Stomatal conductance and transpirational responses of field-grown cotton to ozone

Abstract Stomatal conductance and transpiration were measured on normally-irrigated (NI) and water-stressed (WS) field-grown cotton (Gossypium hirsutum L.) exposed throughout the growing season to a gradient of ozone (O₃) concentrations. Environmental conditions during the growing season strongly affected stomatal responses and yield reductions due to O₃ exposure. Maximum stomatal conductance and transpiration decreased with increased O₃ concentration both in NI and WS treatments. Maximum conductance in severely O₃-stressed plants averaged 30% lower than charcoal-filtered (control) plants, but maximum transpiration was only 17% lower. Conductance in WS plots averaged 22% lower than in NI plots but transpiration rates were the same in both treatments. Yield reductions induced by O₃ were highly correlated (r²= 0.84) with daily transpiration. Stomata of O₃-stressed plants opened and closed at the same rate as control plants in response to changes in light intensity, suggesting that the mechanism of stomatal movement had not been impaired by exposure to O₃. Reductions in conductance and transpiration in O₃-stressed plants were attributed to inhibition of photosynthesis by O₃, leading to accumulation of CO₂ in intercellular spaces.     

Impact of solar ultraviolet-B radiation (290-320 nm) upon marine microalgae

For years scientists and laymen alike have casually noted the impact of solar ultraviolet radiation upon the non-human component of the biosphere. It was not until recently, when human activities were thought to threaten the protective stratospheric ozone shield, that researchers undertook intensive studies into the biological stress caused by the previously neglected short-wavelength edge of the global solar spectrum. Stratospheric ozone functions effectively as an ultraviolet screen by filtering out solar radiation in the 220–320 nm waveband as it penetrates through the atmosphere, thus allowing only small amounts of the longer wavelengths of radiation in this waveband to leak through to the surface of the earth. Although this ultraviolet radiation (UV-B radiation, 290–320 nm) comprises only a small fraction (less than 1%) of the total solar spectrum, it can have a major impact on biological systems due to its actinic nature. Many organic molecules, most notably DNA and proteins, absorb UV-B radiation which can initiate photochemical reactions. It is life's ability, or lack thereof, to cope with enhanced levels of solar UV-B radiation that has generated the concern over the potential depletion of stratospheric ozone. The defense mechanisms that serve to protect both plants and animals from current levels of UV-B radiation are quite varied. Whether these mechanisms will suffice for marine microalgae under conditions of enhanced levels of UV-B radiation is the subject of this review.     

A Historical Overview of the Ozone Exposure Problem

Ozone can be found in essentially all locations in the troposphere. Too much exposure of vegetation and humans to this potent oxidizing gas can prove toxic. Reports of human toxicity to ozone first appeared in the 1800's from accidental occupational exposures when ozone was first discovered. Ozone was recognized as damaging field vegetation with a report of altered leaf morphology in grapes in the 1950s. Ozone is the major oxidant component in photochemical smog, and is produced by reactions of volatile organic compounds and oxides of nitrogen with sunlight present. Soon after the inception of the U.S. Environmental Protection Agency (US EPA), the Agency set a general “oxidants” standard (which included ozone) in 1971. A primary standard was created to protect human health and a secondary standard to protect against agricultural losses, ecological damage, and other losses. Ozone concentrations have decreased steadily over the last two decades in some areas of the U.S., but have increased in other areas. Several aspects of ozone exposure need further characterization, including better determination of rural concentrations and the relationship of outdoor to indoor concentrations. Ozone is one of the six criteria air pollutants requiring a formal reexamination of the new findings of effects on health and vegetation on a periodic basis, a process that leads to the publication of an US EPA criteria document. As a result of further study concerning ozone effects, significant changes were made to pollution standards in 1979 and 1997. This toxicant has remained a major air pollutant of concern in the U.S. despite regulation and intense study over several decades.     

Effects of enhanced UV-B radiation on pea (Pisum sativum L.) grown under field conditions in the UK

A new modulated lamp system is described. This system has successfully provided an ultraviolet-B (UV-B) supplement in proportion to ambient UV-B. The modulated system was used to simulate the UV-B environment resulting from an annual mean reduction of 15% in the stratospheric ozone under UK field conditions, but taking account of seasonal variation in depletion. The effects of this enhanced level of UV-B on the growth, physiology and yield of four cultivars of pea were assessed. Enhanced UV-B resulted in small reductions in the number of stems and total stem length per plant (respectively 4.7 and 8.7%). There were also significant decreases in the dry weight of peas (10.1%), pods (10.3%) and stems (7.8%) per plant. UV-B treatment had no effect on the number of peas per pod or average pea weight, but did significantly reduce (12.1%) the number of pods per plant. This decrease in pod number was partly due to enhanced abscission of pods during the final month of plant growth. UV-B treatment had no significant effect on chlorophyll fluorescence characteristics or CO₂assimilation rate per unit leaf area. These results are consistent with previous controlled environment experiments, and suggest that reduction in yield may be due to direct effects of UV-B on plant growth rather than a decrease in photosynthetic capacity per unit leaf area.     

Effects of elevated ozone and nitrogen addition on leaf nitrogen metabolism in poplar

臭氧和氮添加对杨树叶片氮代谢的影响 臭氧(O₃)污染和氮(N)沉降/施肥都能同时影响植物的生长。然而，几乎没有研究探究O₃和N添加对植物叶片N代谢过程的复合影响。本研究在开顶式气室(OTC)中对杨树进行了为期95 d的熏蒸实验，包括两个O₃水平(NF，环境O₃水平；NF60，NF + 60 ppb O₃)和4个N处理(N0，没有N添加；N50，N0 + 50 kg N ha⁻¹ yr⁻¹；N100，N0 + 100 kg N ha⁻¹ yr⁻¹；N200，N0 + 200 kg N ha⁻¹ yr⁻¹)。测定了与叶片N代谢相关的一些指标，包括叶片N代谢酶的活性、总叶片N浓度、NO₃⁻-N浓度、NH₄⁺-N浓度、总氨基酸浓度(TAA)、总可溶性糖的浓度(TSP)。研究结果表明，相对于NF，在8月份NF60处理显著刺激了硝酸还原酶(NR)的活性，使其升高了47.2%。当平均所有的N处理和两次取样时间时，NF60处理下谷氨酰胺酶(GS)的活性比NF处理下的高57.3%。但是O₃处理并没有显著影响TSP浓度，并且在8月也没有降低TAA的浓度。相对N0，高的N添加处理(N200)显著增加了杨树叶片的饱和光合速率(A_sat) 24%，并且分 别在8和9月增加了总叶片N浓度70.3%和43.3%。但是在8月份，N200处理下光合N利用效率比N0的低26.1%。这表明N添加导致的A_sat和叶片总的N浓度的升高是不匹配的，高N处理下，叶片中一些剩余的N没有被用于优化植物碳的同化。同时，也发现高N添加显著刺激了叶片N代谢过程，叶片中的NO₃⁻-N浓度、NH₄⁺-N浓度、TAA浓度、NR和GS活性都显著升高。然而，O₃和N添加对杨树叶片所有N代谢相关的指标都没有交互影响。这些结果将有助于更好地了解在高O₃污染和N沉降/施肥下植物的N代谢过程以及生物地球化学循环过程。     

Ambient ultraviolet radiation in the Arctic reduces root biomass and alters microbial community composition but has no effects on microbial biomass

We assessed the effects of ambient solar ultraviolet (UV) radiation on below‐ground parameters in an arctic heath in north‐eastern Greenland. We hypothesized that the current UV fluxes would reduce root biomass and mycorrhizal colonization and that these changes would lead to lower soil microbial biomass and altered microbial community composition. These hypotheses were tested on cored soil samples from a UV reduction experiment with three filter treatments (Mylar, 60% UV‐B reduction; Lexan, up to 90% UV‐B reduction+UV‐A reduction; UV transparent Teflon, filter control) and an open control treatment in two study sites after 3 years' manipulation. Reduction of both UV‐A and UV‐B radiation caused over 30% increase in the root biomass of Vaccinium uliginosum, which was the dominant plant species. UV reduction had contrasting effects on ericoid mycorrhizal colonization of V. uliginosum roots in the two sites, while it had no clear effects on fungal (ergosterol) or microbial biomass (measured both with fumigation–extraction and quantitative lipid biomarker analysis) in soil. However, principal component analysis of lipid biomarkers (phospholipid and glycolipid fatty acid profiles) showed that microbial community composition was altered by UV reduction. Although the UV responses were slight considering the large dose difference between the treatments (from near‐ambient to up to 90% UV‐B reduction), we cannot rule out the possibility that the recovery of ozone layer would change the below‐ground functioning of arctic ecosystems.     

The effect of dazomet and fosetyl-Aluminium on indigenous and introduced arbuscular mycorrhizal fungi in commercial strawberry production

Field and outdoor pot trials were conducted to assess the compatibility of an introduced arbuscular mycorrhizal fungal (AMF) isolate Glomus fistulosum ([Skou and Jakobsen sp. nov.] BEG 31) and indigenous AMF isolate/s, with biocides frequently used in commercial strawberry production, namely dazomet and fosetyl-Al (fosetyl aluminium). In the field trial, ‘Elsanta’ plants did not exhibit any mycorrhizal colonisation by indigenous AMF spp. after soil fumigation with dazomet. Recolonisation by indigenous AMF was low one year after soil fumigation and was possibly as a result of viable indigenous AMF propagules being washed in from adjacent non-fumigated fields. The degree of colonisation by the introduced AMF isolate G. fistulosum decreased by approximately 1/2 of its original value after one year in the field. Despite fosetyl-Al application Phytophthora fragariae Hickman infection was still prevalent in ‘Elsanta’ during the trial. Although fosetyl-Al did not significantly affect mycorrhizal colonisation, % total G. fistulosum root length colonisation and the proportion of it that was arbuscular, significantly decreased with increased sampling time. In the pot trial, foliar applications of fosetyl-Al significantly reduced the percentage of AMF colonisation that was vesicular and this was independent of the number of spray applications. Fosetyl-Al did not significantly influence the metabolic activity of G. fistulosum colonisation. This revised version was published online in June 2006 with corrections to the Cover Date.