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The objectives of this study were to investigate chromosomal aberrations in rice field frogs (Fejervarya limnocharis) from gold mine area compared to those from nonaffected area. Three frogs were collected from each site, and chromosomal aberrations were studied in their bone marrow. Arsenic (As) was also measured in water and sediment from both areas. The average As concentrations in samples from the gold mine and the non-affected areas were 0.03 ± 0.003 mg/ L and not detected in water and 351.59 ± 5.73 and 1.37 ± 1.07 mg/kg in sediment, respectively. The values in the gold mine were still higher than that allowed by the water and soil quality standards; however, the As concentrations in the samples from the non-affected area were acceptable. The average concentrations of As in the frog samples from the gold mine and the non-affected areas were 0.35 ± 0.33 and 0.07 ± 0.01 mg/kg, respectively, which were both lower than the standard of As contamination in food. The diploid chromosome number of frogs in both areas was 2n = 26, and the percentage of chromosomal aberrations in rice field frogs in the gold mine area was higher than in the non-affected area. There were seven types of chromosomal aberrations observed: single chromatid gap, isochromatid gap, single chromatid breaks, deletion, fragmentation, centric fragmentation and polyploidy. The most common chromosomal aberration in the samples from the affected area was the single chromatid gap. The difference in the percentages of chromosomal aberrations in rice field frogs from each area was statistically significant (p \ 0.05).

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Heavy metals from electronic waste (e-waste) accumulate in the environment and can affect human health. The purpose of this study was to determine As, Cd, Cr and Pb concentrations in water, sediment and three species of edible aquatic plants (Ottelia alismoides, Ipomoea aquatic and Marsilea crenata) near an e-waste open dumpsite. Samples were collected from six sampling points surrounding an e-waste open dumpsite and heavy metal concentrations were analyzed by inductively coupled plasma optical emission spectrometry (ICP-OES). Bioaccumulation factors (BAFs), estimated daily intake (EDI), hazard quotient (HQ), hazard index (HI) and carcinogenic risk (CR) were evaluated in the plants. The Pb concentration in the water samples exceeded the quality standard. The order of the heavy metal concentrations in the sediment was Pb>Cr>As >Cd, and these concentrations were within the limits of the quality standard. The order of the heavy metal concentrations in O. alismoides, I. aquatic and M. crenata was Cr>Pb>As>Cd, Pb>Cr>As>Cd and Pb>Cr>As>Cd, respectively. The concentrations of As, Cd, Cr and Pb in O. alismoides and As, Cr and Pb in I. aquatic and M. crenata exceeded the quality standard of food consumption. Most of the BAF values of the heavy metals in O. alismoides were more than one, but in I. aquatic and M. crenata, they were less than one. The order of the EDI values in O. alismoides, I. aquatic and M. crenata was Cr>Pb>As>Cd, Pb>Cr>As>Cd and Cr>As>Pb >Cd, respectively. The HQ values were greater than one for As, Cd and Pb in O. alismoides; Pb in I. aquatic; and As and Pb in M. crenata. The HQ and CR values show that the consumption of edible plants from an e-waste open dumpsite is a human health risk.