Table 2 - Chemical properties of investigated <strong>soil</strong> profiles. Profile Horizons Depth (cm) pH EC (1:2,5) dS m Tot. CaCO3 TOC Tot. N C/N -1 g Kg -1 g Kg -1 g Kg -1 A1 0 - 5 7,1 1,95 26 71,2 5,5 13 PW1 A2 5 – 20 7,6 0,71 13 36,6 2,4 16 Cg1 20 – 80 8,3 0,17 85 1,3 0,7 2 Cg2 80 – 100+ 8,2 0,15 60 1,8 0,1 34 A1 0 – 4 6,4 0,24 7 52,3 3,0 17 PW2 AC 4– 17/23 8,0 0,12 20 5,0 1,7 3 C 17/23 – 70+ 8,5 0,10 56 0,8 1,0 1 A1 0 – 5 7,3 5,47 9 76,7 5,7 14 A2 5 – 10 6,8 5,18 9 51,7 3,7 14 PW3 ACg 10 – 35 7,0 5,14 7 28,9 2,3 13 Cg1 35 – 45 8,0 2,29 87 4,0 0,3 14 Cg2 80 –100+ 8,2 2,64 89 1,9 0,2 8 A1 0-5 7,4 0,22 20 31,9 3,0 11 A2 5-20 7,8 0,13 18 16,9 1,2 14 PW4 AC 20-60 7,9 0,10 25 11,0 1,0 11 C1 60-80 8,1 0,21 61 1,3 0,2 6 C2 80-100+ 8,3 0,36 82 / 0,2 / A1 0 – 5 8,3 1,46 18 34,0 2,4 14 PW5 A2 5– 15 8,6 1,86 25 10,8 1,0 11 Cg1 15-30 9,1 0,94 96 0,7 0,2 3 Cg2 30-70+ 8,7 1,61 114 2,9 0,0 96 A1 0 – 3/4 7,4 0,58 11 100,8 6,1 17 PW6 A2 3/4 – 20 7,6 0,23 13 28,1 2,1 13 C 20 – 80 8,1 0,09 31 6,0 0,3 18 Cg 80-100+ 8,4 0,08 51 1,5 0,1 16 A1 0 - 5 7,4 4,25 11 118,1 7,6 16 A2 5 – 13 8,1 4,02 36 25,9 2,2 12 PW7 Cg1 13 – 50 8,6 1,46 116 4,3 0,7 6 Cg2 50 – 80 8,5 1,24 118 6,3 0,2 42 Cg3 80 – 100+ 8,5 1,05 118 2,1 0,2 14 A1 0 – 5 5,8 0,44 0 139,8 6,9 20 A2 5– 20 7,2 0,28 18 46,5 3,0 16 PW8 C1 20-80 8,4 0,18 123 4,2 0,2 24 C2 80-100+ 8,5 0,31 123 7,0 0,2 30 A1 0 – 5 8,1 3,01 11 49,3 4,1 12 A2 5 – 10 8,5 3,00 24 21,4 2,1 10 PW9 Cg1 10 – 30 8,7 2,28 103 3,9 0,5 8 Cg2 30 –80 8,5 3,57 147 2,1 0,3 8 Cg3 80-100+ 8,6 3,56 130 2,0 0,2 9 Au1 0 - 3 7,7 0,60 141 73,1 7,1 10 Au2 3 – 7 7,9 0,49 168 42,9 4,4 10 Au3 7 – 25 8,0 0,33 179 31,8 3,2 10 GP1 Bwu 25 – 57 8,5 0,17 232 5,8 0,8 7 BCu 57 – 80 8,6 0,19 221 2,9 0,8 4 C 80 – 100+ 8,6 0,24 201 0,0 3,2 0 Au1 0 – 5 7,8 0,15 176 33,9 1,0 34 Au2 5 – 30 8,1 0,13 226 6,8 0,8 9 GP2 Bwu 30 - 50 8,4 0,15 234 6.1 0,8 0 BCu 50 - 65+ 8,4 0,13 237 3,5 1,3 3 Ap 0 – 40 7,9 0,19 203 12,4 1,3 10 Bw1 40 – 65 8,3 0,15 208 8,2 1,0 8 2Bw2 65 – 81 8,2 0,22 234 6,4 0,9 7 P<strong>ER</strong>1 3Cg1 81 – 110 8,3 0,21 219 3,2 0,3 10 3Cg2 110 –140 8,3 0,28 214 3,1 0,4 9 4Cg3 140-200+ 8,6 0,40 250 8,5 0,7 13 Ap1 0 – 28 8,5 0,17 203 11,3 1,3 9 Ap2 28 – 53 8,5 0,17 204 9,5 1,1 8 Bw1 53 – 83 8,8 0,20 237 5,9 0,7 9 P<strong>ER</strong>2 2Bw2 83 – 130 9,0 0,48 234 5,6 0,6 10 3Cg1 130 – 153 9,1 0,37 228 3,9 0,4 10 3Cg2 153 – 194 8,7 0,31 241 3,7 0,3 12 3Cg3 194 – 210+ 8,8 0,33 221 2,5 0,4 6 122
C horizons that make up the parent material are characterized by lighter colours, between 2,5Y6/3 <strong>and</strong> 2,5Y7/2 (dry colour). Most of the radical apparatus, usually fine <strong>and</strong> very fine, are located in the epipedon, which are characterised by a fine granular structure that shows an extremely weak aggregation degree. The parent material has fewer roots, generally having a medium or sometimes coarse size, destined to the physical anchorage of plant species present. The trend often turns out to be subhorizontal, mainly as to horizons subject to periodical <strong>water</strong> saturation, highlighted by the presence of mottles (g). The texture, assessed in quick way through the sample manipulation, proves to be always s<strong>and</strong>y, except for the PW9 profile, where it is s<strong>and</strong>y-loam. The rock fragments are usually absent, except for the presence of scattered fragments of shells, <strong>and</strong> the distinctness class of the boundaries between the horizons are either abrupt or clear, having a wavy or smooth topography. The <strong>soil</strong>s of the “Perdisa” farm are very deep, with a sequence of A/B/C horizons. The colour shows quite a moderate variability range (2,5Y7/3 – 2,5Y4/3, dry colour) but with poorly linear trends. This aspect, together with the different texture <strong>and</strong> structure features that can be observed in both profiles, is referable to transport <strong>and</strong> deposition of sediments, that occurred in these environments. The texture of surface horizons is silt loam (P<strong>ER</strong>1) <strong>and</strong> silty clay loam (P<strong>ER</strong>2), while in depth it becomes s<strong>and</strong>y loam <strong>and</strong> silty clay as to P<strong>ER</strong>1, <strong>and</strong> silt loam as to P<strong>ER</strong>2. The surface structure, usually sub-angular blocky of moderate degree at surface, becomes loose (P<strong>ER</strong>1) or weak (P<strong>ER</strong>2) at depth. The biological activity, expressed through the presence of radical apparatus, is generally present up to a depth of about 100 cm while, as far as the P<strong>ER</strong>2 profile observed inside the orchard is concerned, it reaches higher depths. The two profiles observed in the public park of Ravenna show a sequence of A/B/C horizons. The colours of said horizons are between 2,5Y5/2 <strong>and</strong> 2,5Y7/4 (dry colour); <strong>and</strong> similarly to what observed for the farm <strong>soil</strong>s, they have irregular textures <strong>and</strong> structures due to the stratigraphy of river course sediments. However, the remarkable presence of brick fragments along the profiles (u) shall be highlighted, as an evidence of rearrangements <strong>and</strong> disturbance actions carried out by man during the centuries. Soils chemical-physical features. As far as total organic carbon (TOC) is concerned, the <strong>soil</strong>s of the San Vitale Pinewood are characterized by significant rates in the A1 epipedon (139 to 31 g of Corg . kg -1 ), but show a sudden decrease already in A2 horizon, below 5 cm of depth, with rates between 51 <strong>and</strong> 5 g . kg -1 (Vittori Antisari et al., 2008). A similar situation occurs in the profiles of the public park while, as far as the farm is concerned, the values are remarkably lower <strong>and</strong> typical of tilled <strong>and</strong> cultivated <strong>soil</strong>s. Similarly to what observed for TOC, also the total nitrogen content (Tot. N) of surface horizons turned out to be elevated at surface, in the pinewood <strong>soil</strong>s <strong>and</strong> in the public park GP1 profile, <strong>and</strong> rapidly decreased next to C horizons. In the Per- 123
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ALMA MATER STUDIORUM UNIVERSITA DI
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Preface This third volume of the "Q
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Analytic index / Index analytique /
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. Marina Gatti, Anna Flora Campanal
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Sessione/Session I. Air quality Qua
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Mots-clés: Caractérisation physic
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120 100 80 60 40 20 0 . 120 100 80
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na del materiale particellare atmos
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zione degli IPA sui gas direttament
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Discussion The Lichen Biodiversity
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values, even if quite different fro
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CONTI M.E., CECCHETTI G. (2001) Bio
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26
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irrigation. Le déplacement de la z
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ecorded by the use of a GPS and the
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There were observed seasonal variat
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The concentrations of copper in the
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VAN BENNEKOM A.J., SALOMONS W. (198
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d'échanges cationiques à l'interf
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Results The oxygen and hydrogen iso
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References 42 Figure 3 Distributi
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ésultant de la contamination par l
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At selected sites, sampling was car
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Moreover, this process is clearly r
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Fondazione Banco di Sardegna. Autho
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ive ouzbèke, est encore critique.
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cooperative enterprises; Sovkhoz we
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Kazakh and Uzbek cotton fields suff
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evaluation: if finished, it could p
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period such as a reduction of cotto
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PIASTRA S. (1992) «(...) no one ha
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distribuzione fuori commercio del l
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Risultati Alla fine, fu deciso di r
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Riferimenti bibliografici ARCHAIMBA
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Mots-clés : Rana perezi; asymétri
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- Page 82 and 83: 3. F. Reno a Casalecchio Tiro a Vol
- Page 84 and 85: Conclusioni In linea generale, per
- Page 86 and 87: Introduzione Il territorio imolese,
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- Page 103 and 104: Figure 1 - Role of the soil in the
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- Page 107 and 108: Lupicka et al., 1997; Krzysko-Lupic
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- Page 121: Table 1 - (follows) Pro ile GP1 GP2
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- Page 127 and 128: ALLOWAY B.J., (1995) The origins of
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- Page 149 and 150: PRELIMINARY RESULTS ON THE DISTRIBU
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- Page 159 and 160: References ADRIANO D.C. (2001) Trac
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elevati riscontrati nello stesso pu
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.SOIL AND LAND QUALITIES INFLUENCE
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Problematiche di conservazione dei
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colte sono state determinate utiliz
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e i vari fattori in gioco nel cambi
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CONTROL AND ANALYSIS ACTIVITIES ON
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totali) e dei limiti superiori per
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Bibliografia DECRETO LEGISLATIVO 3
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SOIL MICROARTHROPOD CONTRIBUTION TO
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zione fornita dall'ambiente ipogeo
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miorecettori. Queste strutture, che
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di comunità, la struttura di comun
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- non devono migrare su lunghe dist
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TRACE ELEMENTS IN FRUIT AND VEGETAB
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with trace metal may be due to irri
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chronic hazards. In addition the da
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SOIL DEPLETION DUE TO URBANISATION
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207
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Table 1 - Soil types present in the
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Soil delineations Surface in hectar
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Approximately 3.5% of the soil surf
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MINERAL HORIZONS, ELECTROMAGNETIC F
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slope movements, the flows of the m
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Materials and methods The research
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are under higher pressure, the valu