Mobility and Fate of Cerium Dioxide, Zinc Oxide, and Copper Nanoparticles in Agricultural Soil at Sequential Wetting-Drying Cycles

被引:8
作者
Ermolin, Mikhail [1 ]
Fedyunina, Natalia [2 ]
Katasonova, Olesya [1 ]
机构
[1] Russian Acad Sci, Vernadsky Inst Geochem & Analyt Chem, 19 Kosygin St, Moscow 119991, Russia
[2] Natl Univ Sci & Technol MISIS, 4 Leninsky Prospect, Moscow 119049, Russia
基金
俄罗斯科学基金会;
关键词
nanoparticles; cerium dioxide; zinc oxide; copper; soil; mobility; Wetting-Drying cycles; SILVER NANOPARTICLES; ZNO NANOPARTICLES; ENGINEERED NANOPARTICLES; MICROBIAL COMMUNITY; CEO2; NANOPARTICLES; SEED-GERMINATION; CITRIC-ACID; TRANSPORT; GROWTH; RETENTION;
D O I
10.3390/ma12081270
中图分类号
O64 [物理化学(理论化学)、化学物理学];
学科分类号
070304 ; 081704 ;
摘要
Study on the behavior and fate of nanofertilizers in soil plays a key role in the assessment of the efficiency of their use for intended purposes. The behavior of nanoparticles (NPs) in soil depends on environmental scenarios, such as Wetting-Drying cycles (WDCs). In the present work, the mobility and fate of CeO2, ZnO, and Cu NPs in agricultural soil at sequential WDCs have been studied. It has been shown that the mobility of CeO2 and ZnO NPs decreases after each WDC. After four WDCs the relative amount of CeO2 and ZnO NPs leached from soil decreases from 0.11 to 0.07% and from 0.21 to 0.07%, correspondingly. The decrease in the mobility of NPs is caused by their immobilization by water-stable soil aggregates, which are formed at sequential WDCs. Cu NPs are dissolved by soil solution, so their mobility (in ionic forms) increases after each subsequent WDCs. The relative content of Cu2+ sourced from Cu NPs increases up to 0.88% after four WDCs. It has been found that mineral NPs of soil can play an important role in the transport of insoluble engineered NPs. As for soluble NPs, the kinetics of their dissolution governs their mobility in ionic forms.
引用
收藏
页数:13
相关论文
共 53 条
[1]  
Adhikari T, 2016, J PLANT NUTR, V39, P102, DOI [10.1080/01904167.2014.992536, 10.1080/01904167.2015.1044012]
[2]   Effects of uncoated and citric acid coated cerium oxide nanoparticles, bulk cerium oxide, cerium acetate, and citric acid on tomato plants [J].
Barrios, Ana Cecilia ;
Rico, Cyren M. ;
Trujillo-Reyes, Jesica ;
Medina-Velo, Illya A. ;
Peralta-Videa, Jose R. ;
Gardea-Torresdey, Jorge L. .
SCIENCE OF THE TOTAL ENVIRONMENT, 2016, 563 :956-964
[3]  
Baumann T, 2010, NANOPARTICLES IN THE WATER CYCLE, P23, DOI 10.1007/978-3-642-10318-6_3
[4]   BIOLOGICAL AND CHEMICAL INTERACTIONS OF PESTICIDES WITH SOIL ORGANIC-MATTER [J].
BOLLAG, JM ;
MYERS, CJ ;
MINARD, RD .
SCIENCE OF THE TOTAL ENVIRONMENT, 1992, 123 :205-217
[5]   Fungicidal activity of Cu nanoparticles against Fusarium causing crop diseases [J].
Bramhanwade, Kavita ;
Shende, Sudhir ;
Bonde, Shital ;
Gade, Aniket ;
Rai, Mahendra .
ENVIRONMENTAL CHEMISTRY LETTERS, 2016, 14 (02) :229-235
[6]   Effect of zinc oxide nanoparticles on growth and antioxidant system of chickpea seedlings [J].
Burman, Uday ;
Saini, Mahesh ;
Praveen-Kumar .
TOXICOLOGICAL AND ENVIRONMENTAL CHEMISTRY, 2013, 95 (04) :605-612
[7]   Nanomaterials and nanoparticles: Sources and toxicity [J].
Buzea, Cristina ;
Pacheco, Ivan I. ;
Robbie, Kevin .
BIOINTERPHASES, 2007, 2 (04) :MR17-MR71
[8]   Nanofertilizers and nanopesticides for agriculture [J].
Chhipa, Hemraj .
ENVIRONMENTAL CHEMISTRY LETTERS, 2017, 15 (01) :15-22
[9]   Aggregation, Dissolution, and Transformation of Copper Nanoparticles in Natural Waters [J].
Conway, Jon R. ;
Adeleye, Adeyemi S. ;
Gardea-Torresdey, Jorge ;
Keller, Arturo A. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2015, 49 (05) :2749-2756
[10]   Fate and Bioavailability of Engineered Nanoparticles in Soils: A Review [J].
Cornelis, Geert ;
Hund-Rinke, Kerstin ;
Kuhlbusch, Thomas ;
Van den Brink, Nico ;
Nickel, Carmen .
CRITICAL REVIEWS IN ENVIRONMENTAL SCIENCE AND TECHNOLOGY, 2014, 44 (24) :2720-2764