NE-176: Characterization and Mechanisms of Plant Responses to Ozone in the Northeastern U.S.

 

Technical Committee Report of Progress and Accomplishments in 1999

 

Annual Progress Report:  January 1, 1999December 31, 1999

 

COOPERATING AGENCIES & PRINCIPAL LEADERS: C. Andersen (US EPA), F. Booker (USDA-ARS, NC), S. Britz (USDA-ARS, MD), K. Burkey (USDA-ARS, NC), A. Chappelka (AL), B. Chevone (VA), A. Heagle (USDA-ARS, NC), R. Kohut (Boyce Thompson Institute, NY), S. Krupa (MN), W. Manning (MA), M. McGrath (NY, LI), J. Miller (USDA-ARS, NC), C. Mulchi (MD), E. Pell (PA), J. Rebbeck (USDA Forest Service, OH), M. Robinson (USDA-ARS, MD), J. Sinn (PA), B. Zilinskas (NJ).

Advisors: P. Logan (RI), D. Jones (USDA-CSREES)

 

PROGRESS OF THE WORK & PRINCIPAL ACCOMPLISHMENTS, January - December, 1999

 

Objective 1. Characterize whole plant responses to O3, including carbon assimilation and allocation, growth and productivity.

Carbon budgets in ponderosa pine forests.  Carbon budgets for two ponderosa pine stands in Eastern Oregon that differ in age (>250 yrs vs 20 yr old) were constructed in collaboration with researchers at Oregon State University.  Eddy flux measurements, estimates of root productivity, and the contribution of deep and shallow water sources were evaluated over the growing season.  Stable isotopes were used to separate soil heterotrophic from autotrophic respiration. The results provide important inputs for tree and stand level models that are being used to evaluate ozone effects at the ecosystem level.  (C. Andersen, US EPA)

Root growth in forests.  A US Forest Service collaboration on several sites across a natural ozone gradient in Southern California showed that root growth is lowest at the most polluted site.  (C. Andersen, US EPA)

Ecosystem response using native species.  Exposure-response relationships between ambient ozone and visible injury on mature black cherry in two National Parks in the eastern US were developed.  Percent injured trees increased with elevation, and was positively correlated with SUM06 and W126. The relationship was strengthened significantly by combining the data from both parks.  A new study has been initiated investigating the response of tall milkweed to ozone along an elevational gradient in the Great Smoky Mountains National Park.  A study is being developed to investigate the effects of ozone on semi-natural grassland communities.  (A. Chappelka, AL)

Modeling ozone impacts on forest growth and composition.  Research involves the use of mechanistically-based simulation models to address the long-term, complex impacts of air quality and climate change on forest growth and composition.  Effects of air quality on plant population genetics is being investigated.  An on-going study is assessing the effects of escalating levels of CO2 on the phenotypic, physiological, and genetic properties of plant populations over 10 generations of exposure.  (R. Kohut, BTI, NY)

Ozone exposure dynamics.  A stochastic, Weibull frequency distribution, probability generator was tested and applied for replacing missing data on hourly atmospheric concentrations of ozone and other trace gases (oxides of nitrogen and sulfur dioxide).  The method provided highly accurate and realistic results for the replacement of as many as 100 missing values on either side of a measured data sub-set, without altering the overall characteristics of the true frequency distribution of the entire data set.  This method will be used independently to theoretically reconstruct the exposure dynamics underlying single, time-integrated values obtained by the use of passive samplers.  (S. Krupa, MN)

Snap bean and white clover yield loss.  Ambient ozone was shown to be high enough to greatly reduce growth and yield of sensitive plants on Long Island, one of the most important agricultural counties in New York.  Sensitive snap bean lines exhibited yield reductions of 25% in weight of beans harvested for fresh-market consumption and 40% in number of seeds at maturity compared to ozone-tolerant snap beans.  Growth of an ozone-sensitive white clover clone was reduced by an average of 27% compared to an ozone-tolerant clone from May through early Sep, then the two clones grew at a similar rate when ozone concentrations were lower.  Average daily 12-hr ozone mean was 52.5, 48.4, 62.0, 48.9, and 35.9 ppb for the five growth periods.  (M. McGrath, NY)

Screening soybean for ozone tolerance.  Twenty-four cultivars of soybean (eight each from maturity groups III, IV and V) were grown full-season in 5-m diameter open-top chambers purged continuously with charcoal filtered (CF) air or non-filtered (NF) air + 35 ± 5 nL O3 L-1 for 7 h day-1.  In addition to grain yields per plant at maturity, leaf discs were examined for relative changes in chlorophyll content and ion leakage in response to chronic ozone exposure.  The goals of the program are: 1) screen modern soybean cultivars for their relative O3 tolerance in terms of productivity; and 2) develop a leaf assay procedure that may be useful to assess the relative tolerance of soybeans to O3 stress.  The studies will be repeated in 2000.  (C. Mulchi, MD)

 

Objective 2. Identify & delineate factors, both biotic & environmental, that determine plant O3 response.

Ponderosa pine competitiveness.  In a three-year open top chamber study, ponderosa pine seedling growth was reduced by the combination of ozone and grass competition relative to grass competition alone. The reduced competitiveness was associated with altered nitrogen metabolism because ozone-exposed seedlings were unable to either take up or retain as much nitrogen when growing in the presence of grass as when growing alone.  (C. Andersen, US EPA)

Tree species O3/CO2 interaction responses. Growth was significantly stimulated by twice ambient CO2 in seedlings of black cherry, green ash, and yellow-poplar; although there were significant growth responses following exposure to twice ambient O3 or the combination of twice ambient CO2 plus twice ambient O3.  Interactive effects of O3 and CO2 on photosynthesis and stomatal conductance on all three species were limited.  Following a 5-year exposure of white pine to elevated ozone and carbon dioxide, analysis of many growth and biomass variables showed that ambient and twice ambient O3 reduced seedling biomass relative to CF seedlings, and additions of twice ambient CO2 ameliorated those effects.  Findings support the hypothesis that future productivity of eastern US forests will not be negatively impacted by elevated O3 in the presence of elevated ambient CO2.  (J. Rebbeck, USDA Forrest Service)

Ozone/CO2 interaction mechanisms.  A major factor in O3/CO2 interactions is reduced ozone flux into leaves in the presence of elevated CO2. In soybean, amelioration of ozone injury by elevated CO2 also appeared to involve additional physiological and biochemical responses.  However, there was no measurable effect of elevated CO2 on antioxidant metabolism.  Only ozone injury correlated with increased ascorbate, glutathione, glutathione reductase and peroxidase activities.  Superoxide dismutase activities were not affected by either ozone or elevated CO2.  (F. Booker, ARS, NC)

Environmental factors that influence ozone uptake.  A series of field experiments has resulted in determination of some important environmental factors that control ozone uptake by plants and hence expression of foliar injury under real-time ambient conditions.  The degree of solar radiation intensity (PAR at and above 500 mmol m-2 s-1), available soil moisture (greater than 25 %), ozone concentration and degree of stomatal conductance determine ozone uptake and result in foiliar ozone injury to Bel-W3 tobacco.  (W. Manning, MA)

 

Objective 3. Determine the mechanisms of O3 action and plant defense systems, using cultivars and genotypes characterized in whole plant experiments.

Glutathione-S-transferase associated with ozone tolerance.  Ozone exposure at 200 ppb for 4 hrs caused comparable reductions in maximum net photosynthesis (35-42%) and apparent quantum yield (15-27%) in a tolerant (Bel B) and sensitive (Bel W3) tobacco cultivar immediately after fumigation.  By 24 hrs, photosynthetic efficiency had recovered in Bel B, but not in Bel W3, demonstrating that tolerant genotypes are significantly affected by ozone.  The mRNAs of two glutathione-S-transferase genes increased more than tenfold in Bel B, but were unchanged in Bel W3 after ozone treatment, indicating a possible role for ozone tolerance for this enzyme.  (B. Chevone, VPI)

Drought effects on leaf ascorbic acid.  During the summer of 1999, we examined the influence of drought-induced water deficit on the steady-state levels of ascorbic acid (ASC), dehydroascorbate (DHA) and the ASC:DHA redox status in leaflets of the soybean cultivars Essex and Forrest.  This approach was taken as a first step into the eventual examination of the influence of simultaneous drought stress and elevated ozone exposure on soybean mesophyll leaf cell ASC synthesis and redox turnover.  In this present study, done with plants grown and drought stressed for 5 to 7 days either in the growth chamber or in the greenhouse, low leaflet water potential values (‰ -3.00 to -3.95 megaPascals) were accompanied by little or no loss of ASC and maintenance of most of the total ascorbate (ASC+DHA) as ASC.  The results suggested that during drought-induced water stress, activities of enzymes associated with ASC synthesis and ASC-DHA redox turnover were sufficient to sustain ASC levels.  (M. Robinson, ARS, MD)

Cellular localization of ascorbic acid associated with ozone tolerance.  A comparison of antioxidant metabolites (ascorbic acid, glutathione and a-tocopherol) in ozone-sensitive and tolerant snap beans showed that high levels of leaf extracellular ascorbate are associated with ozone tolerance, presumably through protection of plasma membranes from damage via antioxidant reactions that detoxify ozone and activated oxygen intermediates.  (K. Burkey, ARS, NC)

Transgenic plants for testing the role of ascorbic acid in ozone tolerance.  We have initiated a new collaborative project with Dr. M. Robinson (ARS, MD), Dr. K. Burkey (ARS, NC) and Dr. S. Jones-Held (King's College).  Ascorbate (vitamin C) serves as an important antioxidant, and recent evidence suggests that it is critical for providing protection against ozone damage.  Our plan is to produce transgenic plants with altered ascorbate content by manipulating the expression of two enzymes in the ascorbate biosynthetic pathway, namely GDP-D-mannose pyrophosphorylase and L-galactono-1,4-lactone dehydrogenase.  We have made sense and antisense constructs for each of these enzymes and will soon be introducing them into plants to test the hypothesis that higher ascorbate content will provide tolerance to ozone and conversely lower ascorbate content will deem plants more ozone-sensitive.  (B. Zilinskas, NJ)

Ozone responses elicited by cell wall components.  Cell wall oxidation products were recovered from tomato leaves after ozone exposure. Infiltration of these compounds into leaves can induce the expression of ozone-responsive genes without producing visible leaf injury.  (E. Pell & J. Sinn, PA)

Role of ethylene in plant response to ozone.  In Arabidopsis, the expression of ozone-responsive genes was not consistently associated with the evolution of ethylene by exposed plants.  Potato plants which under-express selected genes in the ethylene biosynthetic pathway are being used to further examine ethylene’s role in plant ozone response. (E. Pell & J. Sinn, PA)

Ozone effects on stomatal function.  Studies of membrane ion channels and whole-plant physiology in V. faba have demonstrated that ozone can have direct effects on stomatal function distinct from impacts on the photosynthetic apparatus. (E. Pell & J. Sinn, PA)

 

USEFULLNESS OF FINDINGS:  Tree species and crop cultivars for use as biological monitors of ambient ozone have been identified.  Knowledge of factors that affect plant response to ozone (e.g. soil moisture, elevated CO2, altered plant competition) is required to develop response models.  Predictive models are needed by regulatory agencies to establish air quality standards for the protection of crops and natural ecosystems.  Information about the molecular basis of plant response to ozone is required to effectively use biotechnology as an approach in the development of ozone tolerant plants.


REFERENCES

 

Ajit, S.K.  1999.  Responses of transgenic plants overexpressing antioxidant enzymes to ozone and pathogens.  Ph.D. Thesis, Rutgers University, New Brunswick, NJ.

 

Andersen, C.P.  1999.  Root detachment, developmental stage, and shoot light environment as determinants of root respiration in ponderosa pine.  Abstract and poster presentation, 2nd International Symposium “Dynamics of Physiological Processes in Woody Roots”, Nancy, France, Sept. 26-30.

 

Andersen, C.P. and P.T. Rygiewicz.  1999.  Understanding plant-soil relationships using controlled environment facilities.  Adv. Space Res.  24(3):309-318.

 

Bailey, S., J. Rebbeck, and K. Loats.  1999.  Interactive effects of elevated ozone plus carbon dioxide on open-top chamber exposed duckweed.  Ohio Journal of Science  2: 19-25.

 

Bergweiler, C.J. and W.J. Manning.  1999.  Inhibition of flowering and reproductive success in spreading dogbane, Apocynum androsaemifolium (L) by exposure to ambient ozone.  Environ. Pollut. 105: 333-339.

 

Booker, F.L., S.R. Shafer, C. Wei and S.J. Horton.  2000.  Carbon dioxide enrichment and nitrogen fertilization effects on cotton (Gossypium hirsutum L.) plant residue chemistry and decomposition.  Plant and Soil  (In press).

 

Booker, F.L.  2000.  Influence of carbon dioxide enrichment, ozone and nitrogen fertilization on cotton (Gossypium hirsutum L.) leaf and root composition.  Plant, Cell and Environ.  (In press).

 

Burkey, K.O.  1999.  Effects of ozone on apoplast/symplast partitioning of ascorbic acid in snap bean.  Physiol. Plant.  107: 188-193.

 

Chappelka, A., G. Somers and J. Renfro.  1999.  Ozone effects to forest trees in Great Smoky Mountains National Park, USA.  Water, Air and Soil Pollut.  116: 255-260.

 

Chappelka, A., J. Skelly, G. Somers, J. Renfro and E. Hildebrand.  1999.  Mature black cherry used as a bioindicator of ozone injury.  Water, Air and Soil Pollut.  116: 261-266.

 

Chernikova, T., J.M. Robinson, E.H. Lee and C.L. Mulchi  2000. Ozone tolerance and antioxidant enzyme activity in soybean cultivars.  Photosynthesis Research  (In Press).

 

Eckert, R., R. Kohut, T. Lee. and K. Staplefeldt.  1999.  Foliar ozone injury on native vegetation at Acadia National Park: Results from a six-year (1992-1997) field survey. US National Park Service Air Resources Division, Denver CO 42 pp.

 

Fiscus, E.L., R.B. Philbeck, A.B. Britt and F.L. Booker.  1999.  Growth of Arabidopsis flavonoid mutants under solar radiation and UV filters.  Environ. Exper. Bot.  41: 231-245.

 

Grulke, NE., C.P. Andersen, M.E. Fenn and P.R. Miller.  1998.  Ozone and nitrogen deposition lowers root biomass of ponderosa pine in the San Bernardino Mountains, California.  Environ. Pollut.  103: 63-73.

 

Grulke, N.E. and C.P. Andersen.  1999.  Changes in carbohydrate allocation within ponderosa pine across a pollution gradient in Southern California.  Abstract and poster presentation, 2nd International Symposium “Dynamics of Physiological Processes in Woody Roots”, Nancy, France, Sept. 26-30.

 

Heagle, A.S., J.E. Miller, F.L. Booker and W.A. Pursley.  1999.  Ozone stress, carbon dioxide enrichment, and nitrogen fertility interactions in cotton.  Crop Science  39: 731-741.

 

Heagle, A.S., F.L. Booker, J.E. Miller, W.A. Pursley and L.A. Stefanski.  1999.  Influence of daily carbon dioxide exposure duration and root environment on soybean response to elevated carbon dioxide.  J. Environ. Qual.  28: 666-675.

 

Hogsett, W.E., and C.P. Andersen.  1998.  Ecological effects of tropospheric ozone: A U.S. perspective- past, present, and future. US-Dutch International Symposium, Air pollution in the 21st Century, Noordwijk aan Zee, Netherlands, April 13-17, 1997, Elsevier Publishers, Amsterdam.

 

Islam, K.R., C.L. Mulchi and A.A. Ali.  2000.  Interactions of tropospheric CO2 and O3 enrichments and moisture variations on microbial biomass and respiration in soil.  Global Change Biol.  6: 1-11.

 

Islam, K.R., C.L. Mulchi and A.A. Ali.  1999.  Tropospheric carbon dioxide or ozone enrichment and soil moisture effects on soil organic carbon quality.  J. Environ. Qual.  28: 1629-1636.

 

Kickert, R.N., G. Tonella, A. Simonov, and S.V. Krupa.  1999.  Predictive modeling of effects under global change.  Environ. Pollut.  100: 87-132.

 

Kim, M.S.  1999. Combined effects of elevated tropospheric O3, elevated atmospheric CO2 and soil moisture deficit on soybean using fluorescence imaging.  Ph.D. Thesis. Univ. of Maryland, College Park, MD. 188pp.

 

Kley, D., M. Kleinman, H. Sandermann, S.V. Krupa  1999.  Photochemical oxidants: State of the science.  Environ. Pollut.  100: 19-42.

 

Kohut, R J, J.A. Laurence, P. King, and R. Raba.  1997.  Identification of Bioindicator Species for Ozone and Assessment of the Responses to Ozone of Native Vegetation at Acadia National Park. NPS Acadia D-175. U.S. National Park Service. Air Resources Division, Denver, CO. 137 pp.

 

Kohut, R.J., R. Eckert, and T. Lee.  1998.  Field Survey Handbook: Background and Methodology to Conduct Field Assessments of Ozone Injury on Native Plants at Acadia National Park. U.S. National Park Service. Air Resources Division. Denver, CO. 67 pp.

 

Krupa, S. V., A.H. Legge, M. Nosal, S.B. McLaughlin, and D.J. Downing.  1999.  Ambient ozone and growth of mature loblolly pine. In Proc. UN-ECE Workshop on Critical Levels for Ozone - Level II, Gerzensee, Switzerland, eds. J. Fuhrer & B. Achermann. Swiss Federal Research Station for Agroecology and Agriculture, Institute of Environmental Protection and Agriculture (IUL), Liebefeld-Bern, Switzerland, pp. 233-236.

 

Lipp, C and C.P. Andersen.  1999.  Respiration and substrate use in excised ponderosa pine roots. Abstract and poster presentation, 1999 Annual Meeting, Ecological Society of America, Spokane, Washington.

 

Loats, K.V. and J. Rebbeck.  1999.  The short-term effects of ozone and carbon dioxide on the growth and physiology of seedling black cherry, green ash, and yellow-poplar.  Environ. Pollut.  106: 237-248.

 

McCrady, J.K. and C.P. Andersen.  2000.  The effect of ozone on soluble root exudation of wheat.  Environ. Pollut.  107:465-472.

 

Miller, J.D., R.N. Arteca, and E.J. Pell.  1999.  Senescence-associated gene expression during ozone-induced senescence.  Plant Physiol.  120:1015-1023.

 

Olszyk, D.M., D.T. Tingey, L. Watrud, R. Seidler, and C.P. Andersen.  2000.  Interactions between O3 and CO2 on Terrestrial Ecosystems.  Springer-Verlag, New York, (In press).

 

Pell, E.J., J.P. Sinn, B.E. Brendley, L. Samuelson, C. Vinten-Johansen, M. Tien, and J. Skillman.  1999.  Differential response of four tree species to ozone-induced acceleration of foliar senescence.  Plant, Cell & Environ.  22:779-790.

 

Petersen, R., A. Bosley, and J. Rebbeck.  1999.  Ozone stimulates protonematal growth and gametophore production in pigeon moss, Polytrichumcommune Hedw.  The Bryologist  102: 398-403.

 

Polle, A. and E.J. Pell.  1999.  The role of carbon dioxide in modifying the plant response to ozone. In:  Luo, Y. and Mooney (Eds.).  Carbon Dioxide and Environmental Stress .  Academic Press, New York.  pp. 193-213.

 

Robinson, J.M. and J.A. Bunce.  2000.  Influence of drought-induced water stress on soybean and spinach leaf ascorbate-dehydroascorbate level and redox status.  Int. J.  Plant Sci.  161: (March Issue).

 

Robinson, J.M. and S.J. Britz.  2000.  Tolerance of a field grown soybean cultivar to elevated ozone level is concurrent with higher leaflet ascorbic acid level and higher ascorbate:dehydroascorbate redox status.  Photosynth. Res.  (In Press).

 

Torsethaugen, G., E.J. Pell, and S.M. Assmann.  1999.  Ozone inhibits guard cell K+ channels implicated in stomatal opening. Proc.  Natl. Acad. Sci.  96:13577-13582.