Metal concentration in commonly sold fruit vegetables in dhaka city market and probable health risk

The present study evaluated the concentration of heavy metals in six different fruit vegetables collected from Kawran Bazar market of Dhaka city of Bangladesh. The analyzed fruit vegetable samples were randomly collected, processed and analyzed for heavy metal determination using atomic absorption spectrophotometry (AAS). Mean concentrations (mg kg-1) of Cr, Cd, Pb, Ni, Cu, Zn, Fe and Mn of Lady’s finger, Pumpkin, Tomato, Brinjal, Snake gourd and Cucumber were within the range of 0.83 to 4.88, 0.08 to 0.18, 0 to 3.00, 0.33 to 3.70, 8.10 to 10.88, 17.81 to 45.91, 53.00 to 131.50 and 10.40 to 45.90 mg kg-1 of dry weight, respectively. Mean concentration (mg kg-1) of Cr in Brinjal (4.88); Pb in Pumpkin (3.00) and Brinjal (0.50); Ni in Snake gourd (3.70); Cu in Lady’s finger (10.10), Brinjal (10.88), Snake gourd (10.53) and Cucumber (10.48) were higher than the maximum permissible limit (MPL). The study suggests regular monitoring of heavy metals in vegetables to prevent excessive accumulation in human body. Dhaka Univ. J. Biol. Sci. 30(1): 35-47, 2021 (January)

Heavy Metals in PM10 Aerosols Over an Urban Industrial City

PM10 aerosols were monitored and analyzed for heavy metal concentration at Raipur city Chhattisgarh, India for possible source identification of pollutants. Sampling of PM10 aerosols was carried out by using respirable dust sampler during the year 2016. Daily PM10 average concentrations varied between 122.033 and 197.854 µg/m3, 91.350 and 133.950 µg/m3 and 112.770 and 480.170 µg/m3 in summer, monsoon and winter respectively. Chemical analysis of PM10 samples was carried out for heavy metal determination. Heavy metal (Fe, Mn, Ni and Pb) were analyzed with the help of atomic absorption spectroscopy (AAS) and found in the range of 2.713-36.862, 0.131-9.129. 0.880-4.195 and 0.015-0.321 µg/m3 for Fe, Mn, Pb and Ni respectively. PM10 concentrations shows distinct seasonal variation being twice in winter season than in summer; winter (mean: 241.820 ± 33.912 µg/m3) > summer (mean: 159.512 ± 14.360 µg/m3) > monsoon (mean: 107.480 ± 9.213 µg/m3). The concentration of heavy metal was different in all the seasons depending on their sources. Identification of possible sources was done by principal component analysis (PCA) illustrating industrial activities, soil (crustal) dust and biomass burning as the major sources in the region. The back trajectory analysis of the air masses depicts that the local anthropogenic activities affect the concentration of pollutants at the source. Correlation analysis between the heavy metal concentrations agreed the results obtained by PCA. The work helped in observing the seasonal trend of particulate matter concentrations and in identification of major sources of air pollution in the city.

Heavy metals concentration in “etak” tissue at different processing stages.

Corbicula fluminea, known as “etak” in Kelantan, Malaysia is a freshwater bivalve. This clam is widely consumed as traditional snack by the locals. However, lately there are numerous reports in local newspapers that claim “etak” to cause health effects due to eating contaminated “etak”. Hence, this study aims to determine the heavy metals concentration in fresh, smoked and exposed “etak” sold at the stall as a baseline study in order to develop a method for removing the heavy metals content in its tissues. This study involves sample collection in the stalls around Kelantan, sample preparations via acid digestion and heavy metal determination using Perkin Elmer PinAAcle 900F Atomic Absorption Spectrometer. The results showed the heavy metals (Cr, Zn, Mn and Cu) concentrations (µg/g) in all “etak” tissue were at different level for fresh (Cr: 1.02±0.35ppm, Zn: 74.57±2.76ppm, Mn: 40.22±9.96ppm and Cu: 15.27±1.41ppm), smoked (Cr: 0.42±0.02ppm, Zn: 54.62±17.83ppm, Mn: 50.13±2.31ppm and Cu: 20.94±8.81ppm) and exposed (Cr: 0.53±0.08ppm, Zn: 63.07±8.44ppm, Mn: 50.41±6.92ppm and Cu: 12.80±0.40ppm) samples. The results obtained were compared with the permissible limits set by Malaysian Food Regulations 1985 (Cu: 30.0ppm and Zn: 100.0ppm), FAO/WHO 1984 (Mn: 5.4ppm) and IAEA – 407 (Cr: 0.75ppm). For fresh “etak”, Zn and Cu concentration were below the standards, while Mn and Cr were exceeded the permissible limits. For smoked “etak” and exposed “etak” at stall, all heavy metals concentration were within the permissible limits, except Mn contents. This study successfully determine the baseline concentration of the heavy metals in “etak”.