Trace element biogeochemistry in the soil-water-plant system of a temperate agricultural soil amended with different biochars

2014 ◽  
Vol 22 (6) ◽  
pp. 4513-4526 ◽  
Author(s):  
Stefanie Kloss ◽  
Franz Zehetner ◽  
Jannis Buecker ◽  
Eva Oburger ◽  
Walter W. Wenzel ◽  
...  
2013 ◽  
Vol 374 (1-2) ◽  
pp. 993-1004 ◽  
Author(s):  
Jinghua Fan ◽  
Zhenli He ◽  
Lena Q. Ma ◽  
Yuangen Yang ◽  
Peter J. Stoffella

2014 ◽  
Vol 497-498 ◽  
pp. 319-331 ◽  
Author(s):  
Rosa Cidu ◽  
Riccardo Biddau ◽  
Elisabetta Dore ◽  
Andrea Vacca ◽  
Luigi Marini

2008 ◽  
Vol 22 (4) ◽  
pp. 265-273 ◽  
Author(s):  
Ligang Xu ◽  
Jingsong Yang ◽  
Qi Zhang ◽  
Hailin Niu

2021 ◽  
Author(s):  
Abdurrahman Lermi ◽  
Emmanuel Daanoba Sunkari

Abstract Globally, potentially toxic elements (PTEs) are regarded as an important group of pollutants for the wider environment because of their intrinsic toxicity and probable accumulation in the soil-water-plant system. In this regard, this study assessed the pollution levels and probable human health risks of PTEs in the soil-water-plant system in the Bolkar mining district of the Niğde Province in south-central Turkey. Pollution assessment using contamination factor, enrichment factor, index of geoaccumulation, and soil pollution index reveals moderate to extremely high pollution of PTEs in the soil, exposing the soils to extreme toxicity levels. The areas that fall under the toxic to extremely toxic categories are in proximity to the ore slags and agricultural lands towards the central and southern domains of the study area. The water hazard index (WHI) values indicate that 100% of the samples collected in both winter and fall seasons are of extreme toxicity (WHI > 15). Arsenic is the dominant contaminant among the PTEs in the soil and water samples. The bioconcentration factor values of the PTEs in most of the fruit plants are > 1, indicating very high levels of element transfer from the soil and water to the plants. The probabilistic human health risk assessment involved exposure to arsenic in groundwater (a major pathway to humans) since it is the only carcinogenic element in this study. The estimated daily intake of arsenic-contaminated water exceeds the safe limit of 5 × 10− 8 mg/kg/day. About 33.3% and 55.6% of the groundwater samples have higher hazard quotient and carcinogenic risk values of arsenic in the winter and fall seasons, respectively. This implies that the people are more exposed to the carcinogenic effects of drinking arsenic-contaminated water.


1990 ◽  
pp. 28-41 ◽  
Author(s):  
Jack Keller ◽  
Ron D. Bliesner
Keyword(s):  

2020 ◽  
pp. 207-210
Author(s):  
M.K. Trivedi ◽  
K.S. Hariprasad ◽  
A. Gairola ◽  
D. Kashyap

2020 ◽  
Vol 12 (9) ◽  
pp. 3575
Author(s):  
Thor Kolath ◽  
Lotte Reuss ◽  
Sara Egemose ◽  
Kasper Reitzel

New lakes are established or reestablished to provide ecosystem services such as limiting floods and nutrient discharge and to improve biodiversity. New lakes are often established on fertilized land formerly used for agricultural purposes, thereby posing a risk of issues such as phosphorus (P) release when inundated. Release of P from agricultural soil affects both the developing ecosystem of the new lake and may increase downstream eutrophication. To decrease P release following inundation, three simple and cost-effective soil pretreatments were tested through laboratory soil–water fluxes from the test sites in the new Lake Roennebaek and the fluxes of P, nitrogen (N), and iron (Fe) were compared. The pretreatments compared were sand-capping, depth-plowing, and addition of the commercial iron product CFH-12® (Kemira). Untreated agricultural soil incubated under laboratory conditions released 687 ± 88 mg P·m−2 over 207 days and 85% was released within 60 days from inundation followed by low soil–water P exchange during the remaining incubation period. However, P was still released from the untreated soil 180 days after inundation within the lake. The cumulated P flux of the three pretreatment methods was in comparison negative, between −12 ± 3 and −17 ± 4 mg P·m−2 over 207 days incubation and showed negative P fluxes from cores collected within the lake 180 days after inundation. This study showed that the release of P when establishing new lakes on former agricultural land could be minimized using these simple and cost-effective methods, which may improve the ecological status of future lakes and enable the establishment of new lakes without threatening vulnerable downstream ecosystems.


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