Arsenic Uptake and Accumulation in Curly Endives ( Cichorium endivia L .) Irrigated with Contaminated Water

2006 ◽  
Vol 41 (4) ◽  
pp. 459-470 ◽  
Author(s):  
C. CALVO ◽  
S. BOLADO ◽  
J. ALVAREZ-BENEDÍ ◽  
M. ANDRADE
2016 ◽  
Vol 97 (3) ◽  
pp. 395-400 ◽  
Author(s):  
Bryan E. Hettick ◽  
Jaclyn E. Cañas-Carrell ◽  
Kirt Martin ◽  
Amanda D. French ◽  
David M. Klein

2012 ◽  
Vol 223 (7) ◽  
pp. 4209-4220 ◽  
Author(s):  
Huaming Guo ◽  
Zhennan Zhong ◽  
Mei Lei ◽  
Xiaolei Xue ◽  
Xiaoming Wan ◽  
...  

2018 ◽  
Vol 2 (2) ◽  
Author(s):  
Agwaramgbo Lovell E

The ecosystem (land, water, air) and the organisms that inhabit it are exposed to various heavy metals at varying levels. However, concerns arise when the potential exist for the levels of these toxicants to exceed the regulatory thresholds. Arsenic is a well-known soil and water contaminant with reported toxic and detrimental risks to the ecosystem, human health, aquatic and terrestrial animals, and plants. Intake of arsenic contaminated water and food diet form the major source of arsenic exposure to humans. Rice paddy rice (Oryza sativa), a major staple food for many countries of the world has been reported to have the capacity to accumulate a large amount of arsenic from contaminated soil or from contaminated irrigation water. The sources of these arsenic could be as a result of old agricultural practices that utilized arsenate insecticide. Chinese fern has been identified as a potential agent for the phytoremediation of arsenic contaminated soil. Additionally, biochars and charcoal have been used for the remediation of Pb, Cu, Zn, Cd from contaminated water. The project reported here investigated the use of charred rice hulls for the remediation of arsenic contaminated rice farm in the North-Western part of Louisiana. Results demonstrate that rice is an accumulator of arsenic if the soil is contaminated with arsenic. Irrigation water was not a source of arsenic contamination for this project for all the irrigation water samples showed no trace of arsenic. Furthermore, the rice hull and rice straw from previous year used in the preparation of the charred biomaterial appear to be contaminated and thus, increased the soil arsenic but decreased arsenic uptake into the rice grain


2013 ◽  
Vol 295-298 ◽  
pp. 1139-1143 ◽  
Author(s):  
Jun Ying Zhao ◽  
Hua Ming Guo

The effects of arsenic uptake by Pteris vittata L. and Polystichum craspedosorum were examined. Pteris vittata L. were exposed hydroponically to 4Italic textItalic text.8 mg/L As(V) for 16 d and 4.05 mg/L As(V) for 24 h. Arsenic concentration in solution respectively decreased to 1.61 mg/L and 3.86mg/L. TF after 24 h was 0.81(1). Polystichum craspedosorum were exposed hydroponically to 3.26 mg/L As(V) for 20 days. As concentration decreased to 2.83mg/L after 16d and then increased slowly in the later four days. As contents in roots and fronds of Polystichum craspedosorum were 147 mg/kg and 90mg/kg. The results indicated that Polystichum craspedosorum was not good candidate for removal As(V) from water compared with Pteris vittata L..


2019 ◽  
Vol 01 (03) ◽  
pp. 01-08
Author(s):  
Maimoona Kanwal ◽  
Mubashar Hussain ◽  
Waqar Younus

The aim of the current review is to deliberate on arsenic chemistry, its existence in aquatic ecosystem and its effects on the biological systems of fishes which are regarded as potential indicators for any change in water quality. Water is a major storehouse of arsenic which is present in the form of arsenate and arsenite. Anthropogenic activities including unlimited application of arsenic pesticides, industrial activities and mining operations have increased the universal incidence of soluble arsenic above tolerable levels of 0.010 mg/L. Variations in fish behaviour, growth rate, haematological and biological parameters and organ systems have been observed in arsenic contaminated water. Data regarding these parameters indicate that the fish shows aggressive behaviour and its weight increases due to a high arsenic uptake. The production rate of biochemical compounds like carbohydrates, proteins and lipids is reduced due to arsenic bonding with their precursors. Among organ systems, skin is a highly affected organ, while muscles are the least affected due to high arsenic concentration. Low concentration of arsenic results in bioaccumulation, conspicuously in liver and kidney, upon incessant exposure to freshwater fish. This bioaccumulation turns into biomagnification and becomes the cause of lethal diseases in human beings, such as hyperglycaemia, diminution of enzymatic activities and immune system abnormalities. Keeping in view all of these above mentioned facts, it is imperative to take action against excessive arsenic usage and to develop its eco-friendly management ways.


Author(s):  
Seroor Atalah Khaleefa Alia ◽  
Dr. Mohammed Ibrahimb ◽  
Hussein Ali Hussein

Adsorption is most commonly applied process for the removal of pollutants such as dyes and heavy metals ions from wastewater. The present work talks about preparing graphenic material attached sand grains called graphene sand composite (GSC) by using ordinary sugar as a carbon source. Physical morphology and chemical composition of GSC was examined by using (FTIR, SEM, EDAX and XRD). Efficiency of GSC in the adsorption of organic dyes from water was investigated using reactive green dye with different parameters such as (ph, temperature, contact time and dose). Adsorption isotherm was also studied and the results showed that the maximum adsorption capacity of dye is 28.98 mg/g. This fast, low-cost process can be used to manufacture commercial filters to treat contaminated water using appropriate engineering designs.


2016 ◽  
Vol 15 (4) ◽  
pp. 899-903 ◽  
Author(s):  
Donald E. Macphee ◽  
Efetobor Scott-Emuakpor ◽  
Graeme I. Paton ◽  
Malcolm J. Todd

2020 ◽  
Author(s):  
Andrew John PENDERY

There are some striking similarities between Legionnaire’s disease and COVID-19. Thesymptoms, age group and sex at risk are identical. The geographical distribution of both diseases is similar in Europe overall, and within the USA, France and Italy. The environmental distributions are also similar. However Legionnaire’s disease is caused by Legionella bacteria while COVID-19 is caused by the Corona virus. Whereas COVID-19 is contagious, Legionnaire’s disease is environmental. Legionella bacteria are commonly found in drinking water systems and near air conditioning cooling towers. Legionnaire’sdisease is caught by inhaling contaminated water droplets. The Legionella bacteria does not spread person to person and only causes disease if it enters the lungs.Could the Corona virus be making it easier for Legionella bacteria to enter the lungs?


2019 ◽  
Author(s):  
Chem Int

A study of removal of heavy metal ions from heavy metal contaminated water using agro-waste was carried out with Musa paradisiaca peels as test adsorbent. The study was carried by adding known quantities of lead (II) ions and cadmium (II) ions each and respectively into specific volume of water and adding specific dose of the test adsorbent into the heavy metal ion solution, and the mixture was agitated for a specific period of time and then the concentration of the metal ion remaining in the solution was determined with Perkin Elmer Atomic absorption spectrophotometer model 2380. The effect of contact time, initial adsorbate concentration, adsorbent dose, pH and temperature were considered. From the effect of contact time results equilibrium concentration was established at 60minutes. The percentage removal of these metal ions studied, were all above 90%. Adsorption and percentage removal of Pb2+ and Cd2+ from their aqueous solutions were affected by change in initial metal ion concentration, adsorbent dose pH and temperature. Adsorption isotherm studies confirmed the adsorption of the metal ions on the test adsorbent with good mathematical fits into Langmuir and Freundlich adsorption isotherms. Regression correlation (R2) values of the isotherm plots are all positive (>0.9), which suggests too, that the adsorption fitted into the isotherms considered.


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