Abstract
MCPA (4-chloro-2-methylphenoxy) acetic acid is a common synthetic auxin used as a herbicide. The purpose of this study was to determine the effects of four new forms of MCPA being the herbicidal ionic liquids (HILs) with MCPA as an anion and two previously known formulations (potassium–sodium salt and 2-ethylhexyl ester) on seed germination and seedling development of winter oilseed rape (Brassica napus). Rape plants are susceptible to MCPA and volunteers can be a big problem in crop rotation. Seedling fresh weight and root length were quantified, mitotic activity, as well as lipid, starch, hydrogen peroxide and polyphenol contents were assessed by light and fluorescence microscopy and the computer-aided cytophotometer. In primary roots mitotic activity was almost completely inhibited under the influence of herbicides, cell elongation zones and root hair zones were significantly reduced, and a characteristic bolded root segment formed just above a meristem. In contrast to the traditional salt formulation the new HILs were weak inducers of hydrogen peroxide synthesis, but were potent stimulators of the synthesis of phenolic compounds and storage as well as emergency substances such as lipids and starch. All tested forms of MCPA caused strong phytotoxic effect on winter rape seedlings, but the tested HILs were more effective.
Similar content being viewed by others
Explore related subjects
Discover the latest articles, news and stories from top researchers in related subjects.Avoid common mistakes on your manuscript.
Introduction
Synthetic auxins such as phenoxycarboxylic acids (MCPA, mecoprop, 2,4-D), benzoic acids (dicamba) and pyridinecarboxylic acids (picloram, clopyralid, fluroxypyr) are widely used in agriculture and horticulture as selective herbicides for mostly postemergence control of annual and perennial broad-leaved weeds (Praczyk et al. 2012). Synthetic auxins act similar to indole-3-acetic acid (IAA), but in contrast to natural phytohormones their degradation in plants occurs slowly (Grossmann 2000). They are absorbed by the leaves or roots, translocated via plant conducting system (xylem and phloem) to the meristematic regions and cause stem twisting, leaf epinasty, inhibition of shoot and root growth and finally cells death. However, the specific site of herbicide action is not well known. It is thought that they are active at multiple levels, among others, they disrupt hormone balance, nucleic acid metabolism and protein synthesis (Monaco et al. 2002). The primary action of synthetic auxins includes also cell wall loosening by increasing the activity of the proton pump that causes the reduction of apoplasmic pH (Senseman 2007). The recent studies showed that there was a specific interaction between auxin, ethylene and the abscisic acid biosynthesis (for review see Grossmann 2010).
The purpose of this study was to determine the effects of MCPA on seed germination and seedling development of dicotyledonous plants on the example of winter oilseed rape (Brassica napus L. ssp. napus). The choice of rape as a model plant was motivated by the fact that rape plants are susceptible to MCPA and volunteers can be a big problem in crop rotation. In our study, we used four new formulations of MCPA being the herbicidal ionic liquids with MCPA as an anion and two known formulations, namely the sodium–potassium salt and 2-ethylhexyl ester.
Ionic liquids (ILs) are defined as organic salts composed entirely of ions that are liquid below 100 °C (Rogers and Seddon 2003a, b; Wasserscheid and Welton 2008; Kirchner 2009; Olivier-Bourbigou et al. 2010). They possess unique properties like low vapour pressure, reasonably good conductivity, wide liquid range, as well as high thermal and electrochemical stability and are excellent solvents for a wide range of compounds. ILs have been receiving considerable global attention in recent years due to their potential application (Plechkova and Seddon 2008). Their negligible vapour pressure and non-inflammability reduce or eliminate the risk of polluting emissions to air. The evaluation of ILs proceeds very quickly from the first generation (ILs with unique tuneable physical properties) to the second generation (ILs with targeted chemical properties combined with selected physical properties), and to the third generation (ILs with targeted biological properties combined with selected physical and chemical properties; Hough and Rogers 2007; Hough et al. 2007). The newest third generation ILs was enriched with phytopharmaceuticals called herbicidal ionic liquids (HILs) in which MCPA (Pernak et al. 2011) and 2,4-D are anions (Praczyk et al. 2012). They exhibit higher biological activity than currently used salts of MCPA and 2,4-D. Herbicidal ionic liquids have chemical and thermal stability and show substantially lower water solubility thus reducing soil and groundwater mobility. Acute toxicity of HILs could be controlled by appropriate selection of cation type (Pernak et al. 2011). These novel forms of phenoxy acids possess reduced volatility and drift potential. Ionic liquids are still fairly innovative solvents.
Materials and methods
Plant material
The certificated seeds of winter rape (Brassica napus L.) cv. Libomir with germination capacity of 98 % have been used both in laboratory and glasshouse experiments.
Chemicals
Two commercial formulations of MCPA: MCPA-salt (Chwastox Extra 300 SL® containing MCPA as sodium–potassium salt) and MCPA-ester (Chwastox AS 600 EC® containing MCPA as ester 2-ethylhexyl) as well as four new HILs with MCPA as an anion were used (Fig. 1). HILs were obtained according to the method recently described (Pernak et al. 2011). All prepared HILs were characterized by 1H NMR, 13C NMR. 1H NMR spectra were recorded on a Mercury Gemini 300 spectrometer operating at 300 MHz with tetramethylsilane as the internal standard. 13C NMR spectra were obtained with the same instrument at 75 MHz.
Didecyldimethylammonium (4-chloro-2-methylphenoxy)acetate—HIL-1
1H NMR (CDCl3) δ ppm = 0.88 (t, J = 6.7 Hz, 6H), 1.25 (m, 28H), 1.57 (q, J = 6.9 Hz, 4H), 2.24 (s, 3H), 3.12 (s, 6H), 3.21 (t, J = 8.5 Hz, 4H), 4.41 (s, 2H), 6.75 (d, J = 8.8 Hz, 1H), 7.00 (dd, J 1,2 = 0.6 Hz, J 2,3 = 2.2 Hz, 1H), 7.04 (d, J = 0.6 Hz, 1H); 13C NMR δ ppm = 14.0, 16.3, 22.5, 22.52, 26.1, 29.06, 29.12, 29.26, 29.30, 31.7, 51.1, 63.3, 68.4, 112.7, 124.1, 126.0, 128.4, 129.9, 156.1, 173.1,
Dicocodimethylammonium (4-chloro-2-methylphenoxy)acetate—HIL-2
1H NMR (CDCl3) δ ppm = 0.88 (t, J = 6.7 Hz, 6H), 1.25 (m, 44H), 1.57 (q, J = 6.9 Hz, 4H), 2.24 (s, 3H), 3.13 (s, 6H), 3.18 (t, J = 4.4 Hz, 4H); 4.39 (s, 2H), 6.75 (d, J = 8.5 Hz, 1H), 7.02 (d, J = 2.8 Hz, 1H), 7.05 (s, 1H), 13C NMR δ ppm = 14.1, 16.4, 22.6, 26.2, 29.1, 29.26, 29.29, 29.34, 29.4, 29.54, 29.59, 29.63, 31.8, 51.2, 63.3, 68.5, 112.7, 123.9, 125.9, 128.3, 129.8, 156.0, 172.9,
Dicocotrimethylammonium (4-chloro-2-methylphenoxy)acetate—HIL-3
1H NMR (CDCl3) δ ppm = 0.88 (t, J = 6.7 Hz, 3H), 1.23 (m, 22H), 1.55 (q, J = 3.8 Hz, 2H), 2.21 (s, 3H), 3.08 (s, 9H), 3.15 (t, J = 4.3 Hz, 2H), 4.36 (s, 2H), 6.72 (d, J = 8.2 Hz, 1H), 7.02 (d, J = 3.3 Hz, 1H), 7.04 (s, 1H), 13C NMR δ ppm = 14.1, 16.4, 22.7, 23.0, 26.3, 29.25, 29.30, 29.4, 29.5, 29.6, 29.7, 31.9, 52.9, 66.6, 68.4, 112.7, 124.1, 126.0, 128.3, 129.9, 155.9, 173.1,
Cocodi(2-hydoxyethyl)methylammonium (4-chloro-2-methylphenoxy)acetate—HIL-4
1H NMR (CDCl3) δ ppm = 0.88 (t, J = 6.7 Hz, 3H), 1.24 (m, 22H), 1.58 (q, J = 3.8 Hz, 2H), 2.23 (s, 3H), 3.07 (s, 3H), 3.29 (t, J = 5.8 Hz, 2H), 3.45 (t, J = 5.6 Hz, 4H), 3.92 (t, J = 4.4 Hz, 4H), 4.39 (s, 2H), 5.32 (s, 1H), 6.70 (d, J = 8.5 Hz, 1H), 7.04 (d, J = 2.8 Hz, 1H), 7.06 (s, 1H), 13C NMR δ ppm = 14.1, 16.4, 22.5, 22.7, 26.4, 29.2, 29.3, 29.48, 29.51, 29.59, 29.61, 29.7, 31.8, 31.9, 49.9, 55.5, 63.6, 64.1, 68.2, 112.5, 124.4, 126.0, 128.6, 130.0, 155.7, 174.0.
Application of herbicides, seed germination and culture
In laboratory and glasshouse experiments the influence of MCPA forms on the germination and early growth of winter rape seedlings has been evaluated. HIL-3 and HIL-4 were dissolved in water; however, HIL-1 and HIL-2 were dissolved in a water and ethanol solution (3:1). These new forms of MCPA were compared with the commercial herbicides described above. They were applied on the surface of seeds using a spray chamber with flat fan nozzle type F 110/0—6/3 110º LD-015 and an operating pressure of 0.2 MPa. The concentration of all tested substances was established on 0.2 % (v/v), which was similar to 400 g of MCPA per 1 ha with the water volume carrier of 200 L/ha. The experimental design was a randomized complete block with four replications. All experiments were repeated.
In experiments carried out in Petri dishes the seeds of winter rape were sown on wet filter paper (25 seeds per dish), and after application of herbicides they were incubated at 20 °C in darkness for 5 days. After that the seedlings in Petri dishes were grown with 16-h photoperiod (16 h of light—13,000 lx and 8 h of darkness). In experiments carried out in greenhouse the seeds of winter rape were placed on the surface of a sandy loam soil in 0.5-L plastic pots (25 seeds per pot). After application of herbicides all pots were placed in a greenhouse at temperature 20 °C (±3 °C) and a 16-h photoperiod. Fresh weight of seedlings was measured 2 weeks (for Petri dishes culture) or 3 weeks (for greenhouse culture) after the herbicide application. The results were expressed as the percent of fresh weight reduction compared with untreated plants.
Feulgen staining
Seedlings were fixed in cold Carnoy’s mixture of absolute ethanol and glacial acetic acid (3:1; v/v) for 1 h, washed several times with ethanol, rehydrated, hydrolysed in 4 M HCl for 1 h and stained with Schiff’s reagent (pararosaniline; Sigma-Aldrich) according to the standard methods (Maszewski and Kaźmierczak 1998). After rinsing in SO2-water (three times) and distilled water, 1-mm-long apical segments of roots were cut off, placed in a drop of 45 % acetic acid and squashed onto Super-Frost (Menzel-Gläser, Braunschweig, Germany) microscope slides. Following freezing with dry ice, coverslips were removed, and the dehydrated dry slides were embedded in Canada balsam.
H2O2 detection by the DAB-uptake method
The experimental procedure was performed according to Thordal-Christensen et al. (1997) with some modifications. Three-day-old seedlings of B. napus were incubated in a solution containing 1 mg mL−1 DAB (3,3′-diaminobenzidine) dissolved in Tris buffer (10 mM Tris, 10 mM EDTA-2Na, 100 mM NaCl, pH 7.6) for 12 h. Then roots were fixed for 40 min (4 °C) in PBS-buffered 4 % paraformaldehyde solution, washed three times with PBS and placed in a citric acid-buffered digestion solution (pH 5.0) containing 2.5 % pectinase, 2.5 % cellulose and 2.5 % pectolyase, and incubated at 37 °C for 25 min. After that the roots were washed as before, rinsed with distilled water and squashed onto glass slides.
Cytochemical localization of lipids and starch
Cytochemical detection of lipids and starch content in root cells was performed using standard procedure of staining with the mixture of Sudan III and IV or Lugol’s iodine solution, respectively.
Polyphenols autofluorescence
Several classes of phenolics are autofluorescent under UV light (Schoenwaelder 2008). Seeds were fixed for 1 h in 4 % (v/v) buffered formaldehyde with PBS (pH 7.0) at 4 °C. Than they were rinsed in PBS three times, dehydrated in a graded ethanol, embedded in paraplast and ultrathin sections (5–7 μm) were prepared using Mikrom microtome. Deparaffinisation was performed by heating in 60 °C and washing in xylene, and then sections were hydrated. Staining was performed using 0.1 % toluidine blue in sodium chloride. Slides were washed three times in distilled water, dehydrated in ethanol gradient 75–100 % and cleared in xylene.
Observations, analyses and statistics
Observations of whole seedlings as well as analyses of mitotic activity, lipid, starch and hydrogen peroxide contents in the cells were performed using binocular microscope SMZ-2T (Nikon) and Optiphot-2 microscope (Nikon) containing phase-contrast optics, respectively, equipped with DXM 1200 CCD camera (Nikon).
Observations of polyphenol autofluorescence were performed using Eclipse E-600 epifluorescence microscope (Nikon) equipped with UV filter (λ = 340–380) and DS-Fi1 CCD camera (Nikon).
To evaluate differences in lipid, polyphenol and hydrogen peroxide levels, all images were recorded at exactly the same time of integration. Semiquantitative measurements of the above-mentioned substances staining were made using the computer-aided Cytophotometr V1.2 (Forel, Poland) after converting colour images into grey scale and expressed in arbitrary units as mean pixel value (pv) spanning the range from 0 (white) to 255 (dark). Each mean value (±SD) was based on the analysis of five root meristems (100 cells/meristems). Statistical Student’s t test was used to establish the significance of the differences between the values. The most typical effects were recorded and are presented as a photo.
Results
Morphological analysis of seedlings
Initially, the tested forms of MCPA applied on the surface of winter rape seeds similarly disturbed growth and development of seedlings (Fig. 2). Morphological analyses revealed that MCPA-salt, HIL-1 and HIL-3, regardless of their chemical form caused a significant (almost 14-fold after 96 h of culture) inhibition of seedling growth in comparison with the control. The difference in the size of seedlings was mainly due to a significant reduction of root growth (Figs. 3, 4a–d). In the roots under the influence of herbicides cell elongation zone and root hair zone were significantly reduced (Fig. 4a–d). Moreover, after 96 h of culture, a characteristic protruding section of the root formed just above the meristems. This protruding fragment was the largest in the roots previously treated with HIL-3 (Fig. 4d). During its formation roots often cracked which in consequence led to desiccation and meristem death (Fig. 4e–g).
After 2 weeks of culture in Petri dishes reduction of fresh weight of the seedling whose seeds were treated with HILs varied from 51 to 63 %. Reduction of fresh weight of the seedling whose seeds were treated with commercial forms of MCPA was similar and varied from 55 to 61 % in comparison with the untreated control plants (Table 1). Moreover, the treatments with HILs additionally caused the chlorosis of cotyledons.
Long-term studies conducted in the greenhouse revealed that all tested HILs were more phytotoxic than MCPA-salt or MCPA-ester (Table 2). They caused reduction of seedling fresh weight from 75 to 86 %, while the commercial forms of MCPA from 66 to 68 %. HIL-2 exhibited the highest biological activity.
Hydrogen peroxide content
In the control plants brown polymers of DAB (indicating the presence of hydrogen peroxide) were seen in the root epidermis of cell differentiation and root hair zones (Fig. 4h). Elongated epidermal cells were clearly and homogeneously stained indicating a relatively low level of H2O2 in these cells (Figs. 4l, 5). DAB polymers were mainly localized in the wall and, in smaller amounts, in the cytoplasm of root hair cells. MCPA-salt was the potent inducer of H2O2 formation. It triggered intense production of H2O2 in the root hair zone and cell elongation zone (Figs. 4i, 5). Epidermal cells with limited length were all filled with dark-brown DAB polymers (Fig. 4m). Slightly weaker accumulation of H2O2 was observed in the root hair zone and cell elongation zone under the influence of HIL-1 (Figs. 4j, 5) much shorter epidermal cells of these roots contained DAB polymers mainly in the root hair formation sites (Fig. 4n). The lowest content of H2O2 expressed as the quantity of polymerised DAB was observed in the roots under HIL-3 influence (Fig. 5). Clearly the shortest epidermal cells of these roots contained DAB polymers mainly within the root hair zone (Fig. 4k, o).
Phenol content
Autofluorescence of the cross-sections of roots revealed differences in the localization and content of phenolic compounds (Figs. 6, 7). In the control cells, the blue autofluorescence induced by UV light was detected mainly in small vesicles or in a tubular network of endoplasmic reticulum (Fig. 6a–d). After the interference of the herbicides phenols accumulated mainly in relatively numerous large vacuoles. The content of phenols in the vacuoles was much higher in the cells coming from the HIL-treated seeds than in those treated with the traditional MCPA-salt (Figs. 6, 7e–h).
Cytological analysis of cells
Cytological staining of the control root meristems with Feulgen method revealed the presence of cells at each stage of cell cycle (Fig. 8a–g). The cytoplasm of these cells contained small high-density areas, which were visible in the phase-contrast microscope as opalising points (Fig. 8a′–g′). In root meristems under the influence of herbicides mitotic activity was almost completely inhibited (Fig. 9) and almost only interphase nuclei were observed (not shown). However, phase-contrast microscopy showed the presence of post-telophase cells joined by a common cell wall in the meristems coming from the seeds treated with HIL-3 (Fig. 8h, h′). Both the above-mentioned cells and others (not shown) contained significantly larger areas of increased cytoplasm density in comparison with the control cells. Furthermore, in the protruding zone of roots large cells filled with numerous Feulgen-positive structures (Fig. 8i) as well as iridescent Feulgen-negative structures were observed (Fig. 8i′).
Staining of the meristem cells and of those coming from the protruding zone with the mixture of Sudan III and IV revealed the presence of lipids, while staining with Lugol’s revealed also starch grains (Fig. 10). Areas occupied by lipids coincided with those previously seen opalising in the contrast-phase microscope, while, starch grains in plastids corresponded to Feulgen-positive areas. In the control meristem cells lipid substances were relatively less abundant than in the meristem cells affected by herbicides (Figs. 10a–d, 11). The most abundant lipids were accumulated in the meristem cells under the influence of HIL-3 (compare Fig. 10b–d). Similarly, the cells derived from the protruded zone were rich in lipids (Fig. 10f–h). Significant accumulation of emergency substances characterized also post-telophase cells which already ended the division of their nuclei but did not complete division of cytoplasm and were connected to a common cell wall (Fig. 10i–k).
Discussion
The current study aimed at comparing the impact of a traditional auxin herbicide, MCPA-salt and new MCPA-ionic liquids on the germination and growth of winter rape seedlings. It was shown that both formulations of MCPA caused similar morphological changes expressed in reduced growth and development of the roots and in consequence of whole seedlings, but it should be noted that MCPA-ionic liquid influence was stronger than that of MCPA-salt. The reason of this difference was looked for at the cellular level by assessing the contents of H2O2 and phenols and by analysing the activity of cell division, i.e. the parameters changing under the influence of different stress factors.
H2O2 serves as a signalling molecule activates defence responses to various stresses and is one of the constitutive attributes of plant root physiology. On the other hand, H2O2, like other highly reactive oxygen species (ROS), can disrupt normal metabolism through oxidative damage to lipids, proteins and nucleic acids (Dat et al. 2000; Neill et al. 2002; Vranová et al. 2002; Mittler et al. 2004; Gechev and Hille 2005; Cheng and Song 2006; Gapper and Dolan 2006; Kwak et al. 2006). Therefore, different antioxidative enzymes (e.g. peroxidases) play a key role in the ROS scavenging system. Peroxidases, depending on their chemical environment, can be considered as bifunctional in relation to H2O2. In the peroxidative cycle they catalyse the reduction of H2O2 (thus, converting H2O2 into water) by taking electrons from various donors: phenolic compounds, lignin precursors, auxin or secondary metabolites (thus oxidizing them; Passardi et al. 2004). Whereas in the hydroxylic cycle they can also promote the formation of H2O2, OH· or O ·−2 , provided that an appropriately strong reductant is present (Dunand et al. 2007). In our work H2O2 content was detected indirectly by the DAB-uptake method. DAB polymerizes giving brown staining of cells as soon as it comes into contact with H2O2 in the presence of endogenous peroxidase (Thordal-Christensen et al. 1997).
In the 3-day-old control seedlings of B. napus the presence of H2O2 was observed mainly in root hairs and also in the walls of root epidermal cells from the differentiation zone (where cell elongation ceases), but not in the root meristem and cell elongation zone. This is in line with the report showing that H2O2 is involved in root hair formation and in cell elongation restriction. H2O2 reduces root elongation by cross-linking cell wall constituents and diversification of cell wall composition (e.g. by lignin deposition; Foreman et al. 2003; Dunand et al. 2007). Under the influence of traditional MCPA a significant increase in H2O2 content (both in the cell differentiation and elongation zones) with simultaneous inhibition of cell and consequently root elongation were observed. The obtained results are consistent with the studies of Šimonovičová et al. (2004) showing that auxin herbicides caused oxidative stress and strong inhibition of barley root growth as a consequence of elevated H2O2 production through the root peroxidase system. Analogously, studies carried out by Grossmann et al. (2001) showed that auxin herbicides from different chemical classes caused reduction of internode elongation and stimulated H2O2 generation in Galium aparine L. shoot tissue. Moreover, results of Jin et al. (2010) indicated that herbicide ZJ0273 (a derivative of 2-pyrimidinyloxy-N-aryl benzoate) could deteriorate the enzymatic antioxidant system of rape plants, thereby exposing them to oxidative stress, by accumulating ROS, and ultimately affecting the plant growth. On the other hand, foliar application of 5-aminolevulinic acid (ALA; one of those plant growth regulators being used for stress amelioration) improved relative growth rate (root and shoot) of B. napus and also triggered the further accumulation of antioxidants activity, whereas decreased ROS (H2O2 and O2) production (Naeem et al. 2011; Zhang et al. 2008).
MCPA-ionic liquids (in particular HIL-3) used in these studies, caused a significantly weaker increase in the content of H2O2 in cells. Despite this they caused marked reduction of cell growth and inhibited elongation of roots. Research of Dunand and co-workers (2007) using H2O2 scavengers revealed that the decrease in the level of H2O2 was associated with intensification of cell and root elongation. In our study, lower levels of H2O2, generated by HILs did not correlate with cell and root elongation. On the contrary, cells were significantly shorter than those treated with conventional MCPA. These observations may indicate that mechanisms of HILs action differ from that of the traditional MCPA. On the other hand, in the HIL-treated roots significant (greater than under the influence of traditional MCPA) increase in the content of autofluorescent phenols was observed which may explain the low levels of H2O2 in cells. Phenols are effective scavengers of H2O2 because peroxidases use H2O2 for their oxidation (Passardi et al. 2004; Michalak 2006; Dunand et al. 2007). Increased oxidation of phenols with peroxidases might be the reason why peroxidase is not involved in the production of O ·−2 required for root elongation in the elongation zone and hence we sow no root elongation (Dunand et al. 2007). Such a hypothesis seems possible but requires further confirmation. The precise role of phenolic substances in the processes of differentiation and morphogenesis is still not clear, but it is known that they play an important role in plant stress resistance. In the current study cells dealt with the excess of exogenous auxin, and it is known that phenols modulate the action of auxin. High levels of phenols, through lowering the endogenous IAA content, might maintain appropriate hormonal balance required for root induction (Volpert et al. 1995; Passardi et al. 2004; Michalak 2006; Dunand et al. 2007). Therefore, it seems possible, that in our study cells triggered the production of phenols in order to restore disturbed physiological balance. Studies of Lee (1977) showed that phenolic compounds such as chlorogenic, coffeic, and ferulic acid could interact with IAA oxidase to reduce the rate of auxin oxidation and hence their degradation. While Faivre-Rampant et al. (2002) suggested that high concentration of chlorogenic acid exceeding a certain threshold concentration could lead to the opposite effect and cause the inhibition of root development. Similarly, the study of Schnablová et al. (2006) showed that monophenolic acid stimulated IAA oxidase activity and thereby contributed to the degradation of auxin.
In the current studies, the lack of root growth under the influence of all applied auxin herbicides was also the consequence of almost complete inhibition of meristematic cell division. In the root meristems there were mainly interphase cells probably blocked in the principal control points of the cell cycle, i.e. in the G1 and G2 phase (Polit et al. 2003). No abnormal mitotic figures and chromosome aberrations such as: matted chromosomes, chromosome fragmentation and chromosome bridges were observed. They were reported earlier in the study of Sikka and Sharma (1976) and Kumar et al. (2010) who treated Allium cepa and Triticum aestivum plants with hormonal herbicides. On the contrary, in our results the interphase cells began to accumulate significant amounts of lipids and starch grains. As reported in contemporary literature auxins affect cell division and cell elongation differentially (Campanoni and Nick 2005; Tsugeki et al. 2009; Mithila et al. 2011). Auxin influence on cell division is mediated by a heterotrimeric G-protein whereas that on cell elongation is independent of this protein. Involvement of different receptors may be associated with binding of different ligands. Various auxins should therefore affect cell division and cell elongation with varying dose–response relations through different signal transduction pathways activated by different receptors (Campanoni and Nick 2005). Cytological examination showed that particularly cells treated with HIL-3 that had just passed telophase began rapid growth and accumulation of large amounts of lipids and starch becoming similar to parenchyma cells. Inhibition of cell division and accumulation of large cells in the absence of elongation of epidermal cells result in reduction of meristem and formation of characteristic protruding zone of root. It is also the reason for cracking and detachment root tips. These protruding root segments could also hinder normal development of a vascular tissue as did the abnormal structures formed in roots and shoots under the influence of aminocyclopyrachlor (Flessner et al. 2011). In the present study, it seems that the mechanism or way of standard and ionic MCPA transport-induced changes of varying intensity within the observed cells. Before herbicides reach their site of action they must overcome a number of barriers, both at the tissue level and within membranes of a single cell (Riechers et al. 1994; DiTomaso 1999). Charged molecules definitely influence the efficiency of transport (Zsoldos and Haunold 1979).
Our findings are significant for plant protection based on conjugated phenoxy herbicides because they can lead to long periods of stable and wider performance. Additionally low pricing, worldwide availability, high volume potential, safety for people/environment, cross between green solvents and surfactants are advantageous. The potential of ionic liquids to conceptually fulfil the requirements of environmental sustainability is remarkable.
Author contribution
T. Praczyk, J. Pernak and E. Jakubiak prepared the new formulations of herbicides; Ł. Sobiech carried out, analysed and illustrated greenhouse and Petri dishes experiments; J.T. Polit planned, carried out, analysed, illustrated and described cytological part of the study; G. Skrzypczak was the initiator of research, prepared a theoretical introduction, modified the manuscript and supervised work.
References
Campanoni P, Nick P (2005) Auxin-dependent cell division and cell elongation. 1-naphthaleneacetic acid and 2,4-dichlorophenoxyacetic acid activate different pathways. Plant Physiol 137:939–948
Cheng Y, Song C (2006) Hydrogen peroxide homeostasis and signaling in plant cells. Sci China Ser C Life Sci 49:1–11
Dat J, Vandenabeele S, Vranová E, Van Montagu M, Inzé D, Van Bresugem F (2000) Dual action of the active oxygen species during plant stress response. Cell Mol Life Sci 57:779–795
DiTomaso JM (1999) Barriers to foliar penetration and uptake of herbicides. Proc Calif Weed Sci Soc 51:150–155
Dunand Ch, Crèvecoeur M, Penel C (2007) Distribution of superoxide and hydrogen peroxide in Arabidopsis root and their influence on root development: possible interaction with peroxidases. New Phytol 174:332–341
Faivre-Rampant O, Charpentier J-P, Kevers C, Dommes J, Van Onckelen H, Jay-Allemand C, Gaspar T (2002) Cuttings of the non-rooting rac tobacco mutant overaccumulate phenolic compounds. Funct Plant Biol 29:63–71
Flessner ML, Dute RR, McElroy JS (2011) Anatomical response of St. Augustine grass to aminocyclopyrachlor treatment. Weed Sci 59:263–269
Foreman J, Demidchik V, Bothwell JHF, Mylona P, Mledema H, Torres MA, Linstead P, Costa S, Brownlee C, Jones JDG, Davies JM, Dolan L (2003) Reactive oxygen species produced by NADPH oxidase regulate plant cell growth. Nature 422:442–446
Gapper C, Dolan L (2006) Control of plant development by reactive oxygen species. Plant Physiol 141:341–345
Gechev TS, Hille J (2005) Hydrogen peroxide as a signal controlling plant programmed cell death. J Cell Biol 168:17–20
Grossmann K (2000) The mode of action of quinclorac: a case study of a new auxin-type herbicide. In: Cobb AH, Kirkwood RC (eds) Herbicides and their mechanisms of action. Sheffield Academic Press, Sheffield, pp 181–214
Grossmann K (2010) Auxin herbicides: current status of mechanism and mode of action. Pest Manag Sci 66:113–120
Grossmann K, Kwiatkowski J, Tresch S (2001) Auxin herbicides induce H2O2 overproduction and tissue damage in cleavers (Galium aparine L.). J Exp Bot 52:1811–1816
Hough WL, Rogers RD (2007) Ionic liquids then and now: from solvents to materials to active pharmaceutical ingredients. Bull Chem Soc Jpn 80:2262–2269
Hough WL, Smiglak M, Rodríguez H, Swatloski RP, Spear SK, Daly DT, Pernak J, Grisel JE, Carliss RD, Soutullo DM, Davis JH, Rogers RD (2007) The third evolution of ionic liquids: active pharmaceutical ingredients. New J Chem 31:1429–1436
Jin ZL, Zhang F, Ahmed ZI, Rasheed M, Naeem MS, Ye QF, Zhou WJ (2010) Differential morphological and physiological responses of two oilseed Brassica species to a new herbicide ZJ0273 used in rapeseed fields. Pestic Biochem Physiol 98:1–8
Kirchner B (2009) Ionic liquids. Springer, Berlin
Kumar S, Arya SK, Roy BK, Singh AK (2010) The effects of 2,4-dichlorophenoxy acetic acid and isoproturon herbicides on the mitotic activity of wheat (Triticum aestivum L.) root tips. Turk J Biol 34:55–66
Kwak JM, Nguyen V, Schroeder JI (2006) The role of reactive oxygen species in hormonal responses. Plant Physiol 141:323–329
Lee TT (1977) Role of phenolic inhibitors in peroxidase-mediated degradation of indole-3-acetic acid. Plant Physiol 59:372–375
Maszewski J, Kaźmierczak A (1998) Repression of genetic activity in root meristem cells by peptidic factor derived from male sex organs of Chara. Biol Plant 41:357–368
Michalak A (2006) Phenolic compounds and their antioxidant activity in plants growing under heavy metal stress. Pol J Environ Stud 15:523–530
Mithila J, Hall JC, Johnson WG, Kelley KB, Riechers DE (2011) Evolution of resistance to auxinic herbicides: historical perspectives, mechanisms of resistance, and implications for broadleaf weed management in agronomic crops. Weed Sci 59:445–457
Mittler R, Vanderauwera S, Gollery M, van Breugesem F (2004) Reactive oxygen gene network of plants. Trends Plant Sci 9:490–498
Monaco TJ, Weller SC, Ashton FM (2002) Weed science: principles and practices. Wiley-Blackwell, New York
Naeem MS, Rasheed M, Liu D, Jin ZL, Ming DF, Yoneyama K, Takeuchi Y, Zhou WJ (2011) 5-Aminolevulinic acid ameliorates salinity-induced metabolic, water-related and biochemical changes in Brassica napus L. Acta Physiol Plant 33:517–528
Neill SJ, Desikan R, Clarke A, Hurst RD, Hancock JT (2002) Hydrogen peroxide and nitric oxide as signaling molecules in plants. J Exp Bot 53:1237–1247
Olivier-Bourbigou H, Magna L, Morvan D (2010) Ionic liquids and catalysis: recent progress from knowledge to applications. Appl Catal A 373:1–56
Passardi F, Penel C, Dunand Ch (2004) Performing the paradoxical: how plant peroxidases modify the cell wall. Trends Plant Sci 9:534–540
Passardi F, Tognolli M, De Meyer M, Penel C, Dunand Ch (2006) Two cell wall associated peroxidases from Arabidopsis influence root elongation. Planta 223:965–974
Pernak J, Syguda A, Janiszewska D, Materna K, Praczyk T (2011) Ionic liquids with herbicidal anions. Tetrahedron 67:4838–4844
Plechkova NV, Seddon KR (2008) Applications of ionic liquids in the chemical industry. Chem Soc Rev 37:123–150
Polit JT, Maszewski J, Kaźmierczak A (2003) Effect of BAP and IAA on the expression of G1 and G2 control points and G1-S and G2-M transitions in root meristem cells of Vicia faba. Cell Biol Int 27:559–566
Praczyk T, Kardasz P, Jakubiak E, Syguda A, Materna K, Pernak J (2012) Herbicidal ionic liquids with 2,4-D. Weed Sci 60:189–192
Riechers DE, Wax LM, Liebl RA, Bush DR (1994) Surfactant-increased glyphosate uptake into plasma membrane vesicles isolated from common lambsquarters leaves. Plant Physiol 105:1419–1425
Rogers RD, Seddon KR (2003a) Ionic liquids as green solvents: progress and prospects. American Chemical Society, Washington DC
Rogers RD, Seddon KR (2003b) Ionic liquids—solvents of the future? Science 302:792–793
Schnablová R, Synková H, Vičánková A, Burketová L, Eder J, Cvikrová M (2006) Transgenic ipt tobacco overproducing cytokinins overaccumulates phenolic compounds during in vitro growth. Plant Physiol Biochem 44:526–534
Schoenwaelder MEA (2008) The biology of phenolic containing vesicles. Algae 23:163–175
Senseman SA (2007) Herbicide handbook. Weed Science Society of America, Lawrence
Sikka K, Sharma AK (1976) The effects of some herbicides on plant chromosomes. Proc Indian Natl Sci Acad 42:299–307
Šimonovičová M, Huttová J, Mistrík I, Široká B, Tamás L (2004) Peroxidase mediated hydrogen peroxide production in barley roots grown under stress conditions. Plant Growth Regul 44:267–275
Thordal-Christensen H, Zhang Z, Wei Y, Collinge DB (1997) Subcellular localization of H2O2 in plants. H2O2 accumulation in papillae and hypersensitive response during the barley-powdery mildew interaction. Plant J 11:1187–1194
Tsugeki R, Ditengou FA, Sumi Y, Teale W, Palme K, Okada K (2009) NO VEIN mediates auxin-dependent specification and patterning in the Arabidopsis embryo, shoot, and root. Plant Cell 21:3133–3151
Volpert R, Osswald W, Elstner EF (1995) Effects of cinnamic acid derivatives on indole acetic acid oxidation by peroxidase. Phytochemistry 38:19–22
Vranová E, Inzé D, Van Brensegem F (2002) Signal transduction during oxidative stress. J Exp Bot 53:1227–1236
Wasserscheid P, Welton T (2008) Ionic liquids in synthesis. Wiley, Weinheim
Zhang WF, Zhang F, Raziuddin R, Gong HJ, Yang ZM, Lu L, Ye QF, Zhou WJ (2008) Effects of 5-aminolevulinic acid on oilseed rape seedling growth under herbicide toxicity stress. J Plant Growth Regul 27:159–169
Zsoldos F, Haunold E (1979) Effects of pH changes on ion and 2,4-D uptake of wheat roots. Physiol Plant 47:77–80
Author information
Authors and Affiliations
Corresponding author
Additional information
Communicated by A. Gniazdowska-Piekarska.
Rights and permissions
Open Access This article is distributed under the terms of the Creative Commons Attribution License which permits any use, distribution, and reproduction in any medium, provided the original author(s) and the source are credited.
About this article
Cite this article
Polit, J.T., Praczyk, T., Pernak, J. et al. Inhibition of germination and early growth of rape seed (Brassica napus L.) by MCPA in anionic and ester form. Acta Physiol Plant 36, 699–711 (2014). https://doi.org/10.1007/s11738-013-1448-x
Received:
Revised:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s11738-013-1448-x