Analysis of Zn, Cd, As, Cu, Pb, and Fe in snails as bioindicators and soil samples near traffic road by ICP-OES.

Snails are used as biological indicators of the environment pollution for heavy metals. Living snail samples were collected from different sites at the city of Irbid-Jordan and classified according to their morphological features including Helix pelasga, Eobania vermiculata, Xeropicta derbentina, Oychilus, Xerocrassa seetzenii, Xerocrassa simulata, and Pila. Zn, Cd, As, Cu, Pb, and Fe levels were measured by inductively coupled plasma-optical emission spectroscopy. Results indicated that metal concentrations in all snail shell samples were with an average and range for Zn 22.4 (6.5-105.5) µg g(-1), Cd 7.8 (0.4-48.1) µg g(-1), As 25.9 (0.7-248.5) µg g(-1), Cu 15.1 (1.6-69.0) µg g(-1), Pb 0.4 (0.2-1.7) µg g(-1), and Fe 119.6 (14.0-1102.0) µg g(-1), whereas, in soil samples, the average and range for Zn 204.0 (12.0-709.0) µg g(-1), Cd 5.7 (0.2-39.5) µg g(-1), As 3.2 (1.8-5.2) µg g(-1), Cu 22.1 (2.3-77.4) µg g(-1), Pb 0.2 (0.1-0.3) µg g(-1), and Fe 242.4 (25.0-680.0) µg g(-1).

Uptake of zinc and copper by halophilic bacteria isolated from the Dead Sea shore, Jordan.

Ten Gram-positive and gram-negative bacterial cultures were recovered from nine water, mud, and soil samples collected from the Dead Sea shore at Suwaymah. All bacterial cultures were able to grow at 10% NaCl and at 45 degrees C. They were able to grow in nutrient media supplemented with 1250 ppm of Zn. Most of them, except cultures 2 and 8, were able to grow in nutrient medium supplemented with 1000 ppm of Cu. After 2 wk of incubation of these 10 cultures at different concentrations (5, 25, 100, and 500 ppm), stock solutions of both Zn and Cu elements, the maximum absorption using atomic absorption spectrometry for Zn was achieved by culture 7 at 11.2%, 1.0%, 38.4%, and 84.54%, respectively, from the previous stock solutions, whereas the maximum absorption of the same concentration of Cu was achieved by culture 3 at 6.2%, 55.56%, 85.66%, and 90.82%, respectively, of the different concentrations. After 3 wk of incubation, the estimated absorption for Zn was achieved by cultures 2, 9, and 10 at 19.2%, 16.68%, 42.92%, and 76.5%, 18.2%, 21.56%, 32.22%, and 77.43%, and 20.8%, 23.52%, 32.22%, and 82.84% of the previous stocks. The maximum absorption of the same concentration of Cu was achieved by culture 3 at 32.6%, 49.88%, 90.44%, and 91.86%, respectively. The accumulation of the absorbed metals was found to be maximum in the protoplast of all cultures. The accumulation at the cell wall was maximum for cultures 2 and 6 for Zn and Cu, respectively, and between the cell wall and the plasma membrane, it was maximum for cultures 2 and 8 for Zn and Cu, respectively.

Removal of lead and cadmium by halophilic bacteria isolated from the Dead Sea shore, Jordan.

Ten Gram-positive and Gram-negative bacterial cultures were recovered from nine water, mud, and soil samples from the Dead Sea shore at Suwaymah. They were able to grow at 10% NaCl and at 45 degrees C. Bacterial cultures 6 and 8 were able to grow in nutrient media supplemented with 2250 ppm of Pb. Bacterial cultures 1, 3-6, 9, and 10 were able to grow in nutrient medium supplemented with 1000 ppm of Cd. Atomic absorption spectrometry was used to estimate the absorbed Pb and Cd by bacterial cultures from 5-, 25-, 100-, and 500-ppm stock solutions of both elements. After 2 wk, the results showed that the maximum absorption for Pb was achieved by culture 6 in the following percentages: 79.8%, 70.48%, 89.48%, and 83.39%, respectively. The maximum absorption of the same concentration of Cd was achieved by culture 9 with the following percentages: 69.2%, 32.24%, 44.98%, and 60.0%, respectively. After 3 wk of incubation, the estimated absorption of both heavy metals was achieved by the same cultures (6 and 9), respectively, in the following percentages: 86.8%, 76.72%, 96.25%, and 96.0% for Pb and 82.60%, 93.2%, 92.74%, and 89.79% for Cd. The accumulation of the absorbed metals was found to be maximum in the protoplast of all the cultures. The accumulation at the cell wall was maximum in culture 2, and between the cell wall and the plasma membrane, it was maximum in cultures 2 and 8 for Pb and Cd, respectively.

Effect of different heavy-metal concentrations on Drosophila melanogaster larval growth and development.

The survival percentage of Drosophila melanogaster larvae on synthetic media containing different concentrations of heavy metals, including Cd, Cu, Pb, and Zn, in the first generation indicated no significant reduction in their growth and development up to 500 ppm for all tested heavy-metal concentrations. At 500 ppm, results showed that there was a significant reduction in pupa and adult stages: 65% and 25% for Cd, 50% and 25% for Cu, 100% and 95% for Pb, and 85% and 75% for Zn, respectively. The survival percentages at 1000 ppm were further significantly reduced: 15% and 0% for Cd, 35% and 15% for Cu, 45% and 90% for Pb, and 65% and 35% for Zn, respectively for pupa and adult stages. For the second generation, there was no significant reduction in survival growth and development up to 100 ppm, but above 500 ppm, there was a significant reduction. For most of these heavy-metal concentrations, the survival percentages of the second generation at the pupa stage was higher than the first generation, whereas for the adult, there was a lower survival percentage, indicating some effect on metamorphosis of these heavy-metal concentrations on Drosophila melanogaster Comparing the survival percentage between first and second generations at 500 ppm for pupa indicate a significant increase on Cu only, and for the adult, there was a significant reduction for Cd.