MXene改性材料的制备及其吸附除Sr<sup>2+</sup>性能

张鹏丽; 武莉娅; 杨宗政; 吴志国; 曹井国

doi:10.13801/j.cnki.fhclxb.20221222.001

MXene改性材料的制备及其吸附除Sr²⁺性能

doi: 10.13801/j.cnki.fhclxb.20221222.001

天津科技大学　化工与材料学院，天津 300457

基金项目: 天津市卤水化工与资源生态化利用重点实验室开放基金资助项目(BCERE201902)；国家科技重大项目子项目(2017 ZX07107-001)；天津市教委科研计划项目(自然科学)(2019 KJ225)

详细信息

通讯作者:
曹井国，博士，副教授，硕士生导师，研究方向为水污染防治技术　E-mail：cjg@tust.edu.cn

中图分类号: O647.33；TB333
计量
- 文章访问数: 618
- HTML全文浏览量: 266
- PDF下载量: 17
- 被引次数: 0
出版历程
- 收稿日期: 2022-10-21
- 修回日期: 2022-11-29
- 录用日期: 2022-12-10
- 网络出版日期: 2022-12-26
- 刊出日期: 2023-10-15

Preparation of modified MXene material and its adsorption performance for Sr²⁺

College of Chemical Engineering and Materials Science, Tianjin University of Science and Technology, Tianjin 300457, China

Funds: The Foundation of Tianjin Key Laboratory of Brine Chemical Engineering and Resource Eco-utilization (BCERE201902); Sub Project of National Science and Technology Major Projects (2017 ZX07107-001); Scientific Research Program of Tianjin Municipal Education Commission (Natural Science) (2019 KJ225)

摘要

摘要: 为了评估Ti₃CNT_x/TMAOH材料对模拟放射性废水中Sr²⁺的吸附性能，选用四甲基氢氧化铵(TMAOH)作插层剂，对其进行改性制备处理，优化产物Ti₃CNT_x/TMAOH的合成条件，并采用SEM-EDS、XRD、BET和FTIR等对改性前后的样品进行表征分析。序批式实验中考察了吸附剂Ti₃CNT_x/TMAOH的投加量、时间、pH和竞争离子等因素对除Sr²⁺效果的影响。结果表明：在投加量为1.0 g∙L⁻¹、pH为6、时间为10 min时，对Sr²⁺的去除率可达99.28%。竞争离子的抑制顺序为Ca²⁺$ \text{ > > } $Mg²⁺$ \text{ > } $K⁺$ \text{ > } $Na⁺$ \text{ > } $Cs⁺。经历4次循环再生后，对Sr²⁺的去除率为69.56%。整个吸附过程符合准二级动力学模型，吸附等温线符合Redlich-Peterson (R-P)模型。在以自来水和湖水为背景配制的模拟含Sr²⁺废水中，可分别去除93.80%和68.49%的Sr²⁺。结合各种表征结果分析，表明Ti₃CNT_x/TMAOH对Sr²⁺优异的吸附机制可归因于离子交换、表面螯合、静电吸附和层间截留作用。
- MXene /
- 四甲基氢氧化铵 /
- 改性材料 /
- 吸附 /
- Sr²⁺
Abstract: Ti₃CNT_x/TMAOH was prepared when tetramethylammonium hydroxide (TMAOH) was selected as the intercalating agent. Adsorption performance of Ti₃CNT_x/TMAOH on Sr²⁺ in simulated radioactive wastewater was evaluated. The synthesized Ti₃CNT_x/TMAOH was characterized by SEM-EDS, XRD, BET and FTIR. In the batch experiment, the effects of the dosage of adsorbent Ti₃CNT_x/TMAOH, time, pH and competitive ions on Sr²⁺ removal were investigated. The results show that the removal rate of Sr²⁺ is 99.28% when the dosage is 1.0 g·L⁻¹, pH is 6, and the time is 10 min. The inhibition order of competitive ions is Ca²⁺$ \text{ > > } $Mg²⁺$ \text{ > } $K⁺$ \text{ > } $Na⁺$ \text{ > } $Cs⁺. After four adsorption-desorption cycles, the Sr²⁺ removal rate is 69.56%. The adsorption is consistent with the pseudo-second-order kinetic. The adsorption isotherm data conforms to the Redlich-Peterson (R-P) model. 93.80% and 68.49% Sr²⁺ can be removed in tap water and lake water, respectively. Sr²⁺ is adsorbed by Ti₃CNT_x/TMAOH via ion exchange, surface chelation, electrostatic adsorption and interlayer interception.
- MXene /
- tetramethylammonium hydroxide /
- modified materials /
- adsorption /
- Sr²⁺

HTML全文

图 1 Ti₃CNT_x插层改性前表面 (a) 和断面 (c) 及改性后表面 (b) 和断面 (d) 的SEM图像

Figure 1. SEM images of surface (a) and cross section (c) before Ti₃CNT_x modification, and surface (b) and cross section (d) after modification

下载: 全尺寸图片幻灯片

图 2 Ti₃CNT_x (a) 和Ti₃CNT_x/四甲基氢氧化铵(TMAOH) (b) 的N₂吸脱附及孔径图

Figure 2. N₂ adsorption-desorption and pore size of Ti₃CNT_x (a) and Ti₃CNT_x/tetramethylammonium hydroxide (TMAOH) (b)

下载: 全尺寸图片幻灯片

图 3 Ti₃CNT_x (a) 和Ti₃CNT_x/TMAOH (b) 的EDS能谱

Figure 3. EDS spectra of Ti₃CNT_x (a) and Ti₃CNT_x/TMAOH (b)

下载: 全尺寸图片幻灯片

图 4 Ti₃CNT_x和Ti₃CNT_x/TMAOH的红外光谱

Figure 4. Infrared spectra of Ti₃CNT_x and Ti₃CNT_x/TMAOH

下载: 全尺寸图片幻灯片

图 5 Ti₃CNT_x和Ti₃CNT_x/TMAOH的XRD图谱

Figure 5. XRD patterns of Ti₃CNT_x and Ti₃CNT_x/TMAOH

d—Interplanar spacing

下载: 全尺寸图片幻灯片

图 6 TMAOH用量对吸附剂Ti₃CNT_x/TMAOH去除Sr²⁺的影响(插图为产物 Ti₃CNT_x/TMAOH照片)

Figure 6. Effect of TMAOH dosage on Sr²⁺ removal by adsorbent Ti₃CNT_x/TMAOH (Inset: Photo of Ti₃CNT_x/TMAOH)

下载: 全尺寸图片幻灯片

图 7 Ti₃CNT_x和Ti₃CNT_x/TMAOH对Sr²⁺的去除效果

Figure 7. Removal effect of Ti₃CNT_x and Ti₃CNT_x/TMAOH for Sr²⁺

下载: 全尺寸图片幻灯片

图 8 pH值对Ti₃CNT_x/TMAOH吸附Sr²⁺的效果 (a) 和Zeta电位 (b) 的影响

Figure 8. Effect of pH on Sr²⁺ adsorption effect (a) and Zeta potential (b) of Ti₃CNT_x/TMAOH

K_d—Distribution coefficient; IEP—Isoelectric point

下载: 全尺寸图片幻灯片

图 9 共存离子浓度对Ti₃CNT_x/TMAOH吸附Sr²⁺去除率的影响

Figure 9. Effect of coexisting ion concentration on Sr²⁺ removal by Ti₃CNT_x/TMAOH

下载: 全尺寸图片幻灯片

图 10 时间t对Ti₃CNT_x/TMAOH去除Sr²⁺的影响：(a) 吸附容量；(b) 去除率；(c) 准一级动力学模型；(d) 准二级动力学模型

Figure 10. Effect of contact time t on Sr²⁺ removal by Ti₃CNT_x/TMAOH: (a) Adsorption capacity; (b) Removal rate; (c) Pseudo-first-order kinetic model; (d) Pseudo-second-order kinetic model

q_t—Adsorption capacity at time t; q_e—Adsorption capacity at equilibrium time

下载: 全尺寸图片幻灯片

图 11 Ti₃CNT_x/TMAOH吸附Sr²⁺的吸附等温线：(a) Langmuir；(b) Freundlich；(c) Redlich-Peterson (R-P) (C_e为平衡状态下Sr²⁺的质量浓度)

Figure 11. Adsorption isotherms for Sr²⁺ on Ti₃CNT_x/TMAOH: (a) Langmuir; (b) Freundlich; (c) Redlich-Peterson (R-P) (C_e is the mass concentration of Sr²⁺ in equilibrium)

下载: 全尺寸图片幻灯片

图 12 Ti₃CNT_x/TMAOH吸附去除Sr²⁺的lnK_C与T⁻¹的线性拟合

Figure 12. Linear fit of lnK_C vs T⁻¹ for adsorption Sr²⁺ on Ti₃CNT_x/TMAOH

K_C—Chemical equilibrium constant; T⁻¹—Reciprocal of temperature

下载: 全尺寸图片幻灯片

图 13 Ti₃CNT_x/TMAOH吸附Sr²⁺的再生实验

Figure 13. Regeneration experiment of Ti₃CNT_x/TMAOH for adsorption Sr²⁺

下载: 全尺寸图片幻灯片

图 14 Ti₃CNT_x/TMAOH吸附去除Sr²⁺前后的XPS和FTIR

Figure 14. XPS and FTIR spectra before and after adsorption of Ti₃CNT_x/TMAOH for Sr²⁺

下载: 全尺寸图片幻灯片

图 15 Ti₃CNT_x/TMAOH吸附Sr²⁺的机制示意图

Figure 15. Mechanism diagram of Sr²⁺ adsorption by Ti₃CNT_x/TMAOH

下载: 全尺寸图片幻灯片

图 16 不同水环境下Ti₃CNT_x/TMAOH对Sr²⁺的去除率

Figure 16. Sr²⁺ removal rate of Ti₃CNT_x/TMAOH in various water environments

DIW—De-ionized water; TW—Tap water; LW—Lake water

下载: 全尺寸图片幻灯片

表 1 Ti₃CNT_x和Ti₃CNT_x/TMAOH的比表面积、孔容和孔径数据

Table 1. Surface area, pore volume, and pore diameter of Ti₃CNT_x and Ti₃CNT_x/TMAOH

Material	Surface area/ (m²·g⁻¹)	Pore volume/ (cm³·g⁻¹)	Pore diameter/ nm
Ti₃CNT_x	1.215	0.0044	38.01
Ti₃CNT_x/TMAOH	3.154	0.0029	16.13

下载: 导出CSV

表 2 Ti₃CNT_x/TMAOH吸附Sr²⁺的动力学模型参数

Table 2. Parameters of adsorption kinetics model of Sr²⁺ adsorption on Ti₃CNT_x/TMAOH

Kinetic model		5.5 mg∙L⁻¹	10 mg∙L⁻¹	30 mg∙L⁻¹	50 mg∙L⁻¹
Pseudo-first-order	q_e/(mg∙g⁻¹)	25.02	22.80	10.49	8.061
	k₁/(10⁻⁴ min⁻¹)	0.01869	5.540	34.50	127.10
	R²	0.1065	0.6222	0.6940	0.9302
Pseudo-second-order	q_e/(mg∙g⁻¹)	4.988	8.829	24.16	29.83
	k₂/(g∙mg⁻¹∙min⁻¹)	0.1573	0.08457	0.01053	0.00587
	R²	1.00	0.9986	0.9999	0.9998
Notes: k₁ and k₂—Reaction rate constants of pseudo-first-order and pseudo-second-order equations, respectively; R²—Correlation coefficient.

下载: 导出CSV

表 3 Ti₃CNT_x/TMAOH吸附Sr²⁺的吸附等温线拟合参数

Table 3. Fitting parameters of adsorption isotherm for Sr²⁺ on Ti₃CNT_x/TMAOH

T/℃	Langmuir			Freundlich			R-P
T/℃	q_max/(mg∙g⁻¹)	K_L/(L∙mg⁻¹)	R²	K_F/(mg∙g⁻¹)	n	R²	A/(L∙g⁻¹)	B	g	R²
20	25.04	0.033	0.996	2.90	3	0.970	10.7	13	0.89	0.999
30	37.47	0.036	0.974	3.37	2	0.886	11.9	16	0.96	0.991
40	41.91	0.038	0.990	4.98	3	0.917	12.5	18	0.99	0.999
Notes: T—Reaction temperature; q_max—Maximum adsorption capacity of Langmuir; K_L—Langmuir adsorption constant; K_F—Freundlich adsorption constant; n—Constant related to the adsorption strength; A and B—Constants related to the adsorption capacity; g—Empirical constant between 0 and 1.

下载: 导出CSV

表 4 不同吸附剂对Sr²⁺的吸附去除效果对比

Table 4. Comparison of adsorption and removal effects of different adsorbents for Sr²⁺

Adsorbents	q_max/(mg∙g⁻¹)	C₀/(mg∙L⁻¹)	t/min	pH	Ref.
Mn_xO_y-Sb_mO_n	30.20	4.4	~30	3.0-9.0	[25]
ZrO₂-MnO₂	30.86	100	~100	4.0-8.0	[26]
GO	23.83	7.4	—	6.5-11.0	[27]
M/GO	9.81	4.0	360	1.7-11.8	[28]
Commercial AC	7.58	50	—	8.0-11.0	[29]
Ti₃CNT_x/TMAOH	41.91	5.5	~120	5-11	This study
Notes: t—Adsorption equilibrium time; GO—Graphene; M—Ge, Sn; AC—Activated carbon.

下载: 导出CSV

表 5 Ti₃CNT_x/TMAOH吸附Sr²⁺的热力学参数

Table 5. Thermodynamic parameter for adsorption Sr²⁺ on Ti₃CNT_x/TMAOH

ΔG/(kJ∙mol⁻¹)			ΔH/ (kJ∙mol⁻¹)	ΔS/ (J∙mol⁻¹∙K⁻¹)
293 K	303 K	313 K	ΔH/ (kJ∙mol⁻¹)	ΔS/ (J∙mol⁻¹∙K⁻¹)
−25.34	−26.39	−27.41	4.95	103.42
Notes: ΔG—Gibbs free energy change; ΔH—Enthalpy change; ΔS—Entropy change.

下载: 导出CSV

表 6 Ti₃CNT_x/TMAOH在不同水环境下去除Sr²⁺前后的主要水质参数

Table 6. Main water quality parameters before and after Sr²⁺ removal by Ti₃CNT_x/TMAOH in different water environments

	pH	Na⁺/ (mg∙L⁻¹)	K⁺/ (mg∙L⁻¹)	Mg²⁺/ (mg∙L⁻¹)	Ca²⁺/ (mg∙L⁻¹)	Sr²⁺/ (mg∙L⁻¹)
TW	6.23	8.230	3.382	9.823	45.46	5.500
1.0 g∙L⁻¹		8.129	2.999	7.777	23.38	1.572
3.0 g∙L⁻¹		7.895	2.861	3.772	7.616	0.3411
LW	7.12	23.2	39.98	44.33	98.57	5.982
1.0 g∙L⁻¹		228.1	38.00	41.39	80.69	3.347
3.0 g∙L⁻¹		216.1	33.86	35.93	56.65	1.885

下载: 导出CSV

参考文献(39)

[1]	LIU F F, ZHOU A G, CHEN J F, et al. Preparation of Ti₃C₂ and Ti₂C MXenes by fluoride salts etching and methane adsorptive properties[J]. Applied Surface Science,2017,416:781-789. doi: 10.1016/j.apsusc.2017.04.239
[2]	杨挺. 核电站化学废水的处理技术浅析[J]. 科技视界, 2019(1):212-213, 216. doi: 10.19694/j.cnki.issn2095-2457.2019.01.092 YANG Ting. Treatment technology of chemical wastewater in nuclear power station[J]. Scientific and Technological Horizon,2019(1):212-213, 216(in Chinese). doi: 10.19694/j.cnki.issn2095-2457.2019.01.092
[3]	WANG Y, NIU B, ZHANG X, et al. Review—Ti₃C₂T_x MXene: An emerging two-dimensional layered material in water treatment[J]. ECS Journal of Solid State Science and Technology,2021,10(4):047002. doi: 10.1149/2162-8777/abf2de
[4]	HE X, JIN S, MIAO L, et al. A 3D hydroxylated MXene/carbon nanotubes composite as scaffold for dendrite-free sodium-metal electrodes[J]. Angewandte Chemie,2020,59(38):16705-16711. doi: 10.1002/anie.202006783
[5]	YAGHOUB M. MXenes and other 2D nanosheets for modification of polyamide thin film nanocomposite membranes for desalination[J]. Separation and Purification Technology,2022,289:120777. doi: 10.1016/j.seppur.2022.120777
[6]	HWANG S K, KANG S M, RETHINASABAPATHY M, et al. MXene: An emerging two-dimensional layered material for removal of radioactive pollutants[J]. Chemical Engineering Journal,2020,397:125428. doi: 10.1016/j.cej.2020.125428
[7]	LU M, HAN W, LI H, et al. There is plenty of space in the MXene layers: The confinement and fillings[J]. Journal of Energy Chemistry,2020,48:344-363. doi: 10.1016/j.jechem.2020.02.032
[8]	IBRAHIM Y, KASSAB A, EID K, et al. Unveiling fabrication and environmental remediation of MXene-based nanoarchitectures in toxic metals removal from wastewater: Strategy and mechanism[J]. Nanomaterials,2020,10(5):885-914. doi: 10.3390/nano10050885
[9]	LI S, WANG L, PENG J, et al. Efficient thorium(IV) removal by two-dimensional Ti₂CT_x MXene from aqueous solution[J]. Chemical Engineering Journal,2019,366:192-199. doi: 10.1016/j.cej.2019.02.056
[10]	RETHINASABAPATHY M, HWANG K S, KANG S M, et al. Amino-functionalized POSS nanocage-intercalated titanium carbide (Ti₃C₂T_x) MXene stacks for efficient cesium and strontium radionuclide sequestration[J]. Journal of Hazardous Materials,2021,418:126315. doi: 10.1016/j.jhazmat.2021.126315
[11]	WANG L, TAO W, YUAN L, et al. Rational control of the interlayer space inside two-dimensional titanium carbides for highly efficient uranium removal and imprisonment[J]. Chemical Communications,2017,53(89):12084-12087. doi: 10.1039/C7CC06740B
[12]	ZHANG Z G, GU P, ZHANG M D, et al. Synthesis of a robust layered metal sulfide for rapid and effective removal of Sr²⁺ from aqueous solutions[J]. Chemical Engineering Journal,2019,372:1205-1215. doi: 10.1016/j.cej.2019.04.193
[13]	QADA E, ALLEN S J, WALKER G M. Adsorption of basic dyes from aqueous solution onto activated carbons[J]. Chemical Engineering Journal,2008,135(3):174-184. doi: 10.1016/j.cej.2007.02.023
[14]	YU B, YUEN A, XU X, et al. Engineering MXene surface with POSS for reducing fire hazards of polystyrene with enhanced thermal stability[J]. Journal of Hazardous Materials,2021,401:123342. doi: 10.1016/j.jhazmat.2020.123342
[15]	DENG S B, BAI R B. Aminated polyacrylonitrile fibers for humic acid adsorption: Behaviors and mechanisms[J]. Environmental Science & Technology,2003,37(24):5799-5805.
[16]	吴刚. 材料结构表征及应用[M]. 北京: 化学工业出版社, 2001: 15-21. WU Gang. Characterization and application of material structure[M]. Beijing: Chemical Industry Press, 2001: 15-21(in Chinese).
[17]	LIN H, CHEN L, LU X, et al. Two-dimensional titanium carbide MXenes as efficient non-noble metal electrocatalysts for oxygen reduction reaction[J]. Science China Materials,2019,62(5):662-670. doi: 10.1007/s40843-018-9378-3
[18]	XU G, WANG X, GONG S, et al. Solvent-regulated preparation of well-intercalated Ti₃C₂T_x MXene nanosheets and application for highly effective electromagnetic wave absorption[J]. Nanotechnology,2018,29(35):355201. doi: 10.1088/1361-6528/aac8f6
[19]	QIAN A, HYEON S E, SEO J Y, et al. Capacitance changes associated with cation-transport in free-standing flexible Ti₃C₂T_x (T—O, F, OH) MXene film electrodes[J]. Electrochimica Acta,2018,266:86-93. doi: 10.1016/j.electacta.2018.02.019
[20]	DU F, TANG H, PAN L M, et al. Environmental friendly scalable production of colloidal 2D titanium carbonitride MXene with minimized nanosheets restacking for excellent cycle life lithium-ion batteries[J]. Electrochimica Acta,2017,235:690-699. doi: 10.1016/j.electacta.2017.03.153
[21]	ZHANG M D, GU P, YAN S, et al. Na/Zn/Sn/S (NaZTS): Quaternary metal sulfide nanosheets for efficient adsorption of radioactive strontium ions[J]. Chemical Engineering Journal,2020,379:122227. doi: 10.1016/j.cej.2019.122227
[22]	SHAHZAD A, OH J M, RASOOL K, et al. Strontium ions capturing in aqueous media using exfoliated titanium aluminum carbide (Ti₂AlC MAX phase)[J]. Journal of Nuclear Materials,2021,549:152916. doi: 10.1016/j.jnucmat.2021.152916
[23]	MU W J, DU S Z, YU Q H, et al. Improving barium ion adsorption on two-dimensional titanium carbide by surface modification[J]. Dalton Transactions,2018,47(25):8375-8381. doi: 10.1039/C8DT00917A
[24]	SHAHZAD A, NAWAZ M, MOZTAHIDA M, et al. Ti₃C₂T_x MXene core-shell spheres for ultrahigh removal of mercuric ions[J]. Chemical Engineering Journal,2019,368:400-408. doi: 10.1016/j.cej.2019.02.160
[25]	ZHANG L, WEI J Y, ZHAO X, et al. Removal of strontium(II) and cobalt(II) from acidic solution by manganese antimonate[J]. Chemical Engineering Journal,2016,302:733-743. doi: 10.1016/j.cej.2016.05.040
[26]	WHITE D A, LABAYRU R. Synthesis of a manganese dioxide-silica hydrous composite and its properties as a sorption material for strontium[J]. Industrial and Engineering Chemistry Research,1991,30(1):207-210. doi: 10.1021/ie00049a031
[27]	WEN T, WU X L, LIU M C, et al. Efficient capture of strontium from aqueous solutions using graphene oxide-hydroxyapatite nanocomposites[J]. Dalton Transactions,2014,43(20):7464-7472. doi: 10.1039/c3dt53591f
[28]	DING N, KANATZIDIS M G. Selective incarceration of caesium ions by Venus flytrap action of a flexible framework sulfide[J]. Nature Chemistry,2010,2(3):187-191. doi: 10.1038/nchem.519
[29]	MENG R, CHEN T, ZHANG Y, et al. Development, modification, and application of low-cost and available biochar derived from corn straw for the removal of vanadium (V) from aqueous solution and real contaminated groundwater[J]. RSC Advances,2018,8(38):21480-21494. doi: 10.1039/C8RA02172D
[30]	DENG S B, YU G, XIE S H, et al. Enhanced adsorption of arsenate on the aminated fibers: Sorption behavior and uptake mechanism[J]. Langmuir,2008,24(19):10961-10967. doi: 10.1021/la8023138
[31]	FARD A K, MCKAY G, CHAMOUN R, et al. Barium removal from synthetic natural and produced water using MXene as two dimensional (2-D) nanosheet adsorbent[J]. Chemical Engineering Journal,2017,317:331-342. doi: 10.1016/j.cej.2017.02.090
[32]	XU F J, WANG Z H, YANG W T. Surface functionalization of polycaprolactone films via surface-initiated atom transfer radical polymerization for covalently coupling cell-adhesive biomolecules[J]. Biomaterials,2010,31(12):3139-3147. doi: 10.1016/j.biomaterials.2010.01.032
[33]	DENG S, ZHENG Y Q, XU F J, et al. Highly efficient sorption of perfluorooctane sulfonate and perfluorooctanoate on a quaternized cotton prepared by atom transfer radical polymerization[J]. Chemical Engineering Journal,2012,193-194:154-160. doi: 10.1016/j.cej.2012.04.005
[34]	ZHANG G, WANG T, XU Z, et al. Synthesis of amino-functionalized Ti₃C₂T_x MXene by alkalization-grafting modification for efficient lead adsorption[J]. Chemical Communications,2020,56(76):11283-11286. doi: 10.1039/D0CC04265J
[35]	CHENG Z, ZHU X, SHI Z L, et al. Polymer microspheres with permanent antibacterial surface from surface-initiated atom transfer radical polymerization[J]. Industrial & Engineering Chemistry Research,2005,44(18):7098-7104.
[36]	ZHANG P, WANG L, HUANG Z, et al. Aryl diazonium-assisted amidoximation of MXene for boosting water stability and uranyl sequestration via electrochemical sorption[J]. ACS Applied Materials & Interfaces,2020,12(13):15579-15587.
[37]	CHEN S, XIANG Y, BANKS M K, et al. Polyoxometalate-coupled MXene nanohybrid via poly(ionic liquid) linkers and its electrode for enhanced supercapacitive performance[J]. Nanoscale,2018,10(42):20043-20052. doi: 10.1039/C8NR05760E
[38]	KIM S J, KOH H J, REN C E, et al. Metallic Ti₃C₂T_x MXene gas sensors with ultrahigh signal-to-noise ratio[J]. ACS Nano,2018,12(2):986-993. doi: 10.1021/acsnano.7b07460
[39]	WANG H, CUI H, SONG X, et al. Facile synthesis of heterojunction of MXenes/TiO₂ nanoparticles towards enhanced hexavalent chromium removal[J]. Journal of Colloid and Interface Science,2020,561:46-57. doi: 10.1016/j.jcis.2019.11.120