scholarly journals Effects of particle sizes of rock phosphate on immobilizing heavy metals in lead zinc mine soils

Author(s):  
Z. Zhao ◽  
G. Jiang ◽  
R. Mao
1991 ◽  
Vol 23 (4) ◽  
pp. 381-391 ◽  
Author(s):  
E. S. Hansen

AbstractEighty-seven lichen taxa were collected at four localities near the leadzinc mine at Maarmorilik. These are listed alphabetically and grouped according to their ecological preferences. Lichens, which in Greenland are restricted to calcareous rocks and alkaline soil substrata, are well represented in the Maarmorilik area. In contrast, ferrugineous lichens appear to be comparatively rare. The lichens around the mining town are assumed to have accumulated significant concentrations of airborne lead and zinc. However, no damage to the lichens caused by heavy metals was observed.


2013 ◽  
Vol 634-638 ◽  
pp. 3498-3501
Author(s):  
Zheng Yao Li ◽  
Xiao Fan Guo ◽  
Jun Liu ◽  
Li Li Wang ◽  
Heng Qian Li

The characteristics of process mineralogy of the some lead-zinc mine were studied with scanning electron microscope, optics microscopes,and x-ray diffraction. The species of lead minerals and zinc minerals and the chemical composition of the minerals were analyzed. The liberations at different grinding finenesses and the particle sizes of the minerals had been also determined. The phase shape of lead and zinc in the ore was also analyzed. The behaviors of various minerals and mineralogical factors affecting the flotation had been explained clearly. The investigation results were favorable to reasonable selection of flotation parameters and would provide theoretical guidance to lead-zinc separation.


Chemosphere ◽  
2017 ◽  
Vol 168 ◽  
pp. 1115-1125 ◽  
Author(s):  
Maoyou Ye ◽  
Pingfang Yan ◽  
Shuiyu Sun ◽  
Dajian Han ◽  
Xiao Xiao ◽  
...  

2021 ◽  
Vol 2021 ◽  
pp. 1-11
Author(s):  
Rongguo Sun ◽  
Yue Gao ◽  
Jing Xu ◽  
Yang Yang ◽  
Yutao Zhang

The spatial patterns, ecological risks, and sources of heavy metals (HMs), including Pb, Zn, Mn, Cu, Cd, Hg, and As in river sediments, were identified around a lead-zinc mine of Danzhai, Guizhou, China. The concentrations of selected HMs and their coefficient variations indicated that the river sediments around this typical lead-zinc mine were obviously contaminated with HMs. Anthropogenic activities had further enhanced the accumulation of HMs. The higher contents of the most common selected HMs were mainly distributed in the area close to the lead-zinc mine. Based on the combined evaluations of the single factor pollution index, geo-accumulation index, and potential ecological risk index, it indicated that the ecological risks of Hg, Cd, Zn, and Pb were high or extremely high, and of Mn, Cu, and As were slight or none in the sediments around this lead-zinc mine. It was found that lead-zinc mining and smelting activities, coal mining activities, and agricultural activities (livestock and poultry breeding) are the primary sources of selected HMs, based on the results of correlation analysis together with principal component analysis (PCA) and positive matrix factorization (PMF) model. The pollution of HMs in the river sediments around a lead-zinc mine was predominantly caused by lead-zinc mining and smelting activities. Therefore, for environmental persistence, lead-zinc mining and smelting activities should be given careful consideration and under close surveillance.


1976 ◽  
Vol 80 ◽  
pp. 53-61
Author(s):  
G Asmund ◽  
H.J Bollingberg ◽  
J Bondam

The results of studies of the heavy metal background level in the natural environment ofthe Qaumarujuk and Agfardlikavså fjords, adjacent to the lead-zinc mine Sorte Engel (= Black Angel) near Mârmorilik (71°07'N, 51°16'W), have been briefly communicated by Bondam & Asmund (1974), Asmund (1975), Bohn (1975) and BoIlingberg (1975). FuHdetails of the analyticaI results of these surveys have been reported in Danish elsewhere. (Vandkvalitetsinstituttet 1972; Grønlands Fiskeriundersøgelser et al., 1974; GGU et al., 1975). Since then, renewed sampling has been carried out, both in February and August 1974, and in April and September 1975, in order to follw closely the environmental dissemination of some heavy metals in the fjord region, due to disposal of tailings from the flotation plant adjacent to Agfardlikavsåfjord (fig. 18). This short communication deals with the content of certain heavy metals of bottom sediments, biological tissues and samples of sea water in the fjord regime after full production started in October 1973.


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