Affiliations 

  • 1 School of Environmental Science and Engineering, Chang'an University, Xi'an 710054, PR China; Key Laboratory of Soil Environment and Pollution Remediation, Nanjing Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, PR China
  • 2 School of Environmental Science and Engineering, Chang'an University, Xi'an 710054, PR China
  • 3 Key Laboratory of Soil Environment and Pollution Remediation, Nanjing Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, PR China; Institute of Botany, Jiangsu Province and Chinese Academy of Sciences, Nanjing Botanical Garden, Mem. Sun Yat-Sen, Nanjing 210014, PR China. Electronic address: jcui@cnbg.net
  • 4 Institute of Botany, Jiangsu Province and Chinese Academy of Sciences, Nanjing Botanical Garden, Mem. Sun Yat-Sen, Nanjing 210014, PR China
  • 5 Key Laboratory of Soil Environment and Pollution Remediation, Nanjing Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, PR China
  • 6 Department of Agriculture and Environmental Science, Lincoln University of Missouri, Jefferson City, MO 65201, USA
  • 7 Key Laboratory of Soil Environment and Pollution Remediation, Nanjing Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, PR China. Electronic address: zhoujing@issas.ac.cn
  • 8 Faculty of Engineering, University of Nottingham Malaysia, Semenyih 43500, Malaysia
  • 9 Third Institute of Oceanography, State Oceanic Administration, Xiamen 361005, PR China
Sci Total Environ, 2019 Jun 20;670:1060-1067.
PMID: 31018421 DOI: 10.1016/j.scitotenv.2019.03.245

Abstract

With the population growth, urbanization and industrialization, China has become a hotspot of atmospheric deposition nitrogen (ADN), which is a threat to ecosystem and food safety. However, the impacts of increased ADN on rice growth and grain metal content are little studied. Based on previous long-term ADN studies, greenhouse experiment was conducted with four simulated ADN rates of 0, 30, 60 and 90 kg N ha-1 yr-1 (CK, N1, N2 and N3 as δ15N, respectively) to assess rice growth and metal uptake in a red soil ecosystem of southeast China during 2016-2017. Results showed that simulated ADN could promote rice growth and increase yields by 15.68-24.41% (except N2) and accumulations of cadmium (Cd) or copper (Cu) in organs. However, there was no linear relationship between ADN rate and rice growth or Cd or Cu uptake. The 15N-ADN was mainly accumulated in roots (21.31-67.86%) and grains (25.26-49.35%), while Cd and Cu were primarily accumulated in roots (78.86-93.44% and 90.00-96.24%, respectively). 15N-ADN and Cd accumulations in roots were significantly different between the two growing seasons (p 

* Title and MeSH Headings from MEDLINE®/PubMed®, a database of the U.S. National Library of Medicine.