Source Journal of CSCD
Source Journal for Chinese Scientific and Technical Papers
Core Journal of RCCSE
Included in JST China
Volume 41 Issue 3
Mar.  2023
Turn off MathJax
Article Contents
LUO Qing, WU Zhongping, WANG Congcong, LI Yujie. REMEDIATION CAPABILITY OF FOUR HERBS ON CHLORINATED ORGANOPHOSPHATE FLAME RETARDANTS CONTAMINATED SOIL[J]. ENVIRONMENTAL ENGINEERING , 2023, 41(3): 155-162. doi: 10.13205/j.hjgc.202303021
Citation: LUO Qing, WU Zhongping, WANG Congcong, LI Yujie. REMEDIATION CAPABILITY OF FOUR HERBS ON CHLORINATED ORGANOPHOSPHATE FLAME RETARDANTS CONTAMINATED SOIL[J]. ENVIRONMENTAL ENGINEERING , 2023, 41(3): 155-162. doi: 10.13205/j.hjgc.202303021

REMEDIATION CAPABILITY OF FOUR HERBS ON CHLORINATED ORGANOPHOSPHATE FLAME RETARDANTS CONTAMINATED SOIL

doi: 10.13205/j.hjgc.202303021
  • Received Date: 2022-04-21
    Available Online: 2023-05-26
  • Publish Date: 2023-03-01
  • A pot experiment was conducted to study the tolerance and enrichment characteristics of four herbs (fescue, ryegrass, vetch, and alfalfa), which are commonly used as the remediation plants for organic contaminated soil under the stress of tris-(1-chloro-2-propyl) phosphate (TCIPP), to screen potential plants with high remediation capability for phytoremediation to TCIPP contaminated soil. The results showed that TCIPP could inhibit the growth and development of four herbs, but only the biomass of ryegrass decreased significantly, and the biomass of the other three herbs did not decrease significantly. The concentration distribution of TCIPP in the tissues of four herbs was leaf>root>stem, indicating that TCIPP was easy to migrate from plant roots to aboveground. Among the four herbs, the concentration and accumulation of TCIPP in the leaf of vetch were the highest, 15.0 mg/kg and 34.9 mg/pot, respectively. Vetch and alfalfa had a relatively high efficiency in absorbing, accumulating and transporting TCIPP from the soil. Their shoot concentration factors were 1.39 and 1.50, and the translocation factors were 2.61 and 3.24, respectively. The four herbs had good remediation capability to TCIPP contaminated soil, and their removal rates of TCIPP in soil were 64.7% to 91.6%. Among them, the removal rate of TCIPP in the rhizosphere soil of ryegrass was the highest. However, the phytoextraction rates were less than 2%, indicating that the removal of TCIPP in soil was mainly caused by the degradation of rhizosphere microorganisms. Based on the comprehensive comparison of the tolerance, enrichment characteristics, and removal rates of four herbs for TCIPP in soil, we suggested that ryegrass can be given priority as a remediation plant for TCIPP-contaminated soil.
  • loading
  • [1]
    STAPLETON H, SHARMA S, GETZINGER G, et al. Novel and high volume use flame retardants in US couches reflective of the 2005 pentaBDE phase out[J]. Environmental Science & Technology, 2012, 46(24):13432-13439.
    [2]
    LI T Y, BAO L J, WU C C, et al. Organophosphate flame retardants emitted from thermal treatment and open burning of e-waste[J]. Journal of Hazardous Materials, 2019, 367(4):390-396.
    [3]
    van DER VEEN I, de BOER J. Phosphorus flame retardants:properties, production, environmental occurrence, toxicity and analysis[J]. Chemosphere, 2012, 88(10):1119-1153.
    [4]
    BJORKLUND J, ISETUN S, NILSSON U. Selective determination of organophosphate flame retardants and plasticizers in indoor air by gas chromatography, positive-ion chemical ionization and collision-induces dissociation mass spectrometry[J]. Rapid Communications in Mass Spectrometry, 2004, 18(24):3079-3083.
    [5]
    DISHAW L, POWERS C, RYDE I, et al. Is the PentaBDE replacement, tris (1,3-dichloropropyl) phosphate (TDCPP), a developmental neurotoxicant? Studies in PC12 cells[J]. Toxicology and Applied Pharmacology, 2011, 256(3):281-289.
    [6]
    NI Y, KUMAGAI K, YANAGISAWA Y. Measuring emissions of organophosphate flame retardants using a passive flux sampler[J]. Atmospheric Environment, 2007, 41(15):3235-3240.
    [7]
    FAN X, KUBWABO C, RASMUSSEN P, et al. Simultaneous determination of thirteen organophosphate esters in settled indoor house dust and a comparison between two sampling techniques[J]. Science of the Total Environment, 2014, 491/492:80-86.
    [8]
    LUO Q, SHAN Y, ADEEL M, et al. Levels, distribution, and sources of organophosphate flame retardants and plasticizers in urban soils of Shenyang, China[J]. Environmental Science and Pollution Research, 2018, 25(31):31752-33176.
    [9]
    LUO Q, GU L Y, WU Z P, et al. Distribution, source apportionment and ecological risks of organophosphate esters in surface sediments from the Liao river, northeast China[J]. Chemosphere, 2020, 250:126297.
    [10]
    WANG Y, YAO Y M, LI W H, et al. A nationwide survey of 19 organophosphate esters in soils from China:spatial distribution and hazard assessment[J]. Science of the Total Environment, 2019, 671:528-535.
    [11]
    LEE S, CHO H J, CHOI W, et al. Organophosphate flame retardants (OPFRs) in water and sediment:occurrence, distribution, and hotspots of contamination of Lake Shihwa, Korea[J]. Marine Pollution Bulletin, 2018, 130:105-112.
    [12]
    吴星悦, 孙敦宇, 季秋忆, 等. 氯代有机磷酸酯阻燃剂的去除技术研究进展[J]. 环境化学, 2022, 41(3):1022-1034.
    [13]
    SU G Y, LETCHER R, YU H X. Organophosphate flame retardants and plasticizers in aqueous solution:pH-dependent hydrolysis, kinetics, and pathways[J]. Environmental Science & Technology, 2016, 50(15):8103-8111.
    [14]
    FANG Y D, KIM E, STRATHMANN T. Mineral and base-catalyzed hydrolysis of organophosphate flame retardants:potential major fate-controlling sink in soil and aquatic environments[J]. Environmental Science & Technology, 2018, 52(4):1997-2006.
    [15]
    NANCHARAIAH Y, REDDY G, MOHAN T, et al. Biodegradation of tributyl phosphate, an organosphate triester, by aerobic granular biofilms[J]. Journal of Hazardous Materials, 2015, 283:705-711.
    [16]
    XIONG J K, LI G X, AN T C. The microbial degradation of 2, 4, 6-tribromophenol (TBP) in water/sediments interface:investigating bioaugmentation using Bacillus sp. GZT[J]. Science of the Total Environment, 2017, 575:573-580.
    [17]
    WEI K, YIN H, PENG H, et al. Bioremediation of triphenyl phosphate in river water microcosms:proteome alteration of Brevibacillus brevis and cytotoxicity assessments[J]. Science of the Total Environment, 2019, 649:563-570.
    [18]
    HOU R, LUO X S, LIU C C, et al. Enhanced degradation of triphenyl phosphate (TPHP) in bioelectrochemical systems:kinetics, pathway and degradation mechanisms[J]. Environmental Pollution, 2019, 254:113040.
    [19]
    TAKAHASHI S, KAWASHIMA K, KAWASAKI M, et al. Enrichment and characterization of chlorinated organophosphate ester degrading mixed bacterial cultures[J]. Journal of Bioscience and Bioengineering, 2008, 106(1):27-32.
    [20]
    TAKAHASHI S, KATANUMA H, ABE K, et al. Identification of alkaline phosphatase genes for utilizing a flame retardant, tris (2-chloroethyl) phosphate, in Sphingobium sp strain TCM1[J]. Applied Microbiology and Biotechnology, 2017, 101(5):2153-2162.
    [21]
    HE H, JI Q Y, GAO Z Q, et al. Degradation of tri (2-chloroisopropyl) phosphate by the UV/H2O2 system:kinetics, mechanisms and toxicity evaluation[J]. Chemosphere, 2019, 236:124388.
    [22]
    YE J S, LIU J, LI C S, et al. Heterogeneous photocatalysis of tris (2-chloroethyl) phosphate by UV/TiO2:degradation products and impacts on bacterial proteome[J]. Water Research, 2017, 124:29-38.
    [23]
    HU H, ZHANG H X, CHEN Y, et al. Enhanced photocatalysis degradation of organophosphorus flame retardant using MIL-101(Fe)/persulfate:effect of irradiation wavelength and real water matrixes[J]. Chemical Engineering Journal, 2019, 368:273-284.
    [24]
    OU H S, LIU J, YE J S, et al. Degradation of tris (2-chloroethyl) phosphate by ultraviolet-persulfate:kinetics, pathway and intermediate impact on proteome of Escherichia coli[J]. Chemical Engineering Journal, 2017, 308:386-395.
    [25]
    XU X X, CHEN J, QU R J, et al. Oxidation of Tris (2-chloroethyl) phosphate in aqueous solution by UV-activated peroxymonosulfate:kinetics, water matrix effects, degradation products and reaction pathways[J]. Chemosphere, 2017, 185:833-843.
    [26]
    ANTONOPOULOU M, GIANNAKAS A, BAIRAMIS F, et al. Degradation of organophosphorus flame retardant tris (1-chloro-2-propyl) phosphate (TCPP) by visible light N, S-codoped TiO2 photocatalysts[J]. Chemical Engineering Journal, 2017, 318:231-239.
    [27]
    沈源源, 滕应, 骆永明, 等. 几种豆科、禾本科植物对多环芳烃复合污染土壤的修复[J]. 土壤, 2011, 43(2):253-257.
    [28]
    涂晨, 滕应, 骆永明, 等.多氯联苯污染土壤的豆科-禾本科植物田间修复效应[J]. 环境科学, 2010, 31(12):3062-3066.
    [29]
    何洋, 董志成, 刘林德, 等. 沉积物中多环芳烃的植物修复研究进展[J]. 环境工程, 2018, 36(2):168-172.
    [30]
    MA T T, TENG Y, LUO Y M, et al. Legume-grass intercropping phytoremediation of phthalic acid esters in soil near an electronic waste recycling site:a field study[J]. International Journal of Phytoremediation, 2013, 15(2), 154-167.
    [31]
    BURKEN J, SCHNOOR J. Predictive relationships for uptake of organic contaminants by hybrid poplar trees[J]. Environmental Science & Technology, 1998, 32(21):3379-3385.
    [32]
    LIU Q, WANG X L, YANG R Y, et al. Uptake kinetics, accumulation, and long-distance transport of organophosphate esters in plants:impacts of chemical and plant properties[J]. Environmental Science & Technology, 2019, 53(9):4940-4947.
    [33]
    LUO Q, LI Y J, WU Z P, et al. Phytotoxicity of tris-(1-chloro-2-propyl) phosphate in soil and its uptake and accumulation by pakchoi (Brassica chinensis L. cv. Suzhou)[J]. Chemosphere, 2021, 277:130347.
    [34]
    QIN P, LU S Y, LIU X H, et al. Removal of tri-(2-chloroisopropyl) phosphate (TCPP) by three types of constructed wetlands[J]. Science of the Total Environment, 2020, 749:141668.
    [35]
    HU B B, JIANG L F, ZHENG Q, et al. Uptake and translocation of organophosphate esters by plants:impacts of chemical structure, plant cultivar and copper[J]. Environment International, 2021, 155:106591.
    [36]
    LIU Q, LIU M L, WU S H, et al. Metabolomics reveals antioxidant stress responses of wheat (Triticum aestivum L.) exposed to chlorinated organophosphate esters[J]. Journal of Agricultural and Food Chemistry, 2020, 68(24):6520-6529.
    [37]
    WANG L, HUANG X L, LASERNA A, et al. Metabolomics reveals that tris(1,3-dichloro-2-propyl)phosphate (TDCPP) causes disruption of membrane lipids in microalga Scenedesmus obliquus[J]. Science of the Total Environment, 2020, 708:134498.
    [38]
    LIU S L, ALI S, YANG R J, et al. A newly discovered Cd-hyperaccumulator Lantana camara L[J]. Journal of Hazardous Materials, 2019, 371:233-242.
    [39]
    TRAPP S, EGGEN T. Simulation of the plant uptake of organophosphates and other emerging pollutants for greenhouse experiments and field conditions[J]. Environmental Science and Pollution Research, 2013, 20(6):4018-4029.
    [40]
    陈迪, 李伯群, 杨永平, 等. 4种草本植物对镉的富集特征[J]. 环境科学, 2021, 42(2):960-966.
    [41]
    LIU H W, WANG H Y, ZHANG Y, et al. Comparison of heavy metal accumulation and cadmium phytoextraction rates among tenleadingtobacco (Nicotiana tabacum L.) cultivarsin China[J]. International Journal of Phytoremediation, 2019, 21(7):699-706.
    [42]
    WANG H, ZHAO Y M, ADEEL M, et al. Influence of celery on the remediation of PAHs contaminated farm soil[J]. Soil & Sediment Contamination, 2019, 28(2):200-212.
    [43]
    SCHNOOR J, LICHT L, MCCUTCHEON S, et al. Phytoremediation of organic and nutrient contaminants[J]. Environmental Science & Technology, 1995, 29(7):318-323.
    [44]
    CORGIE S, JONER E, LEYVAL C. Rhizospheric degradation of phenanthrene is a function of proximity to roots[J]. Plant and Soil, 2003, 257(1):143-150.
    [45]
    许超, 夏北成. 运用多隔层根箱研究黑麦草根际微域中芘的降解[J]. 土壤学报, 2009, 46(3):426-433.
    [46]
    杨静. PAHs污染土壤植物修复的根际效应及机制[D]. 杭州:浙江大学, 2012.
  • 加载中

Catalog

    通讯作者: 陈斌, bchen63@163.com
    • 1. 

      沈阳化工大学材料科学与工程学院 沈阳 110142

    1. 本站搜索
    2. 百度学术搜索
    3. 万方数据库搜索
    4. CNKI搜索

    Article Metrics

    Article views (133) PDF downloads(3) Cited by()
    Proportional views
    Related

    /

    DownLoad:  Full-Size Img  PowerPoint
    Return
    Return