Long-term effects of liquid swine manure land surface application in an apple orchard field on soil bacterial community and heavy metal contents in apple (Malus pumila Mill.)

Author(s):  
Hongchao Jiao ◽  
Qin Yin ◽  
Cunhu Fan ◽  
Ling Wang ◽  
Jingpeng Zhao ◽  
...  
Chemosphere ◽  
2006 ◽  
Vol 65 (8) ◽  
pp. 1321-1329 ◽  
Author(s):  
César Plaza ◽  
Diana Hernández ◽  
José M. Fernández ◽  
Alfredo Polo

2020 ◽  
Vol 118 (2) ◽  
pp. 193-205
Author(s):  
E. Martínez ◽  
A. Maresma ◽  
A. Biau ◽  
P. Berenguer ◽  
S. Cela ◽  
...  

2019 ◽  
Vol 102 (4) ◽  
pp. 468-476 ◽  
Author(s):  
Abasiama S. Umoren ◽  
Chioma M. Igwenagu ◽  
Peter I. Ezeaku ◽  
Gloria I. Ezenne ◽  
Sunday E. Obalum ◽  
...  

Author(s):  
A Taraqqi-A-Kamal ◽  
Christopher J. Atkinson ◽  
Aimal Khan ◽  
Kaikai Zhang ◽  
Peng Sun ◽  
...  

The focus of this study is on the soil physicochemical, biological, and microbiological processes altered by biochar application to heavy metal (HM) contaminated soils. The aim is to highlight agronomical and environmental issues by which the restorative capacity of biochar might be developed. Literature shows biochar can induce soil remediation, however, it is unclear how soil processes are linked mechanistically to biochar production and if these processes can be manipulated to enhance soil remediation. The literature often fails to contribute to an improved understanding of the mechanisms by which biochar alters soil function. It is clear that factors such as biochar feedstock, pyrolysis conditions, application rate, and soil type are determinants in biochar soil functionality. These factors are developed to enhance our insight into production routes and the benefits of biochar in HM soil remediation. Despite a large number of studies of biochar in soils, there is little understanding of long-term effects, this is particularly true with respect to the use and need for reapplication in soil remediation.  


2010 ◽  
pp. n/a-n/a ◽  
Author(s):  
Bai-Ye Sun ◽  
Shi-Hong Kan ◽  
Yan-Zong Zhang ◽  
Jun Wu ◽  
Shi-Huai Deng ◽  
...  

2020 ◽  
Vol 194 ◽  
pp. 110433 ◽  
Author(s):  
Qing Xie ◽  
Lishan Qian ◽  
Shanyi Liu ◽  
Yongmin Wang ◽  
Yongjiang Zhang ◽  
...  

2020 ◽  
Vol 20 (4) ◽  
pp. 2093-2106 ◽  
Author(s):  
Muhammad Qaswar ◽  
Liu Yiren ◽  
Huang Jing ◽  
Liu Kaillou ◽  
Muhammad Mudasir ◽  
...  

2015 ◽  
Vol 2015 ◽  
pp. 1-9 ◽  
Author(s):  
Yintao Lu ◽  
Hong Yao ◽  
Dan Shan ◽  
Yichen Jiang ◽  
Shichao Zhang ◽  
...  

Soil and plant samples were collected from Tongliao, China, during the maize growth cycle between May and October 2010. Heavy metals, such as Cr, Pb, Ni, and Zn, were analyzed. The concentrations of Cr, Pb, Ni, and Zn in the wastewater-irrigated area were higher than those in the topsoil from the groundwater-irrigated area. The concentrations of metals in the maize increased as follows: Pb < Ni < Zn < Cr. In addition, Cr, Pb, and Ni mainly accumulated in the maize roots, and Zn mainly accumulated in the maize fruit. The results of translocation factors (TF) and bioconcentration factors (BCF) of maize for heavy metals revealed that maize is an excluder plant and a potential accumulator plant and can serve as an ideal slope remediation plant. In addition, the increasing heavy metal contents in soils that have been polluted by wastewater irrigation must result in the accumulation of Cr, Pb, Ni, and Zn in maize. Thus, the pollution level can be decreased by harvesting and disposing of and recovering the plant material.


2003 ◽  
Vol 60 (4) ◽  
pp. 793-806 ◽  
Author(s):  
Maria Lucia Azevedo Silveira ◽  
Luís Reynaldo Ferracciú Alleoni ◽  
Luiz Roberto Guimarães Guilherme

The application of sewage sludge or biosolids on soils has been widespread in agricultural areas. However, depending on their characteristics, they may cause increase in heavy metal concentration of treated soils. In general, domestic biosolids have lower heavy metal contents than industrial ones. Origin and treatment method of biosolids may markedly influence their characteristics. The legislation that controls the levels of heavy metal contents in biosolids and the maximum concentrations in soils is still controversial. In the long-term, heavy metal behavior after the and of biosolid application is still unknown. In soils, heavy metals may be adsorbed via specific or non-specific adsorption reactions. Iron oxides and organic matter are the most important soil constituents retaining heavy metals. The pH, CEC and the presence of competing ions also affect heavy metal adsorption and speciation in soils. In solution, heavy metals can be present either as free-ions or complexed with organic and inorganic ligands. Generally, free-ions are more relevant in environmental pollution studies since they are readily bioavailable. Some computer models can estimate heavy metal activity in solution and their ionic speciation. Thermodynamic data (thermodynamic stability constant), total metal and ligand concentrations are used by the GEOCHEM-PC program. This program allows studying heavy metal behavior in solution and the effect of changes in the conditions, such as pH and ionic strength and the application of organic and inorganic ligands caused by soil fertilization.


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