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Konferans kitabımız
çıktı...

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1. Dr. Leonard Stone
2.
Prof. Dr. Işık Oray
3. Sibel Aktunç
4.
Prof. Dr. Emur Henden
5.
Prof. Dr. Adnan Aydın
6. Betül Atasayan
7.
Prof. Dr. Fethi Doğan
8.
Prof. Dr. Ümit Erdem
9. Dr.
Konstantin Sobolev
10. Prof. Dr.
Burgio Guiseppe
11. Doc.
Dr. Hüseyin Gökçekuş
12. Prof. Dr.
Aysel Atimtay
13. Dr. Okay Camgöz
14. Prof. Dr.
Ercan Tatlıdil
15. Alan Bates
ABSTRACTS
THE SOCIAL
EFFECTS OF MINING AND THE CMC MINE PROBLEM
Leonard A Stone
ABSTRACT
The objective of this paper is to stress the significance of a local
environmental problem in Lefke, and in particular its social effects. A foreign firm has
created the Lefke environmental problem. Existing laws and regulations, as well as the
willingness of the present generation seems, thus far to be incapable of solving the
problem. A clear cut definition of the property rights of the CMC site and sound
management policies about solid waste problems form an important starting point for the
solution of this specific problem. The social effects of this mining problem on the local
community is of paramount importance and is especially assessed; as is the role of
regional institutions, and in particular the European Union.
------------------------------------Biographical Sketch
Dr Leonard A Stone achieved his PhD from the University of Wales in
1991. He has authored two textbooks, Notes Towards A Definition of Politics (1998),
and Representations of Turkey – a primer (1998). He has also published numerous
articles on Turkey and Eurasia. He is currently researching a book on Central Eurasia.
Dr Stone lectures in International Relations at the European University
of Lefke. Prior to this appointment, he has lectured in Hungary, Czech Republic, and
Singapore, and headed the Department of International Relations at Atılım University,
Turkey. Dr Stone is a member of IPSA-affiliated Geopolitics and Local-Global Relations
Research Committees. He is also a life-long honorary member of the Environmental Society
of Lefke. A Research Profile of Dr Stone is available on the following Web Site: http://myprofile.cos.com/Lentil.html |
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| Investigations on Selected Fishes in the
Bay of Güzelyurt in 2000 – 2001
ABSTRACT
Prof. Dr.Işık K. Oray
European University of Lefke
Gemikonağı, T.R.N.C.
University of İstanbul
Faculty of Fisheries
Laleli, İstanbul
The biological investigations in the waters of the Turkish Republic of
Northern Cyprus (TRNC) were first conducted in the spring of 1977 and in the summer of
1998 by BENLİ et al (1999).
Investigations on:
- Growth, length and weight relationships of Swordfish (Xiphias gladius L. 1758) in the
Bay of Güzelyurt in 2000 – 2001.
- Studies on the CPUE (Catch Per Unit Effort) of Swordfish per longlines in Güzelyurt Bay
in 2000 – 2001.
- Studies on growth, length – weight relationships of Bluefintunas (Thunnus tynnus L.
1758) in the waters of TRNC in 2000 – 2001.
- Studies on growth, length and weight relationships of Atlantic Little Tunny (Euthynnus
alleteratus Refinesque, 1810) in the Bay of Güzelyurt in 2000 – 2001.
- Studies on length – weight relationship of Bogue (Boops boops L. 1758) in Güzelyurt
Bay in 2000 – 2001.
- Investigations on Abudance and Catch Composition of Fish in Güzelyurt Bay in 2000 –
2001.
were started recently by the author.
Investigations on the Effects of Cyprus Mining Company (CMC) on marine
organisms in the Bay of Güzelyurt are urgently needed.
The results of these investigations for the period of 2000 – 2001 will be published
in 2002.
The sea coast of TRNC is 396 km. comprises %50.6 of the total coast line of the Island
of Cyprus.
The predicted bio-mass of demersal fishes in the Bays of Gazimagusa is around 500 tons.
The evaluations carried on demersal fish stocks in Güzelyurt and Gazimagusa Bays indicate
overfishing in those areas. (Benli et al 1999)
In 100 – 600m, the boarfish Capros asper L., 1758 is found very frequently in Cypriot
waters. This fish has no economical value being a very important feed for the swordfish.
(Simones and Andrade, 1999)
The feed for Bluefin tunas; Chub mackerel, Scomber japonicus, Houttuyn, 1780 and
mediterranean horse mackerel, Trachurus mediterraneaus (Steindachner, 1863) are found in
20 – 600m in big quantities in North Cypriot waters.
The annual fish production in North Cyprus in 1996 was 450 tons, i.e. 2.5 Kgs / per
person / year. (Hoşsucu et al 1998)
In the waters of TRNC, big migratory pelagic fish, namely bluefin, little tunny, bullet
tuna, swordfish and greater amberjack are found in sufficient numbers.
If the small fishing boasts of today, mostly between 9 – 12m could be substituted
with more bigger and powerful boats, some of these fish could be caught big numbers.
By introducing fishing with purse seines; big and small pelagic fish could also be
caught in big numbers.
The most commonly used small long – line boats should be in such a way developed,
that they use automatic longlines designed to fish in deeper layers for swordfish and
bluefintunas.
Introducing the aquaculture of see bass and see breams in suited areas in offshore
cages and encouraging farming of Bluefin tunas in pens, as being practiced in the
Mediterranean sea would surely increase the fish production in TRNC waters.
Bearing in mind that the island is surrounded by seawater, a program on sea fisheries
at university level in a TRNC – University should immediately be started.
The fisheries sector should be encouraged with low interest credits.
Sufficient cold storage facilities should be introduced. At least three harbours for
fishing boots should be built in suitable places in TRNC.
The organization of the fishermen in form of fisheries unions should be accomplished.
After introducing a three-year plan for Effective Fisheries in TRNC; a gain of
12.700.000 US dollars per year does not seem utopic (Oray, 1999).
References
Benli et al 1999: Kuzey Kibris Deniz alanlarının
biyoekolojisi üzerinde bir ön araştırma. Tarım ve köyişleri Bakanlığı Su
ürünleri Araştırma Enstitüsü Müdürlüğü, Bodrum.
Hoşsucu H., et al., 1998: Kuzey Kıbrıs Türk
Cumhuriyeti Kıyı Balıkçılığının yönetim Projesi. KKTC. Tarım ve Orman
Bakanlığı Hayvancılık Dairesi T.C. Ege Üniversitesi Su Ürünleri Fakültesi
Oray, I. K., Günyaktı, Çelik B., 2000: Kuzey Kıbrıs Türk Cumhuriyeti ve
Balıkçılık, 1. Ulusal deniz Bilimleri Konferansı, Poster Ankara
Simones, P. R., Andrade, S. P. 1995: Feeding Dynamics of Swordfish (Xiphias gladius) in
Azores Area. ICCAT.SCRS / 99 / 92
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| SİBEL
AKTUNÇ
Abstract
The results and effects of the open cast mining and refinery operations
of the Cyprus Mining Corporation in Lefke, Gemikonagi have been assessed by many
scientists. The accumulation of the chemical wastes has lead to enormous land
contamination, sea pollution, ground water pollution and air pollution. This environmental
problem has been defined by many authorities as the Eastern Mediterranean problem rather
than owing it to the island of Cyprus.
Within the countries of the EU, there is no single policy model for
dealing with contaminated land, and EU itself has not addressed this particular issue yet.
The norm across Europe is that any party causing contamination of a site is obliged to
remediate the soil and contaminated sites. Accordingly, most remediation work is carried
out by private bodies.
The underlying principles of The Sixth Environment Action Programme of
the European Union "Environment 2010: Our future, our choice" is to integrate
environment into economic and social policies and to increase the responsibility of the
stakeholders, citizens and businesses which should take more ownership of efforts to
protect the environment. At the beginning of the 21st century, should this be
an approach of any business, then it is a serious question to pose that what should be the
role of this mining company in restoration of the site in Lefke. |
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| ENVIRONMENTAL RISKS OF MINING USING CYANIDES AND ACIDS
Prof. Dr. Emur Henden, Ege University, Faculty of
Science, Department of Chemistry,
35100 Bornova, Izmir.
Mines are wealth of a country beneath the soil and mining adds a lot to
a country economy when done properly. However, until nineteen seventies understanding our
environment and impact of environmental pollution on life was not enough. Most of the
detailed standards on environmental pollution have been introduced in the last 30 year.
So, most of the earlier miners did not bother about environmental pollution. We can
,therefore , see several deserted mining area left unprotected causing serious risk for
the environment and life. CMC mine remains in Gemikonagi and Karadag regions of Lefke are
of the most serious examples of such cases.
Mining when realized by physical means , example; crushing, grinding
and water extraction and so on, does not usually increase the risk of chemical pollution
significantly. However , when chemicals are introduced at the mining or mine processing
process the risk of chemical pollution also increases drastically. In such cases,
nowadays, very strict measures are required by the regulations to be taken. Such mining
and mine processing plants are better be considered as chemical plants rather than simple
mining.
ACIDS AND CYANIDES IN MINING
Acids are used for extraction of metals from minerals like copper as in
the CMC case and sodium cyanide is used for the extraction of gold and silver. Because of
these extractions processes environmental pollutions with heavy metals and cyanides are
usually observed if strict measures are not taken. It is well known that cyanides are of
the very fast acting toxic substances known and great care are to be taken when used.
Cyanides may cause water air and soil pollution. Some of the metals are
toxic even when enters into body at trace level. They show acute toxicity when taken at
relatively larger amounts and chronic effect when taken slowly at smaller amounts. They
deposit in the body mainly in liver, kidney and cause liver deformation, renal failure and
many other deficiencies. They cause their harm in a very long period and ,therefore, are
usually not detected. Some of the metals are even accepted to be carcinogenic.eg.,
selenium and arsenic. Of these toxic metals lead, cadmium, mercury, arsenic, antimony,
nickel, copper and berillium take more attention. However, some of the metals which are
normally accepted as nontoxic may become very toxic when converted to some of its other
chemical forms in the environment usually by the effect of some specific bacteria,
eg.,inorganic tin compounds are not toxic, but may be converted to tributyltin in the
environment and becomes very toxic. Moreover, some metals even when present at very high
concentration in soil may not be bioavailable for the plants. Toxic metals in such
chemical forms are much less dangerous for the plants and thus animal life compared to
their bioavailable forms. Therefore, for soil pollution testing total and bioavailable
metal contents are both need be measured.
KARADAG MINING AREA
In this area remains of underground mining shafts, leaching ponds, and
contaminated soil piles exist. These wastes may contain various metal sulphides and metal
sulphates incluiding that of toxic metals , eg; copper, arsenic, mercury . The soil pH is
very low and, therefore, can be defined as hazardous. Leaching of the toxic metals
contaminates the water reservoir in the region. Unacceptably high concentrations of
aluminium, iron and manganese were reported (1). These type of mine wastes may form natural
acid leach by a chemical reaction.
FeS2 + 3.5 O2 + H2 O ® Fe2+ + 2SO4 2- + 2H+
Similar chemical reaction takes place with copper, lead and other metal
sulphides, releasing water or acid leachable iron, copper, lead and other metal salts.
Moreover ,the sulphuric acid formed reduces the soil pH and dissolves also other minerals
causing toxic metal contamination of soil, water and ,thus plants .
GEMIKONAGI AREA
During the time of mining,1913-1974, raw ore was brought to Gemikonagi
mine processing area. At present, unattended and unprotected contaminated wastes are
located in this area, including several tailing ponds, waste water clarifiers, row copper
ore piles, waste piles, and remains of mine acid processing plant. Another serious waste
is the possible cyanide containing yellow waste pile.
Chemical reactions are still going on in some of the waste ponds. Acid
generation and reaction of acids with wastes are visible. The solid and liquid wastes are
very highly polluted and acidic. Liquid draining to sea has a pH as low as 2 and contained
at one time 121- 149 mg/L copper, and its electrical conductivity was very high, 8 mmho/cm
(Henden, 1999). These waste water drains from the polluted area are serious sources of sea
water and sediment pollution.
The yellow waste piles are known to be the wastes of gold extraction
process with cyanide. Gold is usually extracted from powdered minerals using about
800-1000mg/ L sodium cyanide solution at pH 10-11, as gold cyanide complex ion. However,
other cyanide complexing metals are also converted to their water soluble cyanide
complexes during the gold extraction. These include zinc, nickel, copper, silver, iron,
mercury, cobalt..etc., according to the following chemical reactions:
4 Au(s) + 8 CN(- aq) +
O2 + 2H 2O Û 4[
Au(CN)2 ] - (aq)
+ 4OH- (aq)
Fe(OH)2 (s) + 6CN(aq)-
Û Fe(CN)64(aq)- + 2 OH- (aq)
Cu(OH)2 (s) + 4CN(aq)-
Û Cu(CN)42(aq)- + 2OH- (aq)
Moreover, because of the high pH used for gold extraction other toxic
metals like
arsenic and antimony are also extracted mainly as AsO43-
and SbO43- . Inside the yellow
waste piles all these highly toxic water soluble metal complex ions may exist at
untolerable levels. All these metals exist originally in the minerals ,but they are either
stable or blocked within the mineral structure so that they are not dissolved in water
under environmental conditions . However, when minerals are treated with cyanide at high
pH solutions, all these heavy metals are converted into their water soluble compounds,
thus become bioavailable and toxic to life. Free cyanide like sodium cyanide, is not very
stable in the environment under unprotected conditions and decompose by the effect of air.
However, heavy metal cyanide complexes are much more stable and may exist for years. Since
gold in minerals is extracted with very high concentration of cyanide all the natural
bacteria in the soil die and, therefore, biodecomposition of cyanides in the wastes do not
take place. Taking into consideration of the possible existence of the high concentration
of cyanides inside the yellow piles ,these piles should not be destroyed until careful
analyses are carried out. If destroyed without taking any care, water pollution with
cyanides and toxic metals , and air pollution with very toxic HCN and dicyan,(CN)2,
gases may take place. Therefore, these yellow piles should be analysed for cyanides and if
cyanides are present, the waste soil should be treated to destroy cyanides and to
stabilize the heavy metals.
IN SUMMARY
It is clear that both Karadag and Gemikonagi regions are very heavily
polluted and need to be cleaned as soon as possible.
- Dangerous pollution exist in soil, surface and possibly ground water, in sea water and
sediments and in air, at least, in the mine processing area and the ponds.
- The Gemikonagi mine processing area is highly dangerous even to walk inside. This area
should be protected and free walking inside should be forbidden.
- Before beginning reclamation of the area, soil, surface and underground water and plants
around and sediments should be analysed in details. Types and concentrations and even, in
some cases , chemical species of the toxic metals are to be determined in order to decide
the measures to be taken for treatment and reclamation.
- Economically valuable wastes or mineral remains are to be determined , and if present
sent to appropriate plants for use.
- Waste water should be avoided to reach the sea and fishing in the close area should be
forbidden.
- Further pollution of water in the Water reservoir should be avoided. For these purpose
acid drain to the reservoir can be avoided. However, if the present sediments in the
reservoir continue to contaminate the water they may be cleaned out from the bottom. Water
quality at present is not good enough for irrigation. If necessary, simple chemical
measures can be taken to clean and obtain a much better quality water for irrigation if
the reservoir protection delays.
- Methods of treatments of such wastes are well known. However, since the capital required
for all these analyses and treatments are very high, supports of international
organizations and CMC need to be search for.
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| IMPACTS OF CONTAMINATED SOIL LEACHATES ON THE ENVIRONMENT Prof.
Dr. Adnan AYDIN
Marmara University, Director of Environmental Research Center
Göztepe Kampüsü, Kadıköy-İstanbul/Turkey
I am pleased to be here with you to present a paper in the
International Conference organized by the European Institute of Cyprus and Lefke
Environmental Society.
Environmental pollution today is an important problem which has been
strongly threatening our world. Industrial processes and the settlements of the people
should be strictly taken under control by regarding regional and global environmental
affects. Circulation of material in different media, carries the effects of regional
pollutions to the near or far parts of the world. Thus, some regional problems may become
important global problems by time.
From environmental point of view, an industry should be judged along
with its supporting minor or initial activities. For example, paper consumption and
marketing data orient the processes in the paper manufacturing industry and the extent of
the use of forests. Uncontrolled destruction of forests are believed to be responsible for
greenhouse effect and changes in climates.
Depletion of the ozone layer and greenhouse effect are the global
environmental problems. However, pollution of water bodies and air are also global
problems. Pollution in Danaube river, as well as extensive marine transportation through
Turkish Straits are very important to protect the Black Sea-Marmara Sea-Mediterrenian Sea
System. In aqueous and gaseous phases, it is not possible to trap the pollutants
efficiently.
Pollutants ,regardless they are domestic or industrial in nature, can
be easily transferred between physical phases. Soil, is a stationary solid phase, unless
it is somehow moved, is an important trap for pollutants. However, it can release the
pollutants into mobile phases by several activities which may be physical, chemical,
biochemical or biological processes.
North Cyprus society has encountered a challenging environmental
pollution problem due to the older copper enrichment factory. The Conference Site is near
of that area of idle mining and floatation factory for copper. We have been informed that
the area had several environmental problems since its running periods during which the
wastes of any kind have not been treated by any means.
Cyprus Copper Mines has not been running
since 1975. The Gemikonağı Copper Mining and Floatation Factory is located by the
Mediterranean shore at Gemikonağı in Northern Cyprus. It is known that stormwater run
off is being discharged into the Mediterranean Sea. The Surface Water Storage Reservoir by
the area has also been seriously threatening by the storm water run off. The floatation pools
are still potential polluting sources which are being activated whenever it rains.
The mining area includes underground mining shafts, leaching ponds and
destroyed natural texture along with contaminated piles of residues. The residues are
estimated to be around 2 million tons which contain sulfates of copper, iron, arsenic,
lead, manganese and aluminium as well as their oxides, silicates etc.,
From the cyanide leaching applied in the mining processes also left
partly leaked cyanide drums in the working area. Although the possibility for the
existence of free cyanides is very low, it can be told that some parts of the residues and
wastes should contain complexed cyanides which are more resistant against decomposition.
However, they are potential danger for the environmental health, since they are
susceptible partially against air oxidation, by which route, some of the polluting heavy
metals can be leached by rain and underground waters.
In the area there are five circular wastewater clarifiers with around
100 m diameter and 3 m depth, and they contain around 100.000 tons of waste material which
need to be handled.
As a result, from the mining , leaching and floatation processes the
soil and sea water should be dangerously contaminated to threaten the public health,
agriculture and ecological properties of the Sea. The contaminated area covers approx. 4
square kilometers.
According to EPA,1991*,1 13 metals are to be detected at
hazardous waste sites.
Silver Mercury
Arsenic Lead
Barium Selenium
Cadmium Thallium
Chromium Antimony
Nickel Copper
Zinc
*EPA (U.S.Environmental Protection Agency),(1991),
Seminar Publication: Site Characterization for Subsurface Remediation, Report No : EPA/
625 / 4-91 / 026, Cincinnati, Ohio,45268 .
The piles of residues from the mining and floatation processes have
most of these elements in appreciable quantities.
Preliminary analytical results of the environment has indicated that
such contaminations are at serious levels. A blended soil sample taken from smelting
facility has been found to have moisture 15.57%; lead 153 mg Pb/kg dry soil ; copper 510
mg Cu/kg dry soil and iron 153.333 mg Fe/kg dry soil2.
Short Analysis of Blended Soil Sample
Taken From Floatation Facility (*,2)
pH 2.73 Cu (mg Cu/kg dry soil) 510
H2O (%) 15.57 Fe (mg Fe/kg dry soil) 153.333
Pb (mg Pb/kg dry soil) 153
(*) Bilge Alpaslan, M.A.Yükselen,”Remediation of Heavy Metal
Contaminated Soils” MSc Thesis on Env.Eng.,Marmara University, Institute for Graduate
Studies in Pure and Applied Sciences, 1999.
At some sites, arsenic, chromium, selenium and manganese have been
found in soil by TCLP (Toxicity Characterization Leaching Procedure ) at appreciable
concentrations. Cyanide, sulfate, arsenate and chloride are the most abundant anions which
have been extracted by water.
Since the contamination levels are to be different for a specific
pollutant from site to site, in the future a detailed study need to be taken into
consideration.
Remediation of the Site
The landfilling of the mining, leaching and/or floatation wastes which
can be a choice to regain the agricultural area needs carefull examinations of the filling
site in order to determine its geology as well as its hydrogeology.
However, landfilling is not always the solving of the problem. The
filled land also may act as an continous polluting source. Thus, a proper remediation
project is needed for the site.
In-situ treatment technique soil flushing and other techniques may be
of worth in future for special restricted areas. Leachability of heavy metals from soil
can be decreased by use of stabilization/solidification(immobilization) techniques.
Application principles of these techniques may be selected regarding the properties of
contaminated site and the intended use of site.
Recreation activities at the mining site is also a problem which should
be planned before the new attempts are held to run the mine and the factory.
For a mid-term conservation, my opinion is that the piles and the silt
could be prevented from conducting with storm waters by use of water-proof clay layers
which are spreaded 1 m beneath the contaminated soil. The clay application can be done by
preparing the compartments of piles. Polluting heavy metals and anions can be taken by the
properly chosen plants from the polluted soil. Thus, selective plantation at the area may
help to inhibit the wind errosion and the surface soil layer can be freed from the
metallic contaminants by several harvestes. The harvested plants need to be fired under
control of wastegases.
Transfer of Pollution
As previously given, transfer of pollution is one of the most important
environmental problems. The natural means of pollution transfer are air and water
circulations. Water supplies and uncontaminated soils can be easily contaminated by
drainage of polluted water through the soil layers or by the surface waters. For
agricultural and domestic usage, polluted underground water need to be effectively treated
or otherwise should be prevented from use. Polluted soil is always a pollution source
since it is open to uncontrollable chemical reactions and to both the biological and
biochemical activities.
Mobility of metals in soil depends upon their reaction capability with
the soil components. This can also be seen from the laboratory experiments. In the thesis
of Alpaslan, extraction of metals by use of water with pH 2 or with pH 4 has given the
mobility order as Cu > Fe > Pb. By 24 hrs contact time at pH 2 , 3% of Pb; 95% of Cu
and 10% of Fe have been leached. At pH 4 , extraction yields are reduced by around 25%.
However, the most emergent problem arises from the storm water drainage
of mining and factory area into the sea.
The metals in the processed mining material may be transferred into the
aqueous phase by chemical or biochemical reactions. Acidity or in some cases the
alkalinity of the water contacted with solid material causes dissolution of heavy metals
and other polluting ions such as complexed cyanides etc. In that case, stormwater can be
regarded as a secondary leachate from the site.
Impact On Natural Water Bodies
Elements occur in nature in their most stable states and
metals in natural waters may exist in dissolved, particulate or colloidal forms. Dissolved
forms are the metal ions complexed with water or with several ligands. Insoluble metallic
oxides, hydroxides, carbonates, sulfides or silicates may yield colloidal or particulate
forms. Metallic ions may also be adsorbed or complexed on insoluble colloids of organic or
inorganic matrix.
The redox and hydrolysis are important processes in the
heavy/transition metals’ chemistry.
Ecological results of flowing of such leachates to natural water
reservoirs have been the subjects for several studies. The quantity and load of the
leachates leaving the site determine the point where it would ultimately drain to.
The stormwater does not have only the ions or molecules but also
contains insoluble soil material. This material covers the bottom of the sea and in the
new chemical environment further reactions occur. Thus, the impact of stormwater contents
on other components of the environment yield different equilibria competing with each
other.
The leachates from the factory site can be in acidic in nature. The
acidic solutions of metallic sulfates, such as ferrous and copper sulfates, will be
carried by surface waters into the sea and will be diluted and neutralized. In the sea
water, the chemical species will be oxidized and hydrolyzed.
The leachates from mining area should be mainly in inorganic nature and
would not have direct correlation with eutrophication, but would cause changes in specific
diversity of planktones which affect the food chain.
By the effect of leachate, the water columns as well as the bottom
sediments should be enriched by heavy metals. The sediment column should be the major
reservoir of metals.
The sediments are the main carrier phases for trace elements. At the
sediment-water interface, during the recycling between phases,metals are buried in the
sediment by adsorption or by complexation and at the same time they are released into the
pore water by diffusion. Metal ion exchanges into the main water body also occur.
Scavenging, the adsorption and removal of dissolved elements from the
water column by sinking particles, is an important process and its rate could be strongly
correlated with the primary productivity at the sea surface.
The processes called mineral weathering, such as dissolution of oxides,
hydroxides and carbonates;incongruent dissolution of aluminosilicates; or sulfate
adsorption onto metal oxides as well as sulfate reduction and assimilation would effect
the alkalinity of sea water.
The nutrients such as phosphate also react with metallic ions such as
iron(II) to yield insoluble hydroxyphosphate particles.
Regarding the points given above, in contact with the leachates, the
sea-water fauna and flora may be exposed to several factors :
. Acidification of the water column via the hydrolysis of metallic
salts ;
. Lowering pH of the water ( pH <2) column contacted with acidic
leachate;
. High oxygen consumption during the oxidation of metals in lower
states;
. Heavy metal accumulation in flora and fauna species;
. Toxicity on flora and fauna ;
. Increase in water turbidity, which effects the sun light penetration
through water to prevent photosynthesis. The weakened light illumination may impact on
bottom macroalgae both in coastal zone and in the offshore areas starting from different
depths.
. Stratifications resulting from different salt content reduce the
mix-up of the water creating different environments for the same or similar living
species.
. Jelly precipitates accumulate on algae which are important in food
chain. Consequently, effective photosynthesis and oxygen releasing into the water are
prevented.
The health of the environment can be assessed by the observation of
biodiversity. The element cycle is to be prevented from breaks. The biological effects of
wastes should be evaluated and should force to introduce changes in the applied
technologies. The process technologies should be rearranged.
At the interested area, probably, the influence of pollution on benthic
organisms should be significant in the shelf and coastal zones.
Pollution Monitoring and Research on Ecological Damages
We are strongly interested in the ecological situations
concerned with the pollution coming from the mining and floatation site.
As far as we know, there are also considerable gaps in the background
informations both on geochemistry of the shelf and on the metal distributions in the sea
water as well as in the bottom sediments of coastal zone and offshore areas.
The marine pollution and ecological monitoring work should be carried
out simultaneously. The network of sampling stations are to be selected to include the
points where potential impacts may be occurred as well as the points in the undisturbed
areas.
It is essential that continous scientific monitoring of water columns,
bottom sediments and marine organisms are needed to notice the possible ecological
damages.
The aims of our research programme on the water pollution can be
outlined as :
. to maintain background data for specific uncontaminated areas;
. to be alert to environmental emergencies coming from the mining and
floatation area;
.to reach the knowledge of restoring and conserving of natural sources;
. to get environmentally safe routes to manage the area;
. to get the transboundary effects of hot points on fisheries, on
biodiversity and on public health including economical aspects.
The long-term project not only will achieve the ecological background
data of water bodies, sediments and soils; but also will give scientific supports for the
recreation and remediation of the mining and floatation site.
The public health is an important branch of environmental protection
and the public health screening affairs should be performed and statistical data of the
past years regarding the public health should be gathered from official registrations as
well as people of the region.
REFERENCES
[ 1] EPA
(U.S.Environmental Protection Agency),(1991), Seminar Publication: Site Characterization
for Subsurface Remediation, Report No : EPA/ 625 / 4-91 / 026, Cincinnati, Ohio,45268.
[ 2] Bilge
Alpaslan, M.A.Yükselen,”Remediation of Heavy Metal Contaminated Soils” MSc Thesis on
Env.Eng.,Marmara University, Institute for Graduate Studies in Pure and Applied Sciences,
1999. |
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BETÜL ATASAYAN
THE EU’s ENVIRONMENTAL POLICIES AND LEFKE CASE
In the latter part of the twentieth century and the beginning of
the twenty-first century serious worldwide attention has focused on the environmental
issues. It is clear that a new agenda of environmental problems will demand international
attention in this century and into the next.
As countries liberalise their economic to allow global companies to
bring in capital and technology, they should be aware of the record of companies in the
production and disposal of hazardous wastes. The byproducts of economic and technological
growth cause cumulative stresses on the physical environment that threaten human health,
habitats, and economic well being. The costs and risks of these activities to future
generations will be much higher than they are to the world’s current population.
International concern about environmental issues has grown dramatically
in recent years. As a result, the environment has started to appear at centre stage of
international politics and features as an agenda priority. The principle reason for this
as mentioned before may be termed the “globalisation” of environmental concerns.
International dimension of environmentalism has become more prominent
because of the identification of genuinely global problems, such as global warming and
ozone depletion and only global cooperation can hope to solve these problems. In
accordance with the original intentions of the six founding states, the European Union has
developed into a supranational government, which is in the process of increasing its
membership, deepening its democratic structure and strengthening its power. In the case of
environment, European Union is also a unique international organisation because it is the
only one “with the power to agree environmental policies binding on its members.
This purpose of this study is to evaluate the environmental policies of
the European Union and to survey the incompatibility of the environmental development and
the economic growth in the light of a case study (CMC). The study consists of two parts:
First part has the aim to investigate the existence of some difficulties in the
enforcement of the European Union environmental policies and the second part will examine
the problems caused by the pollution resulting from CMC’s former mining and refinery
activities, and the cooperation’s failure to clean up their installation after
abandoning the site in 1974. The concept of sustainable development will be tested within
the context of the conditions of the physical, economic and political conditions
prevailing in the Area of Lefke.
Betül ATASAYAN
Lefke Çevre ve Tanıtma Derneği
Yönetim Kurulu Üyesi
E-mail: atasayan@north-cyprus.net |
|
|
THE ENVIRONMENTAL AND PUBLIC HEALTH PROBLEMS DUE TO TAILING PONDS OF
COPPER MİNE IN LEFKA, CYPRUS
Prof. Dr. Fethi
Doğan
Ege University Faculty of Medicine, Department of Public Health
The abandoned copper mine was examined in Lefka, in November 1999. The sample of soil,
water and plant were collected and analyzed at Ege University, Faculty of Agriculture and
Faculty of Chemistry. Lefka mine tailing ponds were build primitive technology so they had
some environmental risks. The wastes stretched large area around the mine and were
contaminated soil, plant and water. Carcinogens were found in waste of the mine. Residents
were exposure these contaminants. Incidence of cancer and chronic diseases would increase
in the future.
The wasted area was a focus of the environmental and health problems. Tailing ponds
should reclaim. Legal and scientific measures should carry out. |
|
| TURKISH REPUBLIC OF NORTHERN CYPRUS
LEFKE-GEMI KONAGI CMC AND ENVIRONMENTAL RELATIONS
Prof.Dr.
Ümit ERDEM¹, Assoc.Prof.Dr. Bahar ZAFER², Res.Ass. Okan YILMAZ¹
¹ Ege University Center For Environmental Studies Bornova IZMIR
²Ege University Department of Landscape Architecture Bornova IZMIR
The mining area in Lefke-Gemi Konağı, Turkish Republic of Northern
Cyprus where the mining works had been started by CMC in 1913, produced primarily copper
at the beginning and later secondary products like copper sulfate (CuSO4),
hydro sulfuric acid (H2SO4) and gold was produced by cyanide
leaching method. Unfortunately, these mining processes left the area as a threat for
Eastern Mediterranean after the American company left the region.
The area is classified as a noticeable coastal ecosystem but sadly the
high amounts of arsenic, barium, cadmium, chromium and selenium in the environment are
surprisingly noticeable in the aspect of human health. When Lefke is examined
historically, agriculture reduced and the soil lost its abundance as soon as mining
started. Even though the mentioned company had promised re-cultivation and recreation. It
didn't keep its promises, so problems increased and expanded because the pollution in
water, air and soil effected the biodiversity, water-soil balance was effected, apart from
agricultural productions of olive, citrus and carobs, many historical values like Vuni
Palace and ruins of Soli encountered the danger of vanishing.
In the study, being conducted by these determinations, necessary implications for the
area has been handled to provide a perspective of the present condition and the future of
the area. Especially the existing situation is analyzed within the environment and
starting from this point all cautions possible were emphasized. The natural and cultural
structure of the area was handled, the phases of a study concerning the relations of the
mine and the environment were determined and suggestions for the future were made. As a
conclusion the study has tried to point out the negative effects of environmental
pollution in the area within the concept of East Mediterranean regional pollution problem.
|
|
HIGH VOLUME MINERAL ADMIXTURES CEMENT FOR UTILIZATION OF
INDUSTRIAL
BY-PRODUCTS AND WASTE
K. SOBOLEV
S. SOBOLEVA
Abstract
The application of High Performance (HP) Cement technology for
production of low cost cement allows using up 60% of mineral indigenous
additives in the cement composition. The additives can be selected from
natural materials: pozzolans, limestone, sand and industrial by-products
and waste: granulated blast furnace slag, fly ash, catalytic wastes,
broken glass and ceramic. This phenomenon leads to the reduction of the
energy consumption per unit of the cement produced. The decreasing of
the area occupied by industrial by-products and wastes, as well as
effect of minimized emissions during manufacturing process provide
positive eco-balance of the high volume mineral admixtures cement. |
|
| ENVIRONMENTAL DEGRADATION AND HAZARDOUS
WASTE MANAGEMENT:
A MEDITERRANEAN PERSPECTIVE
By: Prof. Giuseppe BURGIO
Director of the School of Specialisation in Law and Economics of the
European Communities
University of Rome "La Sapienza"
Email burgio@scec.eco.uniroma1.it
SUMMARY: 1. Environmental degradation and environmental sustainability.
2. The European environmental policy. 3. Protection of Mediterranean environment. 4.
Environmental Liability.
ABSTRACT
This paper deals with environmental degradation and the effects
of breaking "environmental sustainability" over regions far from the place in
which the damage was produced and over future generations as well. Risks related to
environmental degradation and hazardous waste management can no more be considered of
local interest. They should fall instead under international jurisdiction requiring their
dimension global cooperation and partnership between private firms, local and national
governments and non-governmental organisations.
The efforts of the European Commission to put forward a more effective
action, with a stronger international monitoring, in order to protect natural resources
are analysed in detail. The "Sixth Environmental Programme" establishing
principles and actions to be undertaken by the EU Member States until 2010 and the
Commission's intention to propose measures to protect soil quality and put pressure on the
chemical industry for a "non-toxic environment" and better control of hazardous
substances, are also presented.
The environmental protection of the Mediterranean area, as part of the
global environmental problem, is considered. Conclusive remarks relate to Environmental
Liability and the relevance of civil participation in the decision making, in order to
prevent environmental risks and search for solutions to eliminate or reduce damages
already occurred. |
|
| MINING
CONTAMINATION: A CASE STUDY FROM NORTHERN CYPRUS – GEMİKONAĞI (XERO) AREA
Hüseyin
GÖKÇEKUŞ, Near East University, Lefkoşa, TRNC.
ABSTRACT
Cyprus is an island where there has been past historical experience
of copper mining activities since many decades. During early times, the mining process was
performed by old, unefficient techniques by implementing unmodernized equipment. Along
with the global advance of technology, the mining methods and equipment were modernized in
recent years, resulting in an elevated production capacity. This, in turn, had a positive
impact on the Cypriot economy whereas it introduced some environmental and health
problems.
In this article, the historical development of the copper mining
activities were outlined. In parallel, the health and
environmental problems that may result from these mining operations were investigated. To
demonstrate the adverse effects of the mining activities on human health and environment,
the Gemikonağı reservoir and its nearby areas were investigated in detail in a
case study. Water samples, taken from the reservoir and the nearby stream channels, were
chemically analyzed to detect different contamination levels.
As a consequence, as we prerpare ourselves to take on for
the twenty – fır st century, like many other different contamination sources, the
mining areas, with or without current production activity, still pose a vital
contamination hazard for both the underground and surface water resources, over the whole
island. In addition, the health and environmental problems already caused are pending for
extremely rapid effective solutions. But, by the virtue of geographical aspect of the
problems, a good viable solution shall only be possible through overall consideration of
the whole island. |
|
| Prof.
Dr. Aysel Atimtay - Buradan ulaşabilirsiniz.( Geniş yer
tuttuğu için başka yere alınmıştır.) |
|
| RECLAMATION OF THE CMC TAILING PONDS
Dr. Okay Camgoz,
Faculty Membetr
of the Eastern Mediterranian University
ABSTRACT
Cyprus Mines Corporation (CMC) has operated a copper mine at Lefke region from
1916-1974. During these 58 years of mining and copper concentration plant activities a
huge waste material has been accumulated in the tailing ponds at Gemikonagi.
Gemikonagi is a beautiful fishers village in the north coast of Cyprus, and it could
have developed into a prosperous tourism town. However the tailing ponds wich are created
by the CMC copperconcentration plant activity and copper concentrate spilles, during the
loading operations of the boats at the dock side have polluted the coast line and the sea
tremmendeously.
at present unattended tailing ponds are creating a terrible view pollution and a big
threat to the region in case of errosion and collapsing of the pond walls. Since 1974,
most of the water contend of the tailing ponds has been either drained into the sea,
pumped to the pond 3 miles away at the mining side or evvaporated away. The rich pyrite
contend of the ponds has resulted acidity in the pond water and SO2 contamination of the
air. However at present SO2 pollution has been redused and does not effect even the near
by citrous plants.
The aim of this paper is to search the ways of reclaiming the area and rehabilitate it.
It is advisable to treat the pont contend with lime to eliminate the acidity of the ponds.
At the same time, the pond walls should be strengthend and trees should be planted to slow
down the erosion. The treated ponds surface then should be covered by a thin layer (5cm.)
of fertile soil. Afterwords Rye should be planted to caltivate the soil. This was
successfully practiced at the Sudbury Mines tailing ponds of the International Nickel
Company (INCO) of Canada.
The implimentation of this suggested reclamation method will help the people of
Gemikonagi to gin back the lost land and this dead land will be fertile again. |
|
|
THE EFFECTS OF ENVIRONMENT CHANGES ON HUMAN LIVING
WITH IN THE CONCERN OF EU POLICY: THE CASE OF CYPRUS MINES
Prof. Ercan Tatlıdil, Ph.D
U niversity of Ege,
Dept.of Sociology And
Environment Research Centre
ABSTRACT
After industrial revolution, in a world where financial markets
continue to “go global”, developing countries need to work towards beçoming good
homes for long-term foreign investment.
Just as countries economy can be swamped by global economic forces that
it has little power to control or deflect, its environment can be threatened by activities
such as mining taking place beyond its borders and its control. In some low income
countries the threats may be severe enough to jeopardize further sustainable development.
Soil, ground water changes, coast and sea pullotion, for example could effect agriculture
forest and fishing forced to villagers leave from their homeland. Such a like Cyprus as it
is known surface and underground mining have caused environmental problems due to acidic
discharges (commonly referred to as “acid mine drainage”). Here exposed sulfide
minerals react with oxygen and water to produce an acidic solution that dissolves metals
and contains sulfate. Further reactions may accur resulting in a wide range of water
qualitiy characteristics. Additionally, sediment discharge due to inevitable erosion of
the denuded soil hinders future land uses and degrades water qualitiy.
An American mining company called Cyprus Mine Cooperation (CMS), which
operated copper mining industry in Cyprus betweet the years 1914-1974. According to some
expert reports, mine and its waste was left in Lefke region caused very serious
environmental problems such as soil, air and water pullution which is usually defined as
the resorce of “global environmental problem”. The area has been still faced by
environmental pollution with the mine waste left behind alone after the firm leaving the
country in 1974. In this sense, it is undestood that CMC had never been concerned their
waste pollutions effects on environment on their mine closure procedures after 1974.
Governments acting alone, and even regional organizations cannot
respond affectively to this kind of environmental problems. The response must be global.
Industrial countries have been thought to be responsible for the most of the thesi kinds
existing global environmental problems. In this case, not only Cyprus has been face to
face with Cyprus mine problem such as like a local problem, but also all the east
Mediterean countries standing near by Cyprus island could be in the same station in this
case.
In brief, special attention going to be given in accordance with global
environment approach and also European Union’s understanding of environment procedures
and acts. And also in this case going to be discussed European Union-Amsterdam Treaty and
Copenhagen summit approach among the member countries and the countries going to be member
like Cyprus and the countries nearby the European Union.
Human Rights and Environment in the EU Policies
As one can easily see that European Union develops, in which a
growing number of decision has been taken on the everyday lives of its citizens. All these
decisions should be taking account in democratic society. The peoples of Europe creating
an over closer union among them, are resolved to share a peacefull future based on common
values. According charter of fundamental Rights of the EU
Article 1 says: Human dignity is invioble. It must be respected and
proteceted. Article 2 says: Everyone has the right to life. Also Article 41 consists of
right to good anministration. From this respect EU decisions on living of citizens taking
account to environmental cases. As Article 37 mentions environmental protection, and also
in article 35: states that a high level of human health protection shall be ensured in the
definition and implementation of all union policies and activities.
-A high level of environmental protection and the improvement of the
quality of the environment must be integrated into the policies of the union an ensured in
accordance with the principle of sustainable development (European parliament,
charter…Dec.2000, p.6-11).
In accordance with the social summit of 1995 in Capenhagen commitments
were (EESC.; Apr. 2000, p.1-2).
Commitment 1: We commit ourselves to creating an economic, political,
social, cultural and legal environment that will enable people to achieve social
development.
Commitment 3: We commit ourselves to promoting the goal of full
employment as a basic priority of our economic and social policies, and to enabling man
and woman to attain secure and sustainable livelihoods through freely chosen productive
employment and work.
Commitment 9: We commit ourselves to increasing significantly and/or
utilising more efficiently the sources allocated to social development in order to achieve
the goals of the summit through national action and regional and international
cooperation.
20 and 21 September 2000 Economic and Social Committee adopted the
fallowing opinion in the topic of over all political objectives (EESC., Sept.2000, p.1-2).
-Economic Objectives; maintaining low-cost raw materials for private
and public users, securing long-term resources availability guaranteeing energy supply on
a lastin basis, ensuring that everyone has a share in overall rising income and prosperity
-Ecological Objectives; conserving natural resources and protecting the
climate, preserving and developing the natural environment safeguarding natural resources
in the long term through the use of renewable resources, maintaining biodiversitiy.
-Social Objectives; preserving and developing recreational areas,
creating jobs, protecting social and cultural resorces, ensuring equity for a
“fair”distribution of income.
The European union participetd actively in the deliberations on the
right to the development in various bodies of the United Nations concerned with human
rights and development.
According to the UN general assembly; human beign is the central
subject of development and should be the active participant and beneficiary of right to
development. The right to development is based on the understanding that development is a
process targeted at the realisation of civil, cultural, economic, political and social
rights meeting equitably the developmental and environmental needs of present and future
generations. (EU annual report on human rights 1988-99, p.47)
All over EU Treaty communication from the commission on the global
assesment of the European Community program of policy and action in relation to the
environment and sustainable development concerns European citizens living conditions and
related to human kind social, economic, cultural situations. From all these points,
European Community and European Parliament always taking account the citizens believes and
understanding of living.
Understanding of living nowadays becomes global. For that most of the
European citizens thinking of the environmental problems not only consisted of European
community political borders, but the neighbouring and/or the other countries in this
world, may creat global environmental problems for themselves. This idea after
“Chernobil nuclear desastare” awaked world citizens. The committe was affected from
the public opinion of the EU that commission became more influenced with their citizen’s
atitudes. Therefore EU Committie of the Regions, June 2000 Brussels, stated that:
-The committee believe, that the European Commission should pay more
attention to the threats arising from outside the EU, such as nucleer waste, the dumping
of chemical and other weapons and waste water which is polluting rivers and oceans,
particularly the Baltic and Mediterrannean.
In a number of earlier opinions the committee called for stimulating a
more active role for regonal and local authorities in formulating and implementing
environmental policy in the regions and municipalities of the applicant states. The
Committee would reiterate this urgent recommendation in the context of the present Global
Asesment and with a view to the preparation of the sixth Action Programme. The European
Commission should strongly promote cooperation and the exchange of experience and
expertise through twinning arrangements between regions and municipalities in the EU and
the applicant states.
Cyprus as an applicant should widely stimulate the exchange of
information, good practices and experiences in the environmental field with the EU and its
institutions.
Environmental Approach in the European Union
The world has already seen one genuine environmental success story
in the Montreal Protocol of 1987, which brought all countries together to address a common
environmental threat. The Montreal Protocol attempts to solve the problem of
chlorofluorocarbon emissions, which reduce ozone concentrations in the upper atmosphere.
As it has been seen in the 1980s scienti sts realized that allowing these emmissions to
continue unchecked would dangerously increase ultraviolet radiation in the higher
latitudes, rising rates of skin cancer and cataracts and damaging the environment (The
World Bank, 1999-2000 p, 8)
The world faces a number of other pressing environmental problems that
threaten the global commons. Perhaps the best known is the climate change, which is
associated with increasing emmisions of carbon dioxide into the atmosphere. Others include
biodiversing loss, which is occuring at an alarming rate; desertification; the depletion
of fish stocks; the spread of persistent organic pollutants.
In global levels environmental policy become one of the greatest social
challenges facing the public authorities and all sectors of the economy today. It is also
a subject of whom the public is acutely aware, since it is directly affects its welfare
and health. May be after a Montreal Protocol and Rio Treaty, which brought all the
countries together to address a common environmental threat.
In the early days of building Europe, environmental issues were not a
top priority for the public authorities and economic circles.
It was not until the 1970’s, the emergence of environmental concerns
triggered moves in this area at Community level. At the July 1972 Paris Summit the Heads
of State and Government recognised that in the quality of life, particular attention
should be paid to the environment.
Consequently, the signal was given and the first action programme
setting out the framework for community environment policy was adopted, covering the
period from 1973 to 1976.This was followed by other multiannual programmes of the same
type which led to the adoption of a series of directives on protection of natural
resources (air and water) noise abatement, nature conservation and waste management.
However, from the single European Act in 1987, the community measures
had a legal basis explicitly defining the objectives and guiding principles for action by
the European community relating to the environmental protection requirements to become a
component of the community’s other policies.
The entry into force of the EU Treaty in November 1993 brought further
progress on several fronts. First it added the concept of ‘’ sustainable growth
respecting the environment ‘’ to the European Community’s task and wrote the
precautionary principle into the article on which environment policy is founded
The Treaty of Amsterdam should resolve these problems and respond to
the need to make Community environment policy clearer and more efficient.
The Treaty of Amsterdam seeks to provide stranger guarantees than given
by inserting concept of sustainable development plus a new article in the Treaty
establishing the European community.
The new article 6 puts at the start of the Treaty the clause calling
for environmental protection requirement to be integrated into the definition and
implementation of other policies. This was already contained in Article 174. The new
article also cites such integration as one means of promoting sustainable development.
This new article must be seen in conjunction with the decleration on
environmental impact assessment, annexed to the Final Act of the Intergovernmental
Conference, which drafted the Treaty of Amsterdam. In other words Amsterdam Treaty pointed
out that sustainable development and taking the environment into account in all policies,
should be realized (European Commission, The Amsterdam Treaty, p.42).
The Main Environmental Problems in Cyprus
In accordance with the Commission of the European Comminities,
“2000 Regular Report from the Commission on Cyprus Progress Towards Accession” (This
report is excluded North Cyprus-KKTC) “Cyprus continues to fulfill the Copenhagen
political criteria. The pre dominant political problem is the continued division of the
island, but over the last year important efforts have been made in the search for a
political settlement in line with the Accession Partnership”.
Cyprus is a functioning market economy and should be able to cope with
competitive pressure and market forces within the Union. However as regards alignment with
the environment acquise, several laws and orders have been adopted, but the emphasis lay
on preparatory work. Although more attention has been paid to the allocation of sufficient
budgetary and administrative resources to the environmental sector to ensure the
implementation of the acquis, given the size of the alignment task in this area, this
sector still remains a high priority. (İncludes only south
Cyprus)
Cyprus as a Mediterranean country has “mediterranean climate”, is
characterised by hot, dry summers, and mild and wetter wintters, with run off from
infrequent but often massive rain fall causing soil erosion. However Mediterranean regions
of Europe have witnessed rapid changes over the past thirty years, in particular in the
last decade, affecting all aspects of society. For a number of countries, accession to the
European Union has led to major socio-economic change. These upheavals have disrupted the
special relationship between man and environment in these areas with higly specific
climate. At the same time, landscape it self has undergone rapid change. As a result,
Southern Europe is facing a process desertification, which is evident in the cultivated
land, pasture grounds and forests, and in the substantial loss of biological diversity.
Paulo Mairota, John Thornes and Nichola Greeson pointed out that vast rural areas are
temporarily and peramenently abandoned, urban sprawl is rampant, agriculture is
intersifying and water shortage, accentuated by the droughts of the 1980s and 1990s has
become the main problem in the terms of resources and environment (5)
In this sense Cyprus is a Mediterranean country not excluded from this
typicall Mediterranean climate conditions. For that reason badly influenced agricultural
production and biological diversity in accordance with Regular Report of European
Commission on Cyprus:
-Over the years the contribution of agriculture has garually fallen to
4.2% of GDP (Gross Domestic Product) and 9.3% of employment. Due to the fall in
agricultural production, which was particularly badly affected by the recent drought, the
primary sector declined by almost 7% in 2000. Also in the same report declared that no
concrete development in rural development and forestry could be reported in this area
since last regular report. Even if this report concerning with the south Cyprus, the same
stuation can be seen in North Cyprus as well.
As regards Rural Development and Forestry, Cyprus has already some
experiences in these areas also comprising agri-environmental measures. However the
necessary contol bodies for the environmental scheme will have to put in place.
Furthermore, a code of good agricultural practice needs to be established. (CEC, 2000
Regular…p.49-52)
From The Environmental Issues Cyprus Mines Problem
An American mining company called Cyprus Mine Corporation (CMS),
which operated copper mining industry in Cyprus between the years 1914-1974. According to
some expert reports (Ümit Erdem, 1999), mine and its waste was left in Lefke region
caused very serious environmental problems such as soil, air and water pollution which is
usually defined as the resource of “global environmental problem” The areas has been
still faced by environmental pollution with the mine waste left behind alone after the
firm leaving the country in 1974. In this sense, it is understood that CMC had never been
concerned their waste pollutions effects on environment on their mine closure procedures
after 1974.
Pollution through erosion and sediment control should be in a
significant part of every mining waste management stategy. It means every effort should be
made to control the sediment at, or near to, and its source (as opposed to relying on one
or more large sediment settling basins opposite and in the major drainage ways). It is
more desirable to segragate sedimentladen waters from the rest of the surface flow.
However it is understood from expert reports that Cyprus mine Corporation had not been
taken available waste management techniques in this area. In accordance with EPA (United
States Environmental Protection Agency) reports to Congress: The report provides in depth
information on mining process, the wastes produced an associated health and environmental
effects, ways to minimize waste production and the means of treat and dispose of the
wastes as well as mine closure procedures and costs.
Several management alternatives such as prevantation and chemical,
physical and biological treatment are available to minimize the impact of mine drainage on
the environment. In this sense it is understood that CMC had been never taken account in
their mine operation these basic rules or they had not concerned their waste pollutions on
environment in account on their mine closure procedures after 1974. In this case an
example can be given; begining of the 1970s the Court of Lefke punished CMC due to cause
of polluting the agricultural cultivated areas. Also according to expertise reports water,
soil, air, costs and sea pollution comes from ex CMC mines areas. In this region all these
expertise reports say, environmental pollution during the period of 1914 and 1974
responsible firm is the only one private sector CMC. It means environmental pollution with
its legal administration and ethic dimensions caused by an American mining company
operated copper mining industry in Cyprus in Lefke region between the years 1914-1974.
As it is understood nowadays ex-mining wastes still working polluting
water, soil, air, costs and sea, and also it’s wastes produced and associated with
health and cultivated effects.
According to the some expert reports mines and its wastes was left in
Lefke region caused a very serios problem such as soil, air and water pollution which is
usually defined as the resources of ‘’ global environment problem ‘’ .The areas
faced by environmental pollution and the mining waste is left and their storage are in the
frontiers in KKTC since 1974.
Therefore in this region approximently 7000 people are living and
working in cultivated areas under the effects of environmental pollution directly or
indirectly in the mean time circus fruit, vegetables corps and sea foods growth in this
region are distrubuted to the other regions in KKTC for consumption by the way this means
that environmental pollution is also exported to the other regions in Cyprus.
Mining operations in this region has been gone for a long time in this
period authrorized politicans were changed who were responsible for copper mining
industry, mining business, using poisened materials during the operations, storage of
waste and legal-administrative regulations concerning the mine export.
Cyprus was a British Colony during the
standating period of mining operations. Between the years 1960-1974 CMC continued its
operation according to regulations of Cyprus Republic. İn 1974 Intervention of Turkish
Armed Forces to the island under the rights of Guarantee Agreement, Turkish political
authorities started to control these mining area, mining plants and waste storage. For
this reason environmental pollution in this region should be examined with historical and
legal framework
CONCLUSION
An American mining company called Cyprus Mine Coorperation (CMC) which
operated copper mining industry in Cyprus between the years 1914-1974 under the rule of
different authorities and environmental laws. According to some expertise reports, mine
and its waste was left in Lefke region caused very serious environmental problems such as
soil, air, water coasts and sea pollution which is usually defined as the resource of “
global environmental problem”. It is also understood that CMC had never been concerned
their waste pollution effects on environment on their closure procedures after 1974.
As it is understood nowadays ex-mining wastes still working polluting
environment. Governments acting alone, and even regional organizations, can not respond
effectively to this kind of environmental problems. The response must be global.
In other case, according to the opinion on the White Paper on
environmental liability, (COR, Opinion...., 14-15 June 2000, p.1 and 4) proposed European
regime should be comprehensive and help to improve implementation of key environmental
principles such as the “polluter pays”. The costs of preventing and restoring
environmental damage will be paid by the parties responsible for the damage, rather than
being financed by the tax payer. It means that CMC is responsible for this case.
In other sense, the establishment of a European environmental liability
regime will accompany the introduction in the common Agricultural Policy of compulsory
Agri-Environment schemes, which will play a complementary role in protecting the habitats
of the European Union: It believes that the establishment of an effective European
environmental liability regime will help to facilitate candidate countries efforts to
adopted the EU environmental acquis and help to ensure the protection of biodiversity,
landscape, diversity and the environment of Europe as a whole.
In accordance with the environmental policy of EU, Cyprus Governments
(North and South acting together) and non-government organizations and other civil
agencies have a chance to apply to EU institutions within the several funds cleaning up
and restoring the environment which was caused environmental damage by the Cyprus Mines.
REFERENCES
- CEC (Commission of the European Communities)., 2000 Regular Report From The
Commission on Cyprus’ Progress Towards Accession, Brussels, 8.11.2000.
- E.U. Council of European Union., Annual Report on Human Rights, Brussels,
1988-1999.
- European Parliament., Charter of Fundamental Rights of European Union,
Luxembourg, December 2000.
- EESC (European Economic and Social Committee)., Opinion on the Follow-up of the World
Summit of Social Development, Brussels, 27 April 2000.
- EESC (European Economic and Social Committee)., Opinion on Renewable Resources: A
Contribution by Rural Areas to Active Protection of the Climate and Sustainable
Development, Brussels, 20-21 September 2000.
- European Commission., The Amsterdam Treaty; A Comprehensive Guide, European
Community, Germany, 1999.
- COR (E.U. Committee of the Regions)., Opinion on the White Paper on Environmental
Liability, Brussels, 14-15 June 2000.
- Ümit Erdem., Kuzey Kıbrıs Türk Cumhuriyeti Lefke-Gemi
Konağı CMC Madencilik Şirketi tarafından yaratılan çevre sorunu, Ön Rapor, Ege Üniversitesi Çevre Araştırma ve Uygulama Merkezi, İzmir,
Haziran 1999.
- World Resources Institute., World Resources 2000-2001; People and Ecosystems,
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