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  • 1
    ISSN: 1365-2486
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology , Energy, Environment Protection, Nuclear Power Engineering , Geography
    Notes: Field data on the sulphur and cation budget of growing Norway spruce canopies (Picea abies [L.] Karst.) are summarized. They are used to test a spruce decline model capable of quantifying effects of chronic SO2 pollution on spruce forests. At ambient SO2 concentrations, acute SO2 damage is rare, but exposure to polluted air produces reversible thinning of the canopy structure with a half-time of a few years. Canopy thinning in the spruce decline model is highest (i) at elevated SO2 pollution, (ii) in the mountains, (iii) at unfertilized sites with poor K+, Mg2+ or Zn2+ supply, (iv) at low spruce litter decomposition rates, and (v) acidic, shallow soils at high annual precipitation rates in the field and vice versa. Model application using field data from Würzburg (moderate SO2 pollution, alkaline soils, no spruce decline) and from the Erzgebirge (extreme SO2 pollution, acidic soils in the mountains, massive spruce decline) predicts canopy thinning by 2–11% in Würzburg and by 45–70% in the Erzgebirge. The model also predicts different SO2-tolerance limits for Norway spruce depending on the site elevation and on the nutritional status of the needles. If needle loss of more than 25% (damage class 2) is taken to indicate ‘real damage’ exceeding natural variances, then for optimum soil conditions SO2 tolerance limits range from (27.3 ± 7.4) μg m−3 to (62.6 ± 16.5) μg m−3. For shallow and acidic soils, SO2 tolerance limits range from (22.0 ± 5.5) μg m−3 to (37.4 ± 7.5) μ m−3. These tolerance limits, which are calculated on an ecophysiological data basis for Norway spruce are close to epidemiological SO2-toIerance limits as recommended by the IUFRO, UN-ECE and WHO. The observed statistical regression slope of the plot (damaged spruce trees vs. SO2-pollution) in west Germany is confirmed by modelling (6% error). Model application to other forest trees allows deduction of the observed sequence of SO2-sensitivity: Abies 〉 Picea 〉 Pinus 〉 Fagus 〉 Quercus. Thus, acute phytotoxicity of SO2 seems not to be involved in ‘forest decline’. Chronic SO2-pollution induces massive canopy thinning of Abies alba and Picea abies only at unfavourable sites, where natural stress factors and secondary effects of SO2pollution act together to produce tree decline.
    Type of Medium: Electronic Resource
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  • 2
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Publishing Ltd
    Global change biology 2 (1996), S. 0 
    ISSN: 1365-2486
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Biology , Energy, Environment Protection, Nuclear Power Engineering , Geography
    Notes: Regarding time ranges of years, a rationale has been developed which is capable of explaining observed ‘spruce decline’ symptoms observed when spruce is exposed to air containing ambient levels of SO2. It integrates and interrelates (i) ecophysiological data (tree morphology, assimilate partitioning, canopy turnover, senescence physiology, stomatal conductance, canopy throughfall, sulphur metabolism, tonoplast symport), (ii) pedological data (soil leaching, cation recycling, litter decomposition, forest nutrition), and (iii) meteorological data (site elevation, length of the annual trunk growth period, SO2-pollution). Furthermore, it can explain field observations at numerous sites of spruce decline in central Europe where SO2 is implicated as a factor of forest decline: (i) thinning of the canopy structure; (ii) early needle senescence; (iii) cation deficiency; (iv) low SO2 tolerance at sites with depleted soils in the mountains; (v) synergism of SO2pollution and acidic precipitation; (vi) recovery after liming, fertilization and after decreasing SO2 pollution; and (vii) higher SO2 tolerances of deciduous angiosperms. Different SO2tolerance strategies are identified that are employed by more SO2-tolerant tree species. Ecophysiological SO2tolerance factors interact in a complex synergistic or antagonistic manner. It is concluded that chronic SO2 pollution at ambient concentrations predisposes mainly evergreen gymnosperms to suffer under synergistic environmental stresses (frost, drought, pathogens, etc.). Thinning of the crown structure is massive at extreme sites, where several stresses act simultaneously on the trees (depleted soils, high SO2 pollution, acidic rain, etc.). Mathematical formulations allow precise definitions of terms such as cooperativity, synergism, antagonism, vitality, predisposition, latency, etc. This universal rationale, which is applicable to all tree species, is exemplified here for Norway spruce (Picea abies [L.] Karst.). Integration of parameters yields an ordinary differential equation, which can be solved analytically. It predicts reversible dynamics of crown structures and gives an ecophysiological background to‘damage’.
    Type of Medium: Electronic Resource
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  • 3
    ISSN: 1432-2048
    Keywords: Forest decline ; Picea- Pinus ; Sulfur dioxide (tolerance, detoxification)
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology
    Notes: Abstract Contents of organic sulfur, sulfate and the inorganic cations K+, Ca2+, Mg2+, Mn2+ and Na+ were compared in needles of three conifer species differing in tolerance to chronic SO2 immissions. Sulfate and organic sulfur compounds were also measured in bark and wood. Field material was collected from Norway Spruce (Picea abies (L.) Karst.), Colorado Spruce (Picea pungens Engelm.) and Scots Pine (Pinus sylvestris L.) at sites where the SO2 concentration in air was high, and at another site where it was low. In general, sulfate contents were higher but cation contents lower at the sites where SO2 concentrations were high than where they were low. Up to 114mmol · (kg DW)−1 sulfate was measured in fouryear-old needles of Norway Spruce from the Erzgebirge (annual mean of SO2 in air 32 nl · 1−1). Sulfate accumulation in this SO2-sensitive conifer increased with SO2 concentration in ambient air and with needle age, indicating that the main part of the sulfate resulted from the oxidative detoxification of SO2. Loss of inorganic cations from ageing needles was reduced, or cation levels even increased, with increasing needle age, while sulfate accumulated. Apparently, cations served as counter-ions for sulfate, which is sequestered in the vacuoles. Individual trees differed in regard to the nature of cations which accumulated with sulfate. Calcium, potassium and magnesium were the dominating cations. Sodium levels were very low. Needles of the SO2-tolerant conifers Colorado Spruce and Scots Pine growing next to Norway Spruce in the Erzgebirge did not accumulate, or accumulated less, sulfate with increasing needle age as compared to needles of Norway Spruce. However, somewhat more sulfate was found in the bark of the SO2-tolerant species than in the bark of Norway Spruce. Scots Pine contained distinctly more sulfate in the wood than the other conifers. Since accumulation of organic sulfur compounds could not be observed with increasing needle age, or in bark and wood, reduction does not appear to play a major role in the detoxification of SO2 by the investigated species. Physiological mechanisms permitting Colorado Spruce and Scots Pine to avoid the sulfate accumulation in the needles and the accompanying sequestration of cations that are observed in neighbouring Norway Spruce are discussed on the basis of the obtained data.
    Type of Medium: Electronic Resource
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  • 4
    ISSN: 1573-5036
    Keywords: air pollutants (SO2) ; blue spruce (Picea pungens) ; forest decline ; norway spruce (Picea abies) ; pine (Pinus sylvestris) ; volatile sulfur (H2S)
    Source: Springer Online Journal Archives 1860-2000
    Topics: Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Notes: Abstract The emission of reduced volatile sulfur compounds from twigs of Norway spruce (Picea abies (L.) Karst.) was measured in the field by cryosampling and gaschromatographic analysis. Trees were growing in the Erzgebirge (E-Germany) at Oberbärenburg and at the Kahleberg and at a third stand in NW-Bavaria (S-Germany). Emission rates were also measured for Scotch pine (Pinus sylvestris L.) and Blue spruce (Picea pungens Engelm.) at the Kahleberg. Twigs still attached to the trees were enclosed in a flow-through gas exchange cuvette. H2S was detected as the predominant reduced sulfur compound emitted from the twigs. The mean H2S emission rate from twigs of Norway spruce varied between 0.04 pmol kg-1 dw s-1 at Würzburg and 6.21 pmol kg-1 dw s-1 at the Kahleberg. Comparing different species at the Kahleberg, the mean H2S emission rate was almost the same from twigs of Norway spruce (6.2 pmol kg-1 dw s-1) and Blue Spruce trees (5.9 pmol kg-1 dw s-1) but it was approximately 18 times higher for Scotch pine (110 pmol kg-1 dw s-1). The percentage of SO2-exclusion via H2S-emission of the tree species investigated at the Kahleberg is calculated on the basis of data on SO2 fluxes. It is very small for Norway spruce and Blue spruce. However, for Scotch pine, H2S emission contributes about 10% to the detoxification of SO2.
    Type of Medium: Electronic Resource
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  • 5
    ISSN: 1573-5036
    Keywords: air pollutants (SO2) ; biomonitoring (sulfate, SO4 2-) ; forest decline ; immission limits (SO2 tolerance) ; Norway spruce (Picea abies (L.) Karst.) ; stomatal SO2 uptake (dry deposition)
    Source: Springer Online Journal Archives 1860-2000
    Topics: Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Notes: Abstract Monthly uptake rates and the annual deposition of gaseous SO2 via the stomata of six Norway spruce canopies (Picea abies (L.) Karst.) in Germany (Königstein im Taunus, Witzenhausen, Grebenau, Frankenberg, Spessart, Fürth im Odenwald) were calculated (i) from statistical response functions of stomatal aperture depending on meteorological data, and (ii) from the synchronously measured SO2 immission at these stands. The stomatal response functions had been derived on the basis of thorough stomatal water conductance measurements in the field. Calculations of the SO2 conductance of spruce twigs and SO2 uptake rates via stomata need continuously measured complete data sets of the (i) light intensity, (ii) air temperature, (iii) air humidity and (iv) SO2 concentration in spruce forests from all the year. These data were recorded half hourly in different German spruce forests. The apparent needle water vapour pressure difference and transpiration rates were calculated from meteorological data. Additional use of canopy through flow data in dry years allowed the estimation of the mean stomatal conductance for H2O and SO2 of whole spruce canopies. The annual SO2 uptake of a mean unit needle surface in spruce forests was 32% of the SO2 uptake rate of exposed needles at the top of spruce crowns. There is significant SO2 uptake all the year. The mean SO2 dose at all sites and years received through the stomata was (0.25±0.07) μmol SO2 m-2 (total needle surface) (nPa Pa-1)-1 (annual mean of SO2 immission; 1 nPa (SO2) Pa-1 (air) = 1 ppb) day-1 (vegetation period per year). Comparison of calculated SO2 uptake rates into needles with measured SO4 2- accumulation rates in needles from the mentioned sites and additionally from Würzburg, Schneeberg (Fichtelgebirge) and from three sites in the eastern Erzgebirge (Höckendorf, Kahleberg, Oberbärenburg) revealed that oxidative SO2 detoxification (SO4 2- formation) dominates only at sites with high SO2 immission and short vegetation periods. Under these conditions 70 to 90% of the annual stomatal SO2 uptake is detoxified via SO4 2- accumulation in needles. Cations are needed for neutralization of accumulating SO4 2- which are inavailable to support growth. Thus, SO2 induces a dominant and competitive additional nutrient cation demand, cation deficiency symptoms and enhanced needle loss (“spruce decline symptoms”) mainly at sites, where the ratio R=(SO2 immission): (length of the vegetation period) is higher than R=0.07 nPa Pa-1 day-1. Correlation analysis of the relative needle loss versus the SO2-dependent SO4 2- formation rate revealed a significant increase of needle loss at the 98% level (Student). At sites with small SO2 immission and long vegetation periods (R〈0.07 nPa Pa-1 day-1) reductive SO2 detoxification via growth (and/or phloem export of SO4 2-) is not kinetically overburdened. Under these conditions only 30% of the annual SO2 uptake is detoxified via SO4 2- formation and spruce decline is small or absent. On the basis of the critical value R≈0.07 nPa Pa-1 day-1 recommended SO2 immission limits can be deduced on a mere ecophysiological basis. These deduced values are close to the proposed SO2 immission limits of the IUFRO, WHO and the UNECE.
    Type of Medium: Electronic Resource
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  • 6
    Electronic Resource
    Electronic Resource
    Springer
    Plant and soil 178 (1996), S. 295-310 
    ISSN: 1573-5036
    Keywords: acid load (proton balance) ; air pollution (SO2, NO2, NO, O3) ; canopy leaching (SO4 2-, NO3 -, NH4 +, Ca2+, Mg2+, K+, Mn2+) ; dry and wet deposition (canopy throughfall, stomata) ; epicuticular trace gas absorption ; forest decline ; Norway spruce (Picea abies, Pinaceae)
    Source: Springer Online Journal Archives 1860-2000
    Topics: Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Notes: Abstract At six sites in central Germany consequences of SO2, NOX and O3 deposition and of acid precipitation on canopy throughfall of sulphate, nitrate, ammonium, organic acids and of metal cations from Norway spruce crowns were investigated in the field. Measured canopy throughfall rates (mmol ion kg-1 needle dw a-1 are separated in (i) “background” ion throughfall rates in clean air and (ii) trace gas-(or acid interception)-dependent throughfall rates at ambient trace gas concentrations. Based on synchronously measured pollution, precipitation and canopy throughfall data, statistical response functions are given, which allow the separate estimation of annual rates of sulphur and nitrogen deposition into spruce canopies if only annual means of SO2 or NO2 concentrations in air are known. The specific SO2 deposition rate of (0.841±0.214) mmol S kg-1 needle dw a-1 (nPa SO2 Pa-1)-1 is 2.3 times higher than the specific stomatal SO2 uptake. The NO2-dependent nitrogen deposition of (2.464±0.707) mmol N kg-1 needle dw a-1 (nPa NO2 Pa-1)-1 is 2.2 times higher than the specific stomatal NOX (NO2+NO) uptake. These ratios (2.3≈2.2) are explained by the percentage of annual hours with open needle stomata. The shape of observed “epicuticular” SO2 and NOX deposition curves and of stomatal SO2 and NOX uptake curves are congruent. As for stomatal NOX uptake, there is an apparent compensation point at (5 to 8) nPa NO2 Pa-1. There is significant SO2-dependent canopy throughfall of Ca〉K〉Al〉Mg〉Fe in this order of relative importance. NOX deposition in spruce canopies reduces K+ throughfall and it weakly promotes throughfall of Mn2+ and Zn2+. There was no significant codeposition of sulphate and ammonium and no ion exchange of intercepted H3O+ with nutrient cations at the measured ambient pH values of the precipitation water. In the presence of O3, throughfall of Mn2+ is reduced and throughfall of K+, Ca2+ and Al3+ is enhanced. In the cooperative presence of SO2, NO2 and O3 pollution in the field there is a 1.3-fold increase of the annual K+ demand and a 1.5-fold Mg2+ demand of spruce canopies relative to the situation in clean air. This trace gas-dependent additional cation demand of spruce canopies corresponds to a needle loss percentage of (23 to 33)% if the additional K+ and Mg2+ throughfall could not be recycled in spruce ecosystems. Observed canopy thinning ranges from (13 to 26)% at the investigated six spruce stands.
    Type of Medium: Electronic Resource
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