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THE EFFECT OF AIR POLLUTANTS FROM BORZESTI INDUSTRIAL CENTER (BACAU DISTRICT) UPON PHYSIOLOGICAL PROCESSES OF WOODEN ANGYOSPERMES

M. M. Zamfirache, L. Ivanescu

First published: 2006DOI pendingView metrics

Abstract

We took into consideration aspects regarding the physiology at two species of wooden angiosperms cultivated in sites from industrial area of Borzesti, Bacau District: Populus tremula L. and Tilia tomentosa Moench., during their ontogenetic cycle. We also talked about aspects related to some special biochemical and physiological parameters (dry matter content and assimilating pigments content). The researches of vegetal physiology have used classical methods of investigation. The negative influence of air pollutants typical for the studied site is evidenced, first of all, by total or partial defoliation phenomenon, foliar chlorosis and necrosis, various teratological cases, notable especially at the species found on the limitrophe areas of the polluting source. The foliar chlorosis and necrosis represent the clear manifestation of profound physiological modifications, as well as severe structural alterations, which affect the average content of water, dry matter and assimilating pigments. Under the influence of both solid and gas pollutants, in die angiosperms’ leaves, the average content of a chlorophyll, b chlorophyll and carotenoidic pigments drops significantly, comparing with the standard values. The phenomenon is most often connected with the distance from the polluting source.

Publication details

Title
THE EFFECT OF AIR POLLUTANTS FROM BORZESTI INDUSTRIAL CENTER (BACAU DISTRICT) UPON PHYSIOLOGICAL PROCESSES OF WOODEN ANGYOSPERMES
Authors
M. M. Zamfirache, L. Ivanescu
Proceedings
6th International Scientific Conference - SGEM
Publisher
SGEM Scientific GeoConference
Year
2006
Pages
43-56
ISSN
1314-2704
ISBN
954-918181-2
Language
en
Publication type
Conference Paper
Keywords
References6
  1. (20.872 mg/g) and in August (20.659 mg/g). 1.IVANESCU LACRAMIOARA, TOMA C., GOSTIN

  2. IRINA, TOMA O. (2001) In the polluted leaves of the tree closest to the source, this content is minimum in Responses of the plants to the action of atmospheric pollutants. Proceedings of the August (59.63%) and maximum in May (88.10%). The minimum value is caused by the International Conference Ecological Protection of the Planet Earth,

  3. Xanthi, Greece, 5-8 considerable decrease of the chlorophyll “a” (51.37%) and of the chlorophyll “b” June 2001, vol.II : 981 -986 (64.10%) and the less important decrease of the carotenoidic pigments (93.52%). In the 2.IVANESCU

  4. LACRAMIOARA, TOMA C. (2003) Influenta poluarii leaves of the tree located farther from the polluting source, the minimum value is 2.66% atmosferice asupra structurii plantelor. Ed. Fundatiei “Andrei Saguna” Constanta. (as compared with 4.05 in the control leaves) in August; it is determined by the low 3.MANESCU S., CUCU M., DIACONESCU M.L. (1994) Chimia sanitara a content of chlorophyll “a” (53.75%) in relation with the chlorophyll “b” (81.80%), mediului. Ed.

  5. Medicala, Bucuresti compared with the control value. 4.YUNUS M., IQBAL M. (1996) Plant response to air pollution. John Wiley & The ratio chlorophylls a+b/carotenoidic pigments (a+b/c) in the polluted leaves

  6. Sons, Chichester. New York. Brisbane. Toronto. Singapore of the tree closer to the polluting source is minimum in August (3.4 as compared to 5.9 in the control sample), because of the slightly low content of carotenoidic pigments Table no. 1-The variation of water and dry matter content in leaves of some wooden (93.52%). In the leaves of the tree located farther from the polluting source, this ration angiosperms is minimum in May (3.8 as compared to 5.1 in the control sample), because of the lower from Borzesti industrial area (g%) content of chlorophyll “a” (84.57%); as to the chlorophyll “b” and the carotenoidic pigments, their values surpass the control value, being of 106.21% and 116.27%, Month Taxon Control leaves (C) Distanc Polluted leaves respectively. Water Dry e from Water % Dry % content matter the toxic content Contro matter Control CONCLUSIONS content source l content Populus 69.84 30.16 ~100 m 56.27 80.56 43.73 144.99  The species investigated react to the aggression of the polluting agents, and their tremula ~900 m 58.13 83.23 41.87 138.82 reactions are conditioned by a multitude of factors (genetic, pedoclimatic, natural Tilia 70.36 29.64 ~250 m 66.23 94.13 33.77 113.93 MAY habitat, acclimation degree, distance and position in relation to the polluting source, tomentosa ~800 m 6719 95.49 32.81 1 10.69 age, physiological status etc.). AUGUST Populus 67.22 32.78 ~100 m 50.87 75.67 49.13 149.87  The leaf necroses identified on the ligneous species investigated represent the tremula ~900 m 51.35 76.39 48.65 148.41 concrete manifestation of a profound physiological modification that influences the Tilia 68.83 31.17 ~250 m 61.73 89.68 38.27 122.77 medium water and dry substance content in the plants affected by the aggression of tomentosa ~800 m 62.23 90.41 37.77 121.17 the polluting agents in the air. SEPTEMBER Populus 63 19 3681 ~100 m 44.36 70.20 55.64 151.15 tremula ~900 m 48.83 77.27 51.17 139.01  The high dry substance content is not always related to the distance from the Tilia 67.09 32.91 ~250 m 52.63 78.44 47.37 143.93 polluting source. This content is not always directly related to the macroscopically tomentosa ~800 m 58.47 87.15 41.53 126.19 visible necroses, fact which suggests that, in certain cases, the perturbation of some physiological functions is directly followed by defoliation and drying, and in other Tabel nr. 2b-The total medium content of assimilating pigments (a+b+c), the ratio Tabel nr. 2a-The variation of medium content of assimilating pigmentst in leaves of „a”chlorophyll/”b”chlorophyll (a/b) and the ratio chlorophylls and carotenoidic some wooden angiosperms from Borzesti industrial area (mg/g fresh matter) pigments (a+b/c) in leaves of some wooden angiosperms from Borzesti industrial area Taxon Month Distance a+b+c a/b a+b/c from the LC % LP % LC LP LC LP toxic source Populus tremula ~ 100m 11.014 78.30 2.39 4.1 May ~ 900m 14.065 100 13.295 94.52 2.74 2.43 7.1 5.1 ~ 100 10.697 62.94 2.47 2.2 August ~ 9m00m 16.95 100 15.326 90.40 2.56 2.41 7.2 3.0 ~ 100m 3 10.572 62.20 2.45 2.1 Septem ~ 900m 16.995 100 13.879 81.66 2.46 2.31 6.8 2.9 Tilia tomentosa ber ~ 250m 16.256 88.10 3.42 4.2 May ~800m 18.451 100 17.314 93.83 4.53 3.54 5.1 3.8 ~ 250m 12.320 59.63 3.24 3.4 August ~ 800m 20.659 100 13.032 63.08 4.05 2.66 5.9 4.1 ~ 14.194 68.00 2.85 3.7 Septem ~2 58000m m 20.872 100 13.416 64.27 3.99 3.33 5.4 4.3 ber Lc=control leaves, LP=polluted leaves Lc=control leaves, LP=polluted leaves

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