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. 2022 Aug 24;11(17):2193. doi: 10.3390/plants11172193

Effects of Zinc, Copper and Iron Oxide Nanoparticles on Induced DNA Methylation, Genomic Instability and LTR Retrotransposon Polymorphism in Wheat (Triticum aestivum L.)

Kamil Haliloğlu 1,2, Aras Türkoğlu 3,*, Özge Balpınar 4, Hayrunnisa Nadaroğlu 5,6, Azize Alaylı 7, Peter Poczai 8,9,*
Editor: Igor G Loskutov
PMCID: PMC9460560  PMID: 36079574

Abstract

Nanomaterials with unique and diverse physico-chemical properties are used in plant science since they improve plant growth and development and offer protection against biotic and abiotic stressors. Previous studies have explored the effects of such nanomaterials on different plant mechanisms, but information about the effects of nanomaterials on induced DNA methylation, genomic instability and LTR retrotransposon polymorphism in wheat is lacking. Therefore, the present study highlights the key role of nanoparticles in DNA methylation and polymorphism in wheat by investigating the effects of ZnO, CuO and γ-Fe3O4 nanoparticles (NPs) on mature embryo cultures of wheat (Triticum aestivum L.). Nanoparticles were supplemented with Murashige and Skoog (MS) basal medium at normal (1X), double (2X) and triple (3X) concentrations. The findings revealed different responses to the polymorphism rate depending on the nanoparticle type and concentration. Genomic template stability (GTS) values were used to compare the changes encountered in iPBS profiles. ZnO, CuO and γ-Fe3O4 NPs increased the polymorphism rate and cytosine methylation compared to the positive control while reducing GTS values. Moreover, non-γ-Fe3O4 NPs treatments and 2X ZnO and CuO NP treatments yielded higher polymorphism percentages in both MspI- and HpaII-digested CRED-iPBS assays and were thus classified as hypermethylation when the average polymorphism percentage for MspI digestion was considered. On the other hand, the 3X concentrations of all nanoparticles decreased HpaII and MspI polymorphism percentages and were thus classified as hypomethylation. The findings revealed that MS medium supplemented with nanoparticles had epigenetic and genotoxic effects.

Keywords: DNA methylation, genomic instability, in vitro, nanoparticles, retrotransposons, wheat

1. Introduction

Materials with sizes of 1–100 nanometers are known as nanomaterials. The supplementation of such nanomaterials into different substances such as fertilizers and plant nutrients may improve the quality-related traits of these substances. Indeed, studies have revealed the effects of nanoparticle-containing nutrients on plant growth and development [1,2]. Since nano-sized structures are more effective than bulk materials, nutrients containing nanomaterials may have much more toxic or beneficial effects on plants [3]. For example, Zhang et al. [4] investigated the effects of many nanoparticle structures, including gold (Au), copper (Cu), Zinc (Zn), aluminum (Al), titanium oxide (TiO2), zinc oxide (ZnO), copper oxide (CuO) and silver (Ag), on plants. However, previous studies mainly focused on product development, protection and fertilization.

Wheat (Triticum aestivum L.) has an essential role in world nutrition. Notably, stress factors significantly influence wheat plants; serious quality and yield losses are encountered under stress conditions. As such, biotic and abiotic stressors result in changes in wheat DNA [5,6]. Nanotechnological applications may have either stress-related negative effects or very effective beneficial effects on wheat yield. Therefore, it is thought that nanotechnology has tremendous potential to positively affect yield factors [7]. Accordingly, the effects of nanoparticles on plants have been the primary focus of many research projects in recent years. According to [8,9], nanoparticles enter plant cells and leaves and can also transport DNA and chemicals into plant cells. The majority of studies on NPs to date concern toxicity. Recently, several studies have shown that heavy metals, such as Cd, Pb, Co, Ni and Zn, cause changes in DNA methylation [10]. However, less is known about the effects of their respective nanoparticles on the induction of specific gene mutations in plants and DNA methylation changes. It is crucial to determine the effect of nanomaterials on plant genetic stability, especially in this period when the use of nanomaterials in plant fertilizers is becoming more and more widespread [11]. Hence, the current study is among the first to explore the alteration of DNA methylation caused by nanoparticles in plants.

By expressing stress-related genes, plants express their responses to environmental stimuli and stress factors. Another parameter as effective as transcription factors in regulating gene expression is epigenetics, which refers to “heritable and reversible changes in gene expression without alterations of underlying DNA sequence” [12]. Gene expression is regulated by three epigenetic mechanisms: DNA methylation, histone modification and miRNA. Observing epigenetic changes can control many vital processes in plants, from growth development to flowering. Therefore, DNA methylation has become one of the most popular epigenetic phenomena [13,14].

DNA hyper/hypomethylation is largely correlated with gene expression, cell differentiation and phylogenetic development. DNA methylation is also correlated with several biological processes, including the transcriptional silencing of genes and transposable inactivation of transposons [15]. DNA methylation, microRNA (miRNA) and retrotransposon activities may also alter gene expression profiles and ultimately result in genomic instability [10]. Various techniques, including DArTseqMet [16], semiquantitative MSAP [17], methylRAD [18], methyl-seq [19] and a variant of MSAP [19], have recently been used to detect DNA methylation. Methylation-sensitive amplified fragment length polymorphism (metAFLP) is also used to analyze the changes in DNA methylation [20]. Several other techniques or methods, including HPLC, the bisulfites method, methylation-specific PCR (MSP), the sequencing of specific genes, AFLP, MSAP, coupled restriction enzyme digestion–random amplification (CRED-RA) [21] and coupled restriction enzyme digestion–inter-primer binding site (CRED-iPBS) [22], have also been used to detect DNA methylation changes. The CRED-iPBS method employs the methylation-sensitive enzymes HpaII and MspI to detect methylation changes [23].

There are limited studies on nanomaterial-induced epigenetic changes in plant DNA. This study aimed to determine whether there were epigenetic changes in the DNA of wheat that were previously developed in a medium containing nanoparticles [24]. It is thought that this study will contribute to the literature in determining the effects of nanoparticles on DNA methylation changes in wheat. The study basically measured the genomic instability of wheat against nanomaterials. The main purpose of this research was to observe how wheat would respond genetically to the nanotechnological effects that it may be exposed to in the future, due to the increasing use of nanofertilizers. Therefore, the aim of this study was to determine the effects of nanoparticles on methylation and epigenetic changes encountered in wheat DNA using the CRED-iPBS method. It was hypothesized that the high reactivity of nanoparticles could lead to epigenetic changes in wheat DNA.

2. Results

2.1. Characterization of Nanoparticles

ZnO, CuO and γ-Fe3O4 nanoparticles synthesized by green synthesis were characterized by SEM, XRD and FTIR. ZnO, CuO and γ-Fe3O4 nanoparticles were synthesized at 30 °C, 25 °C and 20 °C, respectively. The analyses revealed that ZnO, CuO and γ-Fe3O4 nanoparticles had varying sizes of 60–80 nm, 5–120 nm and 30–80 nm, respectively. The reason for the broad size ranges of nanoparticles is the adhesion of tiny metallic nanomaterials synthesized by green synthesis. This situation is why small nanoparticles may appear larger [25]. According to the XRD analysis findings, it was determined that CuO nanoparticles were in face-centered cubic form, γ-Fe3O4 nanoparticles were spherical and ZnO nanoparticles were in hexagonal crystal from Nadaroğlu et al. [26]. The article presents data associated with the characterization (SEM, XRD and FT-IR) of relevant nanomaterials by Nalci et al. [24].

2.2. iPBS Analysis

In total, 20 oligonucleotide primers with approximately 50–70% GC content were used to analyze the PCR products of the T. aestivum Kirik genome, but only 10 provided specific and stable results. Compared to the PCR products obtained from the control DNA, nanoparticle treatments resulted in apparent changes in the iPBS patterns.

As shown in Table 1, a total of 67 bands was seen in the control treatment; the highest number of bands was seen in iPBS-2382 (nine bands), while the lowest number of bands was observed in iPBS-2387 and iPBS-2392 (six bands). The molecular sizes of polymorphic bands ranged from 100 (iPBS-2385) to 850 (iPBS-2382) bp. These changes were characterized by a variation in band intensity, the loss of regular bands or the appearance of new bands (as shown in Table 1 and Figure 1). There were significant differences in the iPBS profiles of the control and nanoparticle treatments. Compared to the control, 115 new bands appeared, while 106 bands were not present in the experimental groups.

Table 1.

Molecular sizes (bp) of present/absent bands in iPBS profiles under different nanoparticle treatments.

Primer * +/− ** Control *** Experimental Groups
ZnO NPs CuO NPs γ-Fe3O4 NPs
0 a 1X a 2X b 3X c 0 b 1X b 2X b 3X b 0 c 1X c 2X c 3X c
iPBS 2382 + 9 627; 166 239 850; 520 - 458 - 560; 265 - 625; 300 580 750; 536 625; 245
605 287 485 698 308 146 335 420 352 - 485; 146 335
iPBS 2383 + 6 430; 307 440; 207 520 330; 207 - - 610 327 188 350 - 218
- 350 400; 258 350 515; 285 400 258 515; 400 651 285 651 400
iPBS 2384 + 7 608 670; 505 682; 426 285 300 300 483; 322 584 480; 265 185 465 -
- 359 315; 105 - 655; 250 - - 359 450 550; 450 315; 105 655
iPBS 2385 + 8 397 - 100 274 350 - - 428; 125 385 - - 505
- 305; 158 571; 409 - - 550; 350 675 - 450; 158 158 - -
iPBS 2386 + 6 524 440 350; 205 450 287 405 620 355 - - 450; 366 -
352 - 600 - - 750 450 - 450; 305;205 450; 205 600 -
iPBS 2387 + 5 650 392 - 450; 205 - 650; 258 715 115 320 - 452 502
560; 367 - 367; 239 600 239 - - 367 560; 153 239 285 153
iPBS 2388 + 6 - 342 467 565; 295 487 378 350; 258 405 - 482 489; 326 -
221 285 362 160 160 - 221; 160 - 450 650; 362 285 362
iPBS 2389 + 8 118 - 404 - 858; 465 157 248 - 580 571 535; 228 776
- 450 - 285 550 360 - 517 600; 350; 140 - - -
iPBS 2390 + 7 657 267 - - - 850; 609 615 - 305; 127 422 - 115
632; 362 - 605 495 362 405 - - - - 605 503
iPBS 2391 + 5 547 620; 552 - 507 - 535 310; 539 618; 250 778 - - 250
- 450 350 350 650; 407 - 350 - - 209; 450 - -
Total band 67 17 19 23 17 18 16 20 15 25 17 19 14
Polymorphism (%) 25.37 28.35 34.32 25.37 26.86 23.88 29.85 22.38 37.31 25.37 28.35 20.89
GTS value 74.62 71.64 65.67 74.62 73.13 76.11 70.14 77.61 62.68 74.62 71.64 79.10

*, ** and ***, appearance of a new band, disappearance of a normal band and without hormone, respectively; 0 a, MS medium containing 0X ZnO NPs; 1X a, MS medium containing 1X ZnO NPs; 2X a, MS medium containing 2X ZnO NPs; 3X a, MS medium containing 3X ZnO NPs; 0 b, MS medium containing 0X CuO NPs; 1X b, MS medium containing 1X CuO NPs; 2X b, MS medium containing 2X CuO NPs; 3X b, MS medium containing 3X CuO NPs; 0 c, MS medium containing 0X γ-Fe3O4 NPs; 1X c, MS medium containing 1X γ-Fe3O4 NPs; 2X c, MS medium containing 2X γ-Fe3O4 NPs; 3X c, MS medium containing 3X γ-Fe3O4 NPs.

Figure 1.

Figure 1

iPBS profiles for various experimental groups with 2391 primers in wheat. M, 100–1000 bp DNA ladder; 1, control; 2, MS medium containing 0X ZnO NPs; 3, MS medium containing 1X ZnO NPs; 4, MS medium containing 2X ZnO NPs; 5, MS medium containing 3X ZnO NPs; 6, MS medium containing 0X CuO NPs; 7, MS medium containing 1X CuO NPs; 8, MS medium containing 2X CuO NPs; 9, MS medium containing 3X CuO NPs; 10, MS medium containing 0X γ-Fe3O4 NPs; 11, MS medium containing 1X γ-Fe3O4 NPs; 12, MS medium containing 2X γ-Fe3O4 NPs; 13, MS medium containing 3X γ-Fe3O4 NPs.

Each nanoparticle with different concentrations yielded a different response to the polymorphism rate, and decreasing polymorphism rates were seen with increasing nanoparticle concentrations of the MS medium. Polymorphism rates were respectively measured as 25.37%, 28.35%, 34.32% and 25.37% for 0, 1X, 2X and 3X ZnO treatments; as 26.86%, 23.88%, 29.85% and 22.38 % for 0, 1X, 2X and 3X CuO treatments and as 37.31%, 25.37%, 28.34% and 2.89% for 0, 1X, 2X and 3X γ-Fe3O4 treatments.

GTS was used to compare the changes in iPBS profiles. The present findings revealed that ZnO, CuO and γ-Fe3O4 nanoparticle treatments at different concentrations yielded different responses to GTS values. GTS values were determined respectively as 74.62%, 71.64%, 65.67% and 74.62% for 0, 1X, 2X and 3X ZnO treatments; as 73.13%, 76.11%, 70.14% and 77.61% for 0, 1X, 2X and 3X CuO treatments and as 60.68%, 74.62%, 71.64% and 79.10% for 0, 1X, 2X and 3X γ-Fe3O4 treatments. The results strongly showed that the application of all nanoparticles with 3X concentration (particularly γ-Fe3O4 nanoparticle) enhanced GTS values under the tissue culture approach (Table 1).

2.3. CRED-iPBS Analysis

Among the 20 iPBS primers, 10 produced specific and stable bands and were used in CRED-iPBS analysis (Table 2). CRED-iPBS analysis enabled the observation of any possible cytosine methylations caused by non-γ-Fe3O4 treatments. Enhancement was also seen in cytosine methylation with CuO treatments. The results of the CRED-iPBS analysis as the average polymorphism percentages in terms of HpaII and MspI digestions are provided in Table 2. In total, 69 and 67 bands were observed in the MspI- and HpaII-digested control treatments, respectively. According to the results of the CRED-iPBS pattern, the MspI polymorphism percentage was higher than the HpaII polymorphism percentage in all nanoparticle treatments. There were apparent differences in the MspI polymorphism percentages of the experimental groups. Significantly higher polymorphism rates were observed in the control treatments. The present findings revealed that ZnO, CuO and γ-Fe3O4 nanoparticle treatments at different concentrations yielded different responses for the polymorphism percentages of MspI and HpaII digestion.

Table 2.

Results of CRED-iPBS analysis; the molecular size of bands and polymorphism percentages.

Primer M */H ** + ***/− **** Control ***** Experimental Groups
ZnO NPs CuO NPs γ-Fe3O4 NPs
0 a 1X a 2X b 3X c 0 b 1X b 2X b 3X b 0 c 1X c 2X c 3X c
iPBS 2382 M + 8 658; 434 420; 156 590; 660 645 450 660; 450; 305 - 785; 475; 325; 120 - 650; 450 -
- 600 250; 165 - - 250 - 485; 375 298 205 165 345
H + 6 575 497 320; 139 365 335 150; 216 685; 455 - 168; 102 605 335
415 305 - - 180 - - 350 254; 128 - 128 -
iPBS 2383 M + 5 754; 515 555;450 550; 362; 125 538 360 780 785; 650 375 - 605; 515 785 645; 360
- 245 405; 350 - - - - - 350; 245; 165 - 525 -
H + 4 - 450; 325 667; 240 - 455; 300 409; 125 600 - 480 170 - -
405 - - 405 - - 395 540 305 155 305; 155 305
iPBS 2384 M + 7 - 604; 425 475; 282 378 655; 509; 430 - 708; 506 - 360; 270; 235 - 505; 337; 125 475; 345
390; 240 450 350 - - 625; 120 - 390 350; 205 450; 120 - -
H + 6 285 - 125 465 495 - - 275 760; 605; 375 260 550 262
- 350 425; 350 - 250 165 450 450 165 568; 425 425; 350 -
iPBS 2385 M + 11 450 808; 745; 625 350; 128 825; 486 - 760; 456 785; 345 625 458; 325; 124 - 850; 650; 485; 120 625
340 - 785 - 325; 410 325 440 - 705; 650 605 - -
H + 10 - 695 374; 125 560; 393 260 - 755; 550; 469 745 710; 650 330; 280 355 -
425 525; 365 - - 300; 170 751; 636, 225 - 225 345 - 450; 345 525
iPBS 2386 M + 4 340; 115 - 405; 300 807; 485 300; 220 - 615; 430 405 345; 262 600 565; 450 475
- 255; 458 654 - 458; 355 355 - - 255 - -
H + 8 - - 505; 118 715 450 650 685 - 600; 450 605 655 305
525 400; 225 150 605; 150 360; 320 - - 225; 150 375; 225 400; 320 -
iPBS 2387 M + 3 285 - 605 - 425 785; 250 - - 680; 510 670; 466 485 689
185 185 - 650; 580 580 - 650; 185 580; 185 - 580 650 -
H + 9 - 420;285 605; 225 450 500 - 550 780 450; 245;125 - 885; 745; 600 -
850; 405; 365 405;160 - 715 125 365 365; 125 160 345; 205 125 - 550; 205
iPBS 2388 M + 7 450; 226 250; 115 510; 258 388 520; 450 487 650; 255; 125 425 360; 220 - 655; 505 650
- - 405; 100 - - - - - 185; 100 575; 345 405 -
H + 8 250 397; 285 440; 338; 112 746; 350; 119 380 455; 350 580; 375; 120 - 498 624 404; 348 -
535; 453 308 - - - - 405 355; 105 500; 462 - - 500
iPBS 2389 M + 11 375; 198 785; 625; 320 625; 405 550 680; 465; 345 460; 128 645; 460; 355 - 605; 485; 325 652 496; 320 128
- 490 - - - - 105 447 - 520
H + 8 285; 159 153 750; 418 - 785; 560; 245 - 424; 335 - 450; 355; 265 600; 505; 485 525 -
255 350; 228 402; 350 228;125 450 350 320 350 255; 125 - 350 320
iPBS 2390 M + 5 490; 350 485; 309 365; 263 785; 460; 340 - 750 464; 128 - 560; 258 365 775 -
- 180 450; 180 - 654; 350 - 450 350; 180 350;180 - - 245
H + 4 365 - 582; 278; 145 525;410 669; 285 680; 490 325 - 458 635 - 605
125 600;450 - - - 125 600 345 125 600; 450 125
iPBS 2391 M + 8 - 850; 290;185 758; 800; 450 750; 450 800; 285 810; 450 456; 378 830 805; 753; 385 800 850; 450 750; 330
400 - 350; 200 - 705; 200 - - 555 315; 200 645 - 495
H + 4 350; 200 550; 360 - - 346 - 345 775; 555 390 650 350
- 300 490; 245 490; 300 245 - 245 - 605 - - -
Polymorphism % M 32.77 41.34 50.88 31.50 35.60 29.50 43.01 24.84 57.96 32.28 37.94 23.85
H 30.58 39.94 42.56 30.06 34.39 26.61 33.83 22.97 49.81 30.19 35.92 21.31

*, *, ***, **** and *****, M—Msp I, H—Hpa II, appearance of a new band, disappearance of a normal band and without hormone, respectively. 0 a, MS medium containing 0X ZnO NPs; 1X a, MS medium containing 1X ZnO NPs; 2X a, MS medium containing 2X ZnO NPs; 3X a, MS medium containing 3X ZnO NPs; 0 b, MS medium containing 0X CuO NPs; 1X b, MS medium containing 1X CuO NPs; 2X b, MS medium containing 2X CuO NPs; 3X b, MS medium containing 3X CuO NPs; 0 c, MS medium containing 0X γ-Fe3O4 NPs; 1X c, MS medium containing 1X γ-Fe3O4 NPs; 2X c, MS medium containing 2X γ-Fe3O4 NPs; 3X c, MS medium containing 3X γ-Fe3O4 NPs.

For MspI digestion, polymorphism percentages were respectively determined as 32.77%, 41.34%, 50.88% and 31.50% for 0, 1X, 2X and 3X ZnO treatments, as 35.60%, 29.50%, 43.01% and 24.84% for 0, 1X, 2X and 3X CuO NPs treatments and as 57.96%, 32.28%, 37.94%% and 23.85% for 0, 1X, 2X and 3X γ-Fe3O4 NPs treatments. There was a clear increase in polymorphism percentage from 0X to 2X in ZnO NPs treatments but a decrease from 2X to 3X in ZnO NPs treatments. With CuO NPs treatments, a decrease was seen in polymorphism percentage from 0X to 1X, an increase from 1X to 2X and a decrease from 2X to 3X. With γ-Fe3O4 NPs, a decrease was seen in polymorphism percentage from 0X to 1X, an increase from 1X to 2X and again a decrease from 2X to 3X (Table 2). For HpaII digestion, polymorphism percentages were respectively determined as 30.58%, 39.94%, 42.59% and 30.06% for 0, 1X, 2X and 3X ZnO NPs treatments, as 34.39%, 26.61%, 33.83% and 22.97% for 0, 1X, 2X and 3X CuO treatments and as 49.81%, 30.19%, 35.92% and 21.31% for 0, 1X, 2X and 3X γ-Fe3O4 NPs treatments (Table 2).

In general, it was found that the non-γ-Fe3O4 NPs treatment yielded a higher polymorphism percentage in both MspI- and HpaII-digested CRED-iPBS assays (57.96% and 49.81%, respectively). On the contrary, the application of 3X treatments of all nanoparticles decreased both HpaII and MspI polymorphism percentages. In other words, the 2X treatments of ZnO and CuO NPs had an impact on cytosine methylation status and thus could be classified as hypermethylation when the average polymorphism percentage for MspI digestion was taken into consideration. On the other hand, 3X treatments resulted in an apparent decrease in average polymorphism percentages and impacted methylation status, thus classified as hypomethylation (Table 2 and Figure 2).

Figure 2.

Figure 2

CRED-iPBS profiles for various experimental groups with iPBS 2391 primers in wheat. M, 100–1000 bp DNA ladder; 1, control Msp I; 2, control Hpa II; 3, MS medium supplemented with 0X ZnO NPs Msp I; 4, MS medium supplemented with 0X ZnO NPs Hpa II; 5, MS medium supplemented with 1X ZnO NPs Msp I; 6, MS medium supplemented with 1X ZnO NPs Hpa II; 7, MS medium supplemented with 2X ZnO NPs Msp I; 8, MS medium supplemented with 2X ZnO NPs Hpa II; 9, MS medium supplemented with 3X ZnO NPs Msp I; 10, MS medium supplemented with 3X ZnO NPs Hpa II; 11, MS medium supplemented with 0X CuO NPs Msp I; 12, MS medium supplemented with 0X CuO NPs Hpa II; 13, MS medium supplemented with 1X CuO NPs Msp I; 14, MS medium supplemented with 1X CuO NPs Hpa II; 15, MS medium supplemented with 2X CuO NPs Msp I; 16, MS medium supplemented with 2X CuO NPs Hpa II; 17, MS medium supplemented with 3X CuO NPs Msp I; 18, MS medium supplemented with 3X CuO NPs Hpa II; 19, MS medium supplemented with 0X γ-Fe3O4 NPs Msp I; 20, MS medium supplemented with 0X γ-Fe3O4 NPs Hpa II; 21, MS medium supplemented with 1X γ-Fe3O4 NPs Msp I; 22, MS medium supplemented with 1X γ-Fe3O4 NPs Hpa II; 23, MS medium supplemented with 2X γ-Fe3O4 NPs Msp I; 24, MS medium supplemented with 2X γ-Fe3O4 NPs Msp I; 25, MS medium supplemented with 3X γ-Fe3O4 NPs Hpa II; 26, MS medium supplemented with 3X γ-Fe3O4 NPs Msp I.

3. Discussion

Nanotechnology has improved plant genetics through special nanoparticles (materials with dimensions between 1 and 100 nm), thus enhancing agricultural productivity [27] as growth-promoting nanoparticles may increase yield and quality traits [28]. Compared to bulk materials, nanoparticles of the same material have novel and improved physico-chemical and biological characteristics [29]. According to Nadaroglu et al. [29], nanoparticles at appropriate doses could improve seed germination and plant growth and development, increase yield levels, reduce soil pollution and protect plants against biotic and abiotic stressors. However, there are a limited number of studies on the effects of nanoparticles on induced-DNA methylation, genomic instability and LTR retrotransposon polymorphism. The present findings revealed that different concentrations (0, 1X, 2X and 3X) of ZnO, CuO and γ-Fe3O4 NPs had a significant role in wheat’s DNA methylation and genomic instability. Micronutrients are essential for plant growth and development; many are involved in catalytic redox reactions. In this study, inter-primer binding site (iPBS) retrotransposon and CRED-iPBS (coupled restriction enzyme digestion-iPBS) techniques were used to define the DNA damage levels and changes in DNA methylation status. As compared to the control treatments, ZnO, CuO and γ-Fe3O4 NPs treatments increased polymorphism rates and cytosine methylation and decreased GTS values.

While 1X and 2X ZnO treatments increased polymorphism rate and cytosine methylation, 3X treatments reduced these values compared to the negative control (without Zn). Such opposite effects of ZnO NPs treatments were seen on GTS values. It can be thought that the epigenetic modifications that occur in wheat endosperms exposed to ZnO doses may be related to changes in the expression level of the PI-II gene, which may be a key mechanism responsible for developing plant immunity against stress conditions [30]. A previous study revealed that ZnO nanoparticles similarly affect the transcription factors in wheat and cause a change in the expression level of the HSFA4A gene [31]. Another mechanism of action in the epigenetic polymorphism formed by ZnO nanoparticles in callus tissues may be due to the interaction of zinc with biomolecules and cellular organelles [30]. Zinc is an essential nutrient and plays a vital role in synthesizing chlorophyll, carbohydrates and phytohormones required for plant growth and development [32]. It was reported that zinc nanoparticles enhance the plant growth and yield levels of Cyamopsis tetragonoloba L., Gossypium hirsutum, Lycopercicum esculentum and Stevia [33,34]. It was also reported that, at proper doses, zinc nanoparticles improve shoot and root lengths, chlorophyll and protein contents and increased the yield levels of Pennistem americanum L. plants [35]. Excessive quantities of nanoparticles may facilitate oxidative burst, which in turn results in the production of vast quantities of reactive oxygen species (ROS) [36]. It was reported that metal nanoparticles provoke the stress response of plants [37]. According to [38], zinc nanoparticles have significant effects on biomass, root and shoot lengths, chlorophyll and protein contents, as well as enzyme activity in Cyamopsis tetragonoloba L. plants. Excessive or deficient micronutrients may facilitate ROS accumulation and disrupt enzyme activity, resulting in cell cycle anomalies and impairing overall biomass, yield and quality [39,40].

While 1X CuO treatments increased polymorphism rate and cytosine methylation, 2X treatments reduced them, while 3X treatments increased them compared to the negative control (without Cu). The opposite effects of ZnO treatments were seen on GTS values. It can be thought that the effect of CuO nanoparticles on epigenetic modifications is related to oxidative stress, as shown by studies that analyzed transcriptomic data related to the modification of oxidative-stress-related genes following CuO nanoparticle applications [41]. Copper is essential in electron transport and cell wall metabolism [42] and facilitating ethylene receptors [42]. Copper is an essential nutrient for plants, and since it is involved in various physiological processes, it is used mainly in agricultural activities [43]. For example, copper ions protect plant cells against oxidative damage [44] and facilitate the production of hydroxyl radicals [42] and biochemical pathways [45]. CuO nanoparticles are more soluble and toxic at low concentrations [46]; they can affect the Krebs cycle at sublethal concentrations [42]. It was reported that CuO nanoparticle toxicity negatively affects the seed germination and plant growth of lettuce, mung bean, kidney bean, alfalfa, wheat, chickpea and several other crops [47].

The present findings revealed that γ-Fe3O4 treatments at 1X, 2X and 3X concentrations all reduced polymorphism rate and cytosine methylation compared to the negative control (without Fe). However, an opposite effect was seen on GTS values. It has been reported that iron ions (Fe2+) reduce copper absorbance remarkably; therefore, malfunctions may be seen in functions related to the minor copper element in plants. For this reason, it can be thought that iron nanoparticles applied at high doses can regulate many physiological processes that require minor copper elements with epigenetic modifications [48]. Iron (Fe) is an essential nutrient for all organisms. It plays a crucial role in several physiological processes of plants, including chlorophyll biosynthesis, respiration and redox reaction [49]. It was reported that FE nanoparticles decrease chlorophyll content and root hydraulic conductivity, thus influencing nutrient transport within the plant [50]. U Sami and U Rehman [51] indicated that Fe nanoparticles significantly affect the growth and development of Citrus maxima, Lycopersicum esculentum and Triticum aestivum plants. FeO nanoparticles promote plant growth and development in soybean [52], wheat [53] and peanuts [54]. Fe nanoparticles improve FRO2 gene expression levels, increase ferric reductase activity, enhance iron transformation and improve plant tolerance to iron deficiency [51].

Overall, the present findings revealed that epigenetic changes occurred using nanoparticles instead of the main element in the MS medium. Nanoparticles enhance plant growth and yield when used at proper concentrations. They interact with plant cells and change the biochemical pathway by affecting the regulation of gene expression, which enhances plant growth and development, but they also have inhibitory effects on plant growth and production when used above the optimum levels. Such negative effects could be attributed to nanoparticle type, structure, concentration and application period. Epigenetics encompasses heritable changes in gene functions without directly altering the DNA sequence [55]. Epigenetic mechanisms include DNA methylation and histone modifications [56]. In the present study, non-γ-Fe3O4 NPs treatment and 2X ZnO and CuO treatments yielded higher polymorphism percentages in both MspI- and HpaII-digested CRED-iPBS assays and thus could be classified as hypermethylation when the average polymorphism percentage for MspI digestion was taken into consideration.

On the contrary, the 3X concentration of all nanoparticles decreased both HpaII and MspI polymorphisms’ percentages and thus could be classified as hypomethylation. Nanoparticles can influence DNA methylation through two primary mechanisms—the reduced availability of methyl donors and altered activity of DNA methyl-transferases enzymes. The pro-oxidative characteristics of nanoparticles may alter DNA methylation patterns [57]. In addition to oxidative damage, ROS could also alter gene expression levels and thus DNA methylation status [58]. Accordingly, it was previously reported that nanoparticles induce ROS production [59]. Nanoparticles may also result in cytotoxicity, cell death, oxidative stress, genotoxicity and immunotoxicity [60], thus inducing abnormal epigenetic processes [61] and changes in the proteome [62]. Exposure to nanoparticles induces oxidative stress, lipid peroxidation and membrane damage, ultimately resulting in hypomethylation, accompanied mainly by hypermethylation. Environmental factors could also trigger epigenetic changes [46]. In general, it has been observed that nanoparticle structures have an effect on the modification of transcription factors in plants; hence, they are effective both in changing the expression profile and in signal transduction [31]. However, it is known that many factors, such as the size, shape and synthesis method of nanoparticles, can influence epigenetic modifications [63]. In addition, many factors, such as the method of application of nanoparticles on the plant, the dose and the duration of application, can determine the quality and quantity of the effect. Since this process is affected by the changes in many parameters, more studies are needed to clarify the effects of nanoparticles on plants.

4. Materials and Methods

The nanoparticles used in the experiment were obtained using the biological reduction method, and their nano size was confirmed as described by Nalci et al [23]. CuO, ZnO and γ-Fe3O4 nanoparticles were synthesized by green synthesis using a peroxidase enzyme obtained from the Euphorbia amygdaloides plant. Nanoparticles were characterized by SEM, XRD and FTIR analysis. As a result of the characterization findings, it was determined that γ-Fe3O4 NPs are in the size range of 30–80 nm, ZnO NPs are in the range of 60–80 nm and CuO NPs are in the range of 5–120 nm.

Briefly, iron, copper and zinc elements were removed from the Murashige and Skoog (MS) medium and replaced with a nanoparticle version of these elements at 1X, 2X and 3X concentrations [24]. The embryogenic callus is a green formation with a total plant-forming capacity that develops on callus tissue. After the embryogenic callus developed on the callus, they were transferred to different nutrient media under aseptic conditions to form a whole plant. Genomic DNA was isolated from plantlet leaves obtained from embryogenic callus using the method specified by Hosseinpour et al. [64]. The concentration and quality of genomic DNA were measured with a Nanodrop spectrophotometer (Qiagen Qiaxpert, Qiagen, Hilden, Germany) (Thermo Fisher Scientific, Waltham, MA, USA) and run on 1.5% (w/v) agarose gel. Twenty primers were tested for iPBS-PCR amplification [65]. For iPBS analysis, a PCR reaction was carried out by Hosseinpour et al. [22]. Out of 40 iPBS oligonucleotide primers, only 10 resulted in specific and stable DNA profiles in all experimental groups (Table 3).

Table 3.

Reactive primers used in iPBS PCR and their annealing (Ta) temperatures.

No Primer Name Sequence (5′ to 3′) Tm (°C) CG (%)
1 iPBS 2382 TGTTGGCTTCCA 44.9 50
2 iPBS 2383 GCATGGCCTCCA 50.5 66.7
3 iPBS 2384 GTAATGGGTCCA 40.9 50
4 iPBS 2385 CCATTGGGTCCA 45.7 58.3
5 iPBS 2386 CTGATCAACCCA 41.4 50
6 iPBS 2387 GCGCAATACCCA 47.3 58.3
7 iPBS 2388 TTGGAAGACCCA 43.4 50
8 iPBS 2389 ACATCCTTCCCA 43 50
9 iPBS 2390 GCAACAACCCCA 47.6 58.3
10 iPBS 2391 ATCTGTCAGCCA 43.6 50

CRED-iPBS analysis was conducted as specified by Hosseinpour et al. [64], using the primers listed in Table 3 for amplification. PCR steps were the same as for iPBS analysis described by Hosseinpour et al. [22]. iPBS amplification conditions were: initial denaturation for 3 min at 95 °C; 38 cycles of 15 s at 95 °C, 60 s at 51–56 °C and 60 s at 72 °C and a final extension of 5 min at 72 °C. CRED-iPBS amplification conditions were: an initial denaturation step of 5 min at 95 °C; 42 cycles of 60 s at 94 °C, 60 s at 51–56 °C and 120 s at 72 °C and a final extension step of 15 min at 72 °C. The iPBSs and CRED-iPBS PCR products were separated in a 1.5% agarose gel containing 0.05 µg/mL ethidium bromide, using 1X SB buffer in 100 V for 90 min for electrophoresis. The 100–1000 bp (Sigma Aldrich, MO, USA, No: P1473-1VL) DNA ladder was used to estimate the molecular weight of the fragments. The gels were photographed under UV light in a Universal Hood II (Bio-Rad, Hercules, CA, USA).

The iPBS and CRED-iPBS banding patterns were analyzed using TotalLab TL120 software (Nonlinear Dynamics Ltd. Newcastle, UK). Polymorphism and genomic template stability (GTS %) were analyzed as described by Hosseinpour et al. [64]. For CRED-iPBS analysis, the average values of polymorphism (%) were calculated for each concentration [23].

5. Conclusions

In this study, the effects of different nanoparticles (ZnO, CuO and γ-Fe3O4) at different concentrations (1X, 2X and 3X) on methylation and epigenetic changes encountered in wheat DNA were investigated. Based on the present findings, it was concluded that nanoparticles play an essential role in DNA methylation and genomic instability. Current findings indicated that epigenetic modification via cytosine methylation could be an essential regulatory mechanism in plants. It was determined that the three metallic nanoparticles, especially at high doses, caused changes in genomic instability. It was concluded that the excess and the absence of minor elements in the wheat plant revealed changes at the nanoscale DNA level. Exposure to nanoparticles can induce epigenetic changes, but the consequences of these changes have not been fully elucidated. Further research is recommended for the high-throughput analysis of genetic and metabolic responses triggered by nanoparticles and to shed light on various aspects of nanoparticle phytotoxicity in plants.

Acknowledgments

Open access funding provided by University of Helsinki.

Author Contributions

Concept—K.H. and A.T.; Design—K.H. and A.T.; Resource—K.H.; Materials—K.H., H.N., A.A. and Ö.B.; Data Collection and/or Processing—A.T.; Analysis and/or Interpretation—A.T.; Literature Search—A.T. and Ö.B.; Writing A.T.; Critical Reviews—K.H., H.N., A.A. and P.P. All authors have read and agreed to the published version of the manuscript.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are contained within the article.

Conflicts of Interest

The authors have no conflicts of interest to declare.

Funding Statement

Peter Poczai expresses his gratitude for the support of the iASK Research Grant. The authors thank the Helsinki University Library for supporting open access publication.

Footnotes

Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

References

  • 1.Du W., Tan W., Peralta-Videa J.R., Gardea-Torresdey J.L., Ji R., Yin Y., Guo H. Interaction of metal oxide nanoparticles with higher terrestrial plants: Physiological and biochemical aspects. Plant Physiol. Biochem. 2017;110:210–225. doi: 10.1016/j.plaphy.2016.04.024. [DOI] [PubMed] [Google Scholar]
  • 2.Tolaymat T., Genaidy A., Abdelraheem W., Dionysiou D., Andersen C. The effects of metallic engineered nanoparticles upon plant systems: An analytic examination of scientific evidence. Sci. Total Environ. 2017;579:93–106. doi: 10.1016/j.scitotenv.2016.10.229. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Servin A., Elmer W., Mukherjee A., De la Torre-Roche R., Hamdi H., White J.C., Bindraban P., Dimkpa C. A review of the use of engineered nanomaterials to suppress plant disease and enhance crop yield. J. Nanoparticle Res. 2015;17:1–21. doi: 10.1007/s11051-015-2907-7. [DOI] [Google Scholar]
  • 4.Zhang L., Webster T.J. Nanotechnology and nanomaterials: Promises for improved tissue regeneration. Nano Today. 2009;4:66–80. doi: 10.1016/j.nantod.2008.10.014. [DOI] [Google Scholar]
  • 5.Khan A., Zinta G. Drought Stress Tolerance in Plants. Volume 2. Springer; Berlin/Heidelberg, Germany: 2016. Drought stress and chromatin: An epigenetic perspective; pp. 571–586. [Google Scholar]
  • 6.Kumar S., Beena A., Awana M., Singh A. Physiological, biochemical, epigenetic and molecular analyses of wheat (Triticum aestivum) genotypes with contrasting salt tolerance. Front. Plant Sci. 2017;8:1151. doi: 10.3389/fpls.2017.01151. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Wheeler S. Factors Influencing Agricultural Professionals’ Attitudes towards Organic Agriculture and Biotechnology. ANU; Canberra, Australia: 2005. [Google Scholar]
  • 8.Galbraith D.W. Silica breaks through in plants. Nat. Nanotechnol. 2007;2:272–273. doi: 10.1038/nnano.2007.118. [DOI] [PubMed] [Google Scholar]
  • 9.Torney F., Trewyn B.G., Lin V.S.-Y., Wang K. Mesoporous silica nanoparticles deliver DNA and chemicals into plants. Nat. Nanotechnol. 2007;2:295–300. doi: 10.1038/nnano.2007.108. [DOI] [PubMed] [Google Scholar]
  • 10.Erturk F.A., Aydin M., Sigmaz B., Taspinar M.S., Arslan E., Agar G., Yagci S. Effects of As2O3 on DNA methylation, genomic instability, and LTR retrotransposon polymorphism in Zea mays. Environ. Sci. Pollut. Res. 2015;22:18601–18606. doi: 10.1007/s11356-015-5426-2. [DOI] [PubMed] [Google Scholar]
  • 11.Zulfiqar F., Navarro M., Ashraf M., Akram N.A., Munné-Bosch S. Nanofertilizer use for sustainable agriculture: Advantages and limitations. Plant Sci. 2019;289:110270. doi: 10.1016/j.plantsci.2019.110270. [DOI] [PubMed] [Google Scholar]
  • 12.Goldberg A.D., Allis C.D., Bernstein E. Epigenetics: A landscape takes shape. Cell. 2007;128:635–638. doi: 10.1016/j.cell.2007.02.006. [DOI] [PubMed] [Google Scholar]
  • 13.Hauser M.T., Aufsatz W., Jonak C., Luschnig C. Transgenerational epigenetic inheritance in plants. Biochim. Biophys. Acta Gene Regul. Mech. 2011;1809:459–468. doi: 10.1016/j.bbagrm.2011.03.007. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Zemach A., McDaniel I.E., Silva P., Zilberman D. Genome-wide evolutionary analysis of eukaryotic DNA methylation. Science. 2010;328:916–919. doi: 10.1126/science.1186366. [DOI] [PubMed] [Google Scholar]
  • 15.Xue-Lin L., Zhong-Xu L., Yi-Chun N., Xiao-Ping G., Zhang X.-L. Methylation-sensitive amplification polymorphism of epigenetic changes in cotton under salt stress. Acta Agron. Sin. 2009;35:588–596. [Google Scholar]
  • 16.Pereira W.J., Pappas M.D.C.R., Grattapaglia D., Pappas G.J., Jr. A cost-effective approach to DNA methylation detection by Methyl Sensitive DArT sequencing. PLoS ONE. 2020;15:e0233800. doi: 10.1371/journal.pone.0233800. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Bednarek P.T., Orłowska R., Niedziela A. A relative quantitative methylation-sensitive amplified polymorphism (MSAP) method for the analysis of abiotic stress. BMC Plant Biol. 2017;17:1–13. doi: 10.1186/s12870-017-1028-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Wang S., Lv J., Zhang L., Dou J., Sun Y., Li X., Fu X., Dou H., Mao J., Hu X. MethylRAD: A simple and scalable method for genome-wide DNA methylation profiling using methylation-dependent restriction enzymes. Open Biol. 2015;5:150130. doi: 10.1098/rsob.150130. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Brunner A.L., Johnson D.S., Kim S.W., Valouev A., Reddy T.E., Neff N.F., Anton E., Medina C., Nguyen L., Chiao E. Distinct DNA methylation patterns characterize differentiated human embryonic stem cells and developing human fetal liver. Genome Res. 2009;19:1044–1056. doi: 10.1101/gr.088773.108. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.Orłowska R., Pachota K.A., Machczyńska J., Niedziela A., Makowska K., Zimny J., Bednarek P.T. Improvement of anther cultures conditions using the Taguchi method in three cereal crops. Electron. J. Biotechnol. 2020;43:8–15. doi: 10.1016/j.ejbt.2019.11.001. [DOI] [Google Scholar]
  • 21.Lu Y., Rong T., Cao M. Analysis of DNA methylation in different maize tissues. J. Genet. Genom. 2008;35:41–48. doi: 10.1016/S1673-8527(08)60006-5. [DOI] [PubMed] [Google Scholar]
  • 22.Hosseinpour A., Ozkan G., Nalci O., Haliloğlu K. Estimation of genomic instability and DNA methylation due to aluminum (Al) stress in wheat (Triticum aestivum L.) using iPBS and CRED-iPBS analyses. Turk J. Bot. 2019;43:27–37. doi: 10.3906/bot-1804-23. [DOI] [Google Scholar]
  • 23.Hosseinpour A., Ilhan E., Özkan G., Öztürk H.İ., Haliloglu K., Cinisli K.T. Plant growth-promoting bacteria (PGPBs) and copper (II) oxide (CuO) nanoparticle ameliorates DNA damage and DNA Methylation in wheat (Triticum aestivum L.) exposed to NaCl stress. J. Plant Biochem. Biotechnol. 2021;1:1–14. doi: 10.1007/s13562-021-00713-w. [DOI] [Google Scholar]
  • 24.Nalci O.B., Nadaroglu H., Pour A.H., Gungor A.A., Haliloglu K. Effects of ZnO, CuO and γ-Fe3O4 nanoparticles on mature embryo culture of wheat (Triticum aestivum L.) Plant Cell Tissue Organ. Cult. 2019;136:269–277. doi: 10.1007/s11240-018-1512-8. [DOI] [Google Scholar]
  • 25.Nazli A., Baig M.W., Zia M., Ali M., Shinwari Z.K., Haq I.U. Plant-based metallic nanoparticles as potential theranostics agents: Bioinspired tool for imaging and treatment. IET NanoBiotechnol. 2018;12:869–878. doi: 10.1049/iet-nbt.2017.0325. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Nadaroglu H., Cicek S., Gungor A.A. Removing Trypan blue dye using nano-Zn modified Luffa sponge. Spectrochim. Acta A Mol. Biomol. Spectrosc. 2017;172:2–8. doi: 10.1016/j.saa.2016.08.052. [DOI] [PubMed] [Google Scholar]
  • 27.Kuzma J. Moving forward responsibly: Oversight for the nanotechnology-biology interface. J. Nanoparticle Res. 2007;9:165–182. doi: 10.1007/s11051-006-9151-0. [DOI] [Google Scholar]
  • 28.Shankramma K., Yallappa S., Shivanna M., Manjanna J. Fe2O3 magnetic nanoparticles to enhance S. lycopersicum (tomato) plant growth and their biomineralization. Appl. Nanosci. 2016;6:983–990. [Google Scholar]
  • 29.Lengke M.F., Fleet M.E., Southam G. Biosynthesis of silver nanoparticles by filamentous cyanobacteria from a silver (I) nitrate complex. Langmuir. 2007;23:2694–2699. doi: 10.1021/la0613124. [DOI] [PubMed] [Google Scholar]
  • 30.Vafaie Moghadam A., Iranbakhsh A., Saadatmand S., Ebadi M., Oraghi Ardebili Z. New insights into the transcriptional, epigenetic, and physiological responses to zinc oxide nanoparticles in datura stramonium; potential species for phytoremediation. J. Plant Growth Regul. 2021;41:271–281. doi: 10.1007/s00344-021-10305-6. [DOI] [Google Scholar]
  • 31.Safari M., Oraghi Ardebili Z., Iranbakhsh A. Selenium nanoparticle induced alterations in expression patterns of heat shock factor A4A (HSFA4A), and high molecular weight glutenin subunit 1Bx (Glu-1Bx) and enhanced nitrate reductase activity in wheat (Triticum aestivum L.) Acta Physiol. Plant. 2018;40:1–8. doi: 10.1007/s11738-018-2694-8. [DOI] [Google Scholar]
  • 32.Gao X., Zou C., Wang L., Zhang F. Silicon decreases transpiration rate and conductance from stomata of maize plants. J. Plant Nutr. 2006;29:1637–1647. doi: 10.1080/01904160600851494. [DOI] [Google Scholar]
  • 33.Feizi H., Moghaddam P.R., Shahtahmassebi N., Fotovat A. Impact of bulk and nano-sized titanium dioxide (TiO2) on wheat seed germination and seedling growth. Biol. Trace Elem. Res. 2012;146:101–106. doi: 10.1007/s12011-011-9222-7. [DOI] [PubMed] [Google Scholar]
  • 34.Javed R., Usman M., Yücesan B., Zia M., Gürel E. Effect of zinc oxide (ZnO) nanoparticles on physiology and steviol glycosides production in micropropagated shoots of Stevia rebaudiana Bertoni. Plant Physiol. Biochem. 2017;110:94–99. doi: 10.1016/j.plaphy.2016.05.032. [DOI] [PubMed] [Google Scholar]
  • 35.Tarafdar J., Raliya R., Mahawar H., Rathore I. Development of zinc nanofertilizer to enhance crop production in pearl millet (Pennisetum americanum) Agric. Res. 2014;3:257–262. doi: 10.1007/s40003-014-0113-y. [DOI] [Google Scholar]
  • 36.Pagano L., Servin A.D., De La Torre-Roche R., Mukherjee A., Majumdar S., Hawthorne J., Marmiroli M., Maestri E., Marra R.E., Isch S.M. Molecular response of crop plants to engineered nanomaterials. Environ. Sci. Technol. 2016;50:7198–7207. doi: 10.1021/acs.est.6b01816. [DOI] [PubMed] [Google Scholar]
  • 37.Ruotolo R., Maestri E., Pagano L., Marmiroli M., White J.C., Marmiroli N. Plant response to metal-containing engineered nanomaterials: An omics-based perspective. Environ. Sci. Technol. 2018;52:2451–2467. doi: 10.1021/acs.est.7b04121. [DOI] [PubMed] [Google Scholar]
  • 38.Ullah S., Ullah R. Beneficial effects of several nanoparticles on the growth of different plants species. Curr. Nanosci. 2019;15:460–470. [Google Scholar]
  • 39.Mota M.B.S., Carvalho M.A., Monteiro A.N., Mesquita R.D. DNA damage response and repair in perspective: Aedes aegypti, Drosophila melanogaster and Homo sapiens. Parasites Vectors. 2019;12:1–20. doi: 10.1186/s13071-019-3792-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40.Sundaria N., Singh M., Upreti P., Chauhan R.P., Jaiswal J., Kumar A. Seed priming with Iron oxide nanoparticles triggers Iron acquisition and biofortification in wheat (Triticum aestivum L.) grains. J. Plant Growth Regul. 2019;38:122–131. doi: 10.1007/s00344-018-9818-7. [DOI] [Google Scholar]
  • 41.Zhang Z., Ke M., Qu Q., Peijnenburg W., Lu T., Zhang Q., Ye Y., Xu P., Du B., Sun L. Impact of copper nanoparticles and ionic copper exposure on wheat (Triticum aestivum L.) root morphology and antioxidant response. Environ. Pollut. 2018;239:689–697. doi: 10.1016/j.envpol.2018.04.066. [DOI] [PubMed] [Google Scholar]
  • 42.Ravet K., Pilon M. Copper and iron homeostasis in plants: The challenges of oxidative stress. Antioxid. Redox Signal. 2013;19:919–932. doi: 10.1089/ars.2012.5084. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 43.Rafique M., Shaikh A.J., Rasheed R., Tahir M.B., Bakhat H.F., Rafique M.S., Rabbani F. A review on synthesis, characterization and applications of copper nanoparticles using green method. Nano. 2017;12:1750043. doi: 10.1142/S1793292017500436. [DOI] [Google Scholar]
  • 44.Szőllősi R. Superoxide dismutase (SOD) and abiotic stress tolerance in plants: An overview. Oxidative Damage Plants. 2014;3:89–129. [Google Scholar]
  • 45.Cong W., Miao Y., Xu L., Zhang Y., Yuan C., Wang J., Zhuang T., Lin X., Jiang L., Wang N. Transgenerational memory of gene expression changes induced by heavy metal stress in rice (Oryza sativa L.) BMC Plant Biol. 2019;19:1–14. doi: 10.1186/s12870-019-1887-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 46.Alegría-Torres J.A., Baccarelli A., Bollati V. Epigenetics and lifestyle. Epigenomics. 2011;3:267–277. doi: 10.2217/epi.11.22. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 47.Rajput V., Minkina T., Suskova S., Mandzhieva S., Tsitsuashvili V., Chapligin V., Fedorenko A. Effects of copper nanoparticles (CuO NPs) on crop plants: A mini review. BioNano Sci. 2018;8:36–42. doi: 10.1007/s12668-017-0466-3. [DOI] [Google Scholar]
  • 48.Yuan P., Peng C., Shi J., Liu J., Cai D., Wang D., Shen Y. Ferrous ions inhibit Cu uptake and accumulation via inducing iron plaque and regulating the metabolism of rice plants exposed to CuO nanoparticles. Environ. Sci. Nano. 2021;8:1456–1468. doi: 10.1039/D0EN01241F. [DOI] [Google Scholar]
  • 49.Mimmo T., Del Buono D., Terzano R., Tomasi N., Vigani G., Crecchio C., Pinton R., Zocchi G., Cesco S. Rhizospheric organic compounds in the soil–microorganism–plant system: Their role in iron availability. Eur. J. Soil Sci. 2014;65:629–642. doi: 10.1111/ejss.12158. [DOI] [Google Scholar]
  • 50.Martínez-Fernández D., Barroso D., Komárek M. Root water transport of Helianthus annuus L. under iron oxide nanoparticle exposure. Environ. Sci. Pollut. Res. 2016;23:1732–1741. doi: 10.1007/s11356-015-5423-5. [DOI] [PubMed] [Google Scholar]
  • 51.Alidoust D., Isoda A. Effect of γFe 2 O 3 nanoparticles on photosynthetic characteristic of soybean (Glycine max (L.) Merr.): Foliar spray versus soil amendment. Acta Physiol. Plant. 2013;35:3365–3375. doi: 10.1007/s11738-013-1369-8. [DOI] [Google Scholar]
  • 52.Bakhtiari M., Moaveni P., Sani B. The effect of iron nanoparticles spraying time and concentration on wheat. BFIJ. 2015;7:679–683. [Google Scholar]
  • 53.Rui M., Ma C., Hao Y., Guo J., Rui Y., Tang X., Zhao Q., Fan X., Zhang Z., Hou T. Iron oxide nanoparticles as a potential iron fertilizer for peanut (Arachis hypogaea) Front. Plant Sci. 2016;7:815. doi: 10.3389/fpls.2016.00815. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 54.Egger G., Liang G., Aparicio A., Jones P.A. Epigenetics in human disease and prospects for epigenetic therapy. Nature. 2004;429:457–463. doi: 10.1038/nature02625. [DOI] [PubMed] [Google Scholar]
  • 55.Smolkova B., El Yamani N., Collins A.R., Gutleb A.C., Dusinska M. Nanoparticles in food. Epigenetic changes induced by nanomaterials and possible impact on health. Food Chem. Toxicol. 2015;77:64–73. doi: 10.1016/j.fct.2014.12.015. [DOI] [PubMed] [Google Scholar]
  • 56.Simkó M., Gazsó A., Fiedeler U., Nentwich M. Nanoparticles, Free Radicals and Oxidative Stress (NanoTrust Dossier No. 012en–January 2011). 2011. Austrian Academy of Sciences; Legal Person under Public Law (BGBl 569/1921; BGBl I 130/2003); Dr. Ignaz Seipel-Platz 2, A-1010 Vienna. [(accessed on 28 July 2022)]. Available online: epub.oeaw.ac.at/ita/nanotrust-dossiers/dossier012en.pdf.
  • 57.Fratelli M., Goodwin L.O., Ørom U.A., Lombardi S., Tonelli R., Mengozzi M., Ghezzi P. Gene expression profiling reveals a signaling role of glutathione in redox regulation. Proc. Natl. Acad. Sci. USA. 2005;102:13998–14003. doi: 10.1073/pnas.0504398102. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 58.Kim S., Lee S., Lee I. Alteration of phytotoxicity and oxidant stress potential by metal oxide nanoparticles in Cucumis sativus. Water Air Soil Pollut. 2012;223:2799–2806. doi: 10.1007/s11270-011-1067-3. [DOI] [Google Scholar]
  • 59.Dusinska M., Magdolenova Z., Fjellsbø L.M. Toxicological aspects for nanomaterial in humans. Nanotechnol. Nucleic Acid Deliv. 2013;948:1–12. doi: 10.1007/978-1-62703-140-0_1. [DOI] [PubMed] [Google Scholar]
  • 60.Yao Y., Costa M. Genetic and epigenetic effects of nanoparticles. J. Mol. Genet. Med. 2013;7:1–6. [Google Scholar]
  • 61.Georgantzopoulou A., Serchi T., Cambier S., Leclercq C.C., Renaut J., Shao J., Kruszewski M., Lentzen E., Grysan P., Eswara S. Effects of silver nanoparticles and ions on a co-culture model for the gastrointestinal epithelium. Part. Fibre Toxicol. 2015;13:1–17. doi: 10.1186/s12989-016-0117-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 62.Dietz K.J., Herth S. Plant nanotoxicology. Trends Plant Sci. 2011;16:582–589. doi: 10.1016/j.tplants.2011.08.003. [DOI] [PubMed] [Google Scholar]
  • 63.Zeinalzadehtabrizi H., Hosseinpour A., Aydin M., Haliloglu K. A modified genomic DNA extraction method from leaves of sunflower for PCR based analyzes. J. Biodivers. Environ. Sci. 2015;7:222–225. [Google Scholar]
  • 64.Kalendar R., Antonius K., Smýkal P., Schulman A.H. iPBS: A universal method for DNA fingerprinting and retrotransposon isolation. Theor. Appl. Genet. 2010;121:1419–1430. doi: 10.1007/s00122-010-1398-2. [DOI] [PubMed] [Google Scholar]
  • 65.Türkoğlu A., Haliloğlu K., Balpinar Ö., Öztürk H.I., Özkan G., Poczai P. The Effect of Mammalian Sex Hormones on Polymorphism and Genomic Instability in the Common Bean (Phaseolus vulgaris L.) Plants. 2022;11:2071. doi: 10.3390/plants11152071. [DOI] [PMC free article] [PubMed] [Google Scholar]

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