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Handbook of Vitamin C Research

Handbook of Vitamin C Research

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<strong>Vitamin</strong> C as a Stress Bioindicator <strong>of</strong> Norway Spruce 315indirectly, all <strong>of</strong> the damaging free radicals commonly encountered in plant cell (Foyer,1993). As primary antioxidant it reacts with hydrogen peroxide (H 2 O 2 ), with superoxid (O 2 - ),hydroxil radical (OH - ), and lipid hydroperoxides (Yu, 1994), respectively; furthermore, it isalso important secondary antioxidant since it maintenance the α-tocopherol (vitamin E) poolto cope with radicals in deeper layer <strong>of</strong> membranes. <strong>Vitamin</strong> E is an efficient lipophilicantioxidant which is incorporated into photosynthetic membranes, and serves to reduce thepossibility <strong>of</strong> damages caused by singlet oxygen or lipid peroxides (Foyer, 1993; H<strong>of</strong>er et al.,2008).In last two decades, permanent survey (biomonitoring) has been performing in northernSlovenia with the aim to assess the forest health condition in the emission area <strong>of</strong> the largestSlovenian thermal power plant <strong>of</strong> Šoštanj (ŠTPP) by using the Norway spruce (Picea abies(L.) Karst.) needles as bioindicator. In the present paper, a particular attention is focused onthe determination antioxidant defence mechanisms (e.g. content <strong>of</strong> vitamin C) against thepollution stress in Norway spruce, and on assessing the bioindicative value <strong>of</strong> vitamin C as asensitive and early-warning bioindicator <strong>of</strong> environmental pollution with inorganicsubstances.2. Material and Methods2.1. Study Area and Sampling ProceduresThe study area is (used to be) exposed to huge amounts <strong>of</strong> pollutants due to its closevicinity to the largest Slovene thermal power plant <strong>of</strong> Šoštanj. It has been emitting hugeamounts <strong>of</strong> SO 2 , NO x and CO 2 (Table 1); moreover, annual emissions <strong>of</strong> heavy metalsreached up to 298 t <strong>of</strong> Zn, 60.6 t <strong>of</strong> Cr, 22.1 t <strong>of</strong> Pb, 4.5 t <strong>of</strong> As, 0.3 t <strong>of</strong> Hg, and 0.2 t <strong>of</strong> Cdbefore installation <strong>of</strong> desulphurization devices in 1995 and 2000, respectively. A pronouncedimpact <strong>of</strong> air pollution was observed in many environmental segments in the study area (e.g.soils and vegetables: Kugonič & Stropnik, 2001; forest stands: Ribarič Lasnik et al., 2001; AlSayegh Petkovšek et al., 2008; mushrooms: Al Sayegh Petkovšek et al., 2002; lichens:Poličnik et al., 2004, 2008; aquatic organisms: Mazej & Germ, 2009; wild-living ruminants:Pokorny, 2000, 2006; Pokorny et al., 2004).ŠTPP is located at the bottom <strong>of</strong> the Šalek Valley, at an altitude <strong>of</strong> 370 m, in the centralnorthern part <strong>of</strong> Slovenia (Figure 1), in the apline and pre-alpine vegetation province withmoderate continental climate. Prevailing winds are from the west and east, which has animportant impact on the distribution <strong>of</strong> pollutants in the area. In this respect it is importantthat the ground layer <strong>of</strong> the frequent thermal inversions usually does not exceed 100 m,which is far below the height <strong>of</strong> the power station chimneys. Therefore, pollutants are spreadover the hilly margins up to 1100 m above sea level, where the upper inversion layer occurs(Šalej, 1999).

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