Your search found 7 records
1 Simmons, Robert; Pongsakul, P.; Chaney, R. L.; Saiyasitpanich, D.; Klinphoklap, S.; Nobuntou, W. 2003. The relative exclusion of zinc and iron from rice grain in relation to rice grain cadmium as compared to soybean: Implications for human health. Plant and Soil, 257:163-170.
Rice ; Soyabeans ; Cadmium ; Zinc ; Iron ; Public health ; Risks / Thailand
(Location: IWMI-HQ Call no: IWMI 633.18 G750 SIM Record No: H039374)
https://vlibrary.iwmi.org/pdf/H039374.pdf

2 Bandara, W. M. J.; Silva, L. C. 2001. Rice crop response to zinc application in low humic Gley soils of low country intermediate zone. Annals of the Sri Lanka Department of Agriculture, 3:9-18.
Rice ; Paddy fields ; Soil properties ; Zinc / Sri Lanka
(Location: IWMI-HQ Call no: P 7671 Record No: H039434)

3 Simmons, Robert W.; Noble, Andrew D.; Pongsakul, P.; Sukreeyapongse, O.; Chinabut, N. 2009. Cadmium-hazard mapping using a general linear regression model (Irr-Cad) for rapid risk assessment. Environmental Geochemistry and Health, 31(1):71-79. [doi: https://doi.org/10.1007/s10653-008-9157-x]
Rice ; Soyabeans ; Cadmium ; Zinc ; Health hazards ; Risks ; Assessment ; Irrigated farming ; Models ; Soil analysis / Japan / China / Thailand / Vietnam / Myanmar / Laos
(Location: IWMI HQ Call no: e-copy only Record No: H040619)
https://vlibrary.iwmi.org/pdf/H040619.pdf
(0.37 MB)

4 Karunaratne, A. M.; Amerasinghe, Priyanie H.; Ramanujam, V. M. S.; Sandstead, H. H.; Perera, P. A. J. 2008. Zinc, iron and phytic acid levels of some popular foods consumed by rural children in Sri Lanka. Journal of Food Composition and Analysis, 21: 481-488.
Food consumption ; Cereals ; Rice ; Zinc ; Iron ; Phytic acid ; Bioavailability ; Drinking water / Sri Lanka
(Location: IWMI HQ Call no: IWMI 613.2 G744 KAR Record No: H041401)
https://vlibrary.iwmi.org/pdf/H041401.pdf
Zinc (Zn) and iron (Fe) deficiencies may prevail in populations dependent on cereal-based diets containing few animal products. The contribution of Zn and Fe from foods of preschool children of a hill country village in Sri Lanka, is discussed as it is known that the presence of phytic acid (PA) in the diet limits bioavailability of micronutrients. The Zn, Fe and PA contents of cereal-based (rice or wheat flour) composite meals (n ¼ 12), wheat flour-based products (n ¼ 5), pulses used as staples, snacks or accompaniments (n ¼ 6) and other miscellaneous accompaniments (n ¼ 4) were determined. Additionally, 20 rice and 3 paddy varieties consumed were also analysed. Although the Zn and Fe levels were reasonable in the composite meals, the PA to Zn molar ratios (5–43) were relatively high, in a majority of meals. Composite meals containing wheat flour (refined) had lower PA levels (o6 mg/ 100 g) in the absence of pulses and scraped coconut, than rice meals. All rice varieties were partially polished but the A to Zn molar ratios varied. The major contributors of PA appeared to be soy-textured vegetable protein, all types of jak fruit and scraped coconut kernel. Potable water was a poor source of Zn and Fe. These diets could potentially lead to marginal Zn and Fe deficiencies, and dietary diversification and counselling would be beneficial.

5 Jinadasa, B. K. K. K. 2013. A study of trace metal levels in selected fisheries harbours in South and West coast of Sri Lanka. Journal of the National Aquatic Resources Research and Development Agency of Sri Lanka, 42:1-14.
Heavy metals ; Fisheries ; Water pollution ; Harbours ; Coastal area ; Sea water ; Mercury ; Cadmium ; Lead ; Chromium ; Nickel ; Copper ; Zinc / Sri Lanka / Tangalle / Puranawella / Mirissa / Beruwala / Mutwal / Negombo
(Location: IWMI HQ Call no: P 8157 Record No: H047150)
https://vlibrary.iwmi.org/pdf/H047150.pdf
(1.07 MB)
Trace metals generally enter into the harbour environment through atmospheric deposition, erosion or due to anthropogenic activities such as release of industrial effluents, domestic and harbour generated sewage and oil spills. The present study was carried out to assess the levels of several trace metals, namely, Hg, Pb, Cd, Cr, Zn, Cu and Ni, in harbour basin water from six selected fisheries harbours along the Southern and Western coasts of Sri Lanka. A total of 54 samples were collected covering the areas around the harbour jetty, harbour entrance and fuel stations during the period of June to December, 2011. The level of total Hg was analyzed by cold vapour atomic absorption spectrometry (CV-AAS) and the other metals by graphite furnace atomic absorption spectrometry (GF-AAS). The trace metal concentrations in fisheries harbour basin water (n=54) varied widely. The mean concentrations ±SD (µg/L) found in the study were Hg <0.16, Pb 0.40±0.61, Cd 0.06±0.17, Cr 0.49±0.80, Zn 13.60±19.1O, Cu 4.68±8.99 and Ni 5.80± 7.98. These values are all well below the limits for estuary and harbour basin water guideline, set by European Union (EU) and the Food and Agriculture Organization (FAO).

6 Brindha, Karthikeyan; Pavelic, Paul; Sotoukee, Touleelor; Douangsavanh, Somphasith; Elango, L. 2017. Geochemical characteristics and groundwater quality in the Vientiane Plain, Laos. Exposure and Health, 9(2):89-104. [doi: https://doi.org/10.1007/s12403-016-0224-8]
Geology ; Chemical composition ; Toxicity ; Groundwater ; Water quality ; Water level ; Drinking water ; Domestic water ; Irrigation water ; Aquifers ; Plains ; Heavy metals ; Pollutants ; Iron ; Arsenic ; Copper ; Zinc ; Mercury ; Health hazards / Lao People's Democratic Republic / Vientiane Plain
(Location: IWMI HQ Call no: e-copy only Record No: H047651)
https://vlibrary.iwmi.org/pdf/H047651.pdf
Groundwater from the shallow aquifers of the Vientiane Plain, Laos is used for domestic needs including to some extent for drinking and for household gardening. The objective of this study is to assess the groundwater quality for drinking and irrigation activities and to determine the processes that lead to the presence of major ions in groundwater. Twenty groundwater samples were collected from a village on the Plain in December 2014, January 2015, and May 2015, and analysed for major ions and selected suite of minor ions and heavy metals. Groundwater is largely acidic, fresh and soft in nature. Geochemistry showed dominant Ca–Mg–HCO3 and mixed Ca–Na–HCO3 groundwater. Sodium impacts the suitability of water for irrigation to some extent. Hydrogeochemical processes identified and verified through factor analysis indicate weathering, carbonate dissolution, ion exchange, and anthropogenic sources including salinisation, due to irrigation and use of fertilizers as sources for the occurrence of major ions at such concentrations in this area. Only concentrations of lead and iron were above the permissible limits with arsenic, copper, zinc, mercury, and uranium found to be within safe limits. Background sample (groundwater) collected 5 km from the study area and the bottled water sample were all within suitable limits for drinking. This study is the first to provide a local-level assessment of geochemical processes in groundwater of this area indicating that the groundwater does not pose any threat to human health if used for drinking based on major ions, minor ions and a suite heavy metals except for iron and lead.

7 Haroon, B.; Ping, A.; Pervez, A.; Faridullah; Irshad, M. 2019. Characterization of heavy metal in soils as affected by long-term irrigation with industrial wastewater. Journal of Water Reuse and Desalination, 9(1):47-56. [doi: https://doi.org/10.2166/wrd.2018.008]
Wastewater irrigation ; Industrial wastewater ; Irrigated soils ; Heavy metals ; Contamination ; Lead ; Nickel ; Manganese ; Copper ; Cadmium ; Iron ; Zinc ; Soil properties ; Fractionation ; Farmers / Pakistan / Hattar
(Location: IWMI HQ Call no: e-copy only Record No: H049121)
https://iwaponline.com/jwrd/article-pdf/9/1/47/522943/jwrd0090047.pdf
https://vlibrary.iwmi.org/pdf/H049121.pdf
(0.21 MB) (216 KB)
Investigation of heavy metals (HM) fractions in soils irrigated with wastewater (WW) would ascertain their bioavailability and contamination level in soils. This study investigated HM fractions in soils after long-term WW irrigation. WW irrigation profoundly affected HM fractions in soil. The ranges of HM concentrations in soils irrigated with WW were apparently wide. All fractions were significantly higher in the fields irrigated with industrial WW than rain-fed fields. HM concentrations varied in the soils as Pb > Cu > Ni > Zn > Fe > Cd > Mn after WW irrigation. In rainfed fields, HM concentrations differed in soils as Fe > Zn > Mn > Pb > Cd > Cu > Ni. The HM fractions were dominant in the residual form followed by oxides bound and carbonate associated fractions in WW-irrigated soils. Lower contents of HM in the soil were obtained in the exchangeable fraction. WW irrigation resulted in the transformation of HM into different fractions as residual > oxide associated > carbonate associated > organically bound > exchangeable form. Repeated WW irrigation increased pH values of the soils. The higher EC of soil indicated an accumulation of salts in the soils due to WW irrigation. Mitigation of HM contamination in Hattar industrial effluent is required before irrigation.

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