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Visualization of Hg2+ Stress on Plant Health at the Subcellular Level Revealed by a Highly Sensitive Fluorescent Sensor
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Sumeera Asghar1, 2, 3, 4, , Zhenyang Yu4, 5, , Zheng Zhu3, , Dengyue Zheng3, , Zimo Zhao3, Yuming Xu3, Xiao Liu4, Chao Yuan4, 6, Yan Li2, Wei Wang1, Jianfeng Xu3, Huailong Teng4, Jun Li4, 5, *, Wen-Chao Yang1, *, Chunli Chen3, 5, *
Research. Vol 8 Article ID 0570
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Research. Vol 8 Article ID 0570
Research Article
Visualization of Hg2+ Stress on Plant Health at the Subcellular Level Revealed by a Highly Sensitive Fluorescent Sensor
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Sumeera Asghar1, 2, 3, 4, , Zhenyang Yu4, 5, , Zheng Zhu3, , Dengyue Zheng3, , Zimo Zhao3, Yuming Xu3, Xiao Liu4, Chao Yuan4, 6, Yan Li2, Wei Wang1, Jianfeng Xu3, Huailong Teng4, Jun Li4, 5, *, Wen-Chao Yang1, *, Chunli Chen3, 5, *
Affiliations
  • 1 State Key Laboratory of Green Pesticide, Key Laboratory of Green Pesticide and Agricultural Bioengineering, Ministry of Education, Center for R&D of Fine Chemicals of Guizhou University, Guiyang 550025, China.
  • 2 The Key Laboratory of Plant Resources Conservation Germplasm Innovation in Mountainous Region, College of Life Sciences, Institute of Agro-bioengineering, Guizhou University, Guiyang 550025, China.
  • 3 Hubei Hongshan Laboratory, College of Life Science and Technology, Huazhong Agricultural University, Wuhan, Hubei 430070, China.
  • 4 National Key Laboratory for Germplasm Innovation and Utilization for Fruit and Vegetable Horticultural Crops, Wuhan, China.
  • 5 College of Chemistry, Huazhong Agricultural University, Wuhan, Hubei 430070, China.
  • 6 School of Environmental Science and Engineering, Guangdong University of Petrochemical Technology, Maoming 525000, China.
Published: 2025-01-07 doi: 10.34133/research.0570
Outline
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The presence of Hg2+ causes substantial stress to plants, adversely affecting growth and health by disrupting cell cycle divisions, photosynthesis, and ionic homeostasis. Accurate visualization of the spatiotemporal distribution of Hg2+ in plant tissues is crucial for the management of Hg pollution; however, the related research is still at its early stage. Herein, a small-molecule amphiphilic fluorescent probe (termed LJTP2) was developed for the specific detection of Hg2+ with a high sensitivity (~16 nM). Fluorescent imaging applications with LJTP2 not only detected the dynamic distribution of Hg2+ within plant cells at the subcellular level but also enabled the understanding of cell membrane health under Hg2+ stress. This study introduces a valuable imaging tool for elucidating the molecular mechanism of Hg2+ stress in plants, demonstrating the potential of the application of small-molecule fluorescent probes in plant science.

Sumeera Asghar, Zhenyang Yu, Zheng Zhu, Dengyue Zheng, Zimo Zhao, Yuming Xu, Xiao Liu, Chao Yuan, Yan Li, Wei Wang, Jianfeng Xu, Huailong Teng, Jun Li, Wen-Chao Yang, Chunli Chen. Visualization of Hg2+ Stress on Plant Health at the Subcellular Level Revealed by a Highly Sensitive Fluorescent Sensor[J]. Research, 2025 , 8 (1) : 0570 . DOI: 10.34133/research.0570
Heavy metal pollution, which is nonbiodegradable and accumulates in soils through anthropogenic activities, not only affects plant growth and crop yield via complicated mechanisms in agriculture but also induces health problems through food chains. As a mainly toxic species of heavy metal, mercury (Hg) pollution poses a global concern, stemming from both natural phenomena and human activities [13]. As a major form of Hg, Hg2+ is absorbed by plant roots and transferred to the leaves via a transport system, which could further induce severe phytotoxicity and impair plant metabolic processes and growth [4]. Rice, one of the major food sources, played an important role in the survival of human beings and social stability. However, the long-term accumulation of Hg2+ in rice can induce serious issues, including food and ecological safety, human health, and crop yield [57].
Effective management of Hg pollution in modern agriculture requires an accurate assessment of Hg2+ distribution in plant tissues and the damage it causes at the subcellular level [8,9]. Among various detection tools, such as atomic absorption/emission spectroscopy, inductively coupled plasma mass spectrometry, and isotopic labeling [10], fluorescent sensors have displayed marked superiorities, including high sensitivity and spatiotemporal resolution and noninvasive in situ imaging [1123]. So far, some fluorescent sensors have been developed for in vivo detection of Hg2+ [2439]. For example, Chen et al. [33] developed a boron-dipyrromethene-based fluorescent probe for Hg2+ imaging in Arabidopsis with near-infrared emission. Wang et al.'s group [29] developed a coumarin-based fluorescent probe based on the mechanism of Hg2+-induced desulfurization. The probe was successfully applied for fluorescent imaging in Arabidopsis root. Recently, An and co-workers designed a fluorescent probe based on aggregation-induced emission enhancement for Hg2+ detection. The probe can be employed to detect Hg2+ in the rhizome slices of Radix Hedysari under an ultraviolet lamp [39]. Despite great progress achieved in plant imaging, there is still an urgent need to design an efficient probe that can be used to evaluate Hg2+-induced damage against plant cells at the subcellular level, which is crucial for managing Hg pollution.
In this study, a novel fluorescent probe (LJTP2) was synthesized to visualize the subcellular distribution and translocation of Hg2+ in plant tissues. LJTP2 simulated the amphiphilic nature of surfactants, which improved the probe's dispersibility in aqueous solution. It comprises a lipophilic octadecyl group enabling the probe to target cells, a naphthylamide-based fluorophore for signal output, and a hydrophilic tetrakis (N-2-hydroxyethyl) acetamide group as a Hg2+-specific binding component (Fig. 1 and Fig. S11). Due to its amphipathic property, LJTP2 not only showed good selectivity but also displayed an ultralow limit of detection (LOD) of 16 nM toward Hg2+ early detection due to its high sensitivity. The fluorescent probe signals were observed for Hg2+ detection in the model plant Arabidopsis (root tip and leaf), moss (another model plant, an important plant in terms of evolutionary studies), and an onion to visualize its location and further its penetration at the subcellular level. More importantly, the Hg2+ distribution and its damage to plant cells were clearly observed under single- and 2-photon microscopy.
With the probe in hand, we first evaluated the probe's optical properties in aqueous solution. LJTP2 showed a strong absorption peak at 410 nm in Hepes solution (Fig. S12), which was employed as the excitation wavelength for fluorescence measurement. The fluorescence titration experiment of LJTP2 with different metal ions, including Fe3+, Al3+, Fe2+, Zn2+, Cd2+, Hg2+, Mg2+, Cu2+, Pd2+, Mn2+, Li+, Na+, and Ag+, showed that only Hg2+ induced significant fluorescence enhancement at an emission peak of 525 nm, indicating the good selectivity of LJTP2 (Fig. 2A and B). A good linear relationship between the enhancement of fluorescence intensity and the concentration of Hg2+ can be found within a range of 0 to 3 μM (Fig. 2C and D), and the LOD was determined as 16 nM. Due to its special affinity toward S2−, the Hg2+-enhanced fluorescence could be recovered back to that of the free probe. This rapidly reversible sensing behavior is repeated 5 times without obvious signal attenuation (Fig. 2E). To understand the binding mode of LJTP2 with Hg2+, a Job plot experiment was performed. As shown in Fig. 2F, the intersection of the curve was located at a ratio of 0.5, indicating the 1:1 binding ratio of LJTP2 with Hg2+ (Fig. S11). Furthermore, LJTP2 was very stable in the pH range of 6.5 to 8.5, which can be used for Hg2+ sensing under physiological conditions (Fig. S13).
To understand the sensing mechanism (Fig. S11), a density functional theory calculation was conducted using the Gaussian 16 software [40]. The highest occupied molecular orbital and lowest unoccupied molecular orbital were distributed in the phenyl group and fluorophore (naphthalimide), respectively, with an energy gap of 3.61 eV; the photoinduced electron transfer occurred from the phenyl ring to the fluorophore, resulting in fluorescence off. After binding with Hg2+, the distribution of the highest occupied molecular orbital and lowest unoccupied molecular orbital was moved to the alkyl chain and ligand, respectively, with an energy gap of 2.55 eV, leading to the photoinduced electron transfer inhibition and fluorescence on (Fig. 3).
The probe's biocompatibility is crucial for its biological applications; we first evaluated its toxicity on plant growth. The result showed that root length was not affected by Hepes solution or the probe working solution from a time range of 30 min until 24 h (Fig. 4A). A statistical representation of root length data under 3 different growth conditions (water, Hepes, and Hepes plus LJTP2) showed no side effects on root length (Fig. 4B), so it was evident that LJTP2 did not interfere with or change the plant growth pattern. After carefully testing the probe's toxicity toward plant growth, we went on further to explore probe specificity in vivo; the treatment of Cd2+, Mg2+, Zn2+, K+, and Na+ in Arabidopsis thaliana did not show significant fluorescent enhancement under 2-photon microscopy except Hg2+, and the statistically calculated mean fluorescence intensity is presented as well (Fig. 4C and D). In addition, LJTP2 showed good signal stability in the presence and absence of Hg2+. The fluorescent intensity in A. thaliana root increased steadily after treatment with Hg2+ and LJTP2 for 24 h, while no significant fluorescent signal was observed in the LJTP2-treated group (Fig. 4E). The above results indicated that the buffer and probe are nontoxic, stable, and specific for Hg detection without affecting plant health, root length, and overall plant growth.
Subsequently, confocal imaging was employed to investigate the plant tissue through the details of mercury–plant and mercury–plant–probe relationships.
To evaluate the growth environment under Hg2+ stress, the A. thaliana seedlings were incubated in 2.5, 5, and 10 μM Hg2+ media for 7 d and then stained with LJTP2 (10 μM) for 1 h (Fig. 5A). The fluorescence signal was present in both root tip and leaf stomata regions, indicating Hg2+ distribution in A. thaliana (Fig. 5B). To further confirm Hg2+-induced fluorescence enhancement, the different concentrations were evaluated. The probe itself showed very weak fluorescence, but upon the addition of 2.5 μM Hg2+ into the media, the fluorescence signal was detected very clearly and became stronger with the increase in Hg2+ concentration (Fig. 5C). The mean fluorescence intensity statistical calculation is presented as well (Figure 5D). In addition, probe signals at different depths in Arabidopsis roots are shown in Figure S14. Overall, the results clearly indicated that the fluorescence intensity of the probe LJTP2 was positively correlated with Hg2+ concentrations.
To further study probe localization at the subcellular level, a plasmolysis experiment was performed in onion cells treated with NaCl and sucrose. When treated with NaCl, both showed a continuous probe signal at the cell membrane and a discontinued signal at the cell wall in plasmolysis analysis. Clear plasmolysis immediately took place after 3 to 4 min of Hg2+ treatment and 5 min of LJTP2 incubation, followed by 20 min of NaCl (1.0 M concentration) (Fig. 5E). The plasma membrane was progressively detached from its neighboring cell wall, and the plasma membrane gradually shrank to an elliptical shape. Fluorescence signals were seen inside the cell in the cell nucleus when treated with Hg2+ solution for 40 min, followed by 1 min of 50% dimethyl sulfoxide (DMSO) (a dose of 50% was selected mainly because with the help of 50% DMSO, cell permeability was enhanced for Hg2+ penetration inside the cell) and 5 min of probe incubation respectively, as shown in (Fig. 5E). Therefore, the confocal imaging of LJTP2 probe enabled monitoring of the morphological changes in the plasma membrane of the plant cell caused by the external environment under different physiological conditions.
To further confirm the location of LJTP2 within the cell, the moss was sprayed with 5 μM Hg2+ 3 times in 3 d and then incubated with LJTP2 for 1 h. As shown in Fig. 5F, the green fluorescence signals that LJTP2 + Hg2+ induced were observed in the cell boundaries, and the reason is that the double-layer structure of the membrane blocked Hg intake/penetration at first; however, after treatment with DMSO for 10 s, the green fluorescence signal crossed the protoplast barrier and diffused all over the protoplasts except the chloroplast because the double-layer membrane structure of the chloroplast further stopped the entry of Hg2+ ions. Our results showed Hg2+ detection at the cell boundaries at first, and after the cell permeability was enhanced with DMSO treatment, Hg2+ further penetrated the chloroplast, so the probe entered all over the protoplast. Therefore, the fluorescence imaging in moss (another good model plant) reconfirmed the good sensing ability of LJTP2 at the subcellular level.
Considering the advantages of 2-photon microscopy, including deeper penetration depth and reduced photodamage [21,22], 2-photon imaging was further conducted to reaffirm probe efficiency to detect Hg2+ at the subcellular level (Fig. 6).
The translocation of Hg2+ in plants and the stress effect of plant cells under Hg2+ were visualized using 2-photon microscopy (λ ex = 750 nm) in a real-time manner (Fig. 6A). The probe detected a very faded signal, almost negligible, without Hg2+ incubation. When the root tips were incubated in Hg2+ solution and in the probe for 1 h, Hg2+ signals were detected all along the epidermis of the root tip. After 3 h of Hg2+ incubation, Hg2+ detection signals were all over the root tip at each cell. After 5 h of Hg2+ incubation followed by 1 h of the probe, there was a significant amount of Hg2+ translocation signals at the cell boundary of each cell (Fig. 6B). Consistent results were also observed in the leaf. The signals were not seen when the leaf samples were incubated without Hg2+ in the probe only. After 1 h of Hg2+ incubation, signals were observed at the leaf stomata, but after 5 h of Hg2+ incubation, more evident probe signals were observed in every cell. The Hg2+ incubation for different time points and probe soaking for a consistent time point indicated a positive and direct correlation of Hg2+ and the probe (Fig. 6B).
In summary, the fluorescence signal was located at the root epidermis after 1 h of probe incubation and then observed in root epidermal cells and also became stronger after 3- or 5-h incubation. Furthermore, the real-time imaging in leaves indicated that the Hg2+ translocation started from the stomata and moved to the vein and then the whole leaf. The Hg2+ distribution and translocation in the A. thaliana root and leaf were successfully observed spatiotemporally in a real-time manner under 2-photon imaging.
To further investigate the status of cells under Hg2+ stress and signal progression, 2-photon imaging of A. thaliana roots and leaves at different concentrations of Hg2+ (Fig. 6C) showed the fluorescence signal in A. thaliana roots after incubation with 5 μM, which eventually got stronger with the increase in concentration from 5 μM to 1 mM Hg2+. The same trend was also observed in the leaves. Under low concentrations of Hg2+ treatment, the signal was distributed along the boundaries of plant root and leaf cells, whereas at high concentrations, mercury disrupted the integrity of the plant cell membrane, resulting in the signal filling the entire cell (Fig. 6D). The above results proved that LJTP2 can be used to monitor the integrity of the cell structure under Hg2+ stress.
Hg2+ stress seriously affects agricultural and ecological safety; verifying the spatiotemporal distribution of Hg2+ in plant tissues and the accumulation-induced damage at the subcellular level is significant for the management of Hg pollution. Thus, there is an urgent need to develop an efficient imaging tool for monitoring Hg2+ stress in plant tissues. The fluorescent probe (LJTP2) was rationally designed with the amphiphilic nature of surfactants, which improved the probe's dispersibility and sensitivity toward Hg2+ in aqueous solution. Compared with the key parameters and applications of some reported fluorescent probes for Hg2+, LJTP2 displayed significant superiorities (Table S1), indicating the successful design of our probe.
Interestingly, the spatiotemporal dynamic distribution of Hg2+ in A. thaliana under 2-photon imaging revealed that the fluorescence signal initially appeared at the root exodermis within 5 min of probe incubation. The signal was further recorded in root epidermal cells and became stronger after 1 h of probe incubation. Real-time monitoring indicated that Hg2+ accumulation and distribution were mostly at the root. The real-time imaging in leaves indicated Hg2+ translocation from the stomata to the veins and then the whole leaf. Our findings also provided deeper insight, revealing that LJTP2 showed a strong affinity toward cell structure boundaries in onion cells. The shrinkage of the cell protoplast led to a gap between the cell wall and cell membrane, which further resulted in discontinued signals at the cell wall but continued at the membrane as its structure remained intact. Furthermore, the Hg2+-induced damage on the cell membrane and stomata was clearly observed under 2-photon imaging, manifesting that LJTP2 can be employed as an efficient visual tool to evaluate plant health in vivo.
In the future, LJTP2 could be further developed to sense and detect Hg2+ presence fast and accurately to mitigate the problem of mercury contamination by combining the standard method phytoremediation removal of mercury from polluted areas through scavenger plants (a green strategy that uses hyperaccumulator plants and their rhizospheric microorganisms to transfer and degrade pollutants from the soil and environment)—with raising such plants by routine mutagenesis and genetic engineering [5,41].
In summary, an amphiphilic fluorescent probe (LJTP2) was specifically designed to investigate the Hg2+ stress in plant tissues. LJTP2 exhibited excellent selectivity and sensitivity for early Hg2+ detection in aqueous solution with a low LOD of 16 nM (Table S1). The plasmolysis experiment confirmed that LJTP2 selectively targeted the cell membrane structure. Under confocal observations, the continuous and discontinuous distributions of Hg2+ in the cell membrane and cell wall were visualized obviously. Furthermore, the Hg2+ distribution and translocation and Hg2+ stress-induced membrane broken in the root tip cells and leaf stomata were well observed under 2-photon imaging. We believe this study not only provided a novel imaging tool for the investigation of Hg2+ stress on the plant cell structure but also facilitated the management of Hg pollution in agriculture.
LJTP2 was synthesized using 4-bromo-1,8-naphthalic anhydride as a starting material, which further underwent nucleophilic, hydrolysis, condensation, and aminolysis reactions with moderate yields (Fig. 7). The nuclear magnetic resonance and high-resolution mass spectrometry data confirmed the chemical structure of LJTP2. The detailed synthetic procedure is depicted in the Supplementary Materials (Figs. S1 to S10).
A. thaliana was used. The plants were grown as control according to the protocol established by Sugimoto and Meyerowitz [42] and Chen et al. [43]. The seeds underwent a washing process involving a 10-min wash with 75% alcohol, followed by 4 successive washes with sterilized water; each step was kept 20 min. Subsequently, the washed seeds were refrigerated at 4 °C for 2 to 3 d before placing them on ½ Murashige and Skoog media. The medium was autoclaved at 121 °C for 21 min and later poured into petri dishes. After solidification, the seeds were sown, and plates were positioned vertically in a controlled environment growth chamber with conditions set at 22/20 °C for day and night with a 16-h photoperiod and illumination of approximately 500 lux from a white cool fluorescent lamp and maintained for 7 d. Moss, which were initially collected from the lion mountainous region of Wuhan, China, and subsequently grown in the laboratory, and onion were also used.
To evaluate the potential toxicity of the LJTP2 probe on plants, 7-d-old A. thaliana was employed. Three treatments were established: the application of Hepes buffer, the application of the probe solution (10 μM in 40 mM Hepes buffer), and the application of distilled water, which was used as a control. Within each treatment, 4-time gradients were set: 30 min, 1 h, 12 h, and 24 h. The root length after treatment was measured as an index for assessing toxicity.
To explore the distribution of Hg2+ within the plant tissues, A. thaliana was grown on a medium containing HgCl2 (0, 2.5, 5, and 10 μM) for 7 d and then incubated in the LJTP2 probe solution for 1 h. Subsequently, the samples were prepared into slides and imaged using an Olympus FV1000 confocal laser scanning microscope with an excitation wavelength of 405 nm.
The elemental selectivity test of the probe was conducted using A. thaliana as the material. Seven-day-old Arabidopsis seedlings were immersed in a solution containing 100 μM of 6 kinds of ions, namely, Hg2+, Cd2+, Zn2+, Mg2+, Na+, and K+, for 1 h. Distilled water treatment was used as a control. After treatment, the seedlings were rinsed with distilled water and incubated in the LJTP2 probe solution for 1 h. The root signals were observed under a 2-photon mode on an Olympus FV1000 confocal microscope with an excitation wavelength of 750 nm.
The stability experiment of the probe was conducted using A. thaliana as the material. A. thaliana treated with 100 μM mercuric chloride and those treated with distilled water were processed in the LJTP2 probe solution for different durations (5 min, 1 h, 12 h, and 24 h). The signals were observed under an Olympus FV1000 single-photon confocal microscope with an excitation wavelength of 405 nm.
To explore the dynamics of Hg2+ entry into plant cells and the cellular-level distribution of mercury ions within plants. A. thaliana was grown on a culture medium for 7 d and then immersed in a solution of 100 μM mercuric chloride for different durations (1, 3, and 5 h) or in solutions of varying concentrations (5 μM, 10 μM, 20 μM, 1 mM, and 10 mM) of HgCl2 for 2 h. The signals from the root tips and leaf epidermis were observed using the 2-photon mode of an Olympus FV1000 confocal microscope with an excitation wavelength of 750 nm.
Onion epidermis tissues were cut with the help of tweezers and scissors [44]. These tissues were first incubated in Hg2+ solution for 40 min and later dipped for 1 min in probe solution. Then, the plasmolysis experiments were performed with NaCl (1 mol/l). Then, DMSO (50% concentration) treatment for 1 s enhanced the permeability of the cell membrane of the onion tissues to examine the probe's affinity to the membrane
Morphological data, including root length and fluorescence intensities, were calculated using the ImageJ software. Subsequently, data were statistically analyzed, the means and standard deviation were calculated, and the analysis of variance test was applied to check the significance levels. Statistical analyses and graphs were performed and generated using the GraphPad Prism software, respectively.
  • National Natural Science Foundation of China(21806048, 22276041)
  • Advanced Foreign Experts Project(G2023157014L)
  • Central Government Guides Local Science and Technology Development Fund Projects(Qiankehezhongyindi (2023) 001 and (2024) 007)
  • Program of Major Scientific and Technological, Guizhou Province, China(Qiankehechengguo (2024) zhongda007)
  • Cultivating Fund Project of Hubei Hongshan Laboratory(2022hspy002)
1.
Rai PK, Lee SS, Zhang M, Tsang YF, Kim KH. Heavy metals in food crops: Health risks, fate, mechanisms, and management. Environ Int. 2019;125:365–385.
2.
Sun X, Li P, Zheng G. Cellular and subcellular distribution and factors influencing the accumulation of atmospheric Hg in Tillandsia usneoides leaves. J Hazard Mater. 2021;414: Article 125529.
3.
UN Environment. Global mercury assessment 2018 Geneva (Switzerland): Chemical and Health Branch, UN Environment Programme; 2019.
4.
Zhang Y, Shi W, Feng D, Ma H, Liang Y, Zuo J. Application of rhodamine B thiolactone to fluorescence imaging of Hg2+ in Arabidopsis thaliana. Sens Actuators B Chem. 2011;153(1):261–265.
5.
Feng L, Li P, Feng X. Methylmercury bioaccumulation in rice and health effects: A systematic review. Curr Opin Environ Sci Health. 2021;23: Article 100285.
6.
Liu M, Zhang Q, Cheng M, He Y, Chen L, Zhang H, Cao H, Shen H, Zhang W, Tao S, et al. Rice life cycle-based global mercury biotransport and human methylmercury exposure. Nat Commun. 2019;10(1): Article 5164.
7.
Li Y, Chen L, Liang S, Zhou H, Liu YR, Zhong H, Yang Z. Looping mercury cycle in global environmental–economic system modeling. Environ Sci Technol. 2022;56(5):2861–2879.
8.
Yang A, Feng J, Wang H, Cui L, Xie G, Li H, Luo X, Xian Y. A review of mercury uptake, transport and bioaccumulation in rice. Water Air Soil Pollut. 2023;234(6):377.
9.
Quevedo-Ospina C, Arroyave C, Peñuela-Vásquez M, Villegas A. Effect of mercury in the influx and efflux of nutrients in the microalga Desmodesmus armatus. Aquat Toxicol. 2023;258: Article 106496.
10.
Yeung V, Miller DD, Rutzke MA. Atomic absorption spectroscopy, atomic emission spectroscopy, and inductively coupled plasma-mass spectrometry. Food Analysis. 2017;129–150.
11.
Fernández-Suárez M, Ting AY. Fluorescent probes for super-resolution imaging in living cells. Nat Rev Mol Cell Biol. 2008;9(12):929–943.
12.
Yin J, Hu Y, Yoon J. Fluorescent probes and bioimaging: Alkali metals, alkaline earth metals and pH. Chem Soc Rev. 2015;44(15):4619–4644.
13.
Kompa J, Bruins J, Glogger M, Wilhelm J, Frei MS, Tarnawski M, D'Este E, Heilemann M, Hiblot J, Johnsson K. Exchangeable HaloTag ligands for super-resolution fluorescence microscopy. J Am Chem Soc. 2023;145(5):3075–3083.
14.
Yang Z, Sharma A, Qi J, Peng X, Lee DY, Hu R, Lin D, Qu J, Kim JS. Super-resolution fluorescent materials: An insight into design and bioimaging applications. Chem Soc Rev. 2016;45(17):4651–4667.
15.
Zuo J, Zhu E, Yin W, Yao C, Liao J, Ping X, Zhu Y, Cai X, Rao Y, Feng H, et al. Long-term spatiotemporal and highly specific imaging of the plasma membrane of diverse plant cells using a near-infrared AIE probe. Chem Sci. 2023;14(8):2139–2148.
16.
Han X, Wang Y, Huang Y, Wang X, Choo J, Chen L. Fluorescent probes for biomolecule detection under environmental stress. J Hazard Mater. 2022;431: Article 128527.
17.
Chen Y, He B, Hu M, Bao J, Yan W, Han X, Ye Y. Fluorescent probes for imaging and detection of plant hormones and their receptors. Adv Agrochem. 2023;3(1):89–98.
18.
Gao LL, Pang S, Gao Y, Shi D, Guo Y. Recent development of organic small-molecule and nanomaterial fluorescent probes for hydrazine. Adv Agrochem. 2022;1(1):22–38.
19.
Zeng X, Huang Y, Dong J, Ma X, Nan JX, Chen W, Lin HY, Yang WC, Liu X, Yin J, et al. Design of an HPPD fluorescent probe and visualization of plant responses to abiotic stress. Adv Agrochem. 2022;1(1):73–84.
20.
Gao YY, He J, Li XH, Li JH, Wu H, Wen T, Li J, Hao GF, Yoon J. Fluorescent chemosensors facilitate the visualization of plant health and their living environment in sustainable agriculture. Chem Soc Rev. 2024;53:6992–7090.
21.
Du J, Chen K, Yu Z, Qiao Y, Liu J, Zhai Q, Hu Z, Yang SG, Li J, Teng H. Development of bi-oligo (ethylene glycol)-functionalized fluorescent probe for two-photon and non-invasive imaging in Arabidopsis thaliana. Adv Agrochem. 2022;1(1):162–173.
22.
Zhang XX, Qi H, Lu MH, Yang SQ, Li P, Piao HL, Han KL. Semi-quantitatively designing two-photon high-performance fluorescent probes for glutathione S-transferases. Research. 2020;2020: Article 7043124.
23.
Dong J, Qian J, Yu K, Huang S, Cheng X, Chen F, Jiang H, Zeng W. Rational design of organelle-targeted fluorescent probes: Insights from artificial intelligence. Research. 2023;6: Article 0075.
24.
Vengaian KM, Britto CD, Sekar K, Sivaraman G, Singaravadivel S. Phenothiazine-diaminomalenonitrile based colorimetric and fluorescence “turn-off-on” sensing of Hg2+ and S2−. Sens Actuators B Chem. 2016;235:232–240.
25.
Sun C, Sun R, Chen Y, Tong Y, Zhu J, Bai H, Zhang S, Zheng H, Ye H. Utilization of aptamer-functionalized magnetic beads for highly accurate fluorescent detection of mercury (II) in environment and food. Sens Actuators B Chem. 2018;255:775–780.
26.
Chen L, Park SJ, Wu D, Kim HM, Yoon J. A two-photon fluorescent probe for colorimetric and ratiometric monitoring of mercury in live cells and tissues. Chem Commun. 2019;55(12):1766–1769.
27.
Pan SL, Li K, Li LL, Li MY, Shi L, Liu YH, Yu XQ. A reaction-based ratiometric fluorescent sensor for the detection of Hg(ii) ions in both cells and bacteria. Chem Commun. 2018;54(39):4955–4958.
28.
Wang Z, Zhang Y, Yin J, Yang Y, Luo H, Song J, Xu X, Wang S. A novel camphor-based “turn-on” fluorescent probe with high specificity and sensitivity for sensing mercury(II) in aqueous medium and its bioimaging application. ACS Sustain Chem Eng. 2020;8(33):12348–12359.
29.
Wang L, Ma Y, Lin W. A coumarin-based fluorescent probe for highly selective detection of hazardous mercury ions in living organisms. J Hazard Mater. 2024;461: Article 132604.
30.
Neupane LN, Park J, Mehta PK, Oh ET, Park HJ, Lee KH. Fast and sensitive fluorescent detection of inorganic mercury species and methylmercury using a fluorescent probe based on the displacement reaction of arylboronic acid with the mercury species. Chem Commun. 2020;56(19):2941–2944.
31.
Tan T, Zhang C, Han Y, Chu R, Xi W, Chen X, Sun J, Huang H, Hu Y, Huang X. Fine-tuning bromide AIE probes for Hg2+ detection in mitochondria with wash-free staining. J Hazard Mater. 2024;464: Article 132999.
32.
Cheng T, Wang T, Zhu W, Yang Y, Zeng B, Xu Y, Qian X. Modulating the selectivity of near-IR fluorescent probes toward various metal ions by judicious choice of aqueous buffer solutions. Chem Commun. 2011;47(13):3915–3917.
33.
Chen W, Guan Y, Chen Q, Ren J, Xie Y, Yin J. The mark of mercury(II) in living animals and plants through using a BODIPY-based near-infrared fluorescent probe. Dyes Pigments. 2022;200: Article 110134.
34.
Ye M, Xiang Y, Gong J, Wang X, Mao Z, Liu Z. Monitoring Hg2+ and MeHg+ poisoning in living body with an activatable near-infrared II fluorescence probe. J Hazard Mater. 2023;445: Article 130612.
35.
Chen Y, Zhang W, Cai Y, Kwok RT, Hu Y, Lam JW, Gu X, He Z, Zhao Z, Zheng X, et al. AIEgens for dark through-bond energy transfer: Design, synthesis, theoretical study and application in ratiometric Hg2+ sensing. Chem Sci. 2017;8(3):2047–2055.
36.
Wang JH, Liu YM, Dong ZM, Chao JB, Wang H, Wang Y, Shuang S. New colorimetric and fluorometric chemosensor for selective Hg2+ sensing in a near-perfect aqueous solution and bio-imaging. J Hazard Mater. 2020;382: Article 121056.
37.
Duan Q, Zhu H, Liu C, Yuan R, Fang Z, Wang Z, Jia P, Li Z, Sheng W, Zhu B. A carbonothioate-based far-red fluorescent probe for the specific detection of mercury ions in living cells and zebrafish. Analyst. 2019;144(4):1426–1432.
38.
Liu S, Zhang X, Yan C, Zhou P, Zhang L, Li Q, Zhang R, Chen L, Zhang L. A small molecule fluorescent probe for mercury ion analysis in broad low pH range: Spectral, optical mechanism and application studies. J Hazard Mater. 2022;424: Article 127701.
39.
An Y, Li B, Yu Y, Zhou Y, Yi J, Li L, Sun Y, Qiang Z, Liu Y, Wang P. A rapid and specific fluorescent probe based on aggregation-induced emission enhancement for mercury ion detection in living systems. J Hazard Mater. 2024;465: Article 13331.
40.
Li G, Wang J, Li D, Liu S, Yin J, Lai Z, Yang G. A Hg(II)-specific probe for imaging application in living systems and quantitative analysis in environmental/food samples. Chin Chem Lett. 2021;32(4):1527–1531.
41.
Nedjimi B. Phytoremediation: A sustainable environmental technology for heavy metals decontamination. SN Appl Sci. 2021;3(3): Article 286.
42.
Sugimoto K, Meyerowitz EM. Regeneration in Arabidopsis tissue culture. Methods Mol Biol. 2013;959:265–275.
43.
Chen X, Qu Y, Sheng L, Liu J, Huang H, Xu L. A simple method suitable to study de novo root organogenesis. Front Plant Sci. 2014;5: Article 208.
44.
Cheng X, Lang I, Adeniji OS, Griffing L. Plasmolysis-deplasmolysis causes changes in endoplasmic reticulum form, movement, flow, and cytoskeletal association. J Exp Bot. 2017;68(15):4075–4087.
Year 2025 volume 8 Issue 1
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Article Info
doi: 10.34133/research.0570
  • Receive Date:2024-10-26
  • Online Date:2025-07-23
  • Published:2025-01-07
Article Data
Affiliations
History
  • Received:2024-10-26
  • Revised:2024-11-30
  • Accepted:2024-12-13
Funding
National Natural Science Foundation of China(21806048, 22276041)
Advanced Foreign Experts Project(G2023157014L)
Central Government Guides Local Science and Technology Development Fund Projects(Qiankehezhongyindi (2023) 001 and (2024) 007)
Program of Major Scientific and Technological, Guizhou Province, China(Qiankehechengguo (2024) zhongda007)
Cultivating Fund Project of Hubei Hongshan Laboratory(2022hspy002)
Affiliations
    1 State Key Laboratory of Green Pesticide, Key Laboratory of Green Pesticide and Agricultural Bioengineering, Ministry of Education, Center for R&D of Fine Chemicals of Guizhou University, Guiyang 550025, China.
    2 The Key Laboratory of Plant Resources Conservation Germplasm Innovation in Mountainous Region, College of Life Sciences, Institute of Agro-bioengineering, Guizhou University, Guiyang 550025, China.
    3 Hubei Hongshan Laboratory, College of Life Science and Technology, Huazhong Agricultural University, Wuhan, Hubei 430070, China.
    4 National Key Laboratory for Germplasm Innovation and Utilization for Fruit and Vegetable Horticultural Crops, Wuhan, China.
    5 College of Chemistry, Huazhong Agricultural University, Wuhan, Hubei 430070, China.
    6 School of Environmental Science and Engineering, Guangdong University of Petrochemical Technology, Maoming 525000, China.

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* Address correspondence to: (J.L.); (W.-C.Y.); (C.C.)
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表12种不同金属材料的力学参数

Family
属数
Number of
genus
种数
Number of
species
占总种数比例
Percentage of
total species (%)

Genus
种数
Number of
species
占总种数比例
Percentage of total
species (%)
鹅膏菌科Amanitaceae 2 11 5.26 鹅膏菌属 Amanita 10 4.78
小菇科 Mycenaceae 2 12 5.74 丝盖伞属 Inocybe 5 2.39
多孔菌科 Polyporaceae 8 14 6.70 蜡蘑属 Laccaria 5 2.39
红菇科 Russulaceae 3 23 11.00 小皮伞属 Marasmius 6 2.87
小菇属 Mycena 11 5.26
光柄菇属 Pluteus 5 2.39
红菇属 Russula 17 8.13
栓菌属 Trametes 5 2.39
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