Photochemical modeling of hydroxyl and its relationship to other species during the Tropospheric OH Photochemistry Experiment

Because of the extremely short photochemical lifetime of tropospheric OH, comparisons between observations and model calculations should be an effective test of our understanding of the photochemical processes controlling the concentration of OH, the primary oxidant in the atmosphere. However, unambiguous estimates of calculated OH require sufficiently accurate and complete measurements of the key species and physical variables that determine OH concentrations. The Tropospheric OH Photochemistry Experiment (TOHPE) provides an extremely complete set of measurements, sometimes from multiple independent experimental platforms, that allows such a test to be conducted. When the calculations explicitly use observed NO, NO2, hydrocarbons, and formaldehyde, the photochemical model consistently overpredicts in situ observed OH by ∼50% for the relatively clean conditions predominantly encountered at Idaho Hill. The model bias is much higher when only CH4-CO chemistry is assumed, or NO is calculated from the steady state assumption. For the most polluted conditions encountered during the campaign, the model results and observations show better agreement. Although the comparison between calculated and observed OH can be considered reasonably good given the ±30% uncertainties of the OH instruments and various uncertainties in the model, the consistent bias suggests a fundamental difference between theoretical expectations and the measurements. Several explanations for this discrepancy are possible, including errors in the measurements, unidentified hydrocarbons, losses of HOx to aerosols and the Earth's surface, and unexpected peroxy radical chemistry. Assuming a single unidentified type of hydrocarbon is responsible, the amount of additional hydrocarbon needed to reduce theoretical OH to observed levels is a factor of 2 to 3 greater than the OH-reactivity-weighted hydrocarbon content measured at the site. Constraints can be placed on the production and yield of various radicals formed in the oxidation sequence by considering the observed levels of certain key oxidation products such as formaldehyde and acetaldehyde. The model results imply that, under midday clean westerly flow conditions, formaldehyde levels are fairly consistent with the OH and hydrocarbon observations, but observed acetaldehyde levels are a factor of 4 larger than what is expected and also imply a biogenic source. Levels of methacrolein and methylvinylketone are much lower than expected from steady state isoprene chemistry, which implies important removal mechanisms or missing information regarding the kinetics of isoprene oxidation within the model. In a prognostic model application, additional hydrocarbons are added to the model in order to force calculated OH to observed levels. Although the products and oxidation steps related to pinenes and other biogenic hydrocarbons are somewhat uncertain, the addition of a species with an oxidation mechanism similar to that expected from C10 pinenes would be consistent with the complete set of observations, as opposed to naturally emitted isoprene or any of the anthropogenic hydrocarbons examined in the model. Further constraints on the abundance of peroxy radicals are necessary in order to fill the gaps in our understanding of OH photochemistry for the clean continental conditions typical of Idaho Hill.

[1]  Alan Fried,et al.  HO2/OH and RO2/HO2 ratios during the Tropospheric OH Photochemistry Experiment: Measurement and theory , 1997 .

[2]  D. Fahey,et al.  Measurements of the NO x ‐O3 photostationary state at Niwot Ridge, Colorado , 1986 .

[3]  L. Kleinman Photochemical formation of peroxides in the boundary layer , 1986 .

[4]  C. J. Hahn,et al.  NOx measurements in clean continental air and analysis of the contributing meteorology , 1984 .

[5]  Stuart A. McKeen,et al.  Impact of natural hydrocarbons on hydroxyl and peroxy radicals at a remote site , 1987 .

[6]  J. Drummond,et al.  Measurements of tropospheric OH concentrations: A comparison of field data with model predictions , 1987 .

[7]  D. Olszyk,et al.  Terpenes emitted from agricultural species found in California's Central Valley , 1991 .

[8]  S. Mckeen,et al.  A study of the dependence of rural ozone on ozone precursors in the eastern United States , 1991 .

[9]  Patrick R. Zimmerman,et al.  Natural volatile organic compound emission rate estimates for U.S. woodland landscapes , 1994 .

[10]  P. Villalta,et al.  A temperature-dependent kinetics study of the CH3O2 + NO reaction using chemical ionization mass spectrometry , 1995 .

[11]  J. Harder,et al.  Meteorological overview of the 1993 OH Photochemistry Experiment , 1997 .

[12]  D. Helmig,et al.  Organic chemicals in the air at Whitaker's Forest/Sierra Nevada Mountains, California. , 1992, The Science of the total environment.

[13]  John H. Seinfeld,et al.  Aerosol formation in the photooxidation of isoprene and β-pinene , 1991 .

[14]  S. M. Aschmann,et al.  Product study of the gas-phase reactions of monoterpenes with the OH radical in the presence of NO x , 1990 .

[15]  H. Niki,et al.  Measurement of total nonmethane organic carbon (Cy): development and application at Chebogue Point, Nova Scotia, during the 1993 North Atlantic Regional Experiment campaign , 1998 .

[16]  Jack G. Calvert,et al.  Measurements and steady state calculations of OH concentrations at Mauna Loa Observatory , 1996 .

[17]  D. Fahey,et al.  Systematic variations in the concentration of NO x (NO Plus NO2) at Niwot Ridge, Colorado , 1990 .

[18]  B. Heikes,et al.  Factors influencing the concentration of gas phase hydrogen peroxide during the summer at Niwot Ridge, Colorado , 1995 .

[19]  S. Montzka,et al.  The observation of a C5 alcohol emission in a North American pine forest , 1993 .

[20]  A. Ravishankara,et al.  Reaction of Methylbutenol with the OH Radical: Mechanism and Atmospheric Implications , 1995 .

[21]  P. Zimmerman,et al.  Nonmethane hydrocarbons in remote tropical, continental, and marine atmospheres , 1984 .

[22]  H. Hakola,et al.  Product formation from the gas-phase reactions of OH radicals and O3 with a series of monoterpenes , 1994 .

[23]  A. Thompson,et al.  Effect of chemical kinetics uncertainties on calculated constituents in a tropospheric photochemical model , 1991 .

[24]  William H. Brune,et al.  Peroxy radicals from photostationary state deviations and steady state calculations during the Tropospheric OH Photochemistry Experiment at Idaho Hill, Colorado, 1993 , 1997 .

[25]  J. Birks,et al.  Measurement of sub-ppbv concentrations of aldehydes in a forest atmosphere using a new HPLC technique , 1992 .

[26]  L. Newman,et al.  Measurement and speciation of gas phase peroxides in the atmosphere , 1993 .

[27]  S. Wofsy,et al.  Tropospheric chemistry: A global perspective , 1981 .

[28]  Sanford Sillman,et al.  The sensitivity of ozone to nitrogen oxides and hydrocarbons in regional ozone episodes , 1990 .

[29]  M. Molina,et al.  Chemical kinetics and photochemical data for use in stratospheric modeling , 1985 .

[30]  A. Fried,et al.  Comparison of tunable diode laser and long-path ultraviolet/visible spectroscopic measurements of ambient formaldehyde concentrations during the 1993 OH Photochemistry Experiment , 1997 .

[31]  A. M. Dunker The decoupled direct method for calculating sensitivity coefficients in chemical kinetics , 1984 .

[32]  G. Mount,et al.  An overview of the Tropospheric OH Photochemistry Experiment, Fritz Peak/Idaho Hill, Colorado, fall 1993 , 1997 .

[33]  F. Fehsenfeld,et al.  Nonmethane hydrocarbon measurements during the Tropospheric OH Photochemistry Experiment , 1997 .

[34]  Y. Yokouchi,et al.  Semi-volatile aldehydes as predominant organic gases in remote areas , 1990 .

[35]  I. Zenkevich,et al.  Volatile organic compounds in the atmosphere of forests , 1985 .

[36]  A. Lloyd,et al.  An updated chemical mechanism for hydrocarbon/NOx/SO2 photooxidations suitable for inclusion in atmospheric simulation models , 1982 .

[37]  R. Atkinson Gas-Phase Tropospheric Chemistry of Organic Compounds , 1994 .

[38]  S. Mckeen,et al.  Photochemistry of formaldehyde during the 1993 Tropospheric OH Photochemistry Experiment , 1997 .

[39]  D. Crosley 1993 Tropospheric OH Photochemistry Experiment: A summary and perspective , 1997 .

[40]  G. Mount,et al.  An Intercomparison of Tropospheric OH Measurements at Fritz Peak Observatory, Colorado , 1992, Science.

[41]  F. Lurmann,et al.  Modeling potential ozone impacts from natural hydrocarbons—I. Development and testing of a chemical mechanism for the nox-air photooxidations of isoprene and α-pinene under ambient conditions , 1983 .

[42]  R. Atkinson,et al.  Atmospheric lifetimes and fates of a series of sesquiterpenes , 1995 .

[43]  S. Montzka,et al.  Measurements of 3‐methyl furan, methyl vinyl ketone, and methacrolein at a rural forested site in the southeastern United States , 1995 .

[44]  H. Akimoto,et al.  Reactions of OH with α‐pinene and β‐pinene in air: Estimate of global CO production from the atmospheric oxidation of terpenes , 1991 .

[45]  F. Fehsenfeld,et al.  Meteorological characteristics and spatial extent of upslope events during the 1993 Tropospheric OH Photochemistry Experiment , 1997 .

[46]  D. Murphy,et al.  Aerosol characteristics at Idaho Hill during the OH Photochemistry Experiment , 1997 .

[47]  A. Fried,et al.  An intercomparison of spectroscopic laser long‐path and ion‐assisted in situ measurements of hydroxyl concentrations during the Tropospheric OH Photochemistry Experiment, fall 1993 , 1997 .

[48]  D. Blake,et al.  Photostationary state analysis of the NO2‐NO system based on airborne observations from the western and central North Pacific , 1996 .

[49]  M. Wallasch,et al.  The dependence of the concentration of OH on its precursors under moderately polluted conditions: A model study , 1993 .

[50]  An improved method of measuring tropospheric NO2 and RO2 by matrix isolation and electron spin resonance , 1985 .

[51]  F. Fehsenfeld,et al.  Peroxy radicals as measured in ROSE and estimated from photostationary state deviations , 1993 .

[52]  F. Fehsenfeld,et al.  Variations in NO y composition at Idaho Hill, Colorado , 1997 .

[53]  S. Montzka,et al.  Isoprene and its oxidation products, methyl vinyl ketone and methacrolein, in the rural troposphere , 1993 .

[54]  F. Fehsenfeld,et al.  Observations and modeling of the reactive nitrogen photochemistry at a rural site , 1991 .

[55]  B. Heikes,et al.  Formaldehyde and hydroperoxides at Mauna Loa Observatory , 1992 .

[56]  W. Carter A detailed mechanism for the gas-phase atmospheric reactions of organic compounds , 1990 .

[57]  Jerald W. Harder,et al.  Intercomparison of tropospheric OH and ancillary trace gas measurements at Fritz Peak Observatory, Colorado , 1994 .

[58]  Franz Rohrer,et al.  Comparison of measured OH concentrations with model calculations , 1994 .

[59]  Alan C. Lloyd,et al.  A chemical mechanism for use in long‐range transport/acid deposition computer modeling , 1986 .

[60]  J. Milford,et al.  First‐order sensitivity and uncertainty analysis for a regional‐scale gas‐phase chemical mechanism , 1995 .

[61]  S. Liu,et al.  On the nonlinearity of the tropospheric ozone production , 1988 .

[62]  F. Fehsenfeld,et al.  Ground‐based comparison of NO2, H2O, and O3 measured by long‐path and in situ techniques during the 1993 Tropospheric OH Photochemistry Experiment , 1997 .