availability of nutrients and increasing the leaching of mineral elements from the soil(Shaw, McLeod, 1995; Oren, 1996).The cement industry also plays a vital role in the imbalances of the env<strong>ir</strong>onmentand produces a<strong>ir</strong> pollution hazards. Toxic compounds such as fluoride, magnesium,lead, zinc, copper, beryllium, sulphuric acid and hydrochloric acid are found to beemitted by cement manufacturing plants. Cement dust had a significant effect on thegrowth of some plant species as compared with noncement dusted plants.Plants are known to accumulate a wide range of pollutants (Salt et al., 1998),and in the studies of the trees growing in the urban and industrial areas element accumulationby higher plants, lichens and mosses has been documented (Bargagli et al.,1998). The determination of macronutrients (N, P, K, Ca, Mg, S) and micronutrients(Fe, Cu, Mn, Zn, B, Mo, Ni and Cl) in plant materials is recommended to evaluate thenutritional status of crops of economic interest (Trevizan et al., 2008). Leaf analysisintegrates all the factors that might influence soil nutrient availability and plant uptake,and pinpoints the nutritional balance of the plant at the time of sampling.The aim of this study was to evaluate the effect of emitted pollutants from cementfactory JSC “Akmenės cementas” on nutritional status of apple-trees.Object, methods and conditions. The leaves of apple-tree and soil sampleswere collected in the area affected by the cement factory (CF) JSC “Akmenės cementas”.In order to test the influence of a<strong>ir</strong> pollution on the mineral nutrition ofthe apple-tree cv. ‘Antonowka’ (Malus domestica L.), leaf sampling was performedin July. Leaves of apple-trees and soil samples were collected north-eastward frompollution source, in the d<strong>ir</strong>ection of prevailing wind at a distance of 2.0 km fromthe cement factory. The garden of the intermediate location regarding industrial area(Babtai district, Lithuania) and at the same time distant from the mentioned pollutionsource, was taken as a reference site where soil samples and leaves for the analyseswere collected from the apple-tree cv. ‘Antonowka’ (Malus domestica L.). In eachsite the leaves were collected from three apple-trees and soil samples were collectedfrom location. Only fully expanded leaves were collected for elemental analysis. Preparationof the leaf samples for this analysis consisted of heating, gradual primaryashing with free access of oxygen, final ashing at 450 °C and homogenization. Forthe determination of the total content of 18 elements (Ag, Al, B, Ba, Ca, Co, Cr, Cu,Fe, Mn, Mo, Ni, P, Pb, Sr, Ti, V and Zn) the samples of the leaves were analysed byatomic emission spectrophotometry (DFS-13); at a laboratory of the Institute of Geologyand Geography. Internationally certified reference materials were used whenanalyzing the samples of the leaves. The content of N was determined by Kjeldalmethod (Allen, 1989).All data were analyzed by ANOVA (ANOVA for MS Excel, version 3.43) andFisher’s LSD test procedure (α = 0.05) and correlation analyses.Results. The soil pH of “relatively clean” garden (Babtai district, Lithuania) andthe soil sampled in the garden near the cement factory was neutral, accordingly ~ 7,3and ~ 6,9. As compared to control garden (Babtai district, Lithuania), the greatercontent of N was determined in the soil near the cement factory, which influencedthe highest, but at the same time lacking content of this element in the apple-tree30
leaves (Table 1). Deficiency of N stimulates the assimilation of P (Sadowski, 1990).A considerable amount of P was determined in the leaves from the control trees withthe greatest nitrogen deficiency and with significantly lower content in the soil. Thelowest amount of P was determined in the leaves collected from the garden near thecement factory, were significantly higher content of N was determined in the soil andthe leaves of apple-tree. Significantly higher content of Ca, as compared to referencesite, was determined in the garden soil and apple-tree leaves near cement factory.Deficiency of this element was determined in the leaves sampled in the control garden.The foliar and soil Mg level did not present greater variations among selectedgardens. The optimal content of Fe was determined in the leaves of the apple-treesgrowing near the cement factory, while deficiency of this element was determined inthe reference apple-tree leaves. The greater cumulated Fe content in the reference sitesoil does not decided the optimal Fe content in the apple-tree leaves at this site.Table 1. Amount of macroelements (mg kg -1 ) in the leaves of apple-trees (Malusdomestica L.) and soil (mean value ± confidence interval, * indicates significantdifference from the control area, when α = 0.05). C – control (Babtai garden),CF – cement factory.1 lentelė. Makroelementų kiekis obelų lapuose <strong>ir</strong> d<strong>ir</strong>vožemyje (vidurkis ± pasikliautinasintervalas, * žymi sk<strong>ir</strong>tumus nuo kontrolės, kai α = 0,05). C – kontrolė (Babtai), CF –cemento gamykla (AB „Akmenės cementas“).Garden locationSodo vietaControlKontrolėCFCemento gamyklaAmount of the elements (mg kg -1 of dry mass)Elementų kiekis (mg kg -1 sausos masės)N P Ca Mg FeApple-tree leavesLapuose15 683 ± 1 626 3 475 ± 400 9 115 ± 5<strong>28</strong> 3 089 ± 204 94.3 ± 11.820 007 ± 646* 1 134 ± 253* 16 200 ± 3 466* 3 843 ± 1 019 152.2 ± 32.7*SoilD<strong>ir</strong>vožemyjeControl 1 670 ± 210 623 ± 116 15 000 ± 1 700 11 200 ± 1 800 2.80 ± 0.14KontrolėCF3 200 ± 610* 1 163 ± 169* 45 300 ± 6 700* 14 000 ± 2 300 1.92 ± 0.32*Cemento gamyklaThe amount of Mn in the leaves of the apple-trees growing in the control gardenwas significantly higher by a factor 10 as compared to the leaves collected from thesite with industrial emission (Table 2).31
- Page 1 and 2: Lietuvos sodininkystĖs ir darŽini
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- Page 5 and 6: Table 1. Dates of blooming periods
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- Page 9 and 10: Table 4. Harvest date, end of stora
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- Page 27: 9. Leinfelder M. M., Merwin I. A. 2
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- Page 36 and 37: References1. Adriano D. C. 1986. Tr
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- Page 50 and 51: 2 pav. Kanamicino įtaka vienam eks
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- Page 75 and 76: 3. F + humistaras, 50 l ha -1 prie
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2. Eitminavičius L. 1998. Dirvože
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LIETUVOS SODININKYSTĖS IR DARŽINI
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(A-L, Gost 26208-84), mineralinis a
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Pasėlio tankis turėjo silpnai nei
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Lentelės tęsinysTable continuedHR
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3. Didžiausias svogūnų suminis (
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The increase of crop density (r = 0
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žalioji trąša) ir natūralios ki
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Lentelė. Meteorologinės sąlygos
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išeigą (65,8 %). Prekinis derlius
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Aptarimas. Rusijos mokslininkai Kon
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16. Shynkarenka A. 2005. Augalų ap
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investigators, neither single nor r
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Fig. 3. Marketable onion yield3 pav
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SCIENTIFIC WORKS OF THE LITHUANIAN
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Object, methods and conditions. P l
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the sum of chlorophylls a and b. Al
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nitrate decline (see Fig. 1).The te
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20. Matsuda R., Ohashi-Kaneko K., F
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LIETUVOS SODININKYSTĖS IR DARŽINI
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Daigams augant matuota tris kartus.
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Papildomas švitinimas mėlyna švi
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Tai ypač ryškiai rodė paprikų d
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12 pav. Fotosintezės pigmentų kie
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14 pav. Daržovių derlius: agurkų
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saldžiosios paprikos daigų šviti
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SODININKYSTĖ IR DARŽININKYSTĖ. S
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eikvojimas ir fotokvėpavimas, tod
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(1, 2 pav). UV-B spinduliuotė lėm
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įtakos turėjo visi tirti aplinkos
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14. Kirnak H., Kaya C., Tas I., Hig
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LIETUVOS SODININKYSTĖS IR DARŽINI
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Lentelė. Chrizantemų regenerantų
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Literatūra1. Adams S. R., Langton
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SCIENTIFIC WORKS OF THE LITHUANIAN
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Table. The light emitting diode com
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Fig. 2. The contents of phenolic co
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Nevertheless, our pilot results imp
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veikiamų ‘Luokė’ veislės že
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selekcijos procesą. Vienas pagrind
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Tyrimais nustatyta, kad organogenez
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Žalios spalvos augalai regeneranta
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9. Mashayekhi M., Shakib A. M., Ahm
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ATMINTINĖ AUTORIAMS, RAŠANTIEMSĮ
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Bandymų veiksnių gradacijos lente
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GUIDELINES FOR THE PREPARATION AND
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they should be understandable. The
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Turinys - ContentsA. Sasnauskas, D.
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S. Sakalauskienė, A. Brazaitytė,