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Peroxyacetyl nitrate

Peroxyacetyl nitrate (PAN), chemically denoted as CH₃C(O)OONO₂ or C₂H₃NO₅, is a highly oxygenated, unstable organic compound that serves as a key intermediate in atmospheric . Formed primarily through the reaction of (NO₂) with peroxyacetyl radicals derived from the oxidation of volatile organic compounds (VOCs) such as , , and products of and , PAN acts as a temporary reservoir for reactive oxides (), facilitating their long-range transport in the . With a of 121.05 g/mol and CAS number 2278-22-0, PAN exists as a colorless gas or unstable liquid that decomposes thermally, especially in warmer conditions, releasing NOx and contributing to the formation of tropospheric —a major air pollutant. Its sources are predominantly anthropogenic in urban areas during non-growing seasons and biogenic from vegetation like emissions, with global production dominated by (44%) and (30%) precursors. As a component of photochemical , PAN exhibits phytotoxic effects on plants, inhibiting and causing visible leaf damage, while posing risks to human health as an inhalation toxin and eye irritant, with concentrations typically ranging from 0.3 to 2 ppbv in polluted regions. In colder environments, PAN's stability enhances its role in promoting ozone buildup by sequestering NOx until decomposition, whereas in warmer climates, it acts as a sink, modulating radical cycles and oxidant levels.

Chemical Properties

Molecular Structure

Peroxyacetyl nitrate (PAN) has the molecular formula C₂H₃NO₅ and is structurally represented as CH₃C(O)OONO₂. This molecule consists of an (CH₃CO–) linked to a peroxy bridge (–O–O–) that is bonded to a (–ONO₂), forming the characteristic peroxycarboxyl responsible for its role as a reactive reservoir in the atmosphere. A key feature of PAN's structure is the weak O–N bond in the peroxy nitrate linkage, with a bond dissociation enthalpy of approximately 35 kcal/mol, which contributes to the compound's thermal instability and susceptibility to unimolecular decomposition. Although computational studies have identified up to 11 possible isomeric structures for PAN, including variations in the peroxy-nitrate connectivity, the dominant form observed in atmospheric conditions is the specific CH₃C(O)OONO₂ isomer.

Physical and Thermal Properties

Peroxyacetyl nitrate () appears as an unstable, colorless gas at , though it can be condensed to a under certain conditions. Its molecular formula is C₂H₃NO₅, corresponding to a molecular weight of 121.05 g/. Due to its inherent thermal instability, PAN decomposes prior to boiling, with an extrapolated of approximately 106 °C based on measurements up to 291 K. The at 298 K is 29.2 mm , indicating relatively high volatility under ambient conditions. PAN is moderately soluble in , with a constant of approximately 5 M/atm in acidic aqueous solutions at 298 , and it also dissolves in organic solvents such as , , and . The of proceeds via a unimolecular reaction, primarily yielding (NO₂) and the acetyl peroxy (CH₃C(O)OO•), with the rate constant expressed as k = 4.9 \times 10^{16} \exp\left(-\frac{27.5 \, \text{kcal mol}^{-1}}{RT}\right) s⁻¹ over the range 283–313 . This process underscores PAN's sensitivity to , limiting its stability in warmer environments. Spectroscopically, PAN exhibits characteristic infrared absorption bands useful for its detection and quantification, including a prominent peroxy nitrate (–OONO₂) stretch at 1842 cm⁻¹ with a peak cross-section of 0.74 × 10⁻¹⁸ cm² ⁻¹ at 295 K, alongside bands at 794 cm⁻¹ (C–O stretch), 1163 cm⁻¹ (C–O–O asymmetric stretch), 1302 cm⁻¹ (NO₂ symmetric stretch), and 1741 cm⁻¹ (C=O stretch). In the ultraviolet region, PAN shows absorption cross sections that decrease with wavelength and temperature, enabling atmospheric monitoring via UV with significant bands between 200–300 nm.

Synthesis and Production

Laboratory Synthesis

Peroxyacetyl nitrate (PAN) was first prepared in the laboratory in 1956 by Edgar R. Stephens and colleagues through the photolysis of mixtures containing and olefins in air, where PAN emerged as a key byproduct identified via . This method marked the initial isolation and characterization of PAN, enabling further studies on its role in photochemical reactions. A subsequent routine synthesis, developed in the early , involved the photolysis of vapor in dry oxygen within a reactor under blacklight lamps, producing PAN through sequential radical reactions initiated by the decomposition. This approach yielded approximately 30% PAN based on the consumed, with the product collected as a gas and stored under controlled conditions to prevent . A standard for PAN synthesis entails the reaction of with in the presence of oxygen, often conducted in the dark using (N₂O₅) as a source of NO₃ radicals:
\ce{CH3CHO + NO2 + O2 -> CH3C(O)OONO2}
This multi-step process generates the peroxyacetyl radical intermediate, which combines with NO₂ to form PAN, and has been detailed in mechanistic studies confirming high efficiency under controlled gas-phase conditions without photochemical initiation. Alternative routes include the photochemical oxidation of acetone under in the presence of , such as the photolysis of acetone in synthetic air or mixtures with , which produces PAN via acetyl peroxy radical formation and subsequent . Another variant employs the of (1.2 M) with NO₂, followed by extraction into n-heptane.
Purification of PAN typically involves low-temperature trapping in cold solvents or cryogenic distillation to isolate it from byproducts like , acetic acid, and oxides, leveraging its and thermal lability. Preparative with columns such as carbowax on firebrick is commonly used for final separation, eluting PAN after impurities under flow. Normal-phase provides an additional refinement step for solvent-extracted samples, yielding PAN free of acetyl nitrate contaminants. Due to PAN's and thermal instability, these techniques are performed at sub-zero temperatures to maintain . Laboratory yields for PAN synthesis generally range from 20% to 50%, depending on the method and scale, though optimization is limited by side reactions and precursor purity. Key challenges include PAN's inherent , with reports of detonations during or mechanical shock, necessitating the use of shields, remote handling, and avoidance of or heating during purification and storage. These risks, combined with its sensitivity to trace impurities, demand rigorous protocols in controlled environments to ensure reproducible production for atmospheric and studies.

Atmospheric Formation

Peroxyacetyl nitrate () forms in the primarily through photochemical oxidation of volatile organic compounds (VOCs) in the presence of and sunlight. The process begins with the generation of the acetyl peroxy radical (CH₃C(O)OO•) from the reaction of hydroxyl radicals (OH•) with precursors such as : CH₃CHO + OH• (+ O₂) → CH₃C(O)OO• + H₂O. This radical then reacts reversibly with to produce : CH₃C(O)OO• + NO₂ ⇌ CH₃C(O)OONO₂. The is temperature-dependent, with formation favored under conditions of elevated NO₂ typical of polluted atmospheres. Precursors to the acetyl peroxy radical include both and biogenic VOCs. sources, such as vehicle emissions and combustion, release and other oxygenated VOCs directly into urban air, promoting rapid PAN buildup. Biogenic VOCs like , emitted by , contribute indirectly through oxidation pathways that yield and other intermediates leading to CH₃C(O)OO• production. These combined sources drive PAN formation, with influences dominating in industrialized regions and biogenic inputs becoming significant in vegetated areas during warm periods. PAN concentrations are highest in urban areas characterized by elevated NOx, VOCs, and solar irradiance, where photochemical processing is intense. For instance, levels in the have reached up to 10 ppb under such conditions. Globally, PAN serves as a marker of photochemical , with peak abundances in environments and downwind plumes from emission hotspots. Seasonal patterns reflect enhanced , with PAN peaking in summer due to higher OH• levels and VOC reactivity under prolonged sunlight. Concentrations typically decline in winter from reduced insolation, though colder temperatures stabilize existing PAN against decomposition.

Role in Atmospheric Chemistry

Photochemical Reactions

Peroxyacetyl nitrate (PAN) plays a central role in tropospheric photochemical cycles as a temporary reservoir for nitrogen oxides (NOx), facilitating the cycling of reactive nitrogen species that drive oxidant formation. In sunlit conditions, PAN undergoes thermal dissociation, primarily via the reversible reaction CH₃C(O)OONO₂ ⇌ CH₃C(O)OO• + NO₂, where the peroxyacetyl radical (PA) recombines with NO₂ under cooler temperatures but decomposes more rapidly at higher temperatures, typically above 298 K. This equilibrium allows PAN to store NOx during the day and release NO₂ in warmer, illuminated environments, regenerating NOx for further photochemical activity. The rate of dissociation increases with temperature, with effective lifetimes ranging from hours to days depending on ambient conditions, making it a key modulator of local NOx availability. The primary fate of PAN in the troposphere is this thermal cycling rather than direct reactions with other radicals, though minor pathways exist. Reaction with the (•) occurs but is negligible, contributing less than 1% to PAN loss under typical atmospheric concentrations of ~10⁶ molecules cm⁻³, as the rate constant is on the order of 10⁻¹³ cm³ molecule⁻¹ s⁻¹. Interactions with () or alkenes are also minor for PAN itself, with emphasis instead on the released PA radical's reactivity; for instance, PA can react with to form peroxyacetic acid, indirectly influencing PAN cycling by competing with NO₂ recombination. These processes highlight PAN's role in sustaining radical propagation without significant permanent sinks beyond . By releasing NO₂, PAN contributes to ozone (O₃) formation through the well-established photolysis pathway: NO₂ + hν → NO + O (λ < 400 nm), followed by O + O₂ + M → O₃ + M, fueling the NOx-catalyzed O₃ production cycle in polluted atmospheres. In urban settings, this can enhance O₃ levels under NOx-limited conditions, though PAN's net effect varies seasonally—promoting O₃ in cooler periods via radical supply but inhibiting it in warmer seasons by weakening the ROx cycle. PAN's photochemical behavior is incorporated into chemical transport models like CB05, which explicitly simulates its formation (e.g., PA + → PAN) and decomposition to predict urban air quality, improving forecasts of O₃ and secondary pollutants by accounting for multi-day NOx dynamics.

NOx Reservoir and Long-Range Transport

Peroxyacetyl nitrate (PAN) functions as a crucial reservoir for reactive nitrogen oxides () in the , sequestering nitrogen in a relatively stable form that inhibits rapid deposition or reaction near emission sources. Unlike the short-lived NO and species, which persist for only seconds to minutes due to rapid photochemical cycling, PAN's lifetime is highly temperature-dependent, governed primarily by . At ambient temperatures exceeding 25°C, PAN decomposes within minutes, but its stability increases dramatically in colder conditions; for instance, the lifetime extends to approximately 1 hour at 25°C, several weeks in the upper troposphere around 250 K, and up to months at -50°C, effectively doubling with every 4 K decrease in temperature. This thermal lability allows PAN to preserve for advection away from polluted regions, releasing it upon warming to sustain distant formation. The extended lifetime of PAN enables long-range transport of NOx, with molecules traveling hundreds to thousands of kilometers from continental sources to remote areas. In the , for example, PAN concentrations of 100–700 parts per trillion by volume (), or up to approximately 0.7 ppb, have been observed at sites like , and , , during spring, attributable to mid-latitude plumes advected northward. In the colder upper , transport distances can exceed 10,000 km, as PAN resists decomposition and correlates with tracers of long-range such as and . This mechanism is particularly evident in biomass burning events, where PAN facilitates the export of NOx beyond local boundaries. Satellite and ground-based observations highlight PAN's global distribution, with it comprising 10–20% of exported during springtime biomass burning in regions like and , contributing to enhanced NOx levels in the remote . In the upper , PAN's role extends to climate interactions by modulating concentrations; as a NOx source upon decomposition, it promotes ozone production in NOx-limited environments, indirectly influencing tropospheric radiative forcing through 's . PAN typically accounts for 75–90% of total acyl peroxy nitrates, underscoring its dominance in these processes. Quantification of PAN relies on advanced measurement techniques, notably thermal dissociation laser-induced fluorescence (TD-LIF), which thermally decomposes PAN and related peroxy nitrates to NO2 for detection via , enabling precise assessment of total peroxy nitrates with accuracy within 10% of speciated measurements. This method is particularly valuable for aircraft campaigns in the upper , where it distinguishes PAN from other nitrogen reservoirs amid varying temperatures and NOx levels.

Health and Environmental Effects

Toxicity to Humans

Peroxyacetyl nitrate () primarily affects humans through , as it is a volatile gas present in polluted urban air. At concentrations around 0.13 (130 ppb) for 2-hour exposure, PAN can cause eye , with and pulmonary function changes observed at higher levels of 0.24–0.3 in sensitive individuals. In animal studies, acute exposures to high concentrations (LC50 ≈100 for 2-4 hours) result in severe respiratory distress and lesions. Chronic risks from low-level in ambient air are not well-characterized due to limited long-term human studies, but it may contribute to on respiratory tissues. Atmospheric concentrations in polluted areas, typically 0.003–0.078 mg/m³ (0.0006–0.016 ppm), are below thresholds for acute effects.

Effects on Vegetation and Ecosystems

Peroxyacetyl nitrate () exhibits significant , being 10-50 times more potent than in causing damage to plants. This heightened manifests in visible symptoms such as leaf bronzing, glazing, metallic sheen on lower leaf surfaces, tissue collapse, , , and transverse banding on expanding leaves, particularly in sensitive species like petunias, , , and . These effects occur at relatively low atmospheric concentrations, with acute observed after 4-hour exposures around 14 ppb, and at levels as low as 0.1-1 ppb leading to reduced and overall plant stress. At the cellular level, PAN disrupts chloroplast function by inhibiting photophosphorylation and CO₂ fixation, impairing energy production essential for photosynthesis. It also induces stomatal closure, limiting gas exchange and exacerbating oxidative stress, while promoting chlorophyll degradation through reactive oxygen species (ROS) generation, such as hydrogen peroxide, which triggers programmed cell death in sensitive plant tissues. These mechanisms result in diminished photosynthetic rates, with studies on tobacco cell lines showing elevated ROS and calcium signaling leading to plasmolysis and cell shrinkage. In ecosystems, PAN contributes to forest decline, notably in the of , where elevated levels (up to 51 µg/m³ in summer averages) alongside other nitrogenous pollutants exacerbate nitrogen saturation, , and foliar necrosis in like ponderosa pine. For agriculture, it causes yield losses of 5-10% in sensitive crops such as through suppressed growth and biomass reduction, as observed in controlled exposures mimicking photochemical smog conditions. of PAN in food chains is minor due to its gaseous nature and short atmospheric lifetime, though it indirectly enhances by serving as a reservoir, releasing nitrogen oxides that form upon deposition. Regulatory efforts in the highlighted PAN's role within photochemical oxidants, leading to its inclusion in the U.S. (NAAQS) for oxidants, with studies demonstrating greater plant sensitivity to PAN than to or human health thresholds. These findings underscored the need for controls on precursor emissions to protect , influencing ongoing air quality management.

References

  1. [1]
    Peroxyacetyl nitrate - American Chemical Society
    Feb 17, 2020 · Peroxyacetyl nitrate (PAN) is an unstable, atmospheric compound that helps form ozone. It is a temporary reservoir species and an inhalation ...Missing: structure properties
  2. [2]
    Complexities of peroxyacetyl nitrate photochemistry and its control ...
    May 31, 2024 · Peroxyacetyl nitrate (PAN, CH3C(O)OONO2) is a component of photochemical smog and exhibits detrimental effects on both human health and plant ...Missing: formula properties
  3. [3]
    Atmospheric peroxyacetyl nitrate (PAN): a global budget and source ...
    PAN enables the transport and release of NOx to the remote troposphere with major implications for the global distributions of ozone and OH, the main ...Missing: structure properties
  4. [4]
    peroxyacetyl nitrate - the NIST WebBook
    peroxyacetyl nitrate. Formula: C2H3NO5; Molecular weight: 121.0489. IUPAC Standard InChI: InChI=1S/C2H3NO5/c1-2(4)7-8-3(5)6/h1H3
  5. [5]
    Peroxyacetyl nitrate | C2H3NO5 | CID 16782 - PubChem
    Therefore, peroxyacetyl nitrate plays an important role in atmospheric chemistry and has a large effect on ozone formation(2). Peroxyacetyl nitrate was stable ...
  6. [6]
    Ab initio studies of isomerization and dissociation reactions of ...
    The complex potential energy surface for the unimolecular isomerization and decomposition of peroxyacetyl nitrate (PAN, CH3C(O)OONO2), including 11 isomers, ...
  7. [7]
    Thermal decomposition of peroxy acetyl nitrate CH3C(O)OONO2
    The major decomposition reaction of PAN is bond fission of the O-N single bond yielding the peroxy radical. The O-O bond fission pathway is a minor route.
  8. [8]
    Peroxyacetyl nitrate solubility and decomposition rate in acidic water
    Recent investigations have shown that peroxyacetyl nitrate (PAN) is soluble in acidic water samples. A Henry's law constant of has been determined.
  9. [9]
    2278-22-0(peroxyacetyl nitrate) Product Description - ChemicalBook
    Boiling point: 225.69°C (rough estimate) ; Density, 1.438±0.06 g/cm3(Predicted) ; refractive index, 1.4264 (estimate) ; solubility, Soluble in pentane, benzene, ...Missing: physical | Show results with:physical
  10. [10]
    Thermal decomposition of peroxyacetyl nitrate and reactions of ...
    Thermal decomposition of peroxyacetyl nitrate and reactions of acetyl peroxy radicals with nitric oxide and nitrogen dioxide over the temperature range 283-313 ...
  11. [11]
    Improved mid-infrared cross-sections for peroxyacetyl nitrate (PAN ...
    Jan 17, 2005 · Band intensities and band centre absorptivities are also reported for four weaker PAN absorption bands in the mid infrared for the first time.Missing: peroxy | Show results with:peroxy
  12. [12]
    Investigation of the loss processes for peroxyacetyl nitrate in the ...
    Jul 20, 1995 · The absorption cross sections decrease monotonically with increasing wavelength. The cross sections also decrease as the temperature is lowered.Missing: spectroscopic | Show results with:spectroscopic
  13. [13]
    [PDF] PEROXYACETYL NITRATE (PAN): HISTORICAL PERSPECTIVE
    PAN decomposition is known to lead to methyl nitrate formation, which is fairly stable in the atmosphere. ... Prestbo, 1989: Peroxyacyl nitrates (PANS): Their ...Missing: formula | Show results with:formula
  14. [14]
    The Production of Pure Peroxyacyl Nitrates - Taylor & Francis Online
    The preparation of the first member of the series, peroxyacetyl nitrate, by photolysis of ethyl nitrite vapor in dry oxygen is described. All the procedures ...
  15. [15]
    Mechanism of Peroxyacetyl Nitrate Formation
    It accounts for the formation of peroxyacetyl nitrate in the dark reaction of acetaldehyde, oxygen, and N2O5; and, finally, it explains the inhibiting effect ...Missing: laboratory | Show results with:laboratory
  16. [16]
    Synthesis of peroxyacetyl nitrate in air by acetone photolysis
    Synthesis of peroxyacetyl nitrate in air by acetone photolysis | Environmental Science & Technology. YELLOW SPRINGS INSTRUMENT CO.
  17. [17]
    A convenient method for preparation of pure standards of ...
    Peroxyacetyl nitrate (PAN) is synthesized by nitration of peracetic acid (1.2 M), extracted by n- heptane, and purified with normal-phase high-performance ...Missing: laboratory | Show results with:laboratory
  18. [18]
    A novel photochemical conversion technique for reliable calibration ...
    May 10, 2023 · Photochemical synthesis of peroxyacetyl nitrate (PAN) through irradiating air mixtures of NO and acetone is prevailingly adopted for calibrating PAN analyzers.
  19. [19]
  20. [20]
    World-wide ambient measurements of peroxyacetyl nitrate (PAN ...
    PAN in Riverside, California, averaged 8.1 ppb in July, 9.4 ppb in September and 8.8 ppb in October 1980. These values represent the average of 48 measurements ...
  21. [21]
    Understanding summertime peroxyacetyl nitrate (PAN) formation ...
    Jan 23, 2025 · Peroxyacetyl nitrate (PAN), a key indicator of photochemical pollution, is generated similarly to ozone (O3), through reactions involving ...Missing: isomers | Show results with:isomers
  22. [22]
    [PDF] Seasonal characteristics of atmospheric peroxyacetyl nitrate (PAN ...
    Dec 21, 2021 · The reaction of peroxyacetyl ... decomposition, and the indirect sinks of PAN were the reactions of PA with NO, HO2, and RO2 (Wolfe et.
  23. [23]
    [PDF] YOCKE AND COMPANY - CAMx
    Dec 8, 2005 · The new Carbon Bond mechanism is called CB05 because it was developed in. 2005. The CB05 is a condensed mechanism of atmospheric oxidant ...
  24. [24]
    Atmospheric peroxyacetyl nitrate (PAN): a global budget and source ...
    PAN chemistry can also be important for oxidant formation on a regional scale. In polluted environments, PAN formation is a sink for both NOx and hydrogen oxide ...
  25. [25]
    [PDF] Observations of peroxyacetyl nitrate (PAN) in the upper troposphere ...
    Jun 6, 2013 · It should also be noted that PAN has a minor effect on the oxidizing power of the atmosphere through its reaction with the OH radical, but the ...
  26. [26]
    Peroxyacetyl nitrate photochemistry and interactions with the Arctic ...
    Sep 17, 2004 · Peroxyacetyl nitrate (PAN) is a NOx reservoir compound that has the ability to transport NOx to remote environments, allowing for NOx ...
  27. [27]
    Total Peroxy Nitrates (ΣPNs) in the atmosphere: the Thermal ... - AMT
    ... Thermal Dissociation-Laser Induced Fluorescence (TD-LIF) technique and comparisons to speciated PAN measurements. P. J. Wooldridge, A. E. Perring, T. H. ...
  28. [28]
    Toxicity of Peroxyacetyl Nitrate on Human | Insight Medical Publishing
    Pans have many effects on human body like respiratory function, eye irritation, emphysema, and other lung problems. Human exposure to PANs mostly occurs in ...
  29. [29]
    Peroxyacetyl nitrate: review of toxicity - PubMed
    Following acute exposure, severe lung lesions and, at the higher levels, damage to the epithelium of upper parts of the respiratory tract were found in animals.
  30. [30]
    Peroxyacetyl nitrate: review of toxicity - Adolf Vyskocil, Claude Viau ...
    In human, the lowest level causing eye irritations was 0.64 mg/m3 for 2 h. ... PAN is a weak point mutagen or clastogen. The data are not sufficient to evaluate ...Missing: irritation | Show results with:irritation
  31. [31]
    Peroxyacetyl nitrate-induced apoptosis through generation of ...
    We hypothesized that PAN might induce cell death in human leukemia cells by releasing peroxynitrite and other reactive oxygen species (ROS) such as superoxide ...
  32. [32]
    Importance of Peroxyacetyl Nitrate (PAN) as a Phytotoxic Air Pollutant
    Figure 1. Number of 15-minute periods that PAN concentrations exceeded 10 ppb and total oxidant, expressed as ozone, exceeded 10 pphm during the first 18 days ...Missing: potency | Show results with:potency
  33. [33]
    [PDF] detection of peroxyacetyl nitrate at phytotoxic level and its effects on ...
    From July 1992 to April 1993 there were at least 34 d with PAN at significantly phytotoxic concentrations that affected lettuce and other plants.
  34. [34]
    Inhibitory Effect of Peroxyacetyl Nitrate on Cyclic ... - NIH
    Peroxyacetyl nitrate caused inhibition to photophosphorylation, in either the dark or the light, by affecting the chloroplast.Missing: stomatal chlorophyll
  35. [35]
    [PDF] California State University, Northridge Effects of Air Pollution
    Stomatal measurements indicated that stomata were closed shortly after the beginning of the first exposure period of an experiment lasting five (5) days ...
  36. [36]
    Peroxyacetyl nitrate-induced oxidative and calcium signaling events ...
    Briefly, peroxyacetic acid was prepared first by gently adding hydrogen peroxide to acetic anhydride preconditioned with sulfuric acid. ... A convenient method ...<|control11|><|separator|>
  37. [37]
    [PDF] NITROGEN DEPOSITION IN CALIFORNIA FORESTS: A REVIEW
    How- ever, at the presently observed levels in California forests, no toxic effects are expected to occur. Peroxyacetyl nitrate (PAN) and peroxypropionyl.
  38. [38]
    Effect of peroxyacetyl nitrate (PAN) in vivo on tobacco leaf ...
    Jul 1, 1971 · Tobacco plants were exposed to 1 ppm of peroxyacetyl nitrate (PAN) for 1 hr. Subsequent exposure of the plants to light caused leaf-cell ...Missing: yield losses
  39. [39]
    Air Quality Criteria for Ozone and Other Photochemical Oxidants ...
    Based on the rate constant for its reaction with OH radicals (Atkinson et al ... The first observation of peroxypropionyl nitrate (PPN) in heavily polluted air ...
  40. [40]
    Air Quality Criteria for Ozone and Related Photochemical Oxidants ...
    ... peroxyacetyl nitrate (PAN) being about 10 times more phytotoxic than O3 (Darley et al., 1963; Taylor and MacLean, 1970; Pell, 1976). Although more phytotoxic ...