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THE EFFECT OF AIR POLLUTANTS UPON PHYSIOLOGICAL PROCESSES OF THE HORSE-CHESNUT’S LEAVES (AESCULUS HIPPOCASTANUM L.)

M. M. Zamfirache, L. Ivanescu

First published: 2007DOI pendingView metrics

Abstract

In our paper, the investigations have focused on observations regarding the physiological and biochemical changes on the horse-chesnut’s (Aesculus hippocastanum L.) leaves during their ontogenetic cycle under the influence of the atmosphere pollutants (sulphur dioxide, chlorine, ammoniac, lime or cement powders). The foliar chlorosis and necrosis represent the clear manifestation of deep physiological modifications, as well as severe structural alterations, which affect the average content of water, dry matter, and assimilating pigments.

Publication details

Title
THE EFFECT OF AIR POLLUTANTS UPON PHYSIOLOGICAL PROCESSES OF THE HORSE-CHESNUT’S LEAVES (AESCULUS HIPPOCASTANUM L.)
Authors
M. M. Zamfirache, L. Ivanescu
Proceedings
7th International Scientific Conference - SGEM2007
Publisher
SGEM Scientific GeoConference
Year
2007
Pages
Not available yet
ISSN
1314-2704
ISBN
954-918181-2
Language
en
Publication type
Conference Paper
Keywords
References4
  1. IVANESCU LACRAMIOARA, TOMA C., GOSTIN IRINA, TOMA O. (2001) Responses of the plants to the action of atmospheric pollutants. Proceedings of the International Conference Ecological Protection of the Planet Earth, Xanthi, Greece, 5-8 June 2001, vol.II : 981 – 986

  2. IVANESCU LACRAMIOARA, TOMA C. (2003) Influenta poluarii atmosferice asupra structurii plantelor. Ed. Fundatiei “Andrei Saguna” Constanta.

  3. MANESCU S., CUCU M., DIACONESCU M.L. (1994) Chimia sanitara a mediului. Ed. Medicala, Bucuresti

  4. YUNUS M., IQBAL M. (1996) Plant response to air pollution. John Wiley & Sons, Chichester. New York. Brisbane. Toronto. Singapore Table no 1- The variation of water and dry matter content in leaves of Aesculus hippocastanum from Bicazindustrial area (g%) Month Control leaves(C) Polluted leavesTaxon Water content Dry matter content Distance from the toxic source Water content % Control Dry matter content % Control 61,40 38,60 250m 61,08 99,47 38,92 100,82 May Aesculus hippocastanum 600m 60,74 98,92 39,26 101,70 58,38 41,62 250m 41,74 71,49 58,26 139,98August Aesculus hippocastanum 600m 41,30 70,74 58,70 141,03 55,11 44,89 250m 35,77 64,90 64,23 143,08September Aesculus hippocastanum 600m 40,37 73,25 59,63 132,83 Table no 2- The variation of water and dry matter content in leaves of Aesculus hippocastanum from Borzeşti industrial area (g%) Month Control leaves(C) Polluted leavesTaxon Water content Dry matter content Distance from the toxic source Water content % Control Dry matter content % Control 61,40 38,60 200m 46,87 76,33 53,13 137,64 May Aesculus hippocastanum 800m 51,72 84,23 48,28 125.07 63,87 36,13 250m 59,23 92,73 40,77 112,84August Acer pseudoplatanus 1200m 60,07 94,05 39,93 110,51 55,11 44,89 200m 32,78 59,48 67,22 149,74September Aesculus hippocastanum 800m 31,15 56,52 68,85 153,37 Table no 3a- The variation of medium content of assimilating pigmentst in leaves of Aesculus hippocastanum from Bicaz industrial area (mg/g fresh matter) “a”chlorophyll “b”chlorophyll carotenoidic pigmentsMonth Taxon Distance from the toxic source LC % LP % LC % LP % LC % Taxon Dista nce from  250 m 8,263 80,06 3,186 74,75 1,876 93,94May Aesculus hippocastanum  600 m 10,321 100 8,772 84,99 4,262 100 3,613 84,77 1,997 100 2,172 108,76  250 m 7,293 60,61 4,877 100 3,621 74,24 100 1,892 79,06 August Aesculus hippocastanum  600 m 13,072 100 4,117 31,49 3,235 66,33 2,393 1,750 73,12  250 m 7,114 54,60 3,319 78,70 1,768 73,82September Aesculus hippocastanum  60 m 13,027 100 4,028 30,92 4,217 100 3,178 75,36 2,395 100 1,286 53,69 Lc= control leaves, LP = polluted leaves Table no 3b- The total medium content of assimilating pigments (a+b+c), the ratio „a”chlorophyll/”b”chlorophyll (a/b) and the ratio chlorophylls and carotenoidic pigments (a+b/c) in leaves of Aesculus hippocastanum from Bicaz industrial area a+b+c a/b a+b/cTaxon Month Distance from the toxic source LC % LP % LC LP LC LP  200 m 13,283 80,11 1,30 4,3 May  800 m 16,580 100 14,328 86,41 2,42 1,61 7,3 5,0  200 m 9,238 45,41 1,07 2,0 August  800 m 20,342 100 14,286 70,22 2,68 1,40 7,5 3,8  200 m 8,914 45,38 1,16 1,7 Aesculus hippocastanum Septembrie  800 m 19,639 100 12,930 65,83 3,08 1,19 7,2 3,4 Lc= control leaves, LP = polluted leaves Table no 4a- The variation of medium content of assimilating pigmentst in leaves of some wooden angiosperms from Borzesti industrial area (mg/g fresh matter) “a”chlorophyll “b”chlorophyll carotenoidic pigmentsMonth Taxon Distance from the toxic source LC % LP % LC % LP % LC % Taxon Dista nce from  200 m 6,119 59,28 4,683 109,87 2,481 124,23May Aesculus hippocastanum  800 m 10,321 100 7,385 71,55 4,262 100 4,561 107,01 1,997 100 2,382 119,27  200 m 3,197 24,45 4,877 100 2,973 60,95 100 3,068 128,20 August Aesculus hippocastanum  800 m 13,072 100 6,618 50,62 4,727 96,92 2,393 2,941 122,90  200 m 3,027 23,23 2,608 61,84 3,279 136,91September Aesculus hippocastanum  800 m 13,027 100 5,462 41,92 4,217 100 4,584 108,70 2,395 100 2,884 120,41 Lc= control leaves, LP = polluted leaves Table no 4b- The total medium content of assimilating pigments (a+b+c), the ratio „a”chlorophyll/”b”chlorophyll (a/b) and the ratio chlorophylls and carotenoidic pigments (a+b/c) in leaves of Aesculus hippocastanum from Borzesti industrial area a+b+c a/b a+b/cTaxon Month Distance from the toxic source LC % LP % LC LP LC LP  250 m 13,325 80,36 2,59 6,1Mai  600 m 16,580 100 14,557 87,79 2,42 2,42 7,3 5,7  250 m 13,436 66,05 2,18 6,1August  600 m 20,342 100 9,102 44,74 2,68 1,27 7,5 4,2  250 m 12,201 62,12 2,14 5,9 Aesculus hippocastanum Septembrie  600 m 19,639 100 8,492 43,24 3,08 1,26 7,2 5,6 Lc= control leaves, LP = polluted leaves

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