Dergiler / Turkish Journal of Veterinary and Animal Sciences / 2005 / Cilt: 29 - Sayı: 1

Effects of Heavy Metal Accumulation on the 96-h LC50 Values in Tench Tinca tinca L., 1758

Sayfa
139–144
Yayın Tarihi
2005-01-01
DOI
—
🏛️Bu makalenin bibliyografik verileri ve tam metin bağlantısı DergiPark üzerinden sağlanmıştır.
DergiPark Kaydı ↗
✨

Yapay Zeka Hızlı Bakış & Çıkarımlar

AI Insight
⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

This close relationship showed that the previous body accumulation of heavy metals has a direct effect on the 96-h LC50 values of the respective heavy metals and the susceptibility of fish.

📌 3 Maddede Bu Makale

🎯
Amaç & Hipotez:The effects of already accumulated heavy metals (Hg, Cd, Pb) in the body of tench on the 96-h LC50 values of the respective heavy metals were studied.
📊
Temel Bulgular & Veri:The body concentration of mercury, cadmium and lead was 0.011, 0.32 and 1.59 mg/g respectively, and their 96-h LC50 values were 1.0, 6.5 and 300.0, ppm, respectively.
💡
Sonuç & Katkı:This close relationship showed that the previous body accumulation of heavy metals has a direct effect on the 96-h LC50 values of the respective heavy metals and the susceptibility of fish.
🔬Tür:Araştırma Makalesi
📍Kapsam:Genişletilmiş Akademik Örneklem
⚙️Değişkenler:Mercury · cadmium · lead

Özet

The effects of already accumulated heavy metals (Hg, Cd, Pb) in the body of tench on the 96-h LC50 values of the respective heavy metals were studied. The body concentration of mercury, cadmium and lead was 0.011, 0.32 and 1.59 mg/g respectively, and their 96-h LC50 values were 1.0, 6.5 and 300.0, ppm, respectively. The general accumulation order of heavy metals and their respective 96-h LC50 values were Hg< Cd< Pb. It was observed that the fish with lowest body concentration of heavy metal showed the lowest 96-h LC50 value of the respective heavy metal and vice versa. This close relationship showed that the previous body accumulation of heavy metals has a direct effect on the 96-h LC50 values of the respective heavy metals and the susceptibility of fish.

Abstract

The effects of already accumulated heavy metals (Hg, Cd, Pb) in the body of tench on the 96-h LC50 values of the respective heavy metals were studied. The body concentration of mercury, cadmium and lead was 0.011, 0.32 and 1.59 mg/g respectively, and their 96-h LC50 values were 1.0, 6.5 and 300.0, ppm, respectively. The general accumulation order of heavy metals and their respective 96-h LC50 values were Hg< Cd< Pb. It was observed that the fish with lowest body concentration of heavy metal showed the lowest 96-h LC50 value of the respective heavy metal and vice versa. This close relationship showed that the previous body accumulation of heavy metals has a direct effect on the 96-h LC50 values of the respective heavy metals and the susceptibility of fish.

🔖

Bu Makaleye Atıf Yap

SHAH, S. L. (2005). Effects of Heavy Metal Accumulation on the 96-h LC50 Values in Tench Tinca tinca L., 1758. Turkish Journal of Veterinary and Animal Sciences, Cilt: 29 - Sayı: 1, 139–144. https://ajindex.com/articles/161354

📄 Tam Metin PDF Okuyucu

📄

PDF görüntüleyici hazırlanıyor...

Kaynakça (12)

  1. Guerrin, F., Sacaze, V.B., Sannes, P.S.: Level of heavy metals and organochlorine pesticides of cyprinid fish reared four years in a waste water treatment pond. Bull. Environ. Contam. Toxicol., 1990; 44: 461-467.
  2. Das, K.K., Banerjee, S.K., Cadmium toxicity in fishes. Hydrobiology. 1980; 75: 117-121.
  3. Veena, K.B., Radhakrishnan, C.K., Chacko, J.: Heavy metal induced biochemical effects in an estuarine teleost. Indian J. Mar. Sci., 1997; 26: 74-78.
  4. Allen, P.: Changes in the haematological profile of the cichlid, Oreochromis aureus (Steindachner) during acute inorganic mercury intoxication. Comp. Biochem. Physiol., 1994; 108: 117- 121. Mason, C.F., Last, N.I., MacDonald, S.M.: Mercury, cadmium and lead in British otters. Bull. Environ. Contam. Toxicol., 1986; 37: 844-849.
  5. Erdem, C.: Cadmium accumulation in liver, spleen, gill and muscle tissues of Tilapia nilotica. Çukurova Univ. Fac. Fisher. J. Biochem., 1990; 15: 13-22.
  6. Chen, C.Y., Folt, C.L.: Bioaccumulation and diminution of arsenic and lead in a freshwater food web. Environ. Sci. Technol., 2000; 34: 3878-3884.
  7. Giesy, J.P., Wiener, J.G.: Frequency distributions of trace metal concentrations in five freshwater fishes. Trans. Am. Fish. Soc., 1977; 106: 393-403.
  8. Dethloff, G.M., Bailey, H.C., Maier, K.J.: Effects of dissolved copper on select haematological, biochemical and immunological parameters of wild rainbow trout, Oncorhynchus mykiss. Arch. Environ. Contam. Toxicol., 2001; 40: 371-380.
  9. Deb, S.C., Fukushima, T.: Metals in aquatic ecosystems: Mechanism of uptake, accumulation and release. Int. J. Environ. Stud., 1999; 56: 385-33 p. MacLeod, J.C., Pessah, E.: Temperature effects on mercury accumulation, toxicity and metabolic rate in rainbow trout, Salmo gairdneri. J. Fish. Res. Board Can., 1973; 30: 485-492.
  10. Wepener, V., VanVuren, J.H.J., DuPreez, H.H.: Effect of manganese and iron at a neutral and acidic pH on the haematology of the banded Tilapia, Tilapia sparrmanii. Bull. Environ. Contam. Toxicol., 1992; 49: 613-619.
  11. Gill, T.S., Pant, J.C.: Mercury induced blood anomalies in the fresh water teleost, Barbus conchonius. Water Air Soil Pollut., 1985; 24: 165-171.
  12. Kirubagaran, R., Joy, K.P.: Inhibition of testicular 3b-Hydroxy-D5 steroid dehydrogenase (3b-HSD) activity in catfish, Clarius batrachus (L.) by mercurials. Ind. J. Exp. Biol., 1988; 26: 907- 908. IIiopoulou-Georgudaki, J., Kotsanis, N.: Toxic effects of cadmium and mercury in rainbow trout (Oncorhynchus mykiss): A short- term bioassay. Bull. Env