• Spectroscopy and Spectral Analysis
  • Vol. 40, Issue 10, 3038 (2020)
Xiao-hong LIU1、1、*, Hua DENG1、1, Lin CHANG1、1, Wei ZHANG1、1, and Shan JIANG1、1
Author Affiliations
  • 1[in Chinese]
  • 11. Chongqing Youth Vacational & Technical College, Chongqing 400712, China
  • show less
    DOI: 10.3964/j.issn.1000-0593(2020)10-3038-10 Cite this Article
    Xiao-hong LIU, Hua DENG, Lin CHANG, Wei ZHANG, Shan JIANG. Recent Progress of SERS for Environmental Estrogen Detection[J]. Spectroscopy and Spectral Analysis, 2020, 40(10): 3038 Copy Citation Text show less
    AAO template method for fabrication of SERS substrates(a): Cu-base-supported arrays of HS-β-CD decorated Ag-NRs [51];(b): Core@Shell nanoporous Au@Ag nanorod arrays[52]
    Fig. 1. AAO template method for fabrication of SERS substrates
    (a): Cu-base-supported arrays of HS-β-CD decorated Ag-NRs [51];(b): Core@Shell nanoporous Au@Ag nanorod arrays[52]
    Molecular imprinting technology was applied to SERS detection(a): AuNPs substrate covered by imprint-removed MIP layer[58];(b): In situ reduced AgNPs embedded molecularly imprinted for BPA detection [59]
    Fig. 2. Molecular imprinting technology was applied to SERS detection
    (a): AuNPs substrate covered by imprint-removed MIP layer[58];(b): In situ reduced AgNPs embedded molecularly imprinted for BPA detection [59]
    Immunoassays technology and SERS combined detected environmental estrogen(a): SERS immune magnetic beads technology for E2 detection[61];(b): The highly sensitive detection of BPA with SERS-LFA[62]
    Fig. 3. Immunoassays technology and SERS combined detected environmental estrogen
    (a): SERS immune magnetic beads technology for E2 detection[61];(b): The highly sensitive detection of BPA with SERS-LFA[62]
    Label-free SERS detection of PCB-77 based on DNA aptamer modified SERS substrates(a): SiO2 @Au core-shell nanoparticles[68];(b): AgNR array[69]
    Fig. 4. Label-free SERS detection of PCB-77 based on DNA aptamer modified SERS substrates
    (a): SiO2 @Au core-shell nanoparticles[68];(b): AgNR array[69]
    (a) Double strand DNA functionalized Au@Ag NPs for detection of E2 by competitive reaction with Cy3 aptamer[71]; (b) Determination of E2 by the Au@Ag NPs substrate and HCR technology[72]
    Fig. 5. (a) Double strand DNA functionalized Au@Ag NPs for detection of E2 by competitive reaction with Cy3 aptamer[71]; (b) Determination of E2 by the Au@Ag NPs substrate and HCR technology[72]
    基底类型基底环境雌激素LOD特点参考文献
    非修饰基底溅射Ag NPs的纳米金阵列PCB205×10-6 mol·L-1增强效果好, 但缺乏特异性[37]
    溅射Au NPs的SiO2纳米棒4-CB1×10-6 mol·L-1[41]
    锥形ZnO纳米棒上分别组装Ag NPs和银球BPA, PCB1×10-11 mol·L-1[42]
    跨尺度金银协同基底BPA0.5 ppm[43]
    银纳米薄片组装的微半球PCB773×10-6 mol·L-1[44]
    MoS2/ZnO微花复合材料BPA1×10-9 mol·L-1亲和力好, 应用广泛[45]
    硅烷自组装石墨片基底BPA1×10-6 mol·L-1[46]
    修 饰 基 底分 子 修 饰β-CD修饰的金纳米颗粒PCBs特异性识别检测分子, 可区分同系物, 但易受干扰[50]
    HS-β-CD修饰的铜基AgNRs阵列PCB29, PCB77,
    PCB101
    2×10-6~
    2×10-4 mol·L-1
    [51]
    HS-β-CD修饰的核@壳纳米孔金@银纳米棒阵列PCB3,
    PCB77
    5.35×10-7 mol·L-1[52]
    HS-β-CD修饰ITO衬底上的微半球阵列PCB1,
    PCB77
    3×10-7 mol·L-1[53]
    覆盖分子印迹聚合物层的金纳米颗粒(MIP-Au NPs)BPA0.12 mg·L-1特异性识别检测分子, 但制备复杂[58]
    嵌入MIPs基体内的银纳米颗粒BPA5×10-8 mol·L-1[59]
    Au-MBA/Cu2+/MBA-AuNPs的“三明治”基底Cu2+配位识别检测分子[54]
    修饰DT的AgFON基底PCB47, PCB7750 pmol·L-1[55]
    修饰Cys的AgNPs基底BPA[56]
    抗原抗体修饰磁珠表面抗E2抗体与E2-OVAE20.65 pg·mL-1特异性识别检测分子, 间接定量检测, 但成本偏高[61]
    金纳米星为基底的SERS-LFABPA0.073 ppb成本低、 现场快速检测, 灵敏度略低[62]
    核酸适配体修饰SiO2@Au核壳纳米颗粒PCB771×10-6 mol·L-1特异性识别检测分子, 间接定量检测[68]
    银纳米棒有序阵列PCB773.3×10-8 mol·L-1[69]
    金银核壳纳米颗粒二聚体, 4-MBA为信号分子E2, E1, EE20.01~50 nmol·L-1[70]
    金银核壳纳米颗粒, Cy3为信号分子E22.75 fmol·L-1[71]
    微流
    控芯片
    银纳米冠阵列结构PCB771.0×10-8 mol·L-1真实环境检测[73]
    Table 1. SERS for detection of environmental estrogen
    Xiao-hong LIU, Hua DENG, Lin CHANG, Wei ZHANG, Shan JIANG. Recent Progress of SERS for Environmental Estrogen Detection[J]. Spectroscopy and Spectral Analysis, 2020, 40(10): 3038
    Download Citation