- Open Access
Humic substances stimulate maize nitrogen assimilation and amino acid metabolism at physiological and molecular level
© Vaccaro et al.; licensee Springer. 2015
- Received: 29 November 2014
- Accepted: 20 January 2015
- Published: 13 February 2015
The effects of a humic substance (HS) extracted from a volcanic soil on the nitrate assimilation pathway of Zea mays seedlings were thoroughly examined using physiological and molecular approaches. Plant growth, the amount of soluble proteins and amino acids, as well as the activities of the enzymes involved in nitrogen metabolism and Krebs cycle, were evaluated in response to different HS concentrations (0, 1 and 5 mg C L−1) supplied to maize seedlings for 48 h. To better understand the HS action, the transcript accumulation of selected genes encoding enzymes involved in nitrogen assimilation and Krebs cycle was additionally evaluated in seedlings grown for 2 weeks under nitrogen (N) sufficient condition and N deprivation.
HS at low concentration (1 mg C L−1) positively influenced nitrate metabolism by increasing the content of soluble protein and amino acids synthesis. Furthermore, the activity and transcription of enzymes functioning in N assimilation and Krebs were significantly stimulated.
HS treatment influenced the gene expression of Zea mays plants at transcriptional level and this regulation was closely dependent on the availability of nitrate in the growth medium.
- Humic substances
- Biological activity
- Gene expression
- Nitrogen metabolism
Humic substances (HS) are the major components of soil organic matter (SOM) and positively affect crop production  by playing pivotal roles on both soil-plant system  and plant metabolism and development [3-6]. The growing concern for sustainable agriculture, whose goals are to ensure lower environmental costs and long-term productivity of agro-ecosystems , highlights the importance of developing management strategies to maintain and 1protect soil resources and, in particular, SOM . Despite this present awareness, the second half of the past century has seen a massive and indiscriminate use of high-energy input in agriculture and in particular of N fertilizers during the so-called green revolution. These practices led to the selection of genotypes, which were highly productive when fed with high nitrogen inputs, though not efficient in nitrogen use , while they concomitantly caused a progressive impoverishment of soil physical and biological properties, as well as of SOM and nutrients’ bioavailability.
Because of the importance of HS in soil fertility, a larger number of works focused on both the chemical-physical structure and the biological properties of humic matter. HS have been traditionally described as polydispersed heterogeneous organic compounds with large molecular weight . However, recent experimental findings reached a new understanding of the humic conformational nature that is regarded as a supramolecular association of heterogeneous molecules with relatively low molecular weight (≤1.5 kD) held together in only apparently large molecular sizes by weak interactions, such as hydrogen and hydrophobic bondings. The metastable conformations of humic associations can be reversibly disrupted by interactions with small amounts of organic acids [11,12], while the same amount of acids do not alter conformation of the true macropolymers stabilized by covalent bonds . The supramolecular nature of humic matter and its response to organic acids have been advocated to explain the bioactivity of humus on plants , its molecular dynamics  and the slow release of sorbed contaminants . Furthermore, the recognition that NOM is composed by supramolecular associations rather than macropolymers has allowed the development of a fractionation strategy, called humeomics, that enables the analytical detection of most of the single molecules which constitute the supramolecular assembly [16-18]. These findings had profound implications on our understanding of SOM function and reactivity.
Several studies have reported the positive effect of HS on crop yield [19-21] and on root and shoot development [6,22]. In addition, leaf chlorophyll content , nutrient uptake [3,23-26] and the activities of enzymes involved in several physiological pathways, such as nitrogen assimilation [3,24,25,27] and energy metabolism [28-30], seem to be positively affected by HS. However, because of the complexity of HS’ nature, the relationship between their molecular structure and biological activity is not yet completely clear. In the last decades, several studies correlated biological activity to humic chemical features [31-41]. The positive effects of different HS in relation to their chemical structure were shown by Muscolo et al.  and Nardi et al.  on Pinus nigra callus metabolism and Zea mays seedling growth. Moreover, Zancani et al. [42,43] successfully related humic matter molecular features to metabolism of tobacco BY-2 suspension cell cultures and to changes of cellular ATP and glucose-6-phosphate during embryogenesis of Abies cephalonica.
Furthermore, the complexity of the biological action exerted by HS on plant metabolism suggested the existence of hormonal mechanisms, in particular of an auxin-like effect [3,4]. The presence of low amount of IAA in different soil humic substances has been reported [33,44]. Moreover, these substances seem to have a physiological effect on both a maize isoform of H+ ATPase Mha2 [34,37,38], which is a specific auxin target, and a pea phospholipase A2 , which is a component of an auxin-dependent signalling.
The objective of this work was to investigate the effect of humic matter on maize nitrate assimilation and amino acids metabolism when the humic concentration was varied. The response of growth, protein and free amino acid content of maize seedlings to humic supply was evaluated here. Moreover, the activity of the main enzymes involved in the Krebs cycle and nitrogen metabolism was determined, together with the expression of genes encoding the enzymes involved in these two metabolic pathways.
Soil humic matter extraction and chemical characterization
A humic acid (HA) from a Fulvudand soil of the volcanic caldera of Vico, near Rome, Italy, was isolated by standard methods as reported elsewhere . The HA was titrated to pH 7.2 with a 0.5 M KOH solution in an automatic titrator (VIT 90 video titrator, Radiometer, Copenhagen, Denmark) under N2 atmosphere and stirring. After reaching the constant pH 7.2, the solution containing potassium humate was left under titration for 2 h, filtered through a glass microfibre filter (Whatman GF/C; GE Healthcare, Buckinghamshire, UK) and freeze-dried. The elemental analyses and the molecular characterization of this HA by online thermochemolysis-GC-MS and CPMAS-NMR spectroscopy were reported earlier .
Plant material, growth solutions and HS treatment
Maize seeds (Z. mays L. var. DK 585) were soaked in distilled water for one night in running water and germinated for 60 h in the dark at 25°C on a filter paper wet with 1 mM CaSO4 . Then, the maize seedlings were raised in hydroponic conditions for 14 days in growth chamber with 450 mL of a complete nutrient solution (μM) containing KH2PO4 (40), Ca(NO3)2 (200), KNO3 (200), MgSO4 (200), FeNaEDTA (10), H3BO3 (4.6), CuCl2·2H2O (0.036), MnCl2·4H2O (0.9), ZnCl2 (0.09) and NaMoO4·2H2O (0.01). The solution was renewed every 48 h. Growth chamber conditions were the following: day/night period of 14/10 h, air temperature of 27°C/21°C, relative humidity of 6%0/80% and photon flux density (PFD) of 280 μmol m−2 s−1.
To evaluate morphometric parameters, protein and free amino acids content and enzyme activities, on the 12th day of growth, the plants were treated for 48 h with aqueous solutions in which the freeze-dried potassium humate was dissolved at different concentrations expressed as carbon weight per litre: 0 (control), 1 and 5 mg C L−1.
To evaluate the transcript accumulation, the HS were applied on the 13th day at 1 mg C L−1 for 24 h to two different control solutions: a complete nutrient solution (see above) and a nutrient solution N-deprived, where N sources KNO3 and Ca(NO3)2 4H2O were replaced with KCl and CaCl2*2H2O at the same concentrations. The expression analyses were performed by semi-quantitative reverse transcriptase-polymerase chain reaction (RT-PCR) on cDNA obtained from leaves and root tissues.
Determination of protein content
For the extraction of soluble protein, frozen foliar and root tissue (0.5 g) were ground in liquid nitrogen, stirred with the extraction buffer (100 mM Tris-HCl pH 7.5, 1 mM Na2EDTA, 5 mM DTT) and centrifuged at 14,000 g. The supernatants were mixed with 10% (w/v) trichloroacetic acid (TCA) and centrifuged. The pellets obtained were then re-suspended in 0.1 N NaOH. The amount of total proteins in the leaves was determined by using the Bradford method  with bovine serum albumin as a standard. The results were expressed as mg protein/gramme fresh tissue.
Enzyme extraction and assay conditions
The enzymes were solubilized from leaves by manually crashing vegetal tissues in a mortar added with a 100 mM Hepes-NaOH solution at pH 7.5, a 5 mM MgCl2 solution, and a 1 mM dithiothreitol (DTT) solution. The ratio of plant material to mixture solution was 1:3 w/v. The extract was filtered through two layers of muslin and clarified by centrifugation at 20,000 g for 15 min. The supernatant was used for enzymatic analysis. All steps were carefully performed at 4°C, while a Jasco V-530 UV-vis spectrophotometer (Jasco Co., Midrand, Gauteng, South Africa) was used for measuring enzyme activity.
The nitrate reductase (NR EC 18.104.22.168) activity was assayed according to Lewis and collaborators  and expressed as unit per milligramme protein. One unit corresponds to the production of 1 μmol of NO2 − per minute at 25°C.
The nitrite reductase (NiR EC 22.214.171.124) activity was determined on the basis of the drop in NO2 − concentration in the reaction medium . After incubation at 30°C for 30 min, the NO2 − content was determined colorimetrically at A 540 and the activity was expressed as unit per milligramme protein. One unit corresponds to the consumption of 1 μmol of NO2 − per minute at 25°C.
To evaluate the glutamine synthetase (GS EC 126.96.36.199) activity, the mixture for the assay contained 90 mM imidazole-HCl (pH 7.0), 60 mM hydroxylamine (neutralized), 20 mM Na2KAsO4, 3 mM MnCl2, 0.4 mM ADP, 120 mM glutamine and the appropriate amount of enzyme extract. The assay was performed in a final volume of 750 μL. The enzymatic reaction was developed for 15 min at 37°C. γ-Glutamyl hydroxamate (gh) was colorimetrically determined by addition of 250 μL of a mixture (1:1:1) of 10% (w/v) FeCl3.6H2O in 0.2 M HCl, 24% (w/v) trichloroacetic acid and 50% (w/v) HCl. The optical density was recorded at A 540 . The activity was expressed as unit per milligramme protein. One unit corresponds to the production of 1 μmol mg protein per minute at 37°C.
NADH-dependent glutamate synthase (NADH-GOGAT EC 188.8.131.52) assay contained 25 mM Hepes-NaOH (pH 7.5), 2 mM L−1 glutamine, 1 mM α-ketoglutaric acid, 0.1 mM β-NADH, 1 mM Na2 EDTA and 100 μL of enzyme extract in a final volume of 1.1 mL. GOGAT was assayed spectrophotometrically by monitoring β-NADH oxidation at A 340 . The activity was expressed as unit per milligramme protein. One unit corresponds to the oxidation of 1 μmol of β-NADH per minute at 37°C.
The activity of aspartate aminotransferase (AspAT EC 184.108.40.206) was measured spectrophotometrically by monitoring β-NADH oxidation at A 340 at 30°C. The assay medium (final volume 2.4 mL) contained 100 mM Tris-HCl at pH 7.8, 240 mM L-aspartate (Asp), 0.11 mM pyridoxal phosphate, 0.16 mM NADH, 0.93 kU malate dehydrogenase (MDH), 0.42 kU lactate dehydrogenase (LDH), 12 mM 2-oxoglutarate and 200 μL enzyme extract . The activity was expressed as unit per milligramme protein. One unit corresponds to the oxidation of 1 μmol of β-NADH per minute at 37°C.
The activity of asparagine synthetase (AS EC 220.127.116.11) was determined by incubating 10 mM glutamine (Gln), 30 mM ATP, 10 mM Asp, 10 mM MgCl2, 2 mM DTT, 0.1 mM EDTA, Hepes 50 mM pH 7.75 with 400 μL of the desalted extract in a total volume of 500 μL at 30°C for 60 min. The reaction was terminated with 100 μL of sulfosalicylic acid (200 mg mL−1), centrifuged and an aliquot of the supernatant, adjusted to pH 7.0 with NaOH and taken for the analysis and separation of Asp and Asn by HPLC of the ortho-phthalaldehyde (OPA) reagent derivates . The activity was expressed as unit per milligramme protein. One unit corresponds to the production of 1 μmol of Asn per minute at 30°C.
For the assay of citrate synthase (CS EC 18.104.22.168), the leaves were homogenized using 100 mM Tris-HCl buffer pH 8.2, containing 5 mM β-mercaptoethanol (Sigma-Aldrich, St. Louis, MO, USA), 1 mM Na2EDTA and 10% glycerol. The leaves were filtered and centrifuged as reported . All steps were performed at 4°C. The CS enzyme was assayed adding 50 mL of oxalacetic acid 0.17 mM, 50 mL acetyl-CoA 0.2 mM, and 10 mL extract, to 3 mL of Tris-HCl 0.1 M (pH 8.0). This activity was measured spectrophotometrically at 25°C, by monitoring the reduction of acetyl-coenzyme A (acetyl-CoA) to CoA, at wavelength A 232 . The activity was expressed as unit per milligramme protein. One unit corresponds to the reduction of 1 μmol of acetyl-CoA per minute at 30°C.
To extract NADP+-isocitrate dehydrogenase (NADP+-IDH EC 22.214.171.124) and MDH (EC 126.96.36.199), the leaves were homogenized using 100 mM Tris-HCl buffer pH 8.2 containing 5 mM β-mercaptoethanol (Sigma), 1 mM Na2EDTA and 10% glycerol. The extracts were filtered and centrifuged as reported . All steps were performed at 4°C.
For NADP+-IDH activity, 50 μL of crude extract was added to 2.85 final volume of a reaction mixture containing 88 mM imidazole buffer (pH 8.0), 3.5 mM MgCl2, 0.41 mM β-NADP-Na salt and 0.55 mM isocitrate-Na salt. The assay was performed at 25°C following the formation of NADP(H) at A 340 . The activity was expressed as unit per milligramme protein. One unit corresponds to the production of 1 μmol of NADP(H) per minute.
For MDH activity, 3.17 mL of assay mixture contained 94.6 mM phosphate buffer (pH 6.7), 0.2 mM β-NADH-Na2 salt, 0.5 mM oxalacetic acid, and 1.67 mM MgCl2. MDH activity was assayed at 25°C, following the formation of NAD+ at A 340 . The activity was expressed as unit per milligramme protein. One unit corresponds to the production of 1 μmol of NAD+ per minute.
Free amino acids determination
The free amino acids were analyzed, as by the method of Seebauer et al. . Fifty milligrammes of homogenous dry powder was extracted for 1 h at room temperature with 1.5 mL of a 5% (w/v) TCA solution. The sample was clarified by centrifugation, and 1.5 mL of the supernatant was analyzed for free amino acids. The amino acid analysis was accomplished by precolumn OPA derivatization of the sample followed by reverse phase separation, using an Agilent 1100 HPLC (Agilent Technologies, Palo Alto, CA, USA) equipped with a thermo-controlled auto-sampler, fluorescence detector and an Agilent HP Chemstation for data elaboration. The chromatographic conditions were described previously .
RNA extraction and cDNA synthesis
The tissue samples were ground in liquid nitrogen. Aliquots of approximately 100 mg were used for RNA extraction using TRIzol reagent (Invitrogen, Carlsbad, CA, USA) according to the manufacturer's instructions. RNA was quantified by spectrophotometric reading, and the quality was assayed by agarose gel electrophoresis. After DNAse treatment (Promega, Milan, Italy), first-strand cDNA was synthesized from 5 μg of total RNA using 200 U of MMLV Reverse Transcriptase (Promega, Milan, Italy) and oligo(dT) as a primer in 20 μL reactions, as described by Sambrook and collaborators .
Semi-quantitative RT-PCR analysis
Specific forward and reverse primer sequences used in semi-quantitative RT-PCR
Primer forward (5′-3′)
Primer reverse (5′-3′)
NR (nitrate reductase)
AS (asparagine synthetase)
CS (citrate synthetase)
IDH (isocitrate dehydrogenase)
MDH (malate dehydrogenase)
All sets of experiments were repeated three times, and for each set three replicates were assayed. Data were the means of three replicates, and the standard deviations did not exceed 5%. The results obtained were processed statistically by the Student-Newman-Keuls test .
Effects of HS treatments on plant growth
Effects of HS treatments on protein content and enzyme activities
Effect of HS treatment on the amino acid content
Amino acid contents (μmol g −1 fw) in leaves
1.74 ± 0.3
1.97 ± 0.52
1.8 ± 0.45
2.78 ± 0.92
3.06 ± 0.96
2.76 ± 0.92
1.31 ± 0.27
1.46 ± 0.35
1.3 ± 0.62
1.36 ± 0.32
1.53 ± 0.47
1.3 ± 0.31
1.7 ± 0.4
1.55 ± 0.18
2.4 ± 0.39
2.85 ± 0.90
3.19 ± 0.96
2.71 ± 0.52
Effect of humic sample on gene expression
A similar expression pattern in response to humic substances provision was also observed for the genes encoding MDH, CS and IDH enzymes which are involved in the Krebs cycle and N organication. In the case of MDH, a slight decrease of mRNA abundance was found in N-deprived leaves after humic supply. Moreover, the transcript level of these three genes was always lower in N deficiency conditions in respect to that for N-supplied plants.
Since the 1980s, several studies have highlighted the existence of biological effects of HS on plant physiology and metabolism [1,3,6,25,32]. However, only more recently, the attention of researchers has been focused on HS fractions characterized by an apparently low-molecular-weight (LMW), which seems to influence plant growth and physiology more than other fractions [3,63]. In fact, several works focused on effects of LMW fraction on nitrogen uptake [33,34,37,64] and assimilation , but the results obtained were often contradictory [66,67]. Their positive effects have mainly been attributed to a large content of carbohydratic and carboxyl-C groups [32,68].
More recently, Nardi and coworkers  evaluated the effect on the respiratory metabolism of maize seedlings provided by different size fractions of a soil humic acid, after their separation by preparative high-performance size-exclusion chromatography (HPSEC). The evaluation of the biological activity of size fractions showed that the size fraction with the smallest molecular size was more bioactive, followed by, in the order of, both the original bulk humic acid and the larger size fractions. Such effect was attributed to the larger flexibility of the smallest size fraction conferred by its greater content of hydrophilic components . In fact, both the conformational flexibility and the hydrophilicity of this small-sized humic fraction should facilitate the release from its supramolecular structure upon the action of organic acids exuded by roots of humic molecules with plant stimulation activity. The diffusion of such bioactive molecules in solution should be less easy from humic matrices with larger and more compact conformations [37,38,69]. Here, we used the same bulk humic acid that was found bioactive and second only to its separated smallest size fractions in order to evaluate its effects on nitrogen assimilation in maize at both physiological and molecular levels. This species was chosen because of its worldwide economic and agronomic importance and also because of its importance as a model plant .
Our results indicate that the HS treatment influenced the activities of all these enzymes in a dose-dependent manner. In particular, the increase of enzyme activity in relation to the dose of HS supplied was exponential as a significant stimulation was observed when plants were treated with 5 mg C L−1. A different trend was observed for AS, because its specific activity was strongly stimulated only in response to the 5 mg C L−1 humic solution, while it was slightly inhibited by the 1 mg C L−1 treatment.
The synthesis of Asn is in competition with that of Asp, Lys, Thr and Ile, which represent, together with the amino acids of the aspartate family , the main substrates for the synthesis of structural proteins and enzymes required for the optimal plant development . However, Asn may also represent a transitory store of N to be later used to meet specific demands during plant growth . Our results showed a significantly higher accumulation of Lys, Ile and Thr in leaves of seedlings grown with 1 mg C L−1 of HS in comparison to those observed in control plants that is in accordance with the higher content of soluble proteins measured in HS-treated leaves.
To deepen the understanding of molecular events underlying the HS effects on plant physiology, the expression of five genes encoding the enzymes involved in few key steps of N assimilation was evaluated. To discriminate N-dependent from N-independent molecular effects of HS, the transcript amount was measured in leaves of both nitrate-supplied and nitrate-depleted HS-treated seedlings. In this case, the choice of a 24-h treatment was aimed at evaluating the earlier molecular effects of humic matter. In fact, Trevisan et al.  showed that the gene transcription in response to HS is regulated already after a few hours of treatment.
Our findings show an increase of mRNA abundance of all genes therein studied upon HS treatment only when seedlings were grown in the presence of nitrate. On the contrary, HS did not induce any increase of transcript accumulation when the nutrient solution was depleted of nitrate. These results globally suggest that the enzyme stimulation observed after the humic supply may be generally regulated at the transcriptional level. An exception seems to be represented by the expression of the AS gene that was strongly induced after 24 h of treatment with 1 mg C L−1 solution, whereas the AS activity measured after 48 h was lower than for the control. This may be due either to a more rapid down-regulation of the AS activity in response to the duration of HS treatment or otherwise to the occurrence of some post-transcriptional regulatory mechanisms. Furthermore, since most of the genes analyzed are nitrate-responsive, it may be hypothesized that the HS regulation of the transcription of genes involved in nitrogen metabolism may be mediated by a nitrate-dependent signal, since HS’ stimulatory effect is evident only when the nutrient solution contained nitrate.
Our results indicate a positive dose-dependent effect of the humic acid used here on the activities of the main enzymes involved in the reduction and assimilation of inorganic nitrogen. The enhanced bioactivity of HS may be explained with the tendency to increase the size of supramolecular aggregation of humic molecules with concentration  and the concomitant enhanced capacity to provide specific bioactive molecules to targeted root cell membranes .
Among all enzymes, only the AS showed a different trend of regulation in response to HS, possibly because of a competition of its own substrate with the biosynthesis of amino acids of the Asp family , thus favouring the accumulation of a large amount of Asn in seedling leaves treated with the greatest HS concentration. This is not surprising considering that Asn accumulation in young leaves is an indirect result of the restriction of protein synthesis when the metabolism is subjected to stress conditions . While further studies should be certainly conducted to increase our understanding on the dose-response of HS, molecular findings suggest that the biochemical response to humic treatments may principally depend on a transcriptional mechanism of regulation, as previously hypothesized for the regulation of a maize isoform of H+-ATPase  and with a more holistic approach by Trevisan et al. . However, the induction of a gene expression in response to HS seems to depend closely on the presence of nitrate in the growing medium because humic matter alone was not able to up-regulate the transcription of genes. These findings suggest that HS may act as an additional signal in the regulation of gene expression mediated by nitrate, by either promoting its bioavailability or interfering with the signalling pathway that leads plants to adapt their metabolism to the nutrient availability [64,76].
This work was partially supported by the project COFIN 2003 no. 2003071271 funded by the Italian Ministry of University and Research (MIUR).
- Vaughan D, Malcom RE (1985) Influence of humic substances on growth and physiological processes. In: Vaughan D, Malcom RE (ed) Soil organic matter and biological activity. Martinus Nijhoff/Junk W, Dordrecht, pp 37–76View ArticleGoogle Scholar
- Piccolo A (1996) Humic substances in terrestrial ecosystems. Elsevier, Amsterdam, pp 225–264View ArticleGoogle Scholar
- Nardi S, Carletti P, Pizzeghello D, Muscolo A (2009) Biological activities of humic substances. In: Senesi N, Xing B, Huang PM (ed) Biophysico-chemical processes involving natural nonliving organic matter in environmental systems. Part I. Fundamentals and impact of mineral-organic-biota interactions on the formation, transformation, turnover, and storage of natural nonliving organic matter (NOM). Wiley, Hoboken, pp 305–339Google Scholar
- Muscolo A, Sidari M, Nardi S (2013) Humic substance: relationship between structure and activity. Deeper information suggests univocal findings. J Geochem Explor 129:57–63View ArticleGoogle Scholar
- Nardi S, Pizzeghello D, Reniero F, Rascio N (2000) Chemical and biochemical properties of humic substances isolated from forest soils and plant growth. Soil Sci Soc Am J 64:639–645View ArticleGoogle Scholar
- Canellas LP, Olivares FL (2014) Physiological responses to humic substances as plant growth promoter. Chem Biol Technol Agric 1:1–11View ArticleGoogle Scholar
- Horrigan L, Lawrence RS, Walker P (2002) How sustainable agriculture can address the environmental and human health harms of industrial agriculture. Environ Health Persp 110:445–456View ArticleGoogle Scholar
- Smith EG, Young DL (2000) The economic and environmental revolution in semi-arid cropping in North America. Annal Arid Zone 39:347–361Google Scholar
- Hirel B, Le Gouis J, Ney B, Gallais A (2007) The challenge of improving nitrogen use efficiency in crop plants: towards a more central role for genetic variability and quantitative genetics within integrated approaches. J Exp Bot 58:2369–2387View ArticlePubMedGoogle Scholar
- Stevenson FJ (1994) Humus chemistry: genesis, composition, reactions, 2nd edition. Wiley, New YorkGoogle Scholar
- Piccolo A (2002) The supramolecular structure of humic substances. A novel understanding of humus chemistry and implications in soil science. Adv Agron 75:57–134View ArticleGoogle Scholar
- Piccolo A, Conte P, Spaccini R, Chiarella P (2003) Effects of some dicarboxylic acids on the association of dissolved humic substances. Biol Fert Soils 37:255–259Google Scholar
- Piccolo A, Conte P, Cozzolino A (2001) Chromatographic and spectrophotometric properties of dissolved humic substances compared with macromolecular polymers. Soil Sc 166:174–185View ArticleGoogle Scholar
- Orsi M (2014) Molecular dynamics simulation of humic substances. Chem Biol Technol Agric 1:1–14View ArticleGoogle Scholar
- Beiraghi A, Pourghazi K, Amoli-Diva M (2014) Mixed supramolecular hemimicelles aggregates and magnetic carrier technology for solid phase extraction of ibuprofen in environmental samples prior to its HPLC-UV determination. Chem Eng Sci 108:103–110View ArticleGoogle Scholar
- Nebbioso A, Piccolo A (2011) Basis of a humeomics science: chemical fractionation and molecular characterization of humic biosuprastructures. Biomacromolecules 12:1187–1199View ArticlePubMedGoogle Scholar
- Nebbioso A, Piccolo A (2012) Advances in humeomic: enhanced structural identification of humic molecules after size fractionation of a soil humic acid. Anal Chim Acta 720:77–90View ArticlePubMedGoogle Scholar
- Nebbioso A, Piccolo A, Lamshoft M, Spiteller M (2014) Molecular characterization of an end-residue of humeomics applied to a soil humic acid. RSC Adv 4:23658–23665View ArticleGoogle Scholar
- Niklewski B, Woiciechowski J (1937) Uber den Einfluss der wasserlöslichen Humusstoffe auf die Entwicklung einiger Kulturpflanzen. Z. Pflanzenernaehr Dueng. Bodenkd 49:294–327Google Scholar
- Čatsky J (1958) Uber den Einfluss der Oxy humolithen auf die mineralische Ernährung der Pflanzen. Folia Biol 4:443–448Google Scholar
- Khristeva LA, Gallushko AM, Gorovaya AI, Kolbassin AA, Shortshoi LP, Tkatshenko LK, Fot LW, Luk’Yakenko NV (1980) The main aspects of using physiologically active substances of humus nature. VI International Peat Congress, MinnesotaGoogle Scholar
- Nardi S, Concheri G, Dell’Agnola G (1996) Biological activity of humic substances. In: Piccolo A (ed) Humic substances in terrestrial ecosystems. Elsevier, Amsterdam, pp 361–406View ArticleGoogle Scholar
- Vaughan D, Linehan DJ (1976) The growth of wheat plants in humic acid solutions under axenic conditions. Plant Soil 44:445–449View ArticleGoogle Scholar
- Varanini Z, Pinton R (1995) Humic substances and plant nutrition. In: Behnke HD et al. (ed) Progress in botany, vol 56. Springer, Berlin, pp 97–117View ArticleGoogle Scholar
- Varanini Z, Pinton R (2001) Direct versus indirect effects of soil humic substances on plant growth and nutrition. In: Pinton R et al. (ed) The rizosphere. Marcel Dekker, Basel, pp 141–158Google Scholar
- Nardi S, Concheri G, Pizzeghello D, Sturaro A, Rella R, Parvoli G (2000) Soil organic matter mobilization by root exudates. Chemosphere 41:653–658View ArticlePubMedGoogle Scholar
- Vaccaro S, Muscolo A, Pizzeghello D, Spaccini R, Piccolo A, Nardi S (2009) Effect of a compost and its water-soluble fractions on key enzymes of nitrogen metabolism in maize seedlings. J Agric Food Chem 57:11267–11276View ArticlePubMedGoogle Scholar
- Sladky Z (1959) The effects of extracted humus substances on growth of tomato plants. Biolol Plant 1:142–150View ArticleGoogle Scholar
- Vaughan D (1967) Effect of humic acid on the development of invertase activity in slices of beetroot tissues washed under aseptic conditions. Humus et Planta 4:268–271Google Scholar
- Ferretti M, Ghisi R, Nardi S, Passera C (1991) Effect of humic substances on photosynthetic sulfate assimilation in maize seedlings. Can J Soil Sci 71:239–242View ArticleGoogle Scholar
- Nardi S, Concheri G, Dellagnola G, Scrimin P (1991) Nitrate uptake and ATPase activity in oat seedlings in the presence of 2 humic fractions. Soil Biol Biochem 23:833–836View ArticleGoogle Scholar
- Piccolo A, Nardi S, Concheri G (1992) Structural characteristics of humic substances as related to nitrate uptake and growth-regulation in plant-systems. Soil Biol Biochem 24:373–380View ArticleGoogle Scholar
- Canellas LP, Olivares FL, Okorokova-Facanha AL, Facanha AR (2002) Humic acids isolated from earthworm compost enhance root elongation, lateral root emergence, and plasma membrane H+-ATPase activity in maize roots. Plant Physiol 130:1951–1957View ArticlePubMed CentralPubMedGoogle Scholar
- Quaggiotti S, Ruperti B, Pizzeghello D, Francioso O, Tugnoli V, Nardi S (2004) Effect of low molecular size humic substances on nitrate uptake and expression of genes involved in nitrate transport in maize (Zea mays L.). J Exp Bot 55:803–813View ArticlePubMedGoogle Scholar
- Muscolo A, Sidari M, Attinà E, Francioso O, Tugnoli V, Nardi S (2007) Biological activity of humic substances is related to their chemical structure. Soil Sci Soc Am J 71:75–85View ArticleGoogle Scholar
- Nardi S, Muscolo A, Vaccaro S, Baiano S, Spaccini R, Piccolo A (2007) Relationship between molecular characteristics of soil humic fractions and glycolytic pathway and krebs cycle in maize seedlings. Soil Biol Biochem 39:3138–3146View ArticleGoogle Scholar
- Canellas LP, Piccolo A, Dobbss LB, Spaccini R, Olivares FL, Zandonadi DB, Façanha AR (2010) Chemical composition and bioactivity properties of size-fractions separated from a vermicompost humic acid. Chemosphere 78:457–466View ArticlePubMedGoogle Scholar
- Canellas LP, Dantas DJ, Aguiar NO, Peres LEP, Zsögön A, Olivares FL, Dobbss LB, Façanha AR, Nebbioso A, Piccolo A (2011) Probing the hormonal activity of fractionated molecular humic components in tomato auxin mutants. Ann Appl Biol 159:202–211View ArticleGoogle Scholar
- Pizzeghello D, Francioso O, Ertani A, Muscolo A, Nardi S (2012) Isopentenyladenosine and cytokinin-like activity of four humic substances. J Geochem Explor 129:103–111Google Scholar
- Trevisan S, Pizzeghello D, Ruperti B, Francioso O, Sassi A, Palme K, Quaggiotti S, Nardi S (2010) Humic substances induce lateral root formation and expression of the early auxin-responsive IAA19 gene and DR5 synthetic element in Arabidopsis. Plant Biol 12:604–614PubMedGoogle Scholar
- Trevisan S, Botton A, Vaccaro S, Vezzaro A, Quaggiotti S, Nardi S (2011) Humic substances affect Arabidopsis physiology altering the expression of genes involved in primary metabolism, growth and development. EEB 74:45–55View ArticleGoogle Scholar
- Zancani M, Petrussa E, Krajňáková J, Casolo V, Spaccini R, Piccolo A, Macrì F, Vianello A (2009) Effect of humic acids on phosphate level and energetic metabolism of tobacco BY-2 suspension cell cultures. Env Exp Bot 65:287–295View ArticleGoogle Scholar
- Zancani M, Bertolini A, Petrussa E, Krajňáková J, Piccolo A, Spaccini R, Vianello A (2011) Fulvic acid affects proliferation and maturation phases in Abies cephalonica embryogenic cells. J Plant Physiol 168:1226–1233View ArticlePubMedGoogle Scholar
- Muscolo A, Cutrupi S, Nardi S (1998) IAA detection in humic substances. Soil Biol Biochem 30:1199–1201View ArticleGoogle Scholar
- Russell L, Stokes AR, Macdonald H, Muscolo A, Nardi S (2006) Stomatal responses to humic substances and auxin are sensitive to inhibitors of phospholipase A(2). Plant Soil 283:175–185View ArticleGoogle Scholar
- Piccolo A, Conte P, Trivellone E, Van Lagen B, Buurman P (2002) Reduced heterogeneity of a lignite humic acid by preparative HPSEC following interaction with an organic acid. Characterization of size-separates by PYR-GC-MS and 1H-NMR spectroscopy. Envir Sci Technol 36:76–84View ArticleGoogle Scholar
- Nardi S, Sessi E, Pizzeghello D, Sturaro A, Rella R, Parvoli G (2002) Biological activity of soil organic matter mobilized by root exudates. Chemosphere 46:1075–1081View ArticlePubMedGoogle Scholar
- Bradford MM (1976) A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal Biochem 72:248–254View ArticlePubMedGoogle Scholar
- Lewis OAM, James DM, Hewitt EJ (1982) Nitrogen assimilation in barley (Hordeum vulgare L. cv. Mazurka) in response to nitrate and ammonium nutrition. Ann Bot 49:39–49Google Scholar
- Lillo C (1984) Diurnal variations of nitrite reductase, glutamine synthetase, glutamate synthase, alanine aminotransferase and aspartate aminotransferase in barley leaves. Physiol Plant 61:214–218View ArticleGoogle Scholar
- Cánovas FM, Cantón FR, Gallardo F, García-Gutiérrez A, De Vicente A (1991) Accumulation of glutamine synthetase during early development of maritime pine (Pinus pinaster) seedlings. Planta 185:372–378View ArticlePubMedGoogle Scholar
- Rej R, Horder M (1983) Aspartate aminotransferase (glutamate oxaloacetate transaminase). In: Methods of enzymatic analysis, 3rd edition. Bergmeyer, H. U, WeinheimGoogle Scholar
- Lima JD, Sodek L (2003) N-stress alters aspartate and asparagine levels of xylem sap in soybean. Plant Sci 165:649–656View ArticleGoogle Scholar
- Bergmeyer HU (1986) In: Bergmeyer J, Marianne G (ed) Methods of enzymatic analysis. Weinheim, BaselGoogle Scholar
- Goldberg DM, Ellis G (1986) Isocitrate. In: Bergmeyer HU (ed) Methods of enzymatic analysis. Academic, New YorkGoogle Scholar
- Seebauer JR, Moose SP, Fabbri BJ, Crossland LD, Below FE (2004) Amino acid metabolism in maize earshoots. Implications for assimilate preconditioning and nitrogen signaling. Plant Physiol 136:4326–4334View ArticlePubMed CentralPubMedGoogle Scholar
- Henderson JW, Ricker RD, Bidlingmeyer BA, Woodward C (2000) Rapid, accurate, sensitive and reproducible analysis of amino acids. Agilent Publication Number 5980-1193EN. Agilent Technologies, Palo AltoGoogle Scholar
- Sambrook J, Fritsch EF, Maniatis F (1989) Molecular cloning: a laboratory manual, 2nd edition. Cold Spring Harbor Laboratory, Cold Spring Harbor, New YorkGoogle Scholar
- Quaggiotti S, Ruperti B, Borsa P, Destro T, Malagoli M (2003) Expression of a putative high-affinity NO3 − transporter and of an H+-ATPase in relation to whole plant nitrate transport physiology in two maize genotypes differently responsive to low nitrogen availability. J Exp Bot 54:1023–1031View ArticlePubMedGoogle Scholar
- Sanger F, Nicklen S, Coulson AR (1977) DNA sequencing with chain-terminating inhibitors. PNAS 74:5463–5467View ArticlePubMed CentralPubMedGoogle Scholar
- Sokal RR, Rohlf FJ (1969) Biometry, 1st edition. Freeman & Co, San FranciscoGoogle Scholar
- Stevenson FJ (1994) Humus chemistry: genesis, composition, reactions, 2nd edition. Wiley, New YorkGoogle Scholar
- Nardi S, Pizzeghello D, Muscolo A, Vianello A (2002) Physiological effects of humic substances on higher plants. Soil Biol Biochem 34:1527–1536View ArticleGoogle Scholar
- Pinton R, Cesco S, Iacolettig G, Astolfi S, Varanini Z (1999) Modulation of NO3 − uptake by water-extractable humic substances: involvement of root plasma membrane H(+)ATPase. Plant Soil 215:155–161View ArticleGoogle Scholar
- Sessi E, Nardi S, Gessa C (2000) Effects of low and high molecular weight humic substances from two different soils on nitrogen assimilation pathway in maize seedlings. Humic Subst Environ 2:39–46Google Scholar
- Malcolm RE, Vaughan D (1979) Humic substances and phosphatase activities in plant tissues. Soil Biol Biochem 11:253–259View ArticleGoogle Scholar
- Mato MC, Olmedo MG, Mendez J (1972) Inhibition of indoleacetic acid-oxidase by soil humic acids fractionated on sephadex. Soil Biol Biochem 4:469–473View ArticleGoogle Scholar
- Nardi S, Pizzeghello D, Gessa C, Ferrarese L, Trainotti L, Casadoro G (2000) A low molecular weight humic fraction on nitrate uptake and protein synthesis in maize seedlings. Soil Biol Biochem 32:415–419View ArticleGoogle Scholar
- Piccolo A (2001) The supramolecular structure of humic substances. Soil Sci 166:810–833View ArticleGoogle Scholar
- Hirel B, Bertin P, Quillere I, Bourdoncle W, Attagnant C, Dellay C, Gouy A, Cadiou C, Retailliau S, Falque M, Gallais A (2001) Towards a better understanding of the genetic and physiological basis for nitrogen use efficiency in maize. Plant Physiol 125:1258–1270View ArticlePubMed CentralPubMedGoogle Scholar
- Azevedo RA, Lancien M, Lea PJ (2006) The aspartic acid metabolic pathway, an exciting and essential pathway in plants. Amino acids 30:143–162View ArticlePubMedGoogle Scholar
- Hirel B, Martin A, Terce-Laforgue T, Gonzalez-Moro MB, Estavillo JM (2005) Physiology of maize I: a comprehensive and integrated view of nitrogen metabolism in a C4 plant. Physiol Plant 124:167–177View ArticleGoogle Scholar
- Lea PJ, Sodek L, Parry MAJ, Shewry PR, Halford NG (2007) Asparagine in plants. Ann Appl Biol 150:1–26View ArticleGoogle Scholar
- Smejkalova D, Piccolo A (2008) Aggregation and disaggregation of humic supramolecular assemblies by NMR diffusion ordered spectroscopy (DOSY-NMR). Envir Sci Technol 42:699–706View ArticleGoogle Scholar
- Azevedo RA, Arruda P, Turner WL, Lea PJ (1997) The biosynthesis and metabolism of the aspartate derived amino acids in higher plants. Phytochem 46:395–419View ArticleGoogle Scholar
- Nikolic M, Cesco S, Römheld V, Varanini Z, Pinton R (2003) Uptake of iron complexed to water-extractable humic substances by sunflower leaves. J Plant Nutr 26:2243–2252View ArticleGoogle Scholar
This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly credited.