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Albanian j. agric. sci. 2013;12 (4): 729-733 Agricultural University of Tirana

Correspondence: Seit Shallari; Agricultural University of Tirana, Albania; Email: [email protected] (Accepted for publication 4 December 2013)

RESEARCH ARTICLE

(Open Access)

Identification of environmental aspects and oil pollution pressure on

spontaneous flora in the Patos-Marinëz industrial area

ALMA SHEHU1, ALFRED MULLAI2, SEIT SHALLARI1*

1

Agricultural University of Tirana, Department of Agri-Environment and Ecology, Tirana

2

University of Tirana, Faculty of Natural Sciences, Tirana

Abstract

Oil industry activities have contributed to environmental pollution in general showing direct impacts on ecosystems and living creatures. Hydrocarbons are hydrophobic or water-insoluble, making difficult their removal or degradation from terrestrial environment. The aim of the study is the "identification of environmental aspects causing environmental impacts and assessment of oil pollution pressure on spontaneous vegetation”. The study area is the oil field of Patos-Marinëz. In the area under study, the pollution lies in about 200 km2, of which 60000 ha are farmland. The water receiver environment of the oil industry emissions is Gjanica River. The effects extend to Seman River delta and then to the Adriatic Sea. Consequently, the water pollution causes impacts on living creatures in marine aquatic environments. These impacts can be accumulated in the marine and terrestrial food chain endangering human health. Leaks from well mouths, oil leaks and water layer leaks from the well hole, discharges and emissions from Ballsh Processing Plant, fluid collection groups and pipelines leaks are some of the most important environmental aspects in the study area. The dominant species of the spontaneous flora are Glyceria plicata dhe Sparganium erectum accompanied by a large number of species. Natural vegetation in this area is degraded and a reduction of the photosynthesis activity is observed. Pollution control and rehabilitation of the area are necessary.

Key Words: Pollution, oil, aspect, pressure, spontaneous flora.

1. Introduction

Oil exploitation is a complex process that begins with research, opening of wells, oil extraction and continues for many years. Oil pollution can be caused due to various reasons; obsolete equipment, discharges, and accidents due to human errors [1]. Oil industry activities have contributed to environmental pollution in general featuring direct impacts on ecosystems and living creatures. Environmental effects occur upon soil, water, air, flora, fauna and human health. Various authors [4], have identified the extent of environmental pollution in areas exploited by oil industry. The data show high content of oil components such as phenols, aromatic hydrocarbons in water and soil, etc..

Oil consists of various components. There are many different oil fractions ranging from the very light oils to the heavy ones or crude oil depending on the number of carbon atoms in the chain of hydrated carbons [3]. Pollution from hydrocarbons is consistent by the fact of low availability of microorganisms and soil biological activity.

A small oil amount can be dissolved in water. This is the most bio-available part and therefore is the part that has the highest potential to cause damage to

the living creatures. This part contains potentially toxic compounds such as naphthalene, phenanthrene and dibenzothiophene [10]. The aim of this study is "identification of environmental aspects1 causing environmental impacts and impact assessment of oil pollution on spontaneous vegetation.

2. Methodology of the study

2.1. Description of the study area

The area under study is the oil field of Patos-Marinëz which extends to about 200 km2. In the area under study pollution lies in about 200 km2 of which about 60 000 ha are farmland (table 1). Contamination of soil, water and air has caused adverse effects associated with the reduction of soil fertility, plant production and contamination of food chain up to the provocation of human diseases.

The water receiver environment of oil industry emissions is Gjanica River. The effects extend to Seman River delta and then to the Adriatic Sea. Consequently, water pollution causes effects on living

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creatures in the marine aquatic environments. These effects can be accumulated in the marine and terrestrial food chain endangering human health.

Also in this area (figure 1), pollution is accumulated due to the long use of oil extraction and the lack of plans for the management of environmental impacts. The obsolete and amortized

technology is another factor that has contributed to the pollution of the area from hydrocarbons.

The industrial activities in this area have to do with the tracking or research and exploitation of oil and natural gas. At the peak of production, there were developed 338 wells in the northern zone and 123 wells in the southern zone for a total of 461 wells [9].

Figure 1. Satellite view of the study area

Table 1. Data for the territory of the area affected by the oil industry activity [9]

Form of the land use (ha)

A B C D E F

Ballsh Municipality 27,77 - 3,12 10,72 - 10,99

Patos Municipality 2,434 Roskovec

Municipality

1,157 57 - - - 20

Bubullimë Commune 2,878 42 - - - -

Cakran Commune 4,371 111 - 1,626 1,497 -

Kolonja Commune 2,833 - - 32 - -

Krutje Commune 3,781

Kuman Commune 2,281 89 110 15 36 82

Mbrostar Commune 3,280 - - 69 - -

Portëz Commune 2,104 - 55 284 21 -

Qendër Commune 3,858 256 42 40 - 33

Zharrëz Commune 2,090 2,090 36 77 36 36 77 21 77 21 - 77 21 -

Ruzhdie Commune 1,093 29 3 284 285 648

A- farmland; B-land; C- meadows; D-forests; E- pastures; F-not productive

The area under study is one of the most important agricultural areas of the country. Agricultural activity accounts for about 60% of economic activity in the area.

2.2. Identification of environmental aspects

Leaks from the mouthes of wells. In general, oil extraction wells during the work process cause environmental pollution. This situation results due to the bad hermetization of well mouths, therefore there are leaks in more than 50% of them. Oil and water

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Identification of environmental aspects and oil pollution pressure on spontaneous flora in the Patos-Marinëz industrial area

Oil storage in reservoirs. The oil is stored in

open reservoirs from which hydrocarbons evaporate. In this area is felt a strong odor from the high presence of hydrogen sulphide in the air. If inhaled for a long time, it can cause headaches and respiratory disorder.

Emissions from Ballsh Processing Plant. The

plant discharges large quantities of oil in the environment, particularly in Gjanica River. One of the causes of the oil spill on the environment is that polluted wastewater plant is not treated to function properly.

Fluid accumulation groups. Another potential

source, which causes environmental pollution are also fluid accumulation groups. These are distributed throughout the oil field sites. These groups serve for the development of gas separation process from oil and a portion of the water layer. Currently, in most of the groups, the gas separators are not in working condition, and the accompanying gas is discharged into the atmosphere, causing its pollution.

Defects and accidents. Environmental pollution

is caused by defects that occur in gas or oil pipelines, which are associated with cracks or ruptures, thus discharging gas or oil into the environment.

2.3. Identification of spontaneous fauna in the

area under study

The dominant species are Glyceria plicata dhe Sparganium erectum which are accompanied by:Glyceria fluitans, Juncus effusus, Nasturtium officinale, Veronica beccabunga, Callitriche cophocarpa, Apium nodiflore, Bidens tripartita, Apium nodiflorum, Catabrosa aquatica etj

In addition, there is identified the presence of the following species: Brachypodium ramosum, Ruscus aquleatus, Asparagus acutifolius, Teucrium polium, Cistus incanus, Cistus salviafolius, Bellis perennis, Smilax aspera, Dactylis glomerata, Poa bulbosa, Micromeria juliana, Cynosurus echinatus, Pistacia lentiscus, Paliurus spina-christi, Pyrus amygdaliformis

, Quercus ilex, Arum italicum,, Cynodon dactylon, Anthoxanthum odoratum, Briza maxima, Chrysopogon gryllus.

The accompanying species with high value of coverage amount are represented by: Typha angustifolia, Lythrum salicaria, Cladiummariscus, Alismaplantago-aquatica, Sparganumerectum, etj.

2.3. Pollution pressure on spontaneous flora

The effect of a substance on an organism or creature is determined by the bio-availability. Bio-availability means the ability of a substance to enter or penetrate the body of a living creature. Furthermore, bio-availability is dependent on physical-chemical properties of the substance. Water solubility is a feature that affects bio-availability [2].

Chronic effects occur when the body is exposed to a low concentration for a long period of time. The effects may be different; growth reduction, anomalies, reproduction or production reduction etc., [4; 6].

Pollution can affect the distribution of species in the affected area. Some species may be more sensitive than others towards oil pollution. Some species may be reduced in number or disappear from the polluted areas. Other organisms may be more tolerant towards oil being able to colonize and dominate the contaminated areas [11].

From time to time, as a result of technological processes of oil wastes, significant oil quantities are discharged in Gjanica. The presence of high level of pollution has caused serious consequences on the flora and fauna of this area. This oil has not only changed the color of the river, where occasionally oil stains the entire surface of the water, but also the vegetation that once accompanied this watershed.

The plant leaves identified in the polluted site are covered with insects Necrosis is another symptom on the leaves of spontaneous plants observed under the effect of the pollution.

Table 2. Fluorescence parameters and photosynthetic activity in some species

Plant Fluorescence parameters Photosynthetic activity

Fo Fm Fv Rfd qN NPQ

Ph. australis 126.7 357.2 230.58 1.479 0.855 1.087

Ph. australis 120.01 362.91 242.9 1.552 0.834 1.124

E.camaldulensis 159.94 640.33 480.39 1.786 0.856 1.718

E. camaldulensis 132.79 601.69 468.9 3.072 0.922 2.737

Ph.australis 110.99 509.71 398.72 3.043 0.94 2.583

Ph. australis 163.65 774.58 610.93 1.806 0.793 1.639

E. camaldulensis 124.46 459.3 334.84 1.557 0.856 1.186

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Identification of environmental aspects and oil pollution pressure on spontaneous flora in the Patos-Marinëz industrial area

Thorn). Other indicators of this degradation are the spread in a considerable degree of the invasive species

such as Dittrichia viscosa, and anthropogenic types

Asphodelus aestivus, Andropogon ischaemum,

Erigeron sp.,etc.

As a conclusion we can say that in the polluted area is observed degradation of natural vegetation; it is necessary its improvement through afforestation with native species. Afforestation would rehabilitate and improve the landscape.

4. References

1. Anderson CM, LaBelle RP.: Update of

comparative occurrence rates for offshore oil spills. Spill Sci. Technol. Bull. 2000, 6(5/6): 303-321.

2. Baussant, T., Sanni, S., Skadsheim, A., Jonsson,

G., Børseth, J. F. & Gaudebert, B.:

Bioaccumulation of polycyclic aromatic compounds: 2. Modeling bioaccumulation in marine organisms chronically exposed to

dispersed oil. Environmental Toxicology and

Chemistry, 2001, 20 (6): 1185-1195.

3. Boyd, J. N., Kucklick, J. H., Scholz, D. K. S.,

Walker, A. H., Pond, R. G. & Bostrom, A.:

Effects of oil and chemically dispersed oil in

the environment. Health and Environmental

Sciences Departement. Cape Charles: American Petroleum Institute,. 2001, 63: 2-14 pp.

4. Charls, M. G., Babcock, M. M., Harris, P. M.,

Irvine, G. V., Cusick, J. A. & Rice, S. D.:

Persistence of oiling in mussel beds after the

Exxon Valdez oil spill. Marine Environmental

Research, 2001, 51 (2): 167-190.

5. Eggen, R. I. L., Behra, R., Burkhardt-Holm, P.,

Escher, B. I. & Schweigert, N.: Peer Reviewed:

Challenges in Ecotoxicology. Environmental

Science & Technology, 2004, 38 (3): 58A-64A.

6. Fukuyama, A. K., Shigenaka, G. & Hoff, R. Z.:

Effects of Residual Exxon Valdez Oil on

Intertidal Protothaca staminea: Mortality, Growth, and Bioaccumulation of

Hydrocarbons in Transplanted Clams. Marine

Pollution Bulletin, 2000, 40 (11): 1042-1050.

7. Gomez Gesteira, J. L., Dauvin, J. C. & Salvande

Fraga, M.: Taxonomic level for assessing oil

spill effects on soft-bottom sublittoral benthic

communities. 2003. Marine Pollution Bulletin,

46 (5): 562-572.

8. Harwell, M. A. & Gentile, J. H.: Ecological

Significance of Residual Exposures and Effects from the Exxon Valdez Oil Spill.

Integrated Environmental Assessment and

Management, 2006, 2 (3): 204-246.

9. Ministria e Ekonomisë: Plani i integruar

sektorial për zhvillimin e prodhimin e hidrokarbureve në vendburimin

Patos-Marinës. Miratuar me VKM. Nr. 477, datë

16.7.2004, 15 faqe.

10. Neff, J. M. & Stubblefield, W. A.: Chemical

And Toxicological Evaluation of Water Quality following the Exxon Valdez Oil Spill.

In Wells, P. G., Butler, J. N. & Huges, J. S. (eds) Exxon Valdez Oil Spill: Fate and Effects in

Alaskan Waters, 1995, pp. 141- 177.

Philadelphia: American Society for Testing and Materials.

11. Peterson, C. H., Rice, S. D., Short, J. W., Esler,

D., Bodkin, J. L., Ballachey, B. E. & Irons, D.

B.: Long-Term Ecosystem Response to the

Exxon. Valdez Oil Spill. Science, 2003, 302

(5653): 2082-2086.

12. Regulation (EC) no 1221/2009 of the European

Parliament and of the Council of 25 november 2009 on the voluntary participation by

organisations in a community Eco-Management

and Audit Scheme (EMAS), repealing

Imagem

Table 1. Data for the territory of the area affected by the oil industry activity [9]
Table 2. Fluorescence parameters and photosynthetic activity in some species

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