Trophic transfer, bioaccumulation, and health risk assessment of heavy metals in Aras River: case study-Amphipoda- zander - human.

Heavy metals (As, Pb, Cd, and Cu) were traced in a model of the aqueous food chain in the Aras River, located in northwest of Iran. The selected model included the zander (Sander lucioperca L.) and crustacean species known as amphipods (Gammarus sp.) which belong to the food chain of this ray-finned fish. A total of 172 samples (70 fish and 102 amphipods) were collected randomly and analyzed for heavy metals using atomic absorption spectrophotometry (AAS). The results showed that the accumulation of heavy metals in both taxa are in the order of As > Pb > Cd > Cu, and concentrations of heavy metals in fish muscle are higher than Gammarus sp. in all stations in different seasons. Specimens of station (1) displayed the highest heavy metal content due to local industrial activities. The recorded concentrations of As, Pb, and Cd exceed the permissible limits. There is a close correlation between the concentrations of heavy metals in the amphipods and zanders. Target hazard quotient (THQ), total target hazard quotient (TTHQ), and carcinogenic risk (CR) were calculated to assess risks to human health. The average of THQ for As (1.43) exceeded the international standards and presenting health risks to the consumers of this fish species. The TTHQ for heavy metals was estimated higher than 1. At all stations, the value of CRCd > 1 × 10-3 indicating the degree of carcinogenicity of this metal in all parts of the Aras River. Therefore, according to our results, efficient control measures and regular biomonitoring should be established in this region.

Reproduction of Limnatis paluda (Tennent 1859) in laboratory conditions.

The reproductive functions of Limnatis paluda were studied in laboratory conditions including imposing of two thermal conditions (T1: 18 ± 2 °C and T2: 26 ± 2 °C) and with there being placement of three bedding substrates (tile, moss, and stone) in the containers specimens were confined. Furthermore, values for reproductive variables of cocoons and hatchlings were recorded. With the T2 treatment, gravid adults had cocoon depositions, whereas those when there was imposing of the T1 treatment did not have cocoon depositions. There was cocoon deposition only on the moss bedding, and it is presumed that moss could provide a robust and stable nursing microenvironment for developing embryos. Frequency (%) of cocoon depositions did not vary during the months of the deposition period. Hatching occurred after 26 ± 2 days when there was imposing of the T2 treatment. There was no correlation between the values for size of the ovigerous cocoons and number of offspring. There was a negative correlation between number and mean weight of hatchlings. There was a difference in cocoon weight for the different months and fluctuation in mortality and hatching rate which is assumed to be related to differences in feeding behaviors.