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摘要
超表面具有强烈的局域等离子体共振特性,其共振频率对周围介质环境十分敏感,可应用于无标记环境检测领域。本文设计了一种优化了品质因数和有效模体积之比(Q/Veff)的蝴蝶结型太赫兹超表面结构。该结构单元由中间镜像对称的金属蝴蝶结及两侧的连续金属边带组成。针对Q/Veff这一重要指标,分别从连续金属边带的宽度和蝴蝶结间隙长度这两个参数对结构进行了仿真优化。当连续金属边带宽度为25 μm,间隙长度为2 μm时,在0.7 THz处有效模体积为3.6 μm3,相应的Q/Veff为2.2 μm-3。在实验中,将不同浓度的铅离子溶液滴于超表面传感器表面,利用太赫兹时域光谱系统测量透射谱。实验结果表明,在0.1 ng/mL~20 ng/mL范围内铅离子溶液浓度与超表面共振频率的漂移值具有线性关系,铅离子溶液的检测最低限为0.1 ng/mL。该太赫兹超表面传感器具有体积小、样品制备简单、检测速度快和实时现场测量等优点,将在环境保护和食品安全领域有广泛应用。
Abstract
The strong localized plasmon resonance of metasurfaces makes the resonance frequency extremely sensitive to the dielectric environment, which can be applied to label-free environment detection. In this paper, a bow-tie terahertz metasurface with an optimized ratio of the quality factor to effective mode volume(Q/Veff) is designed. The unit cell of the proposed structure is composed of a mirror-symmetrical metallic bow tie in the middle and continuous metallic strips on both sides. The width of each metal strip and the length of the bow-tie gap are optimized for the parameter Q/Veff. When the metal strip width is 25 μm and the gap length is 2 μm, the effective mode volume is 3.6 μm3 and Q/Veff is 2.2 μm-3 at 0.7 THz. In the experiment, different concentration of the lead ion solution was dropped on the proposed metasurface. The transmission spectrum was measured by a terahertz time-domain spectroscopy system. The results showed that there is a linear relationship between resonance frequency shift and lead ion solution concentration from 0.1 ng/mL to 20 ng/mL. The detection limit is 0.1 ng/mL. The terahertz metasurface sensor has the advantages of the miniaturized size, easy sample preparation, fast measurement capability and real-time detection, which will be widely used in environmental protection and food safety.
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Key words:
- terahertz /
- metasurface /
- lead ion /
- effective mode volume /
- high sensitivity
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Overview
Overview: Lead ion pollution in water is becoming a serious worldwide environmental problem. Effective and efficient detection of lead ion pollution requires sensitive and selective sensors with rapid on-site detection ability for performing the desired detection. Traditional spectroscopy, electrochemical, and inductively coupled plasma mass spectrometry (ICP-MS) methods for lead ion detection have some problems, such as complex experimental technology, long measuring period, expensive equipment and so on, which are only suitable for laboratory analysis. In this direction, one appropriate alternative approach is exploring plasmonic metasensor technology for low-level lead ion detection, which offers sophisticated opportunities in lead ion detection and ecological environment protection. Terahertz wave has unique characteristics of low photon energy, excellent security and the nonionizing effect. Metasurfaces are promising tools that have facilitated precise screening and recognition of diverse molecules and biomolecules through substantial field confinement at subwavelength geometries. The terahertz metasurface sensor stems from its capability to squeeze electromagnetic fields, simultaneously in frequency and space. However, the radiative and nonradiative losses limit the quality factor (Q) of the metasurface. The observation and study of the effectively low mode volume (Veff) were firstly reported in the middle of the twenty century, which was primarily established based on quantum electrodynamics. Metasurface designs with Q/Veff cavities become extremely important for enhancing the light-matter interaction.
In this work, we demonstrate a modified bow-tie terahertz metasurface platform containing a micron-sized cavity with an optimized Q/Veff value. The structural unit is composed of a mirror symmetrical metallic bow tie in the middle and two continuous metallic strips on both sides. Continuous metallic strip enhances the overall capacitance of metasurface unit cell, which allows the capacitive split gap cavity to store larger electromagnetic energy. When the continuous metal strip width is 25 μm and the gap size is 2 μm, the Q/Veff of the proposed bow-tie terahertz metasurface reaches a maximum of 2.2 μm-3 at 0.7 THz. For 4 µm thick analyte layer, and the sensitivity is about 80 GHz/RIU (refractive index unit), which is higher than traditional bow tie metasurface. The proposed metasurface is manufactured using a surface micromachining process and characterized by a THz time-domain spectroscopy (THz-TDS) system. For the lead ion solution with different concentrations, the experimental results indicate that the resonance frequency of the terahertz metasurface sensor decreases with the increase of the concentration of lead ion solution on the surface. When the concentration of lead ion solution ranges from 0.1 ng/mL to 20 ng/mL, the resonance frequency shift shows good linearity to the concentration of lead ion solution and the limit of detection (LOD) reaches 0.1 ng/mL. It is expected to provide a new lead ion solution detection scheme for the field of environmental protection and food safety.
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图 3 MBS结构中(a) 带宽W取不同值时的透射谱; (b) 带宽W的取值对品质因数Q及有效模体积Veff的影响; (c) 带宽W的取值对Q/Veff的影响
Figure 3. (a) Transmission spectra with different values of the bandwidth W in MBS design; (b) The effect of the bandwidth W on the quality factor Q and effective mode volume Veff in MBS design; (c) The effect of the bandwidth W on Q/Veff in MBS design
图 7 (a) 样品厚度取不同值时MBS共振峰的变化; (b) 样品厚度取不同值时TBS共振峰的变化;(c) 折射率取不同值时MBS共振峰的变化;(d) 折射率取不同值时TBS共振峰的变化;(e) 共振频率变化与样品厚度的关系; (f) 共振频率变化与样品折射率的关系
Figure 7. (a, b) Transmission spectra with respect to the thicknesses of analyte in (a) MBS design and (b) TBS design; (c, d) Transmission spectra with respect to refractive index in (c) MBS design and (d) TBS design; (e) Resonant peak shift with respect to the thicknesses of analyte in MBS and TBS design; (f) Resonant peak shift with respect to refractive index in MBS and TBS design
图 8 (a) MBS对不同浓度铅离子溶液的透射谱; (b) 图8(a)的局部放大图; (c) TBS对不同浓度铅离子溶液的透射谱; (d) 图8(c)的局部放大图
Figure 8. (a) Transmission spectra of MBS for different concentrations of the lead ion solution; (b) Magnified view of Fig. 8(a); c) Transmission spectra of TBS for different concentrations of the lead ion solution; (d) Magnified view of Fig. 8(c)
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