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Iranian Journal of Environmental Health, Science and Engineering
Iranian Association of Environmental Health (IAEH)
ISSN: p-ISSN: 1735-1979
Vol. 6, Num. 2, 2009, pp. 73-80

Iranian Journal of Environmental Health, Science and Engineering, Vol. 6, No. 2, 2009, pp. 73-80


1M. Öztürk, 2G. Özözen, 2O. Minareci, 2E. Minareci

1Science Education Department, Faculty of Education, Celal Bayar University, Manisa,Turkey
2 Biology Department, Faculty of Sciences and Arts, Celal Bayar University, Manisa, Turkey

*Corresponding author:, Tel: 0236 2412151-152, Fax: 0236 241215873

Received 26 November 2008; revised 25 March 2009; accepted 10 April 2009

Code Number: se09013


In the present study, some heavy metals (Cd, Cr, Cu, Fe, Ni and Pb) were seasonally determined in water, sediment and some tissues of Cyprinus carpio from Avsar Dam Lake, which is an important water source for irrigation and drinking in Turkey. Heavy metal levels in water, sediment and fish samples were analyzed by inductively coupled plasma spectroscopy (ICP/AES). The obtained results showed that the average values of Fe in water samples were higher than the respective reference values for fresh water. Results for levels in water were compared with national and international water quality guidelines, as well as literature data reported for the lakes. The analysis of heavy metals in sediments indicated that among the six heavy metals tested, Fe was maximally accumulated, followed by Ni, Cu, Cr, Pb and Cd. Heavy metal concentrations were found to decrease in sequence of the Cyprinus carpio samples, in the muscle and stomach-intestine as Fe > Cu > Pb> Ni > Cr > Cd; in the gill, heart and liver as Fe > Cu > Ni > Pb > Cr > Cd and in the air sac as Fe > Cu > Ni > Pb > Cd >Cr. In the fish samples, cadmium, chromium, nickel and lead concentrations exceeded the tolerable values provided by international institutions.

Key words: Heavy metal, Cyprinus carpio, sediment, pollution, environment


The pollution of the aquatic environment with heavy metals has become a worldwide problem during recent years, because they are indestructible and most of them have toxic effects on organisms (MacFarlane and Burchett, 2000). Among environmental pollutants, metals are of particular concern, due to their potential toxic effect and ability to bioaccumulate in aquatic ecosystems (Censi et al., 2006).

Heavy metal concentrations in aquatic ecosystems are usually monitored by measuring their concentrations in water, sediments and biota (Camusso et al., 1995), which generally exist in low levels in water and attain considerable concentration in sediments and biota (Namminga and Wilhm, 1976). Heavy metals including both essential and non-essential elements have a particular significance in ecotoxicology, since they are highly persistent and all have the potential to be toxic to living organisms (Storelli et al., 2005).

Studies on heavy metals in rivers, lakes, fish and sediments (Özmen et al., 2004; Begüm et al., 2005; Fernandes et al., 2008; Öztürk et al., 2008; Pote et al., 2008and Praveena et al., 2008) have been a major environmental focus especially during the last decade. Sediments are important sinks for various pollutants like pesticides and heavy metals and also play a significant role in the remobilization of contaminants in aquatic systems under favorable conditions and in interactions between water and sediment. Fish samples can be considered as one of the most significant indicators in freshwater systems for the estimation of metal pollution level (Rashed, 2001). The commercial and edible species have been widely investigated in order to check for those hazardous to human health (Begüm et al., 2005).

Heavy metals such as copper, iron, chromium and nickel are essential metals since their play an important role in biological systems, whereas cadmium and lead are non-essential metals, as they are toxic, even in trace amounts (Fernandes et al., 2008). For the normal metabolism of the fish, the essential metals must be taken up from water, food or sediment (Canlı and Atlı, 2003). These essential metals can also produce toxic effects when the metal intake is excessively elevated (Tüzen, 2003).

The Avsar Dam Lake is located on the West of Turkey and it is included in the National Water Reserves. The Lake was constructed to help alleviate the water problems of the Gediz basin and many inhabitants of the area also carry out fisheries on the Lake. The quality of this ecosystem has been degrading due to agriculture and human activities. To the best of our knowledge, from literature survey, no work has been carried out on the environmental quality of water, sediments and biota of the Lake.

The aim of this study was to determine the heavy metals concentrations (Cd, Cr, Cu, Fe, Ni, Pb) in water, sediments and in muscle, liver, gill, stomach-intestine, air sac and heart of fish species (Cyprinus carpio L., 1758) from the Avsar Dam lake, since this fish is an important component of the human diet in this zone. The results obtained from this study would provide information for background levels of metals in the water, sediment and fish species of the lake, contributing to the effective monitoring of both environmental quality and the health of the organisms inhabiting the lake ecosystem.


Description of study area

Avsar Dam Lake is on the Gediz River in west Anatolia, Turkey (38° 13’ N 28°.33’ E - 38° 13’ N 28°.37’ E). The Maximum lake capacity is 69.000.000 m3. Lake area is 5.25 km2 (Anonymous, 1997). The lake is located approximately 120 km from the city of Manisa. It is used for irrigation and fisheries. In this study, surface water and sediment samples were taken from two different sampling sites at Avsar Dam Lake(Fig. 1). Cyprinus carpio. samples were also caught from the same localities. The two stations were determined considering the geographical structure of the dam, environmental conditions and sediment structure.

Sampling and sample preparation

Water, sediment and fish samples were collected 4 times (from July to April) for every 3 months from two sites in the lake. The sampling bottles were pre-conditioned with 5% nitric acid and later rinsed thoroughly with distilled de-ionized water. At each sampling site, the polyethylene sampling bottles were rinsed at least three times before sampling was done. Pre-cleaned polyethylene sampling bottles were immersed about 10 cm below the water surface. About 0.5 L of the water samples were taken at each sampling site. Samples were acidified with 10% HNO3, placed in an ice bath and brought to the laboratory. The samples were filtered through a 0.45 µm micropore membrane filter and kept at 4 °C until analysis. The samples were analyzed directly.

Sediment samples were collected using grab sampler from two sites. Samples were transported to the laboratory and air-dried in the laboratory at room temperature. Once air-dried, sediment samples were powdered and passed through 160 µm sieve. The samples packed in polyethylene bags and stored below −20°C prior to analysis. Sediments samples were weighed placed into the digestion bombs with 10 mL of HNO3/HCl (1:3 v/v) and digested in a microwave digestion system. Sediments analysis was carried out according to the procedure described earlier (Binning and Baird, 2001).

A total of 36 samples of mirror carp, Cyprinus. carpio species were collected with nets by local fishermen. Fish samples were transported to the laboratory in a thermos flask with ice on the same day. The mean length and weight of the fish were 303.6±12.4 mm and 526.6±32.15 g for Cyprinus. carpio. All fish samples were kept at -30°C until analysis. Sample preparation and analysis were conducted according to the procedure described by Bernhard (1976). Before analysis, muscle, liver, gill, stomach-intestine, air sac and heart from Cyprinus. carpio were removed. Fish samples were homogenized in a blender and one gram of homogenate was digested. A microwave digestion system (CEM Mars 5 ESP 1500 PLUS) was used to prepare the samples for analysis. In recent years, microwave digestion processes have been used in numerous studies (Machado et al., 1999; Kucuksezgin et al., 2001; Usero et al., 2003) owing to the advantages of this technique, which include speed of digestion and less possibility of contamination during the process. Samples (without skin) were mixed with 5 mL HNO3 (65%) and 5 mL H2SO4 in polypropylene vials. After 10 minutes of mixing, 1 mL H2O2 was added and samples were placed in a microwave (1 hour at 105°C). After digestion, the residues were diluted to 25 mL with HNO3 (0.3%) (Canlı and Atlı, 2003).

Determination of the elements in all samples was carried out by ICP–AES (Varian-Terra Model Liberty II). Detection limits are given in Table 1. The detection limit is defined as the lowest analytical signal to be distinguished qualitatively at a specified confidence level from the background signal (Kackstaetter and Heinrichs, 1997). The accuracy of analytical procedure was checked by analyzing the standard reference materials (water: SRM-143d, National Institute of Standards and Technology; sediment: CRM-277, Community Bureau of Reference; fish: DORM-2, National Research Council). Recovery rates ranged from 79 to 96% for all elements the investigated.


Table 2 shows the water quality constituents of Avsar Dam Lake water, reference freshwater values and other global published values on Lakes in different continents. In water samples, according to analysis results, the following findings were obtained for the concentration ranges of the metals: Cd: 0.0001 – 0.0012 mg/L; Cr: 0.001 – 0.012 mg/L; Cu: 0.01 – 0.02 mg/L; Fe: 0.28 – 2.39 mg/L; Ni: 0.0004 – 0.012 mg/L and Pb: 0.0003 – 0.019 mg/L were found. Heavy metal concentrations in the lake water were decreased in the sequence of Fe > Cu > Pb > Cr > Ni > Cd.

Table 3 shows the total extractable metals from Avsar Dam Lake water sediments and other global published values for Lake sediments. The concentrations in sediment samples were as follows: Cd: 0.34 – 1.23 mg/L; Cr: 9.41 – 19.9 mg/L; Cu: 18.2 – 38.4 mg/L; Fe: 19680 – 28560 mg/L; Ni: 19.8 – 39.4 mg/L and Pb concentration 0.64 – 6.35 mg/L were found. Heavy metal concentrations in the lake sediments decreased in the sequence of Fe > Ni > Cu > Cr > Pb > Cd.

The mean concentrations of heavy metals in the muscle, liver, heart, stomach-intestine, air sac and gills of Cyprinus carpio samples are given in Table 4. Heavy metal concentrations in the fish samples decreased in the sequence for the muscle as Fe > Cu > Pb > Ni > Cr > Cd, for the gill as Fe > Cu > Ni > Pb > Cr > Cd, for the stomach-intestine as Fe > Cu > Pb > Ni > Cr >Cd, for the air sac as Fe > Cu > Ni > Pb > Cd >Cr, for the heart as Fe > Cu > Ni > Pb > Cr >Cd and for the liver as Fe > Cu > Ni > Pb > Cr > Cd.


The Cd, Cr, Cu, Fe, Ni, Pb concentrations in lake water in the two sampling sites were compared with international standards. The obtained results showed that, with the exception of Fe, the heavy metal concentrations in water did not exceed WHO (World Health Organization, 1993), EC (Europian Community, 1998), EPA (Environment Protection Agency, 2002), WPCL (Water Pollution Control Legislation, 2004), CIW (Anonymous, Criterions of the Irrigation Water, 1997) and TSE-266 (Turkish Standards, 2005) guidelines (Table 2).

In the criterions of the irrigation water report (CIW) given as a result of “Gediz River Basin Study”, maximum heavy metal concentrations allowed in irrigation waters were stated (Anonymous, 1997). These values and our results were compared and it was found as low heavy metal concentrations. In this case, the water taken from Avsar Dam Lake is proper for irrigation.

The heavy metal levels of water in Avsar Dam Lake were lower compared to the metal levels in Gediz River (Uzunoğlu, 1999) and Atatürk Dam Lake(Karadede and Ünlü, 2000) with the exception of Fe. Meanwhile Cu and Fe concentrations were higher than the Hazar Lake (Özmen et al., 2004) and Fe concentration was higher than the Demirköprü Dam Lake(Öztürk et al., 2008). Also, all heavy metal concentrations of water in Avsar Dam Lake were higher than the reported values for Lapland Lakes and Siberian Pond (Mannio et al., 1995; Gladyshev et al., 2001), (Table 2).

The metal concentrations obtained from the sediment samples were compared with Sediment Quality Guideline which showed that these concentrations did not exceed the probable effect concentration (PEC) levels. The average concentrations of Cd and Fe were higher than those reported in Gediz River. Also, Cr, Cu, Fe and Ni concentrations were higher than the Demirköprü Dam Lakeand Cu concentration was higher than the Hazar Lake. Ni concentration was lower than the Atatürk Dam Lake (Table 3). Generally, the average Cd and Pb concentrations in Avsar Dam Lake were found to be lower than the other studies but Ni and Fe were higher. Differences between our data and the literature probably originate from variations in geological mining history of localities and urban and domestic activities.

When the values obtained in the Cyprinus carpio samples were compared with the tolerable values, it has been determined that the pollution has reached to hazardous levels for the health of human (Table 5). Cd, Cr, Ni and Pb values were higher than tolerable values.

The results confirmed the differences of accumulation of heavy metals in different tissues. The highest concentrations of Cr, Fe, and Pb were found in the stomach-intestine. Although, the highest level of Cu was found in the heart. Moreover, Cu accumulation in Cyprinus carpio was found to be the highest level in liver (Yaramaz, 1986).

Papagiannis et al., (2004) have determined the level of Cu in various tissues of the Cyprinus carpio species in Pomvatis Lake ,Greece they reported the highest level of Cu in the liver and the lowest level of Cu in the muscle. In this study, the level of Cu in the liver was found to be higher than the muscle.

Fe, Cu and Pb accumulation in the muscle of Cyprinus carpio samples of Avsar Dam Lake were higher than the carps of Atatürk Dam Lake and Gölcük Lake (Uysal et al., 1986). According to the analysis of the results, the heavy metal levels in muscles showed that Fe had the highest and Cd had the lowest concentrations(Table 4). Similar results were reported from a number of fish species which shows that muscle is not an active tissue in accumulating heavy metals (Khan et al., 1989; Karadede and Ünlü, 2000).

Öztürk et al., (1995) found the highest level of Fe and the lowest level of Cd in the muscle, gill, air sac, stomach-intestine and liver of Cyprinus carpio samples in Altınkaya Dam, respectively. Also, Öztürk et al., (2008) determined the highest level of Fe and the lowest level of Cd in all studied tissues of Cyprinus. carpio samples in Demirköprü Dam Lake. The result of our study was similar to the above studies.

Alam et al. (2002) has reported the concentrations of elements in the muscle, liver, intestine, kidney and gonads of cultured and wild carps caught in Lake Kasumigaura, Japan. They reported that the metal concentrations were lowest in muscle, and did not exceed the established quality standards for fish. In this study, the heavy metal levels in fish were found to be high. The high heavy metal levels in Cyprinus carpio would pose health hazards to the consumers.

Consequently, it can be concluded that the concentrations of heavy metals in water from Avsar Dam Lake are lower than the TSE-266, WPCL, CIW, WHO, EPA and EC standards, with the exception of Fe. The average concentration of Fe in the lake water was higher than the TSE-266, WPCL, EPA and EC standards. The concentrations of Cr, Cu, Fe and Pb in sediments from Avsar Dam Lake were lower than the sediment samples obtained from Gediz River, which is known as a polluted site. There were high levels of heavy metals in fish. It was determined that the pollution has reached hazardous levels for the health of human. Also, a potential danger may exist in the future, depending on the agricultural development in this region. As the Avsar Dam Lake is also used for agricultural irrigation purposes, performance of pollution researches at certain periods is of significance for both environment and public health.


The authors are grateful for the support of the Institute of Natural and Applied Sciences of Celal Bayar University. The authors would like to thank Dr. Murat Tutam for his constant help in analysis of heavy metals by ICP/AES in different samples.


  • Alam, M.G.M., Tanaka, A., Allinson, G., Laurenson, L.J.B., Stagnitti, F., and Snow, E.T., (2002). A comparison of trace element concentrations in cultured and wild carp (Cyprinus carpio) of Lake Kasumigaura, Japan. Ecotox. Environ. Safe., 53: 348–354.
  • An, Y.J., and Kampbell, D.H., (2003). Total, dissolved, and bioavailable metals at Lake Texoma marinas. Environ. Pollut., 122: 253–259.
  • Anonymous, (1997). Gediz Havzası Çalışmaları. T.C. İzmir Çevre İl Müdürlüğü, Türkiye. (In Turkish)
  • Begüm, A., Amin, M.d.N., Kaneco, S., and Ohta, K., (2005). Selected elemental composition of the muscle tissue of three species of fish, Tilapia nilotica, Cirrhina mrigala and Clarius batrachus, from the fresh water Dhanmondi Lake in Bangladesh. Food Chemistry, 93: 439–443.
  • Bernhard, M., (1976). Manual of methods in aquatic environment research, part 3: sampling and analyses of biological material. FAO Fish Tech Paper No. 158, UNEP Rome.
  • Binning, K., Baird, D., (2001). Survey of heavy metals in the sediments of the Swartkops River Estuary, Port Elizabeth South Africa. Water SA., 27: 461–466.
  • Camusso, M., Vigano, L., Baitstrini, R., (1995). Bioaccumulation of trace metals in rainbow trout. Ecotox. Environ. Safe., 31: 133–141.
  • Canlı, M., Atlı, G., (2003). The relationships between heavy metal (Cd, Cr, Cu, Fe, Pb, Zn) levels and the size of six Mediterranean fish species. Environ. Pollut., 121: 129–136.
  • Censi, P., Spoto, S. E., Saiano, F., Sprovieri, M., Mazzola, S., Nardone, G., Di Geronimo, S. I., Punturo, R., Ottonello, D., (2006). Heavy metals in coastal water systems. A case study from the northwestern Gulf of Thailand. Chemosphere, 64: 1167–1176.
  • EC (European Commission), (1998). Council Directive 98/83/. EC of 3 November 1998 on the quality of water intended for human consumption. L 330/32, 5.12.98.
  • EC (European Commission), (2005). Commission Regulation (EC) No 78/2005 of 19 January 2005 amending Regulation (EC) No 466/2001 as regards heavy metals, L 16/43–45.
  • EPA (Environmental Protection Agency), (2002). Risk assessment: Technical background information. RBG Table. Available from (online update: 23.03.2009).
  • Fernandes, C., Fontaínhas-Fernandes, A., Cabral, D., Salgado, M. A., (2008). Heavy metals in water, sediment and tissues of Liza saliens from Esmoriz–Paramos lagoon, Portugal. Environ. Monit. Assess. 136: 267–275.
  • Gladyshev, M. I., Gribovskaya, I. V., Moskvicheva, A. V., Muchkina, E. Y., Chuprov, S. M., Ivanova, E. A., (2001). Content of metals in compartments of ecosystem of a Siberian pond. Arch. Environ. Contam. Toxicol., 41: 157–162.
  • Kackstaetter, U. R., Heinrichs, G., (1997). Validity of lowcost laboratory geochemistry for environmental applications. Water Air Soil Pollut., 95: 119–131.
  • Karadede, H., and Ünlü, E., (2000). Concentrations of some heavy metals in water, sediment and fish species from the Atatürk Dam Lake(Euphrates), Turkey. Chemosphere, 41(9): 1371–1376.
  • Khan, A.T., Weis, J.S., and D’andrea, L., (1989). Bioaccumulation of four heavy metals in two populations of Grass Shrimp, Palaemonotes pugio. B. Environ. Contam. Tox., 42: 339–343.
  • Kishe, M.A., and Machiwa, J.F., (2003). Distribution on heavy metals in sediments of Mwenza Gulf of Lake Victoria, Tanzania. Environ. Int., 28: 619–625.
  • Kucuksezgin, F., Altay, O., Uluturhan, E., Kontas, A., (2001). Trace metal and organochlorine residue levels in Red Mullet (Mullus barbatus) from the Eastern Aegean, Turkey. Water Res., 35: 2327–2332.
  • MacFarlane, G. B., Burchettt, M. D., (2000). Cellular distribution of Cu, Pb, and Zn in the Grey Mangrove Avicemnia marina (Forsk.). Vierh Aquatic Botanic, 68: 45–59.
  • Machado, L. M., Bebianno, M. J., Boski, T., Moura, D. M., (1999). Trace metals on the Algarve Coast, II: Bioaccumulation in mussels Mytilus galloprovincialis (Lamarck, 1819). Bol. Inst. Esp. Oceanogr., 15: 465–471.
  • Mannio, J., Järvinen, O., Tuominen, R., Verta, M., (1995). Survey of trace elements in Lake waters of Finnish Lapland using the ICP–MS technique. Sci. Tot. Environ., 160: 433–439.
  • Namminga, H. N., Wilhm, J., (1976). Effects of high discharge and an oil refinery cleanup operation bon heavy metals in water and sediments in Skeleton Creek. Proceedings of the Oklahoma Academy of Science, 56: 133–138.
  • NOAA (National Oceanic and Atmospheric Administration), (2009). SQUIRT, Screening Quick Reference Tables for in Sediment, (online update: 23.03.2009).
  • Özmen, H., Külahçı, F., Çukurovalı, A., and Doğru, M., (2004). Concentrations of heavy metal and radioactivity in surface water and sediment of Hazar lake (Elazığ, Turkey). Chemosphere, 55: 401–408.
  • Öztürk, M., Bat, L., and Öztürk, M., (1995). Altınkaya Barajında (Samsun) yaşayan Cyprinus carpio L. 1758 türünün çeşitli organ ve dokularındaki bazı ağır metallerin birikimi. II. Ulusal Ekoloji ve Çevre Kongresi, 11-13 Eylül, Ankara, Türkiye. (In Turkish)
  • Öztürk, M., Özözen, G., Minareci, O., and Minareci, E., (2008). Determination of heavy metals in of fishes, water and sediment from the Demirköprü Dam Lake(Turkey). Journal of Applied Biological Sciences, 2(3): 99–104.
  • Papagiannis, L., Kagalou, L., Leonardos, J., Petridis, D., and Kalfakakou, V., (2004). Copper and zinc in four freshwater fish species from lake Pamvotis (Greece). Environ. Int., 30: 357–362.
  • Pote, J., Haller, L., Loizeau, J.L., Bravo, A.G., Sastre, V., and Wildi, W., (2008). Effects of a sewage treatment plant outlet pipe extension on the distribution of contaminants in the sediments of the Bay of Vidy, Lake Geneva, Switzerland. Bioresource Technol., 99: 7122–7131.
  • Praveena, S. M., Radojevic, M., Abdullah, M. H., Aris, A. Z., (2008). Application of sediment quality guidelines in the assessment of mangrove surface sediment in Mengkabong lagoon, Sabah, Malaysia. Iran. J. Environ. Health. Sci. Eng., 5 (1): 35–42.
  • Rashed, M.N., (2001). Monitoring of environmental heavy metals in fish from Nasser lake. Environ. Int., 27: 27–33.
  • Storelli, M. M., Storelli, A., D’ddabbo, R., Marano, C., Bruno, R., Marcotrigiano, G. O., (2005). Trace elements in loggerhead turtles (Caretta caretta) from the eastern Mediterranean Sea: Overview and evaluation. Environ. Pollut., 135: 163–170.
  • Szymanowska, A., Samecka-Cymerman, A., Kempers, A.J., (1999). Environmental Research, Section B. Heavy Metals in Three Lakes in West Poland. Ecotox. Environ. Safe., 43: 21–29.
  • TFC, Turkish Food Codes, (2002). Official Gazette, 23 September 2002, No. 24885.
  • TSE–266 (Turkish standars), (2005). Insani tüketim amaçlı sular hakkında yönetmelik. Türk Standartları, Ankara. (In Turkish)
  • Tüzen, M., (2003). Determination of heavy metals in fish samples of the MidDam Lakee Black Sea (Turkey) by graphite furnace atomic absorption spectrometry. Food Chemistry, 80: 119–123.
  • UNEP, (1985). Reference Methods for Marine Pollution Studies, Determination of total Hg in marine sediments and suspended solids by cold vapour AAS, 26.
  • Usero, J., Izquierdo, C., Morillo, J., Gracia, I., (2003). Heavy metals in fish (Solea vulgaris, Anguilla anguilla and Liza aurata) from salt marshes on the southern Atlantic coast of Spain. Environ. Int., 29: 949–956.
  • Uysal, H., Tunçer, S., and Yaramaz, Ö., (1986). Gölcük ve Gölmarmara göllerinde yaşayan Cyprinus. carpio, S glanis, A. anguilla’da bazı ağır metal düzeylerinin araştırılması. VIII. Ulusal Biyoloji Kongresi Tebliğleri, İzmir, Türkiye. (In Turkish)
  • Uzunoğlu, O., (1999). Gediz nehrinden alınan su ve sediment örneklerinde bazı ağır metal konsantrasyonlarının belirlenmesi. Yüksek lisans tezi. Celal Bayar Üniversitesi Fen Bilimleri Enstitüsü, Manisa, Türkiye. (In Turkish)
  • WHO (World Health Organization), (1993). Guidelines for drinking water quality. Recommendations, vol. 1, 2nd ed., Geneva.
  • WPCL (Water Pollution Control Legislation), (2004). Land-Based Water Quality Classification, Official journal, 25687, Turkey.
  • Wyse, E. J., Azemard, S., and Mora, S. J., (2003). Report on the World-wide Intercomparison Exercise for the Determination of Trace Elements and Methylmercury in Fish Homogenate IAEA-407, IAEA/AL/144 (IAEA/MEL/72), IAEA, Monaco.
  • Yaramaz, Ö., (1986). Investigation of some heavy metal accumulation in Cyprinus. carpio, S. glanis, A. anguilla from Gölcük and Marmara lake. VII Turkish Biology Congress, Izmir, Turkey, 2: 444–453.

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