Subscriber access provided by READING UNIV
Article
The retention of CdS/ZnS quantum dots (QDs) on the root epidermis of woody plant and its implications by benzo[a]pyrene: Evidences from the in situ synchronous nanosecond time-resolved fluorescence spectra method Ruilong Li, Haifeng Sun, Shaopeng Wang, Yinghui Wang, and Kefu Yu J. Agric. Food Chem., Just Accepted Manuscript • DOI: 10.1021/acs.jafc.7b04258 • Publication Date (Web): 04 Jan 2018 Downloaded from http://pubs.acs.org on January 4, 2018
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Journal of Agricultural and Food Chemistry is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 31
Journal of Agricultural and Food Chemistry
1
The retention of CdS/ZnS quantum dots (QDs) on the root epidermis of woody plant
2
and its implications by benzo[a]pyrene: Evidences from the in situ synchronous
3
nanosecond time-resolved fluorescence spectra method
4 5
Ruilong Li1,2,3, Haifeng Sun4, Shaopeng Wang1,2,3, Yinghui Wang1,2,3*, Kefu Yu1,2,3*
6 7
1
School of Marine Sciences, Guangxi University, Nanning 530004, P.R. China
8
2
Guangxi Laboratory on the Study of Coral Reefs in the South China Sea, Guangxi
9
University, Nanning 530004, P.R. China
10
3
11
China
12
4
13
China
Coral Reef Research Center of China, Guangxi University, Nanning 530004, P.R.
College of Environment and Resource, Shanxi University, Taiyuan 030006, P.R.
14 15 16 17 18 19
*
20
University, Nanning 530004, P.R. China; Coral Reef Research Center of China,
21
Guangxi University, Nanning 530004, P.R. China. E-mail:
[email protected] 22
(Yinghui Wang) and
[email protected] (Kefu Yu)
Corresponding to: Yinghui Wang and Kefu Yu, School of Marine Sciences, Guangxi
1
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
23
Table of Contents Graphic
24
25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 2
ACS Paragon Plus Environment
Page 2 of 31
Page 3 of 31
Journal of Agricultural and Food Chemistry
42
Abstract
43
The retention of CdS/ZnS QDs on the epidermis has been confirmed to be one of
44
core procedures during root uptake process. However, the retention mechanisms of
45
QDs on the epidermis of woody plant were poorly understood for lacking of
46
appropriate QDs quantitative method. In this study, a novel method for in situ
47
determination of CdS/ZnS QDs retained on the root epidermis was established using
48
synchronous nanosecond time-resolved fluorescence spectroscopy. No correlations
49
between Kf values of Oleylamine-CdS/ZnS QDs retained on the epidermal tissues and
50
the surface/bulk composition of mangrove root were observed (p> 0.05) due to the
51
existence of endocytosis mechanisms during the QDs uptake processes. Moreover, the
52
difference of the CdS/ZnS QDs in water and further translocated to xylem/phloem of
53
root rather than the combination with cell wall/membranes were the predominant
54
reason that caused the Kf values follow the sequence of PEG-COOH-CdS/ZnS QDs
A. corniculata
345
(0.41).
41
. These results
C-NMR data showed that the aliphatic carbon component accounted for 52.3 %,
346
It can be clearly seen that there exists no strong correlation between Kf-oc values
347
and the aromatic/aliphatic carbon of the bulk mangrove root with the coefficients (R2)
348
of 0.64/0.03 (table 2). These divergent findings reveal that it is necessary to further
349
probe
the
relationships
of
root
surface
polarity
16
ACS Paragon Plus Environment
and
the
retention
of
Page 17 of 31
Journal of Agricultural and Food Chemistry
42
350
Oleylamine-CdS/ZnS QDs. Fortunately, similar with the retention of PAHs
, the
351
Oleylamine-CdS/ZnS QDs retained on the epidermal tissues of mangrove root
352
ascends with the decreasing of the surface polarity ((N+O)/C) (table 2). However, no
353
strong negatively correlations were found between the (N+O)/C values and Kf-oc
354
values with coefficients (R2) of 0.22 (table 2). These two unexpected results indicated
355
that the existence of other Oleylamine-CdS/ZnS QDs transport or binding with root
356
epidermal tissues mechanisms made the compositions of mangrove root was not the
357
sole determination factor of the retention of Oleylamine-CdS/ZnS QDs.
358
As previously reported showed, no specific interactions including hydrogen
359
bonds and electrostatic attraction were existed between Oleylamine-CdS/ZnS QDs
360
and root cell/menbranes 43. Therefore, the existences of endocytosis, an invagination
361
of the cell membrane for the uptake of extracellular materials (nm), was likely to be
362
the reasons that the reduction of the correlations of Kf and chemical composition of
363
root. To confirm our assumption, the effects of temperature on the retention of
364
Oleylamine-CdS/ZnS QDs on the epidermal tissues were evaluated (figure S4).
365
Results showed that the retention of Oleylamine-CdS/ZnS QDs at 298.15 K were
366
markedly higher than 277.15 K (p< 0.05). Due to the passive apoplastic transport is a
367
non-metabolic, non-energy consuming process, the retention of Oleylamine-CdS/ZnS
368
QDs largely affected by temperature was an indicator that the transportation of this
369
compound including biochemically processes, which, as Kettiger et al pointed out 44,
370
was attributed to the apoplastic transport (refer the ‘‘Apoplastic versus symplastic
371
transport’’ section) or endocytosis.
17
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 18 of 31
372
Another evidence for the presences of endocytosis that affects the retention of
373
QDs on the epidermal tissues of mangrove root come from the images of FLIM
374
instrument,
375
Oleylamine-CdS/ZnS QDs (green, 15-25 ns) and auto-fluorescence signal of root (red
376
to yellow, < 10 ns) separately (Figure S5). In this figure, it can be clearly seen that
377
although the dominant concentrations of Oleylamine-CdS/ZnS QDs located on the
378
cell wall of epidermis, there still existed a small percentage of Oleylamine-CdS/ZnS
379
QDs distributed on the intracellular of roots epidermis. As previously reports shown,
380
the apoplastic transport (refer the ‘‘Apoplastic versus symplastic transport’’ section)
381
or endocytosis were important pathways of neutrally QDs across the plant cell
382
wall/membrane and thus the phenomenon described above reconfirmed our
383
assumption
384
Oleylamine-CdS/ZnS QDs retained on the mangrove root epidermal tissues were
385
highly focused “stream” (aggregated) rather than patchily located in both longitudinal
386
and transverse directions.
which
was
suitable
to
display
the
fluorescence
signal
of
41
. In addition, similar as parent/alkyl/heterocyclic PAHs, the
387 388
3.3.2 The implications of charges of the QDs coating on its retained on the epidermal
389
tissues of mangrove root
390
Similar as Oleylamine-CdS/ZnS QDs, no positive/negative relationships were
391
obtained
between
the
Kf-oc
values
of
PEG-COOH-CdS/ZnS
392
PEG-NH2-CdS/ZnS QDs (Equilibrium time: 5 d) with different coating charges (The
393
zeta potentials of -4.3 mV, -21.6 mV and 17.1 mV for Oleylamine-CdS/ZnS QDs,
18
ACS Paragon Plus Environment
QDs
or
Page 19 of 31
Journal of Agricultural and Food Chemistry
394
PEG-COOH-CdS/ZnS QDs and PEG-NH2-CdS/ZnS QDs, respectively) and
395
aromatic/aliphatic carbon of bulk root/surface polarity with the corresponding
396
coefficients of 0.62/0.54/0.88 and 0.14/0.73/0.01 (table 2). More noteworthy was that
397
the retention of ZnSe/ZnS and PEG-NH2-CdS/ZnS QDs on the epidermal tissues did
398
not ascend with the decreasing of surface polarity of mangrove root. These results
399
indicated that the surface coating charge of CdS/ZnS QDs, aside from the chemical
400
composition of mangrove root, has potential ability to affect the retention of
401
PEG-NH2-CdS/ZnS QDs on the epidermal tissues of mangrove root.
402
As figure 3a showed, the Kf values of PEG- NH2-CdS/ZnS QDs on the epidermal
403
tissues of K. obovata root were 7.4 (ng/spot)/(ng Cd /mg)n, which was a little higher
404
than PEG-COOH-CdS/ZnS QDs (p> 0.05) but much lower than Oleylamine-CdS/ZnS
405
QDs (p< 0.05). Similar results were obtained for A. marina and A. corniculata. Both
406
of the cationic and anionic coating QDs easily dissolved in water and then majority of
407
these kinds of QDs transport to the xylem/phloem tissues through root water and
408
nutrients absorption pathways instead of retaining on the epidermal tissues 45, which
409
leading to the Kf values of cationic and coating QDs much smaller than
410
Oleylamine-CdS/ZnS QDs. Besides, the strong electrostatic attraction of positive
411
charged QDs coating and the negatively charged root cell wall made the retention of
412
PEG-NH2-CdS/ZnS QDs a little higher than PEG-COOH-CdS/ZnS QDs
413
Overall, in this study, multi-factors, including the root composition, endocytosis
414
and surface coating charges of CdS/ZnS QDs, were confirmed to be the factors that
415
affect the retention of CdS/ZnS QDs on the epidermal tissues of mangrove root.
19
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
416 417
3.4 The implications of B[a]P on the retention of CdS/ZnS QDs on the epidermal
418
tissues of mangrove root
419
The implications of PAHs on the retention of PEG-NH2-CdS/ZnS QDs on the
420
epidermal tissues were displayed in figure 3b and 3c. The lower concentrations of
421
B[a]P exposures (100 µg/L) inhibited the retention of PEG-NH2-CdS/ZnS QDs on the
422
epidermal tissues of K. obovata root, with the Kf values decreased to 4.8
423
(ng/spot)/(ng Cd /mg)n at 298.15 K. On the contrary, there existed almost no
424
differences for the retained concentration of Oleylamine-CdS/ZnS QDs and
425
PEG-COOH-CdS/ZnS QDs with and without the presence of B[a]P (p>0.05). Similar
426
results were also obtained for A. marina and A. corniculata. When low concentrations
427
of phenanthrene were presented, Yin et al confirmed that the depolarization of root
428
membrane potential was obvious, and the magnitude of depolarization is in good
429
accordance with the phenanthrene concentration uptake by root 24. Thus, the attractive
430
force between the positively charged PEG-NH2-CdS/ZnS QDs located on the root
431
surface and negatively charged root cell wall and membranes were weakened, which
432
lowers the retention of PEG-NH2-CdS/ZnS QDs on the epidermal tissues of mangrove
433
root. Meanwhile, the other physiological statuses of root did not affected by PAHs and
434
the retained concentrations of Oleylamine-CdS/ZnS QDs and PEG-COOH-CdS/ZnS
435
QDs kept constant.
436
However, it should be noted that the Kf values of PEG-NH2-CdS/ZnS QDs retained
437
on the epidermal tissues decreased to 3.1, 2.5 and 2.0 (ng/spot)/(ng Cd /mg)n for K.
20
ACS Paragon Plus Environment
Page 20 of 31
Page 21 of 31
Journal of Agricultural and Food Chemistry
438
obovata, A. marina and A. corniculata, respectively, while the phenomenon was also
439
an observer for Oleylamine-CdS/ZnS QDs and PEG-COOH-CdS/ZnS QDs at high
440
B[a]P concentrations (500 µg/L, 298.15 K). Despite the depolarization of root
441
membrane potential that inhibited the retention of PEG-NH2-CdS/ZnS QDs, as was
442
reported by Dupuy et al
443
endodermis of woody plant largely increased the possible adsorption sites for
444
Oleylamine-CdS/ZnS QDs and PEG-COOH-CdS/ZnS QDs with the neutrally and
445
negatively charge after 7 d exposure.
25
, the extensive deposition of suberin on exodermis and
446
In this study, the S-NSFS method were established, which detection limits can
447
reach as low as 1.2-2.0 ng/spot for the three kinds of CdS/ZnS QDs, providing a novel
448
approach for sensitive and accurately in situ determination of trace concentration of
449
the CdS/ZnS QDs retained on the epidermal tissues of root. More importantly, our
450
studies firstly confirmed that the retention of CdS/ZnS QDs on the epidermal tissues
451
was determined by multi-factors, which includes the composition of mangrove root,
452
the endocytosis and the charge of the CdS/ZnS QDs coating, and further work showed
453
that this fraction of CdS/ZnS QDs were largely affected by the PAHs in root. Overall,
454
the findings of this work may be helpful in understanding the role of epidermal tissues
455
in the uptake of CdS/ZnS QDs by woody plants.
456 457
Supporting Information
458
The nanosecond time resolved fluorescence spectra of different kinds of QDs at
459
optimal emission wavelength; The NSFS of the Oleylamine-CdS/ZnS QDs retained
21
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
460
on the epidermal tissues of K. obovata root with the presence of B[a]P after filter out
461
< 10 ns fluorescence signal (Figure S2); The rates of QDs retained on the epidermal
462
tissues of mangrove root (Figure S3); The partition coefficients (Kf) of the QDs
463
retained on the epidermal tissue of mangrove root at two different temperatures
464
(Figure S4); The FLIM images of Oleylamine-CdS/ZnS QDs retained on the
465
epidermal tissue of mangrove root (Figure S5); Results of recovery experiment for the
466
CdS/ZnS QDs retained on the epidermal tissues of mangrove root (Table S1);
467
Integration results from
468
Surface functionalities of the epidermal tissue of mangrove root acquired by XPS
469
(Table S3)
13
C-NMR of different kinds of mangrove roots (Table S2);
470 471
Acknowledgments
472
The authors are grateful for financial support from the Natural Science
473
Foundation of China (No. 91428203, No. 21507077, No. 41673105, No. 41273139)
474
and the BaGui Scholars Program Foundation (2014).
475 476
References
477 478 479 480 481 482 483 484 485 486
(1) Wang, P.; Lombi, E.; Zhao, F. J.; Kopittke, P. M. Nanotechnology: A new opportunity in plant sciences. Trends Plant Sci. 2016, 21, 699-712. (2) Jayant, K.; Hirtz, J. J.; Plante, J. L.; Tsai, D. M.; De Boer, W. D. A. M.; Semonche, A.; Peterka, D. S.; Owen, J. S.; Sahin, O.; Shepard, K. L.; Yuste, R. Targeted intracellular voltage recordings from dendritic spines using quantum-dot-coated nanopipettes. Nat. Nanotechnol. 2017, 12, 335-342. (3) Ke, C. S.; Fang, C. C.; Yan, J. Y.; Tseng, P. J.; Pyle, J. R.; Chen, C. P.; Lin, S. Y.; Chen, J.; Zhang, X.; Chan, Y. H. Molecular engineering and design of semiconducting polymer dots with narrow-band, near-infrared emission for in vivo biological imaging. ACS Nano 2017, 11, 3166-3177. (4) Chen, F. P.; Ou, S. Y.; Tang, C. H. Core-shell soy protein-soy polysaccharide complex (nano)particles as carriers for improved stability and sustained release of curcumin. J. Agric. Food
22
ACS Paragon Plus Environment
Page 22 of 31
Page 23 of 31
Journal of Agricultural and Food Chemistry
487 488 489 490 491 492 493 494 495 496 497 498 499 500 501 502 503 504 505 506 507 508 509 510 511 512 513 514 515 516 517 518 519 520 521 522 523 524 525 526 527 528 529 530
Chem. 2016, 64, 5053-5059. (5) Wang, D. Biological effects, translocation, and metabolism of quantum dots in the nematode caenorhabditis elegans. Toxicol. Res. 2016, 5, 1003-1011. (6) Dimkpa, C. O.; White, J. C.; Elmer, W. H.; Gardea-Torresdey, J. Nanoparticle and ionic Zn promote nutrient loading of sorghum grain under low NPK fertilization. J. Agric. Food Chem. 2017, 65, 8552-8559. (7) Goswami, L.; Kim, K. H.; Deep, A.; Das, P.; Bhattacharya, S. S.; Kumar, S.; Adelodun, A. A. Engineered nano particles: Nature, behaviour, and effects on the environment. J. Environ. Manage. 2017, 196, 297-315. (8) Pradhan, S.; Mailapalli, D. R. Interaction of engineered nanoparticles with the agri-environment. J. Agric. Food Chem. 2017, 65, 8279-8294. (9) Silva, B. F.; Andreani, T.; Gavina, A.; Vieira, M. N.; Pereira, C. M.; Rocha-Santos, T.; Pereira, R. Toxicological impact of cadmium-based quantum dots towards aquatic biota: Effect of natural sunlight exposure. Aquat. Toxicol. 2016, 176, 197-207. (10) David Wegner, A.; Hildebrandt, N. Quantum dots: bright and versatile in vitro and in vivo fluorescence imaging biosensors. Chem. Soc. Rev. 2015, 44, 4792-4834. (11) Kwak, J. I.; An Y. J. The current state of the art in research on engineered nanomaterials and terrestrial environments: Different-scale approach. Environ. Res. 2016, 151, 368-382. (12) Zahra, Z.; Waseem, N.; Zahra, R.; Lee, H.; Badshah, M. A.; Mehmood, A.; Choi, H. K.; Arshad, M. Growth and metabolic responses of rice (Oryza sativa L.) cultivated in phosphorus-deficient soil amended with TiO2 nanoparticles. J. Agric. Food Chem. 2017, 65, 5598-5606. (13) Feng, Y.; Cui, X.; He, S.; Dong, G.; Chen, M.; Wang, J.; Lin, X. The role of metal nanoparticles in influencing arbuscular mycorrhizal fungi effects on plant growth. J. Agric. Food Chem. 2013, 47, 9496-9504. (14) Werlin, R.; Priester, J. H.; Mielke, R. E.; Kramer, S.; Jackson, S.; Stoimenov, P. K.; Stucky, G. D.; Cherr, G. N.; Orias, E.; Holden, P. A. Biomagnification of cadmium selenide quantum dots in a simple experimental microbial food chain. Nat. Nanotechnol. 2011, 6, 65-71. (15) Bouldin, J. L.; Ingle, T. M.; Sengupta, A.; Alexander, R.; Hannigan, R. E.; Buchanan, R. A. Aqueous toxicity and food chain transfer of quantum dots in freshwater algae and Ceriodaphnia dubia. Environ. Toxicol. Chem. 2008, 27, 1958-1963. (16) Lee, W. M.; An, Y. J. Evidence of three-level tropic transfer of quantum dots in an aquatic food chain by using bioimaging. Nanotoxicology 2015, 9, 407-412. (17) Al-Salim, N.; Barraclough, E.; Burgess, E.; Clothier, B.; Deurer, M.; Green, S.; Malone, L.; Weir, G. Quantum dot transport in soil, plants, and insects. Sci. Total Environ. 2011, 409, 3237-3248. (18) Das, S.; Wolfson, B. P.; Tetard, L.; Tharkur, J.; Bazata, J.; Santra S. Effect of N-acetyl cysteine coated CdS: Mn/ZnS quantum dots on seed germination and seedlings growth of snow pea (Pisum saativum L.): imaging and spectroscopic studies. Environ. Sci.: Nano 2015, 2, 203-212. (19) Lewis, M.; Pryol, R.; Wilking, L. Fate and effects of anthropogenic chemicals in mangrove ecosystems: a review. Environ. Pollut. 2011, 159, 2328-2346. (20) Lonard, R. I.; Judd, F. W.; Summy, K. R.; DeYoe, H.; Stalter, R. The biological flora of coastal dunes and wetlands: Avicennia germinans (L.) L. J. Coastal Res. 2017, 33, 191-207. (21) Wang, J.; Yang, Y.; Zhu, H.; Braam, J.; Schnoor, J. L.; Alvarez, P. J. J. Uptake, translocation, and transformation of quantum dots with cationic versus anionic coatings by Populus deltoides× nigra Cuttings. Environ. Sci. Technol. 2014, 48, 6754-6762.
23
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
531 532 533 534 535 536 537 538 539 540 541 542 543 544 545 546 547 548 549 550 551 552 553 554 555 556 557 558 559 560 561 562 563 564 565 566 567 568 569 570 571 572 573 574
(22) Koo, Y.; Wang, J.; Zhang, Q.; Zhu, H.; Wassim Chehab, E.; Colvin, V. L.; Alvarez, P. J. J.; Braam, J. Fluorescence reports intact quantum dot uptake into roots and translocation to leaves of Arabidopsis thaliana and subsequent ingestion by insect herbivores. Environ. Sci. Technol. 2015, 49, 626-632. (23) Song, Y.; Bian, Y.; Wang, F.; Xu, M.; Ni, N.; Yang, X.; Gu, C.; Jiang, X. Dynamic effects of biochar on the bacterial community structure in soil contaminanted with polycyclic aromatic hydrocarbons. J. Agric. Food Chem. 2017, 65, 6789-6796. (24) Yin, X.; Liang, X.; Xu, G.; Zhan, X. Effect of phenanthrene uptake on membrane potential in roots of soybean, wheat and carrot. Environ. Exp. Bot. 2014, 99, 53-58. (25) Dupuy, J.; Leglize, P.; Vincent, Q.; Zelko, I.; Mustin, C.; Ouvrard S.; Sterckeman, T. Effect and localization of phenanthrene in maize roots. Chemosphere 2016, 149, 130-136. (26) Moquin, A.; Neibert, K. D.; Maysinger, D.; Winnik, F. M. Quantum dot agglomerates in biological media and their characterization by asymmetrical flow field-flow fractionation. Eur. J. Pharm. Bio. 2015, 89, 290-299. (27) Sousa, J. C. L.; Vivas, M. G.; Ferrari, J. L.; Mendonca, C. R.; Schiavon, M. A. Determination of particle size distribution of water soluble CdTe quantum dots by optical spectroscopy. RSC Adv. 2014, 4, 36024-36030. (28) Lewinski, N. A.; Zhu, H.; Jo, J. H.; Pham, D.; Kamath, R. R.; Ouyang, C. R.; Vulpe, C. D.; Colvin, V. L.; Drezek, R. A. Quantification of water solubilised CdSe/ZnS quantum dots in Daphnia magna. Environ. Sci. Technol. 2010, 44, 1841-1846. (29) Subbaiah, L. V.; Prasad. T. N. V. K. V.; Krishna, T. G.; Sudhakar, P.; Reddy, B. R.; Pradeep, T. Novel effects of nanoparticulate delivery of zinc on growth, productivity, and zinc biofertification in maize (Zea mays L.). J. Agric. Food Chem. 2016, 64, 3778-3788. (30) Rocha, T. L.; Mestre, N. C.; Saboia-Morais, M. T.; Bebianno, M. J. Environmental behaviour and ecotoxicity of quantum dots at various tropic levels: A review. Environ. Int. 2017, 98, 1-17. (31) Patra, D.; Mishra, A. K. Recent developments in multi-component synchronous fluorescence scan analysis. Trends Anal. Chem. 2002, 21, 787-798. (32) Patra, D.; Ghaddar, T. H. Application of synchronous fluorescence scan spectroscopy for size dependent simultaneous analysis of CdTe nanocrystals and their mixtures. Talanta 2009, 77, 1549-1554. (33) Tan, H. D.; Li, R. L.; Zhu, Y. X.; Zhang, Y. In situ quantitative and visual investigation of the retention of polycyclic aromatic hydrocarbons on the root surface of Kandelia obovata using a microscopic fluorescence spectral analysis method. Talanta 2017, 167, 86-93. (34) Li, R. L.; Zhu, Y. X.; Zhang, Y. In situ investigation of the mechanisms of the transport to tissues of polycyclic aromatic hydrocarbons adsorbed onto the root surface of Kandelia obvata seedlings. Environ. Pollut. 2015, 201, 100-106. (35) Qi, X. P.; Wickham, E. D.; Garcia, R. A. Structural and thermal stability of β-lactoglobulin as a result of interacting with sugar beet pectin. J. Agric. Food Chem. 2014, 62, 7567-7576. (36) Badoni, A.; Chauhan J. S. In vitro sterilization protocol for micropropagation of solanum tuberosum cv. ‘Kufri Himalini’. Academia Arena, 2010, 2(4): 24-27. (37) Peters, R. J. B.; Bemmel, G. V.; Herrera-Rivera, Z.; Helsper, H. P. F. G.; Marvin, H. J. P.; Weigel, S.; Tromp, P. C.; Oomen, A. G.; Rietveld, A. G.; Bouwmeester, H. Characterization of titanium dioxide nanoparticles in food products: analytical methods to define nanoparticles. J. Agric. Food Chem. 2014, 62, 6285-6293. (38) Subashchandrabose, S. R.; Krishnan, K.; Gratton, E.; Megharaj, M.; Naidu, R. Potential of
24
ACS Paragon Plus Environment
Page 24 of 31
Page 25 of 31
Journal of Agricultural and Food Chemistry
575 576 577 578 579 580 581 582 583 584 585 586 587 588 589 590 591 592 593 594 595 596 597 598 599 600 601 602 603
fluorescence imaging techniques to monitor mutagenic PAH uptake by microalga. Environ. Sci. Technol. 2014, 48, 9152-9160. (39) Zhang, Z. X.; Zhu, Y. X.; Zhang, Y. Simultaneous determination of 9-ethylphenanthrene, pyrene and 1-hydroxypyrene in an aqueous solution by synchronous fluorimetry using the double scans method and hydroxyl-propyl-beta-cyclodextrin as a sensitizer. Talanta 2015, 144, 836-843. (40) Li, W.; Zhang, Y.; Zhang, H.; Liu, Z.; Su, W.; Chen, S.; Liu, Y.; Zhuang, J.; Lei, B. Phytotoxicity, uptake, and translocation of fluorescent carbon dots in mung bean plants. ACS Appl. Mater. Inter. 2016, 8, 19939-19945. (41) Schwab, F.; Zhai, G.; Kern, M.; Turner, A.; Schnoor, J. L.; Wiesner, M. R. Barriers, pathways and processes for uptake, translocation and accumulation of nanomaterials in plants-Critical review. Nanotoxicology 2016, 10, 257-278. (42) Li, R. L.; Tan, H. D.; Zhu, Y. X.; Zhang, Y. The retention and distribution of parent, alkylated, and N/O/S-containing polycyclic aromatic hydrocarbons on the epidermal tissue of mangrove seedlings. Envion. Pollut. 2017, 226, 135-142. (43) Etxeberria, E.; Gonzalez, P.; Baroja-Fernandez, E.; Romero, J. P. Fluid phase endocytic uptake of artificial nano-spheres and fluorescent quantum dots by sycamore cultured cells: evidence for the distribution of solutes to different intracellular compartments. Plant Signaling Behav. 2006, 1, 196-200. (44) Kettiger, H.; Schipanski, A.; Wick, P.; Huwyler, J. Engineered nanomaterial uptake and tissue distribution; from cell to organism. Int. J. Nanomed. 2013, 8, 3255-3269. (45) Zhang, D.; Hua, T.; Xiao, F.; Chen, C.; Gersberg, R. M.; Liu, Y.; Ng, W. J.; Tan, S. K. Uptake and accumulation of CuO nanoparticles and CdS/ZnS quantum dot nanoparticles by Schoenoplectus taabernaemontani in hydroponic mesocosms. Ecol. Eng. 2014, 70, 114-123.
25
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
(a)
(b)
Fig. 1 The emission fluorescence spectra of 100 ng/spot Oleylamine-CdS/ZnS QDs on the epidermal tissues of mangrove root with (a) and without (b) filter the short lifetime auto-fluorescence signal (< 10 ns).
26
ACS Paragon Plus Environment
Page 26 of 31
Page 27 of 31
Journal of Agricultural and Food Chemistry
5
1
Fig. 2. The S-NSFS of the Oleylamine-CdS/ZnS QDs retained on the epidermal tissues of K. obovata root with the presence of B[a]P after filters out the short-lived fluorescence signals (< 10 ns). Concentrations of Oleylamine-CdS/ZnS QDs adsorbed from 1-5 were 100, 200, 300, 400 and 550 ng/spot, respectively.
27
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
(a)
(b)
(c)
Fig. 3. The partition coefficients (Kf) of the CdS/ZnS QDs retained on the epidermal tissue of mangrove root (a) without B[a]P and (b) 100 µg/L B[a]P (c) 500 µg/L B[a]P.
28
ACS Paragon Plus Environment
Page 28 of 31
Page 29 of 31
Journal of Agricultural and Food Chemistry
Table 1. Analytical merits of the established method. Detection limita
Linear range Mangrove
QDs
Calibration curve
Correlation coefficient (ng/spot)
K. obovata
A. marina
A. corniculata
a
(ng/spot)
Oleylamine-CdS/ZnS
yb=9.2xc+127
15.5-2100
0.9826
1.5
PEG-COOH-CdS/ZnS
y=20.3x+101
21.0-3310
0.9711
1.2
PEG-NH2-CdS/ZnS
y=12.1x+203
34.5-1970
0.9909
2.0
Oleylamine-CdS/ZnS
y=14.7x+314
20.0-2700
0.9940
1.1
PEG-COOH-CdS/ZnS
y=22.6x+148
35.5-1700
0.9832
1.3
PEG-NH2-CdS/ZnS
y=15.5x+262
40.0-1260
0.9917
1.7
Oleylamine-CdS/ZnS
y=18.4x+186
15.5-4200
0.9944
1.5
PEG-COOH-CdS/ZnS
y=14.2x+210
28.5-1460
0.9809
1.8
PEG-NH2-CdS/ZnS
y=15.3x+226
36.0-2410
0.9922
1.6
detection limit of the method, which was calculated by 3SB/m, where ‘SB’ is the standard deviation of the blank, and ‘m’ is the slope of the calibration curve; b y
represents the S-NSFS intensity of CdS/ZnS QDs adsorbed onto the epidermal tissue of mangrove root. c x represents the concentrations of CdS/ZnS QDs adsorbed onto the epidermal tissue of mangrove root.
29
ACS Paragon Plus Environment
Journal of Agricultural and Food Chemistry
Page 30 of 31
Table 2 The correlation coefficients between the retained concentration of QDs and surface (O+N)/C or bulk compositions (aromatic carbon and aliphatic carbon) of mangrove root. QDs
Oleylamine-CdS/ZnS
PEG-COOH-CdS/ZnS
PEG-NH2-CdS/ZnS
a
Mangrove
Kf-oca
K. obovata
72.2
A. marina
74.5
A. corniculata
118.3
K. obovata
35.3
A. marina
24.1
A. corniculata
31.9
K. obovata
31.2
A. marina
23.9
A. corniculata
31.7
Fitting equation (S) b
R(S)2
Fitting equation (B) c
R(B)2
Fitting equation (A) d
R(A)2
ye=-0.0063xf+0.2859
0.22
y=-0.7117x+44.892
0.64
y=-0.0537x+55.844
0.03
y=-0.0023x+0.6803
0.62
y=-0.1451x+36.073
0.54
y=0.0712x+47.809
0.88
y=0.0075x+0.2659
0.14
y=-1.1383x+55.408
0.73
y=-0.0323x+55.013
0.01
Mean value of Kf-oc of six measurements, the units of Kf-oc was (ng/spot)/(ng Cd /mg)n; b Fitting equation (S) and R(S) represent the fitting equations and correlation
coefficient between Kf-oc value of CdS/ZnS QDs. and surface (O+N)/C, respectively; c Fitting equation (B) and R(B) represent the fitting equations and correlation coefficient between Kf-oc value of CdS/ZnS QDs. and aromatic carbon content of bulk root, respectively d Fitting equation (A) and R(A) represent the fitting equations
30
ACS Paragon Plus Environment
Page 31 of 31
Journal of Agricultural and Food Chemistry
and correlation coefficient between Kf-oc value of QDs. and aliphatic carbon content of bulk root, respectively; e y represents the value of surface polarity ((O+N)/C), bulk aromatic carbon or aliphatic carbon content of epidermal tissue of mangrove root; f x represents the Kf-oc value of QDs.
31
ACS Paragon Plus Environment