Cadmium and lead contamination in japonica rice grains and its variation among the different locations in southeast China

2006 ◽  
Vol 359 (1-3) ◽  
pp. 156-166 ◽  
Author(s):  
Cheng Fangmin ◽  
Zhao Ningchun ◽  
Xu Haiming ◽  
Li Yi ◽  
Zhang Wenfang ◽  
...  
2018 ◽  
Vol 25 (18) ◽  
pp. 17611-17619 ◽  
Author(s):  
Xueqiong Lin ◽  
Lin Peng ◽  
Xijin Xu ◽  
Yanrong Chen ◽  
Yuling Zhang ◽  
...  

2017 ◽  
Vol 68 (6) ◽  
pp. 1163-1169 ◽  
Author(s):  
Cornelia Purcarea ◽  
Malgorzata Dzugan ◽  
Monika Wesolowska ◽  
Adriana Monica Chis ◽  
Grzegorz Zagula ◽  
...  

The aim of the study was to compare the heavy metal contamination and study the mineral content of Polish and Romanian honeys. We used Polish varietal honeys (n=18) produced in the year 2013-2014 in ecologically clean Podkarpackie region, and Romanian honeys (n=36) from Bihor district produced in 2013. The heavy metals concentration as well as mineral composition of honey was assayed by ICP-OES method with prior microwave mineralization. The cadmium and lead level in tested Polish honeys ranged from 0.007 to 0.021mg/kg and 0.02 to 0.098 mg/kg, respectively. Cadmium was not detected in Romanian honeys, and the lead contamination was lower than in Polish honey (0.018-0.05 mg/kg). Mercury was not detected in any tested honey samples. The aluminum content in Polish honeydew honeys was 34.6-times higher than in Romanian honeys. Honey samples from Poland were richest in potassium (2.5-fold for honeydew, lime and acacia, excluding heather), but they included less calcium. Generally, dark honeys include the highest mineral concentration and are more contaminated by heavy metals. However, all tested samples met the legal requirements for heavy metals residues. The geographical origin and soil composition strongly influenced honey chemical composition and the crucial factor for heavy metal transfer seems to be soil pH.


2020 ◽  
Vol 264 ◽  
pp. 110477 ◽  
Author(s):  
Zeeshan Ajmal ◽  
Muhammad Usman ◽  
Ioannis Anastopoulos ◽  
Abdul Qadeer ◽  
Runliang Zhu ◽  
...  

2020 ◽  
Vol 32 (1) ◽  
pp. 66-78
Author(s):  
Shuangyin Zhang ◽  
Teng Fei ◽  
Xiang You ◽  
Yinkang Wan ◽  
Yunjiang Wang ◽  
...  

Land ◽  
2021 ◽  
Vol 10 (6) ◽  
pp. 558
Author(s):  
Modian Xie ◽  
Hongyi Li ◽  
Youwei Zhu ◽  
Jie Xue ◽  
Qihao You ◽  
...  

Potentially toxic element (PTE) pollution in farmland soils and crops is a serious cause of concern in China. To analyze the bioaccumulation characteristics of chromium (Cr), zinc (Zn), copper (Cu), and nickel (Ni) in soil-rice systems, 911 pairs of top soil (0–0.2 m) and rice samples were collected from an industrial city in Southeast China. Multiple linear regression (MLR), support vector machines (SVM), random forest (RF), and Cubist were employed to construct models to predict the bioaccumulation coefficient (BAC) of PTEs in soil–rice systems and determine the potential dominators for PTE transfer from soil to rice grains. Cr, Cu, Zn, and Ni contents in soil of the survey region were higher than corresponding background contents in China. The mean Ni content of rice grains exceeded the national permissible limit, whereas the concentrations of Cr, Cu, and Zn were lower than their thresholds. The BAC of PTEs kept the sequence of Zn (0.219) > Cu (0.093) > Ni (0.032) > Cr (0.018). Of the four algorithms employed to estimate the bioaccumulation of Cr, Cu, Zn, and Ni in soil–rice systems, RF exhibited the best performance, with coefficient of determination (R2) ranging from 0.58 to 0.79 and root mean square error (RMSE) ranging from 0.03 to 0.04 mg kg−1. Total PTE concentration in soil, cation exchange capacity (CEC), and annual average precipitation were identified as top 3 dominators influencing PTE transfer from soil to rice grains. This study confirmed the feasibility and advantages of machine learning methods especially RF for estimating PTE accumulation in soil–rice systems, when compared with traditional statistical methods, such as MLR. Our study provides new tools for analyzing the transfer of PTEs from soil to rice, and can help decision-makers in developing more efficient policies for regulating PTE pollution in soil and crops, and reducing the corresponding health risks.


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