in future
363
laboratory and field studies. We utilize these ATOFMS results to propose that dry SSA
364
generating BioSS are likely particles containing a microbial cell adhered to a sodium
365
chloride node encompassed by a magnesium-rich coating. Such in situ descriptions of
366
microbial SSA are rare as details of the structure of SSA are lost utilizing impinger or
367
filter collection techniques commonly employed with offline analysis of aerosolized
368
microbes. Finally, the chlorine and chlorine-containing ion clusters ubiquitous in the SSA
369
BioSS population are the first ion markers proposed to be useful in distinguishing
370
terrestrial from ocean-derived aerosolized microbes in marine influenced air masses.
371
In addition the analytical techniques applied herein while specifically employed
372
for the identification of microbe-containing SSA particles could be applied to the wider
373
examination of SSA, ambient, and other chemically complex aerosol populations. Our
374
work suggests that particle size can be utilized to help discriminate mass spectral types
375
generated by SSA containing insoluble residues beyond microbes, such as dust or soot. In
376
addition we introduce mass spectral signature dependence on total ion intensity as a
377
useful tool to support the classification of distinct particle types within a realistic mixed
378
aerosol population. This technique is especially valuable as it can be applied to existing
379
SPMS datasets and does not require explicit variable laser pulse energy experiments. The
380
expansion of SPMS data analyses beyond the grouping of particles by comparison of
381
mass spectral signatures could not only improve the robustness of scientific conclusions
382
but also expand the limits of knowledge discovery within the field.
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ASSOCIATED CONTENT
384
Supporting Information Online location of data set; Details on the flow cytometry
385
method; Concentration of nutrients added to the MART; m/z values used in the ion signal
386
analysis; Ion markers common to the representative MS in Figure 1; Decision tree
387
utilized to discriminate BioSS; Average MS before and after growth medium addition;
388
Relative ion signal distribution before and after growth medium additions; Continuum of
389
BioSS single particle MS; Covariance matrix for BioSS positive ion signals; Number
390
fraction of particle types by size; Representative MS of Kphos (not BioSS); Scatter plot
391
of phosphate and potassium ion signal; Distribution of relative ion signals for BioSS
392
grouped by total ion intensity; Distribution of relative ion signals for BioSS grouped by
393
laser pulse energy.
394
AUTHOR INFORMATION
395
Corresponding Author
396
*Phone: +1 858 822 5312. E-mail:
[email protected].
397
ACKNOWLEDGEMENTS
398
This work was supported by the National Science Foundation through the Centers of
399
Chemical Innovation Program via the Center for Aerosol Impacts on Chemistry of the
400
Environment (CHE-1305427). The authors would like to thank all collaborators involved
401
in the MART microcosm study, notably C. Lee and D. B. Collins. The authors would also
402
like to thank Grant Deane for helpful discussions.
403
REFERENCES
404 405
(1)
Aller, J. Y.; Kuznetsova, M. R.; Jahns, C. J.; Kemp, P. F. J. Aerosol Sci. 2005, 36, 801–812.
406 407
(2)
Hultin, K. A. H.; Krejci, R.; Pinhassi, J.; Gomez-Consarnau, L.; Mårtensson, E. M.; Hagström, Å.; Nilsson, E. D. Atmos. Res. 2011, 99, 1–14.
18
ACS Paragon Plus Environment
Page 18 of 29
Page 19 of 29
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
408
(3)
Leck, C.; Bigg, E. K. Tellus 2005, 57B, 305–316.
409 410 411 412
(4)
Patterson, J. P.; Collins, D. B.; Michaud, J. M.; Axson, J. L.; Sultana, C. M.; Moser, T.; Dommer, A. C.; Conner, J.; Grassian, V. H.; Stokes, M. D.; Deane, G. B.; Evans, J. E.; Burkart, M. D.; Prather, K. A.; Gianneschi, N. C. ACS Cent. Sci. 2016, 2, 40–47.
413
(5)
Blanchard, D. C. Estuaries 1989, 12, 127–137.
414
(6)
Blanchard, D. C.; Syzdek, L. D. J. Geophys. Res. 1972, 77, 5087.
415
(7)
Bexdek, H. F.; Carhcci, A. F. Limnol. Oceanogr. 1972, 17, 566–569.
416 417 418 419 420 421 422
(8)
DeMott, P. J.; Hill, T. C. J.; McCluskey, C. S.; Prather, K. A.; Collins, D. B.; Sullivan, R. C.; Ruppel, M. J.; Mason, R. H.; Irish, V. E.; Lee, T.; Hwang, C. Y.; Rhee, T. S.; Snider, J. R.; McMeeking, G. R.; Dhaniyala, S.; Lewis, E. R.; Wentzell, J. J. B.; Abbatt, J.; Lee, C.; Sultana, C. M.; Ault, A. P.; Axson, J. L.; Diaz Martinez, M.; Venero, I.; Santos-Figueroa, G.; Stokes, M. D.; Deane, G. B.; Mayol-Bracero, O. L.; Grassian, V. H.; Bertram, T. H.; Bertram, A. K.; Moffett, B. F.; Franc, G. D. Proc. Natl. Acad. Sci. 2015, 113, 5797–5803.
423
(9)
Knopf, D. A.; Alpert, P. A.; Wang, B.; Aller, J. Y. Nat. Geosci. 2011, 4, 88–90.
424 425 426 427 428 429
(10)
Wilson, T. W.; Ladino, L. A.; Alpert, P. A.; Breckels, M. N.; Brooks, I. M.; Browse, J.; Burrows, S. M.; Carslaw, K. S.; Huffman, J. A.; Judd, C.; Kilthau, W. P.; Mason, R. H.; McFiggans, G.; Miller, L. A.; Nájera, J. J.; Polishchuk, E.; Rae, S.; Schiller, C. L.; Si, M.; Temprado, J. V.; Whale, T. F.; Wong, J. P. S.; Wurl, O.; Yakobi-Hancock, J. D.; Abbatt, J. P. D.; Aller, J. Y.; Bertram, A. K.; Knopf, D. A.; Murray, B. J. Nature 2015, 525, 234–238.
430
(11)
Schnell, R. C. J. Atmos. Sci. 1977, pp 1299–1305.
431
(12)
Junge, K.; Swanson, B. D. Biogeosciences Discuss. 2007, 4, 4261–4282.
432
(13)
Fall, R.; Schnell, R. C. J. Mar. Res. 1985, 43, 257–265.
433 434
(14)
Bassett, D. R.; Boucher, E. A.; Zettlemoyer, A. C. J. Colloid Interface Sci. 1970, 34, 436–446.
435 436
(15)
Gavish, M.; Popovitz-biro, R.; Lahav, M.; Leiserowitz, L. Science. 1990, 250, 973–975.
437 438
(16)
Cziczo, D. J.; Froyd, K. D.; Gallavardin, S. J.; Moehler, O.; Benz, S.; Saathoff, H.; Murphy, D. M. Environ. Res. Lett. 2009, 4, 44013.
439 440
(17) Cahill, J. F. Novel techniques and applications in single particle mass spectrometry, University of California, San Diego, 2014.
441 442 443
(18)
Gaston, C. J. Direct Measurements of Marine Aerosols to Examine the Influence of Biological Activity, Anthropogenic Emissions, and Secondary Processing on Particle Chemistry, University of California, San Diego, 2012.
444 445 446 447
(19)
Fergenson, D. P.; Pitesky, M. E.; Tobias, H. J.; Steele, P. T.; Czerwieniec, G. a; Russell, S. C.; Lebrilla, C. B.; Horn, J. M.; Coffee, K. R.; Srivastava, A.; Pillai, S. P.; Shih, M.-T. P.; Hall, H. L.; Ramponi, A. J.; Chang, J. T.; Langlois, R. G.; Estacio, P. L.; Hadley, R. T.; Frank, M.; Gard, E. E. Anal. Chem. 2004, 76, 373– 19
ACS Paragon Plus Environment
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
448
378.
449 450
(20)
Cziczo, D. J.; Froyd, K. D.; Hoose, C.; Jensen, E. J.; Diao, M.; Zondlo, M. a; Smith, J. B.; Twohy, C. H.; Murphy, D. M. Science. 2013, 340, 1320–1324.
451 452 453
(21)
Russell, S. C.; Czerwieniec, G.; Lebrilla, C.; Tobias, H.; Fergenson, D. P.; Steele, P.; Pitesky, M.; Horn, J.; Srivastava, A.; Frank, M.; Gard, E. E. J. Am. Soc. Mass Spectrom. 2004, 15, 900–909.
454
(22)
Holecek, J. C.; Spencer, M. T.; Prather, K. A. J. Geophys. Res. Atmos. 2007, 112.
455 456
(23)
Creamean, J. M.; Lee, C.; Hill, T. C.; Ault, A. P.; DeMott, P. J.; White, A. B.; Ralph, F. M.; Prather, K. A. J. Aerosol Sci. 2014, 76, 13–27.
457 458 459
(24)
Creamean, J. M.; Suski, K. J.; Rosenfeld, D.; Cazorla, A.; Demott, P. J.; Sullivan, R. C.; White, A. B.; Ralph, F.; Minnis, P.; Comstock, J. M.; Tomlinson, J. M.; Prather, K. A. Science (80-. ). 2013, 339, 1572–1578.
460 461
(25)
Pratt, K. A.; DeMott, P. J.; French, J. R.; Wang, Z.; Westphal, D. L.; Heymsfield, A. J.; Twohy, C. H.; Prenni, A. J.; Prather, K. A. Nat. Geosci. 2009, 2, 398–401.
462 463 464
(26)
Lee, C.; Sultana, C. M.; Collins, D. B.; Santander, M. V; Axson, J. L.; Malfatti, F.; Cornwell, G. C.; Grandquist, J. R.; Deane, G. B.; Stokes, M. D.; Azam, F.; Grassian, V. H.; Prather, K. A. J. Phys. Chem. A 2015, 119, 8860–8870.
465 466
(27)
Sultana, C. M.; Cornwell, G.; Rodriguez, P.; Prather, K. A. Atmos. Meas. Tech. Discuss. 2016, No. October, 1–18.
467 468 469
(28)
Czerwieniec, G. A.; Russell, S. C.; Tobias, H. J.; Pitesky, M. E.; Fergenson, D. P.; Steele, P.; Srivastava, A.; Horn, J. M.; Frank, M.; Gard, E. E.; Lebrilla, C. B. Anal. Chem. 2005, 77, 1081–1087.
470 471 472
(29)
Srivastava, A.; Pitesky, M. E.; Steele, P. T.; Tobias, H. J.; Fergenson, D. P.; Horn, J. M.; Russell, S. C.; Czerwieniec, G. a; Lebrilla, C. B.; Gard, E. E.; Frank, M. Anal. Chem. 2005, 77, 3315–3323.
473 474 475
(30)
Steele, P. T.; Tobias, H. J.; Fergenson, D. P.; Pitesky, M. E.; Horn, J. M.; Czerwieniec, G. a; Russell, S. C.; Lebrilla, C. B.; Gard, E. E.; Frank, M. Anal. Chem. 2003, 75, 5480–5487.
476 477
(31)
Steele, P. T.; Srivastava, A.; Pitesky, M. E.; Fergenson, D. P.; Tobias, H. J.; Gard, E. E.; Frank, M. Anal. Chem. 2005, 77, 7448–7454.
478 479
(32)
Tobias, H. J.; Pitesky, M. E.; Fergenson, D. P.; Steele, P. T.; Horn, J.; Frank, M.; Gard, E. E. J. Microbiol. Methods 2006, 67, 56–63.
480 481
(33)
Silva, P. J.; Prather, K.; Noble, C. A.; Prather, K. A. Environ. Sci. Technol. 1999, 33, 3068–3076.
482
(34)
Russell, S. C. Mass Spectrom. Rev. 2009, 28, 376–387.
483 484 485
(35)
Silva, P. J. Source Profiling and Apportionment of Airborne Particles: A New Approach Using Aerosol Time-of-Flight Mass Spectrometry, University of California, Riverside, 2000.
486
(36)
Abbatt, J. P. D.; Lee, A. K. Y.; Thornton, J. A. Chem. Soc. Rev. 2012, 41, 6555–
20
ACS Paragon Plus Environment
Page 20 of 29
Page 21 of 29
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
487
6581.
488 489 490
(37)
491 492
(38) Dueker, M. E.; Weathers, K. C.; O’Mullan, G. D.; Juhl, A. R.; Uriarte, M. Environ. Sci. Technol. 2011, 45, 3386–3392.
493 494
(39)
Zawadowicz, M. A.; Froyd, K. D.; Murphy, D. M.; Cziczo, D. J. Atmos. Chem. Phys. 2017, 17, 7193–7212.
495 496
(40)
Zelenyuk, A.; Juan, Y.; Chen, S.; Zaveri, R. A.; Imre, D. J. Phys. Chem. A 2008, 112, 669–671.
497
(41)
Cai, Y.; Zelenyuk, A.; Imre, D. Aerosol Sci. Technol. 2006, 40, 1111–1122.
498 499
(42)
Wenzel, R. J.; Prather, K. A. Rapid Commun. Mass Spectrom. 2004, 18, 1525– 1533.
500 501
(43)
Weiss, M.; Verheijen, P. J. T.; Marijnissen, J. C. M.; Scarlett, B. J. Aerosol Sci. 1997, 28, 159–171.
502 503 504
(44)
Steele, P. T.; Tobias, H. J.; Fergenson, D. P.; Pitesky, M. E.; Horn, J. M.; Czerwieniec, G. A.; Russell, S. C.; Lebrilla, C. B.; Gard, E. E.; Frank, M. Anal. Chem. 2003, 75, 5480–5487.
505 506 507
(45)
Gaston, C. J.; Furutani, H.; Guazzotti, S. A.; Coffee, K. R.; Bates, T. S.; Quinn, P. K.; Aluwihare, L. I.; Mitchell, B. G.; Prather, K. A. J. Geophys. Res. 2011, 116, D18310.
508 509 510 511 512 513 514 515
(46)
Prather, K. A.; Bertram, T. H.; Grassian, V. H.; Deane, G. B.; Stokes, M. D.; Demott, P. J.; Aluwihare, L. I.; Palenik, B. P.; Azam, F.; Seinfeld, J. H.; Moffet, R. C.; Molina, M. J.; Cappa, C. D.; Geiger, F. M.; Roberts, G. C.; Russell, L. M.; Ault, A. P.; Baltrusaitis, J.; Collins, D. B.; Corrigan, C. E.; Cuadra-Rodriguez, L. a; Ebben, C. J.; Forestieri, S. D.; Guasco, T. L.; Hersey, S. P.; Kim, M. J.; Lambert, W. F.; Modini, R. L.; Mui, W.; Pedler, B. E.; Ruppel, M. J.; Ryder, O. S.; Schoepp, N. G.; Sullivan, R. C.; Zhao, D. Proc. Natl. Acad. Sci. U. S. A. 2013, 110, 7550– 7555.
516
(47)
Carranza, J. E.; Hahn, D. W. Anal. Chem. 2002, 74, 5450–5454.
517 518
(48)
Vera, C.; Trimborn, A.; Hinz, K.; Spengler, B. Rapid Commun. Mass Spectrom. 2005, 19, 133–146.
519 520
(49)
McJimpsey, E. L.; Jackson, W. M.; Lebrilla, C. B.; Tobias, H.; Bogan, M. J.; Gard, E. E.; Frank, M.; Steele, P. T. J. Am. Soc. Mass Spectrom. 2008, 19, 315–324.
521 522
(50)
Dall’Osto, M.; Harrison, R. M.; Beddows, D. C. S.; Freney, E. J.; Heal, M. R.; Donovan, R. J. Environ. Sci. Technol. 2006, 40, 5029–5035.
523 524
(51)
Wade, E. E.; Farquar, G. R.; Steele, P. T.; McJimpsey, E. L.; Lebrilla, C. B.; Fergenson, D. P. J. Aerosol Sci. 2008, 39, 657–666.
525 526
(52)
Ault, A. P.; Moffet, R. C.; Baltrusaitis, J.; Collins, D. B.; Ruppel, M. J.; CuadraRodriguez, L. A.; Zhao, D.; Guasco, T. L.; Ebben, C. J.; Geiger, F. M.; Bertram, T.
Gaston, C. J.; Furutani, H.; Guazzotti, S. a.; Coffee, K. R.; Bates, T. S.; Quinn, P. K.; Aluwihare, L. I.; Mitchell, B. G.; Prather, K. a. J. Geophys. Res. 2011, 116, D18310.
21
ACS Paragon Plus Environment
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1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
527
H.; Prather, K. A.; Grassian, V. H. Environ. Sci. Technol. 2013, 47, 5603–5612.
528 529
(53)
Ge, Z. Z.; Wexler, A. S.; Johnston, M. V. J. Colloid Interface Sci. 1996, 183, 68– 77.
530
(54)
Ge, Z.; Wexler, A. S.; Johnston, M. V. J. Phys. Chem. A 1998, 5639, 173–180.
531 532
(55)
Russell, L. M.; Hawkins, L. N.; Frossard, A. A.; Quinn, P. K.; Bates, T. S. Proc. Natl. Acad. Sci. 2010, 107, 6652–6657.
533 534
(56) Xiao, H. S.; Dong, J. L.; Wang, L. Y.; Zhao, L. J.; Wang, F.; Zhang, Y. H. Environ. Sci. Technol. 2008, 42, 8698–8702.
535 536
(57)
Gupta, D.; Eom, H. J.; Cho, H. R.; Ro, C. U. Atmos. Chem. Phys. 2015, 15, 11273–11290.
537 538
(58)
Cziczo, D. J.; Nowak, J. B.; Hu, J. H.; Abbatt, J. P. D. J. Geophys. Res. 1997, 102, 18843.
539 540
(59)
Schoolcraft, T. A.; Constable, G. S.; Zhigilei, L. V; Garrison, B. J. Anal. Chem. 2000, 72, 5143–5150.
541 542
(60)
Schoolcraft, T. A.; Constable, G. S.; Jackson, B.; Zhigilei, L. V; Garrison, B. J. Nucl. Instruments Methods Phys. Res. B 2001, 180, 245–250.
543 544 545
(61)
Ault, A. P.; Guasco, T. L.; Ryder, O. S.; Baltrusaitis, J.; Cuadra-Rodriguez, L. A.; Collins, D. B.; Ruppel, M. J.; Bertram, T. H.; Prather, K. A.; Grassian, V. H. J. Am. Chem. Soc. 2013, 135, 14528–14531.
546 547
(62)
Sultana, C. M.; Collins, D. B.; Prather, K. A. Environ. Sci. Technol. 2017, 51, 3660–3668.
548 549
(63)
Heldal, M.; Norland, S.; Erichsen, E. S.; Sandaa, R.; Larsen, A.; Thingstad, F.; Bratbak, G. ISME J. 2012, 6, 524–530.
550 551
(64)
Heldal, M.; Scanlan, D. J.; Norland, S.; Thingstad, F.; Mann, N. H. Limnol. Ocean. 2003, 48, 1732–1743.
552
(65)
Fagerbakke, K. M.; Norland, S.; Heldal, M. Can. J. Microbiol. 1999, 45, 304–311.
553 554 555
(66)
Forestieri, S. D.; Cornwell, G. C.; Helgestad, T. M.; Moore, K. A.; Lee, C.; Novak, G. A.; Sultana, C. M.; Wang, X.; Bertram, T. H.; Prather, K. A.; Cappa, C. D. Atmos. Chem. Phys. 2016, 16, 9003–9018.
556 557 558 559 560
(67)
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(68) Cochran, R. E.; Laskina, O.; Jayarathne, T.; Laskin, A.; Laskin, J.; Lin, P.; Sultana, C.; Lee, C.; Moore, K. A.; Cappa, C. D.; Bertram, T. H.; Prather, K. A.; Grassian, V. H.; Stone, E. A. Environ. Sci. Technol. 2016, 50, 2477–2486.
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Cochran, R. E.; Laskina, O.; Trueblood, J. V; Estillore, A. D.; Morris, H. S.; Jayarathne, T.; Sultana, C. M.; Lee, C.; Lin, P.; Laskin, J.; Laskin, A.; Dowling, J.
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Figure 1. Two representative dual-polarity mass spectra illustrating the continuum of SSA ion signatures identified as BioSS. Some mass spectra were characterized by (a) a number of relatively intense positive and negative organic nitrogen markers, particularly m/z +59, +74 and -146, or (b) a series of less intense peaks above +100 (highlighted in inset). To help eliminate noise, these are averages of 28 (a) and 64 (b) single particle mass spectra.
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Figure 2
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Figure 2. Distributions of relative ion signals for BioSS with either low (961 total BioSS mass spectra) or high (5253 total BioSS mass spectra) total positive ion intensity. Data is shown for m/z +74 (a), -90 (b), -146 (c), the sum of -26 and -42 (d), -66 (e), and the sum of +104 and +120 (f). Results shown are for all BioSS generated during the experiment with 1.22+-0.04 mJ laser pulse energy.
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Figure 3. Distributions of relative ion signals on September 17th for BioSS generated with either low (130 total BioSS mass spectra) or high (271 total BioSS mass spectra) laser pulse energies. Data is shown for m/z +74 (a), -90 (b), -146 (c), the sum of -26 and 42 (d), -66 (e), and the sum of +104 and +120 (f).
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Figure 4. (a) The fraction of BioSS, grouped by total positive ion intensity (TPII), with large -Cl, +Na, or -Mg relative ion signals. The number of BioSS within each ion intensity range are also shown. (b) The TPII distribution of BioSS grouped by particle diameter. The legend indicates the total number of BioSS particles within each size range. Results shown are for all BioSS generated during the experiment.
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Figure 5. Temporal trends of (a) chlorophyll-a (Chl-a), heterotrophic bacteria (HB), and dissolved organic carbon (DOC) concentrations in seawater as well as (b) the total number of BioSS and number fraction relative to all SSA mass spectra. In addition, for each day (b) the number fraction of -Mg-rich BioSS relative to all BioSS and (c) the number fraction of -Mg-rich BioSS within each total positive ion intensity range, normalized to the maximum -Mg-rich number fraction for each day . Results shown are for mass spectra generated with the ATOFMS operating at 1.22+-0.04 mJ laser pulse energy.
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