Enrichment of cadmium in rice (Oryza sativa L.) grown under different exogenous pollution sources

In order to unravel the cadmium (Cd) enrichment patterns in rice ( Oryza sativa L.) grown under different exogenous exposure pathways, the pot experiment was conducted in a greenhouse. Cd was added to the soil-rice system via mixing soil with Cd-containing solution, irrigating the pots with Cd-conta...

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Veröffentlicht in:Environmental science and pollution research international 2020-12, Vol.27 (35), p.44249-44256
Hauptverfasser: Zhou, Yi-Min, Long, Si-Si, Li, Bing-Yu, Huang, Ya-Yuan, Li, Yong-Jie, Yu, Jia-Yan, Du, Hui-Hui, Khan, Sardar, Lei, Ming
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container_issue 35
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container_title Environmental science and pollution research international
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creator Zhou, Yi-Min
Long, Si-Si
Li, Bing-Yu
Huang, Ya-Yuan
Li, Yong-Jie
Yu, Jia-Yan
Du, Hui-Hui
Khan, Sardar
Lei, Ming
description In order to unravel the cadmium (Cd) enrichment patterns in rice ( Oryza sativa L.) grown under different exogenous exposure pathways, the pot experiment was conducted in a greenhouse. Cd was added to the soil-rice system via mixing soil with Cd-containing solution, irrigating the pots with Cd-containing water and leaf-spraying with Cd solution to simulate soil pollution (SPS), irrigation water pollution (IPS), and atmospheric deposit pollution sources (APS), respectively. No significant ( p  > 0.05) differences in plant height and rice grain yield were observed among all treatments including three different Cd pollution sources and control. The contents of Cd in rice plants significantly ( p   stems > leaves > husk > brown rice, while it was leaves > roots > stems > husk > brown rice treated with APS. At the same level of treatment, the highest concentration of Cd was observed in rice organs (except for middle and high concentrations treatment roots) grown under APS, followed by IPS and SPS, suggesting that the Cd bioavailability from different pollution sources followed the order of APS > IPS > SPS. It is concluded that the atmospheric pollution contributed more enrichment of rice with Cd. Therefore, in field environment, air deposits should also be analyzed for toxic metals during assessment of food chain contamination and health risk.
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Cd was added to the soil-rice system via mixing soil with Cd-containing solution, irrigating the pots with Cd-containing water and leaf-spraying with Cd solution to simulate soil pollution (SPS), irrigation water pollution (IPS), and atmospheric deposit pollution sources (APS), respectively. No significant ( p  &gt; 0.05) differences in plant height and rice grain yield were observed among all treatments including three different Cd pollution sources and control. The contents of Cd in rice plants significantly ( p  &lt; 0.05) increased with increase in Cd concentrations in three pollution sources. The distribution pattern of Cd in the rice plant organs treated with SPS and IPS followed the order: roots &gt; stems &gt; leaves &gt; husk &gt; brown rice, while it was leaves &gt; roots &gt; stems &gt; husk &gt; brown rice treated with APS. At the same level of treatment, the highest concentration of Cd was observed in rice organs (except for middle and high concentrations treatment roots) grown under APS, followed by IPS and SPS, suggesting that the Cd bioavailability from different pollution sources followed the order of APS &gt; IPS &gt; SPS. It is concluded that the atmospheric pollution contributed more enrichment of rice with Cd. 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Cd was added to the soil-rice system via mixing soil with Cd-containing solution, irrigating the pots with Cd-containing water and leaf-spraying with Cd solution to simulate soil pollution (SPS), irrigation water pollution (IPS), and atmospheric deposit pollution sources (APS), respectively. No significant ( p  &gt; 0.05) differences in plant height and rice grain yield were observed among all treatments including three different Cd pollution sources and control. The contents of Cd in rice plants significantly ( p  &lt; 0.05) increased with increase in Cd concentrations in three pollution sources. The distribution pattern of Cd in the rice plant organs treated with SPS and IPS followed the order: roots &gt; stems &gt; leaves &gt; husk &gt; brown rice, while it was leaves &gt; roots &gt; stems &gt; husk &gt; brown rice treated with APS. At the same level of treatment, the highest concentration of Cd was observed in rice organs (except for middle and high concentrations treatment roots) grown under APS, followed by IPS and SPS, suggesting that the Cd bioavailability from different pollution sources followed the order of APS &gt; IPS &gt; SPS. It is concluded that the atmospheric pollution contributed more enrichment of rice with Cd. 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Cd was added to the soil-rice system via mixing soil with Cd-containing solution, irrigating the pots with Cd-containing water and leaf-spraying with Cd solution to simulate soil pollution (SPS), irrigation water pollution (IPS), and atmospheric deposit pollution sources (APS), respectively. No significant ( p  &gt; 0.05) differences in plant height and rice grain yield were observed among all treatments including three different Cd pollution sources and control. The contents of Cd in rice plants significantly ( p  &lt; 0.05) increased with increase in Cd concentrations in three pollution sources. The distribution pattern of Cd in the rice plant organs treated with SPS and IPS followed the order: roots &gt; stems &gt; leaves &gt; husk &gt; brown rice, while it was leaves &gt; roots &gt; stems &gt; husk &gt; brown rice treated with APS. At the same level of treatment, the highest concentration of Cd was observed in rice organs (except for middle and high concentrations treatment roots) grown under APS, followed by IPS and SPS, suggesting that the Cd bioavailability from different pollution sources followed the order of APS &gt; IPS &gt; SPS. It is concluded that the atmospheric pollution contributed more enrichment of rice with Cd. Therefore, in field environment, air deposits should also be analyzed for toxic metals during assessment of food chain contamination and health risk.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><pmid>32767006</pmid><doi>10.1007/s11356-020-10282-5</doi><tpages>8</tpages><orcidid>https://orcid.org/0000-0003-4575-6744</orcidid></addata></record>
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subjects Air pollution
Aquatic Pollution
Atmospheric Protection/Air Quality Control/Air Pollution
Bioavailability
Cadmium
Cereals
Coal mining
Crop yield
Earth and Environmental Science
Ecotoxicology
Enrichment
Environment
Environmental Chemistry
Environmental Health
Environmental science
Environmental Sciences
Environmental Sciences & Ecology
Fertilizers
Food chains
Food contamination
Food contamination & poisoning
Health risks
Heavy metals
Irrigation
Irrigation water
Leaves
Life Sciences & Biomedicine
Organs
Oryza sativa
Pollution
Pollution sources
Research Article
Rice
Roots
Science & Technology
Soil contamination
Soil pollution
Soil water
Spraying
Stems
Waste Water Technology
Water Management
Water pollution
Water Pollution Control
title Enrichment of cadmium in rice (Oryza sativa L.) grown under different exogenous pollution sources
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