Skip to main content
Download PDF

Use of fulvic acid-like compounds from pulp-derived black liquor for enhancing the selenium content of peanut buds

BMC Plant Biology volume 22, Article number: 546 (2022) Cite this article

Abstract

Background

Cleaner production involving the extraction of useful material from the black liquor by-product of straw pulp would be environmentally beneficial and would permit increased wastewater usage.

Results

The fulvic-acid-like components of pulp black liquor (PFA) with molecular weights below 10 kDa were isolated. The chemical and physiological characteristics of PFAs were investigated. Selenite can enhance the selenium nutrition level of crops, but excessive selenite may be toxic to plant growth. In order to explore how to increase selenite tolerance and selenium accumulation in peanut, the effects of PFA on selenium-associated properties in peanut seedlings were examined by growing seedlings with sodium selenite (0, 5, 15, and 25 mg·L− 1 Na2SeO3, 15 mg·L− 1 Na2SeO3 solution containing 60 mg-C/L PFA, and 25 mg·L− 1 Na2SeO3 containing 60 mg-C/L PFA).

Conclusion

The results showed that with 15 mg·L− 1 Na2SeO3, PFA significantly increased both the total and hypocotyl fresh weight of the seedlings but reduced the fresh weight of the root. PFA also effectively promoted the conversion of Se from inorganic to organic compounds in the root and hypocotyl, increased the soluble total sugar and soluble protein contents of the hypocotyl, and thus improved the edible quality and food safety of the selenium-enriched peanut buds. The results suggest that PFA can be used as an innovative bio-based substance for selenium-enriched sprout vegetable production.

Peer Review reports

Introduction

Black liquor is a by-product in the paper industry and its treatment is essential for cleaner production. Cost-effective reclamation of the organic constituents in black liquor reduces potentially deleterious environmental effects of the waste material. Yao investigated the fulvic-acid-like components of black liquor (PFA), examining their chemical structures and effects on physiology and growth. These authors observed that salt-stressed rice seedlings grew well in the presence of low molecular weight (below 5 kDa) PFAs but less so in the presence of PFAs with higher molecular weights (above 10 kDa) [1]. PFAs from pulp black liquor were also reported to have the same growth-promoting activities in rice seed germination as compounds from leonardite [2].

Selenium (Se) is an essential mineral, playing vital roles in various metabolic processes, and Se deficiency can cause multiple health issues [3]. It has been found that organic compounds are a better source of Se than their inorganic counterparts due to their reduced toxicity [4, 5]. As plants convert Se from inorganic to organic forms, they are useful for the provision of organic Se compounds. Se levels in crop plants can be increased in several ways. The principal method is the use of Se-containing fertilizer [6]. However, not all plants are able to accumulate Se effectively; while Se-accumulating plants may be highly efficient in this respect [7], the majority are non-accumulators and may even be sensitive to high Se concentrations, resulting in damage such as poor growth and withered leaves [8]. In plants, Se toxicity is thought to be the consequence of the over-production of nonspecific selenoproteins, although recent evidence has suggested that Se-induced oxidative stress may also be responsible [9].

Peanuts (Arachis hypogaea L.) are grown throughout the world and are not Se hyperaccumulators [10]. Application of selenite to the soil has been shown to elevate the organic Se content of the peanut kernel, providing a useful source of organic Se for human nutrition [11]. Peanut sprout is a kind of sprout vegetable whose seeds germinate and grow into edible in a short time. However, the selenium content of peanut sprouts is lower than that of other selenium rich sprouts such as soybean sprouts and mung bean sprouts, and the proportion of organic selenium needs to be further improved to enhance its edible safety [12, 13]. If the selenium concentration in the culture medium is further increased, it will lead to excessive production of non-specific selenoproteins in plant tissues and peroxidation stress, resulting in toxicity to plants. Therefore, it is necessary to explore new methods of Se enrichment.

Fulvic acid (FA) is known to enhance plant growth as it has a low molecular weight [14], is rich in functional groups, and is able to pass through cell membranes with ease [15]. FA can induce changes in the primary and secondary metabolic pathways of plants associated with abiotic stress tolerance. PFA was similar to the FA extracted from leonardite (non-renewable resource). They contained similar elemental compositions and functional groups [2]. However, the compounds in paper mill effluents tend to be larger and thus lack the physiological activities necessary for agricultural utilization [16,17,18]. Here, we extracted PFAs from the spent liquor of ammonium sulfite pulping. After fractionation by ultrafiltration, PFAs of lower molecular weight (below 10 kDa) were used to investigate their use in the production of Se-enriched peanut sprouts under selenite stress.

Results and discussion

Elemental analyses

The elemental contents and atomic ratios of the pulp black liquor (PBL) and PFA are shown in Table 1. The PFA contained less C, N, H, S, and more O than PBL. The H/C ratio was inversely proportional to the aromaticity of a compound and the O/C ratio is directly proportional to the numbers of oxygen-containing functional groups such as carboxyl groups. Fulvic acid-like compounds have higher H/C and O/C ratios than other compounds in the PBL and thus are less aromatic and contain more oxygen-containing functional groups.

Table 1 Elemental composition and atomic ratio of PBL and PFA
Full size table

FT-IR spectroscopy

The infrared spectra of the PBL and PFA are illustrated in Fig. 1. Overall, a broad band in the region of 3400 cm− 1 resulted from both O-H stretching in hydroxyl groups derived from phenol or carboxyl groups. Bands in the region of 2900 cm− 1 were the consequence of both symmetric and asymmetric stretching vibrations in aliphatic C-H bonds in ethyl and methyl groups. The band seen at 1710 cm− 1 was the result of C=O stretching vibrations in carboxyl groups or derived from additional carbonyl components [19]. A substantial band at 1630 cm− 1 was caused by C=C vibrations in aromatic structures conjugated with C=O. PFA samples showed a band at 1465 cm− 1, resulting from C-H stretching in aliphatic ethyl and methyl moieties. Thus, more hydroxyl, carboxyl, and small active groups were present in PFA compared with PBL.

Fig. 1
figure 1

Infrared spectra of PBL and PFA. PBL, Pulp black liquor; PFA, fulvic acid-like in paper mill effluents

Full size image

PFA enhanced seedling growth under selenite stress

There was a gradual decrease in the total fresh weight, root fresh weight, and hypocotyl fresh weight of the peanut seedlings in response to increasing Na2SeO3 concentrations, while the cotyledon fresh weight did not change significantly; The total fresh weight of peanut seedlings treated with S3 and S4 decreased by 27.9 and 27.2%, respectively, compared with S1. In seedlings treated with 15 mg·L− 1 Na2SeO3, the addition of PFA (S5) significantly increased both the total and hypocotyl fresh weights by 23.8 and 21.5%, respectively, compared with S3. The addition of PFA did not affect the fresh weights of the roots and cotyledons. Treatment with 15 mg·L− 1 Na2SeO3 did not significantly alter either the total or hypocotyl fresh weights after the addition of PFA (S5) compared with the control (S1), although the root fresh weight decreased by 56%. When PFA (S6) was added to seedlings treated with 25 mg·L− 1 Na2SeO3, the total and hypocotyl fresh weights did not change in comparison with S4 but were significantly reduced compared with the control (S1). These results indicate that in 15 mg · L− 1 Na2SeO3 treatment, the addition of PFA can significantly improve the total fresh weight of peanut seedlings, which has no significant difference with the control (Fig. 2).

Fig. 2
figure 2

Effects of PFA on the fresh weight of peanut (Arachis hypogaea L.) seedlings treated with different selenite concentrations on the 3rd day and 5th day after germination (S1-S6: 0, 5, 15, and 25 mg·L− 1 Na2SeO3, 15 mg·L− 1 Na2SeO3 solution containing 60 mg-C/L PFA, and 25 mg·L− 1 Na2SeO3 containing 60 mg-C/L PFA. The same as below). Letters above the bars indicate significant differences (P < 0.05). Vertical bars represent ± SD (n = 5). A Total fresh weight, B Fresh weight of roots, C Fresh weight of hypocotyls, D Fresh weight of cotyledons

Full size image

The diameters of the peanut hypocotyl did not change significantly with the different treatments; however, the hypocotyl lengths did decrease significantly with increasing concentrations of Na2SeO3. The hypocotyl lengths in peanuts treated with S3 and S4 decreased by 9.9 and 12.3%, respectively, compared with S1. When PFA was included with 15 mg·L− 1 Na2SeO3 (S5), the hypocotyl length increased by 12.7% compared with S3 while with the Na2SeO3, with no differences seen between the Na2SeO3 treatment and control. With 25 mg·L− 1 Na2SeO3 treatment, no significant differences were observed in the hypocotyl length of peanuts treated with PFA (S6) and without PFA (S4), which were significantly reduced in comparison with the control (S1). This indicates that the inclusion of PFA with 15 mg·L− 1 Na2SeO3 significantly increased the total fresh weight of peanut seedlings, which may be due to the increased length of the peanut hypocotyl (Fig. 3).

Fig. 3
figure 3

Effects of PFA on the morphology of peanut (Arachis hypogaea L.) seedlings treated with different selenite concentrations. Letters over the bars indicate significant differences (P < 0.05). Vertical bars represent ± SD (n = 5). A Length of hypocotyls, B Diameter of hypocotyls

Full size image

High Se concentrations have been found not only to reduce the lengths of the hypocotyl and root but also to adversely affect lateral roots in a dose-dependent manner [20]. We found that PFA mitigated the growth-inhibiting effects of Se and that the increase in the total fresh weight of the seedling was mainly due to increases in the weight of the hypocotyl. The addition of PFA, however, did not affect the fresh weight of roots. Moderate applications of humus improve both plant growth and metabolism, leading to increased root lengths and densities, while high concentrations of humic components reduce root growth [1, 21]. Increases in the weight of the hypocotyl and decreases in the weight of the root imply increased weight of the edible part of the peanut bud, promoting the nutritional quality of the peanut bud.

PFA enhanced the conversion of inorganic to organic se in peanut seedling

The total Se content of the peanut bud hypocotyl and root increased with increasing Na2SeO3 concentration, seen as a gradual increase in the content of inorganic Se while the organic Se content increased to a maximum with treatment with 15 mg·L− 1 Na2SeO3 and then decreased. PFA in conjunction with 15 mg·L− 1 Na2SeO3 treatment (S5) resulted in an increase of 22.3% of the total Se content of the hypocotyl in comparison with treatment without PFA (S3); this included an increase of 84.8% in organic Se concentration while the inorganic Se content did not change significantly. Interestingly, under the treatment of 25 mg·L− 1 Na2SeO3, while the total Se content in the hypocotyl did not change significantly after the addition of PFA, the organic Se content increased 15.1-fold together with a decrease of 47.8% in the content of inorganic Se (Fig. 4). These results show that the addition of PFA promoted the conversion of inorganic to organic Se in roots and hypocotyls. As organic Se compounds have lower toxicity than their inorganic counterparts, this implies elevated nutritional safety of the Se-enriched peanut sprouts.

Fig. 4
figure 4

Selenium contents in roots and hypocotyls of the peanut (Arachis hypogaea L.) seedling treated with different selenite concentrations on the 6th day after germination

Full size image

Liu and Wang found that humic acid (HA) can promote selenite absorption by wheat under hydroponic conditions [22]. Fulvic acid (FA) has a simple structure and, when combined with Se, can be mineralized to available Se compounds that are easily absorbed and metabolized by plants, such as Se (IV), Se (VI), and low-molecular-weight organic Se compounds [23, 24]. HA is a large aromatic compound with a stable macromolecular structure that is not easily degraded and is thus not readily available for absorption by plants. Organic Se can be divided into potentially bioavailable Se (hydrophilic organic acid-bound Se and fulvic acid-bound Se) and non-bioavailable Se (HA-bound Se) [25,26,27]. In the present study, compared with PBL, PFA was less aromatic and contained greater numbers of oxygen-containing functional groups (Table 1), which would be conducive to combining with Se to form bioavailable Se compounds.

The absorption of Se by plants depends on sulfur transporters, an energy-intensive process that operates against an electrochemical potential gradient found that the characteristics of Se-sulfur interactions in tobacco differed with different concentrations of Se and sulfur [28, 29]. Under low-sulfur conditions, Se accumulated in response to increasing sulfur concentrations, with Se and sulfur functioning synergistically. Under high-sulfur conditions, however, Se accumulation decreased in correspondence with increased sulfur concentration, with the two elements behaving antagonistically. Here, it was observed that under 15 mg·L− 1 Na2SeO3 treatment, when PFA was added (S5) the hypocotyl contents of both total and organic Se were significantly raised, possibly linked to the presence of low molecular weight (below 10 kDa) PFA and sulfur in the culture medium. The content of protein-bound Se in the peanut is reported to be high, accounting for 69.29% of the total Se content [30]. The observed increase in organic Se content after the addition of PFA may be related to elevated cysteine and methionine concentrations, which help to synthesize seleno-amino acids.

PFA activated antioxidant enzymes in peanut seedlings treated with moderate selenite concentrations

Increasing Na2SeO3 concentrations resulted in increased activity of the antioxidant enzymes POD, GPX, and GST in the hypocotyl of the peanut bud (S1-S4). Interestingly, the addition of PFA to seedlings treated with 15 mg·L− 1 Na2SeO3 (S5) resulted in increases in POD and GPX activities of 33.0 and 58.6%, respectively, with no significant effect on GST activity. Under 25 mg·L− 1 Na2SeO3 treatment, the addition of PFA reduced POD activity by 82.8% with no observed change in the activity of GST (Fig. 5). Yao found that FA and FA-like substances at appropriate concentrations enhanced rice resistance to salt stress by upregulating the levels of antioxidant enzymes and thus lowering MDA accumulation [1]. The present study shows that the addition of PFA in appropriate concentrations significantly elevated both POD and GPX activity, thus improving the plant’s ability to scavenge free radicals. Xu found that FA influenced Se incorporation into POD isozymes. At low Se concentrations, FA prevented Se incorporation into POD, while at high Se concentrations, Se incorporation was promoted. This may be the reason why the addition of PFA under moderate Se concentrations enhanced POD activity, with the opposite effect seen under high-Se conditions [31].

Fig. 5
figure 5

Effects of PFA on the activities of antioxidant enzymes in hypocotyls of peanut (Arachis hypogaea L.) seedlings treated with different selenite concentrations on the 6th day after germination. A Peroxidase activity, B GSH-Px activity, C Glutathione S-transferase activity. Letters over the bars indicate significant differences (P < 0.05) Vertical bars represent ± SD (n = 5)

Full size image

Effects of PFA on the activities of enzymes in the ascorbate−glutathione cycle

Increased Na2SeO3 concentrations resulted in increasing GR and APX activities in the peanut germ hypocotyl (S1-S4). Addition of PFA to seedlings treated with 15 mg·L− 1 Na2SeO3 led to significant increases of 55.9 and 38.7% in GR and APX activity, respectively, in comparison to seedlings not treated with PFA. With 25 mg·L− 1 Na2SeO3, APX activity decreased by 40.7% after PFA addition, while no effect was seen on GR activity (Fig. 6). The ascorbate-glutathione cycle is responsible for the maintenance of cell homeostasis through the scavenging of free radicals [32]. APX reduces H2O2 to water through the action of ascorbic acid, leading to the formation of an ascorbyl radical and oxidized ascorbate [33] followed by the regeneration of ascorbic acid and the production of GSSG [32, 34]. GSSG is then reduced by GR to maintain normal GSH levels [35]. GSH is responsible for the regeneration of ascorbic acid and GR maintains the ascorbic acid level through the ascorbate−glutathione cycle [36]. Both GSH and ascorbic acid are powerful antioxidants as function as electron donors to numerous cellular processes reactions [37]. Here, we observed that the activities of both APX and GR were significantly raised by PFA treatment in conjunction with 15 mg·L− 1 Na2SeO3. This is important because APX and GR play extremely important roles in the ascorbate−glutathione cycle.

Fig. 6
figure 6

Effects of PFA on activities of enzymes of the ascorbate−glutathione cycle in hypocotyls of peanut (Arachis hypogaea L.) seedlings treated with different selenite concentrations on the 6th day after germination. A Glutathione reductase activity, B Ascorbate peroxidase activity. Letters over the bars indicate significant differences (P < 0.05). Vertical bars represent ± SD (n = 5)

Full size image

Effects of PFA on the MDA content under selenite stress

The MDA levels in the peanut bud hypocotyls increased gradually with increasing Na2SeO3 concentration (S1-S4). When PFA was added to seedlings treated with 15 mg·L− 1 Na2SeO3 (S5) the MDA content was found to decrease by 21.4% compared with seedlings without PFA (S3). However, with 25 mg·L− 1 Na2SeO3, the MDA content was unchanged after PFA addition (S6) compared with seedlings not treated with PFA (S4) (Fig. 7).

Fig. 7
figure 7

Effects of PFA on the MDA contents in hypocotyls of peanut (Arachis hypogaea L.) seedlings treated with different selenite concentrations on the 6th day after germination. Letters over the bars indicate significant differences (P < 0.05). Vertical bars represent ± SD (n = 5)

Full size image

Effects of PFA on soluble sugar and soluble protein content of peanut seedlings treated with different selenite concentrations

As the concentration of Na2SeO3 rose, the soluble sugar content of the peanut bud hypocotyls increased initially but then decreased (S1-S4). Treatment with 15 mg·L− 1 Na2SeO3 and 25 mg·L− 1 Na2SeO3 increased the soluble sugar content by 62.9 and 21.9%, respectively, after the addition of PFA (S5, S6) compared with before the addition (S3, S4). Surprisingly, the soluble sugar content of the S5-treated seedlings was 42.3% greater than the controls (S1). The soluble protein content in the hypocotyls also increased gradually in response to Na2SeO3 concentration (S1-S4) with protein concentrations 21.8% greater in the S5 treatment than in the S3 treatment. No significant change in soluble protein content was observed in seedlings treated with 25 mg·L− 1 Na2SeO3 with or without PFA (Fig. 8).

Fig. 8
figure 8

Effects of PFA on soluble sugar and soluble protein contents in hypocotyls of peanut (Arachis hypogaea L.) seedlings treated with different selenite concentrations on the 6th day after germination. Letters over the bars indicate significant differences (P < 0.05). Vertical bars represent ± SD (n = 5). A Soluble sugar content. B Total soluble protein content in hypocotyls (mg•g-1FW)

Full size image

Effects of PFA on amino acid contents of peanut seedlings treated with different selenite concentrations

The cysteine and methionine contents of peanut bud hypocotyls decreased by 36.0 and 35.0%, respectively, in comparison with S1 when treated with 15 mg·L− 1 Na2SeO3 (S3). However, after the addition of PFA (S5), the cysteine and methionine contents were raised by 57.1 and 65.7%, respectively, compared with S3. The reduction in these amino acids in the hypocotyls of peanut buds can be explained by the mutual competition for sulfur and Se absorption seen in plants [38], leading to reduced sulfur absorption when plants are treated with Se. Se is mostly found in the form of Se-substituted amino acids, usually as a replacement for sulfur. This would lead to reduced concentrations of sulfur in cysteine and methionine. The addition of FA was found to increase both cysteine and methionine contents in the peanut hypocotyls, together with an increase in the overall content of organic Se. In Se-rich peanut seeds, Se is mostly present in the form of protein [30], indicating raised levels of Se-substituted amino acids. This may be because FA treatment increases the contents of cysteine and methionine, to provide sufficient precursors for the synthesis of seleno-amino acids (Fig. 9).

Fig. 9
figure 9

Effects of PFA on amino acid contents in hypocotyls of peanut seedlings treated with different selenite concentrations

Full size image

Conclusions

The processing of black liquor is increasingly important as the demand for paper increases. FA-like compounds extracted from black liquor have can be used for environmentally friendly applications. Here, it was found that, under appropriate Na2SeO3 concentrations, the addition of PFA significantly increased the total fresh weight of the seedling while decreasing the fresh weight of the root, as well as effectively promoting Se conversion from the inorganic to non-toxic organic forms in the root and hypocotyl, increasing the contents of both soluble sugars and proteins, and thus improving the edible quality and food safety of the Se-enriched peanut buds. This study offers methods for the application of FA-like compounds from black liquor for the production of high-quality Se-enriched peanut sprouts together with the promotion of environmentally friendly uses for paper and pulp by-products.

Materials and methods

Isolation of fulvic acid-like compounds from black liquor

Spent liquor was obtained from the Shandong Tranlin Group (Liaocheng, Shandong, China), a wheat-straw processing company. The straw is digested with (NH4)2SO3 and ammonia−water at 240 °C and 0.2 mPa for 400 min. PFAs were isolated as described [39], focusing on PFAs with molecular weights below 10 kDa. PFA concentrations (mg-C/L) were expressed by the organic carbon concentration measured by potassium dichromate oxidation [40].

Characterization of PFAs

The elemental contents were measured using a Vario EL III (Elementar, Germany) [41]. Fourier-transform infrared spectroscopy (FTIR) was performed on a Nicolet iS10 spectrometer (Thermo Fisher, Waltham, MA, USA) at 400–4000 cm− 1 [42].

Plant materials and treatments

Selected healthy peanut seeds (Yunnan colorful wild ground peanuts) were sterilized in 5% NaClO for 20 min, followed by three to five rinses with sterile water. The seeds were germinated in culture dishes at 20 °C with a sprouting machine (DYJ-S6365, Bear). They were divided into six groups (60 seeds in each group) and sprayed for 1 min once per hour with different concentrations of Na2SeO3 (0, 5, 15, and 25 mg·L− 1 Na2SeO3; 15 mg·L− 1 Na2SeO3 solution containing 60 mg-C/L PFA; 25 mg·L− 1 Na2SeO3 containing 60 mg-C/L PFA). Following a 6-day growth period, seedlings were sampled to assess relevant changes in physiology or biochemistry.

Measurement of MDA

After 6 days of seed germination, the MDA content in hypocotyls was determined by the method of Ding et al. (2018) using the formula [43]:

$$\textrm{MDA}\left(\textrm{mmol}\cdot {\textrm{kg}}^{-1}\right)=\frac{\left[6.45\times \left({OD}_{532}-{OD}_{600}\right)-0.56\times {OD}_{450}\right]}{V_s\times m}\times {V}_t\times {V}_r$$

where m is the sample mass, Vr, Vs, and Vt are the total volume of the reaction solution, the volume of the extract in the solution, and the complete volume of the extract, respectively.

Enzyme isolation and measurement

One gram of hypocotyls from each treatment condition was homogenized in 3 mL of chilled 50 mM potassium phosphate buffer (pH 7.0) containing 1 mM EDTA, 3 mM β-mercaptoethanol, and 2% (w/v) polyvinylpyrrolidone. After centrifugation (10,000 g, 15 min, 4 °C), the enzyme activities in the supernatants were measured.

Ascorbate peroxidase (APX) was measured as described by Nakano and Asada (1981) using 0.5 mM ascorbate, 0.6 mM H2O2, and 0.1 mL of enzyme extract in 50 mM potassium phosphate buffer (pH 7.0) in a volume of 3.0 mL. After initiation of the reaction by adding H2O2, the reduction in absorbance at 290 nm was determined from 1 to 60 s [44].

Glutathione reductase (GR) activity was determined as described by Knörzer (1996) using a 3 mL reaction solution containing 5 mM MgCl2, 0.2 mM NADPH, 1 mM oxidized glutathione (GSSG), and 0.1 mL PFA in 50 mM Tris-HCl, pH 7.5. GSSG was added to initiate the reaction and absorbances at 340 nm were monitored over 60 s [45].

Glutathione S-transferase (GST) activities were determined as described by Habig et al. (1974) [46], Mauch and Dudler (1993) [47]. The 2 mL reaction solution contained 100 μL of glutathione, 800 μL of 1.25 Mm 1-chloro-2,4-dinitrobenzene, and 200 μL PFA in 100 mM PBS, pH 6.5. Increases in absorbance at 340 nm were measured at 30 s intervals and GST activity was calculated as an increase in absorbance of 0.001 per milligram of protein within 1 min.

Peroxidase (POD) activity was assessed as the change in absorbance at 470 nm resulting from the catalysis of H2O2, according to Wang (2017) [13]. The reaction solution was prepared by the addition of 112 μL ml guaiacol to 200 ml of PBS (50 mM, pH 6.0), followed by heating and stirring to dissolve it. After cooling to room temperature, 112 μL of 30% H2O2 was added and mixed well. One hundred microliters of the enzyme extract were added to 2.9 mL of the solution and changes in absorbance at 470 nm were recorded immediately and at 15 s intervals thereafter for 3 min. The enzyme activity was calculated from the absorbance change of 0.01 per milligram of protein within 1 min.

GSH-Px activity was assessed as described by Flohe and Gunzler (1984) [48], Zhang and Wu (2004) [49]. Four hundred microliters of 1.0 mM GSH (containing 2.5 mM NaN3) were placed in a 10 mL tube, followed by 400 μL of enzyme solution (blank control was water), and the reaction was initiated by the addition of 200 μL 1.5 mM pre-warmed H2O2 at 37 °C. After 3 min, 4 mL 1.67% metaphosphoric acid precipitant was added to precipitate the protein and the solution was centrifuged at 3000 rpm for 10 min. Two milliliters of the supernatant were aspirated (blank tube contained 0.4 mL double-distilled water and 1.6 mL 1.67% metaphosphoric acid precipitant) and 2.5 mL of 0.32 M Na2HPO4 and 0.5 mL DTNB (5,5 ‘- disulfide-p-dinitrobenzoic acid) were added for color development, and the absorbance was measured at 423 nm within 5 min. GSH-Px activity was calculated based on the change of absorbance value of 0.001 per gram of material fresh weight within 1 min (excluding the GSH of non-enzymatic reaction).

Determination of total soluble sugar content

The total sugar content was determined by the phenol sulfuric acid method described by Dubois (1956) [50]. One gram of the powdered hypocotyls from the different treatments was weighed into a centrifuge tube and 20 mL of double-distilled water was added. The tube was vortexed and placed in a water bath in boiling water for 10 min to fully destroy the cell wall and release the soluble sugars. After centrifugation at 10000 g for 10 min, the supernatant containing the sugar extract was collected, diluted threefold, and 100 μL of the diluent was added to 1 mL of water. Phenol solution (0.5 mL of 6% phenol solution) and concentrated sulfuric acid (2.5 mL) were then added. The solution was mixed well, allowed to stand for 30 min at room temperature, and the absorbance at 490 nm was measured in a spectrophotometer. Standard glucose solutions of different concentrations were prepared in double-distilled water using anhydrous glucose as the reference, and absorbances were read as above. A standard curve was drawn and the total soluble sugar content of the sample was calculated.

Determination of total soluble protein content

One gram of powdered hypocotyls was added to 3 mL of pre-chilled extraction solution (50 mM potassium phosphate buffer, pH 7.0, containing 1 mm EDTA, 3 mm β- mercaptoethanol, and 2% polyvinylpyrrolidone), vortexed for 1 min, and allowed to stand at 4 °C for 2 h. After centrifugation at 10000 g for 14 min at 4 °C, the total protein content in the supernatant was measured by the Bradford method using bovine serum albumin as the standard [51].

Determination of organic and inorganic selenium

Six days after the start of selenium enrichment treatment, hypocotyls and roofs were collected from the peanut seedlings, rinsed three to five times with tap water, and blotted to remove the excess water. One gram of sample was used to determine the total and inorganic Se concentrations, as below.

The total Se content was determined according to the national food safety standard of the People’s Republic of China (GB 5009.93–2010, China) for measuring Se in food products. The total Se content was calculated by plotting a standard curve from the data obtained by the Se standard detection.

Measurement of inorganic Se requires sample pretreatment with the addition of 10 mL of 50% hydrochloric acid to the samples in a stoppered test tube. The material was mixed well, ultrasonicated for 30 min, and placed in boiling water for 30 min. After cooling naturally, the material was filtered through absorbent cotton, and the Se-containing filtrate was collected. The Se concentration was measured as described above for the total Se content and was calculated from the standard curve. The organic Se content was calculated as the difference between the total Se content and the inorganic Se content.

Determination of amino acid content

Two hundred micrograms of hypocotyls were weighed into a hydrolysis tube to which was added 10 mL of 6 M hydrochloric acid. The tube was degassed ultrasonically for 10 min, evaporated under nitrogen, sealed, and placed in an oven at 111 °C for 23 h. The material was then cooled to room temperature, diluted to 100 mL with deionized water, shaken well, and filtered through a 0.45 μm filter. One milliliter was then pipetted into a 10 mL volumetric flask and an aliquot was filtered through a 0.45 μm filter into the injection bottle and analyzed on an L-8900 automatic amino acid analyzer (Hitachi High-Technologies Corp., Tokyo, Japan) [52].

Statistical analyses

Data were analyzed by SPSS v10.0 using one-way ANOVA with Duncan’s test and significance levels set at P < 0.05.

Availability of data and materials

The datasets used and/or analysed during the current study available from the corresponding author on reasonable request.

Abbreviations

FA:

Fulvic acid

PFA:

Fulvic acid-like in paper mill effluents

PBL:

Pulp black liquor

MDA:

Malondialdehyde

References

  1. Yao Y, Wang X, Yang Y, Shen T, Wan Y. Molecular composition of size-fractionated fulvic acid-like substances extracted from spent cooking liquor and its relationship with biological activity. Environ Sci Technol. 2019;53:14752–60.

    Article  PubMed  CAS  Google Scholar 

  2. Wang Z, Shen T, Yang Y, et al. Fulvic acid-like substance and its characteristics, an innovative waste recycling material from pulp black liquor. J Clean Prod. 2019;243:118585.

    Article  Google Scholar 

  3. Zeng H. Selenium as an essential micronutrient: roles in cell cycle and apoptosis. Molecules. 2009;14:1263–78.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  4. Kieliszek M, Błażejak S. Selenium: significance, and outlook for supplementation. Nutrition. 2013;29:713–8.

    Article  PubMed  CAS  Google Scholar 

  5. Eiche E, Bardelli F, Nothstein A, Charlet L, Göttlicher J, Steininger R, et al. Selenium distribution and speciation in plant parts of wheat (Triticum aestivum) and Indian mustard (Brassica juncea) from a seleniferous area of Punjab. India Sci Total Environ. 2015;505:952–61.

    Article  PubMed  CAS  Google Scholar 

  6. Ávila FW, Faquin V, Yang Y, Ramos SJ, Guilherme LRG, Thannhauser TW, et al. Assessment of the anticancer compounds Se-methylselenocysteine and glucosinolates in Sebiofortified broccoli (Brassica oleracea L. var. italica) sprouts and florets. J Agric Food Chem. 2013;61:6216–23.

    Article  PubMed  Google Scholar 

  7. Lavu RVS, Du Laing G, Van De Wiele T, Pratti VL, Willekens K, Vandecasteele B, et al. Fertilizing soil with selenium fertilizers: impact on concentration, speciation, and bioaccessibility of selenium in leek (Allium ampeloprasum). J Agric Food Chem. 2012;60:10930–5.

    Article  PubMed  CAS  Google Scholar 

  8. Terry N, Zayed A, De Souza M, Tarun A. Selenium in higher plants. Annu Rev Plant Physiol Plant Mol Biol. 2000;51:401–32.

    Article  PubMed  CAS  Google Scholar 

  9. Van Hoewyk D. A tale of two toxicities: malformed selenoproteins and oxidative stress both contribute to selenium stress in plants. Ann Bot. 2013;112:mct163.

    Google Scholar 

  10. Iwashita Y, Nishi K. Cultivation of selenium-enriched vegetables in large scale. Biomed Res J Trace Elements. 2004;15:72–5.

    CAS  Google Scholar 

  11. Sorensen R, Nuti R. Fertilization of peanut with selenium. Peanut Sci. 2011;38:26–30.

    Article  Google Scholar 

  12. Meng J, Dong MN, Zhang JS, Xu QP. Study on cultivation of selenium-rich bean sprouts. Food Res Dev. 2019;40:57–61.

    CAS  Google Scholar 

  13. Wang G. Mechanisms of organic selenium accumulating in peanut seedlings and the bioactivities of organic selenium. Guangzhou: South China Univ. of Technol; 2017.

    Google Scholar 

  14. Canellas LP, Olivares FL. Physiological responses to humic substances as plant growth promoter. Chem Biol Technol Agric. 2014;1:1–11.

    Article  Google Scholar 

  15. Qin Y, Zhu H, Zhang M, Zhang HF, Xiang C, Li BC. GC-MS analysis of membrane-graded fulvic acid and its activity on promoting wheat seed germination. Molecules. 2016;21:1–11.

    Article  Google Scholar 

  16. Leiviskä T, Nurmesniemi H, Pöykiö R, Rämö J, Kuokkanen T, Pellinen J. Effect of biological wastewater treatment on the molecular weight distribution of soluble organic compounds and on the reduction of BOD, COD and P in pulp and paper mill effluent. Water Res. 2008;42:3952–60.

    Article  PubMed  Google Scholar 

  17. Duarte RM, Santos EB, Duarte AC. Spectroscopic characteristics of ultrafiltration fractions of fulvic and humic acids isolated from an eucalyptus bleached Kraft pulp mill effluent. Water Res. 2003;37:4073–80.

    Article  PubMed  CAS  Google Scholar 

  18. Ciputra S, Antony A, Phillips R, Richardson D, Leslie G. Comparison of treatment options for removal of recalcitrant dissolved organic matter from paper mill effluent. Chemosphere. 2010;81:86–91.

    Article  PubMed  CAS  Google Scholar 

  19. Xie JZ, Yang YC, Gao B. Biomimetic superhydrophobic biobased polyurethane-coated fertilizer with atmosphere “outerwear”. ACS Appl Mater Interfaces. 2017;9:15868–79.

    Article  PubMed  CAS  Google Scholar 

  20. Wang G, Zhang H, Lai F, Wu H. Germinating Peanut (Arachis hypogaea L.) seedlings attenuated selenite-induced toxicity by activating the antioxidant enzymes and mediating the ascorbate-glutathione cycle. J Agric Food Chem. 2016;64:1298–308.

    Article  PubMed  CAS  Google Scholar 

  21. Zhang ZC, Xiao P, Gao JH, Zhang GZ, Wang TT, Xie XS, et al. Study on the effect of mineral potassium fulvic acid on rooting and sprouting of hydroponic Epipremnum Aureum. Fertil Heal. 2021;48:5.

    Google Scholar 

  22. Liu YG, Wand DC. Effects of humic acid on the absorption of selenite and selenate by hydroponic wheat. J Anhui Agri Sci. 2016;44:53–6.

    Google Scholar 

  23. Coppin F, Chabroullet C, Martin-Garin A, Balesdent J, Gaudet JP. Methodological approach to assess the effects of soil aging on selenium behaviour: first results concerning mobility and soil fractionation of selenium. Biol Fertil Soils. 2006;42:379–86.

    Article  CAS  Google Scholar 

  24. Bruggeman C, Maes A, Vancluysen J. The interaction of dissolved boom clay and gorlebenhumic substances with selenium oxyanions selenite and selenate. Appl Geochem. 2007;22:1371–9.

    Article  CAS  Google Scholar 

  25. Gustafsson JP, Johnsson L. The association between selenium and humic substances in forested ecosystems—laboratory evidence. Appl Organomet Chem. 1994;8(2):141–7.

    Article  CAS  Google Scholar 

  26. Qin HB, Zhu JM, Su H. Selenium fractions in organic matter from Se–rich soils and weathered stone coal in selenosis areas of China. Chemosphere. 2012;86:626–33.

    Article  PubMed  CAS  Google Scholar 

  27. Supriatin S, Terrones CA, Bussink W, Weng L. Drying effects on selenium and copper in 0.01M calcium chloride soil extractions. Geoderma. 2015;255–256:104–14.

    Article  Google Scholar 

  28. Hawkesford MJ, Davidian JC, Grignon C. Sulphate/ proton cotransport in plasma-membrane vesicles isolated from roots of Brassica napus L.: increased transport in membranes isolated from Sulphur-starved plants. Planta. 1993;190:297–304.

    Article  CAS  Google Scholar 

  29. Ma YH, Ding RX, Zhang JZ, Zhu WM. Interaction of se and S on uptake of se by flue-cured tobacco (Nicotina tabacum L.). J Nanjing Agric Univ. 2001;24:55–8.

    CAS  Google Scholar 

  30. Li J, Shi YX, Du ZY, Kong DQ, Meng FQ. Analysis of selenium speciation in se-rich peanuts. Food Sci. 2012;33:57–9.

    Google Scholar 

  31. Xu Y. Effects of fulvic acid on the bioavailability and toxicity of sodium selenite in the environment. Beijing Graduate Sch Chin Acad Sci. 1996. http://www.irgrid.ac.cn/handle/1471x/306880. Accessed 9 Oct 2021.

  32. Aravind P, Prasad MNV. Modulation of cadmium-induced oxidative stress in Ceratophyllum demersum by zinc involves ascorbate−glutathione cycle and glutathione metabolism. Plant Physiol Biochem. 2005;43:107–16.

    Article  PubMed  CAS  Google Scholar 

  33. Chew O, Whelan J, Millar AH. Molecular definition of the ascorbate-glutathione cycle in Arabidopsis mitochondria reveals dual targeting of antioxidant defenses in plants. J Biol Chem. 2003;278:46869–77.

    Article  PubMed  CAS  Google Scholar 

  34. Camejo D, MaC M, Roman P, Ortiz A, Jime ́nez A. Antioxidant system and protein pattern in peach fruits at two maturation stages. J Agric Food Chem. 2010;58:11140–7.

    Article  PubMed  CAS  Google Scholar 

  35. Kovacs I, Durner J, Lindermayr C. Crosstalk between nitric oxide and glutathione is required for nonexpressor of pathogenesis-related genes 1 (NPR1)-dependent defense signaling in Arabidopsis thaliana. New Phytol. 2015;208:860–72.

    Article  PubMed  CAS  Google Scholar 

  36. Kachout SS, Mansoura AB, Leclerc J, Mechergui R, Rejeb M, Ouerghi Z. Effects of heavy metals on antioxidant activities of: Atriplex hortensis and A. rosea. Electronic J. environ., Agric. Food Chem. 2010;9:444–57.

    Google Scholar 

  37. Hasanuzzaman M, Hossain MA, Fujita M. Selenium-induced up-regulation of the antioxidant defense and methylglyoxal detoxification system reduces salinity-induced damage in rapeseed seedlings. Biol Trace Elem Res. 2011;143:1704–21.

    Article  PubMed  CAS  Google Scholar 

  38. Du YX, Li YN, Chen DQ. Progress in selenium metabolism and accumulation and key enzymes in plants. J Trop Subtrop Bot. 2007;15:269–76.

    Google Scholar 

  39. Yao Y, Wang C, Wang X, Yang Y, Chen WY, J, Ding F, Tang Y, Wang Z, Liu L, Xie J, Gao B, Li YC. Sigua GC. Activation of fulvic acid-like in paper mill effluents using H2O2/TiO2 catalytic oxidation: characterization and salt stress bioassays. J Hazard Mater. 2019;378:120702.

    Article  PubMed  CAS  Google Scholar 

  40. Alguacil MM, Torrecillas E, García-Orenes F, RoldÁn A. Changes in the composition and diversity of AMF communities mediated by management practices in a Mediterranean soil are related with increases in soil biological activity. Soil Biol Biochem. 2014;76:34–44.

    Article  CAS  Google Scholar 

  41. Zhang J, Lv B, Xing M, Yang J. Tracking the composition and transformation of humic and fulvic acids during vermicomposting of sewage sludge by elemental analysis and fluorescence excitation-emission matrix. Waste Manag. 2015;39:111–8.

    Article  PubMed  CAS  Google Scholar 

  42. Dang Y, Lei Y, Liu Z, Xue Y, Sun D, Wang LY, et al. Impact of fulvic acids on bio-methanogenic treatment of municipal solid waste incineration leachate. Water Res. 2016;106:71–8.

    Article  PubMed  CAS  Google Scholar 

  43. Ding F, Wang RM, Chen BC. Effect of exogenous ammonium gluconate on growth, ion flux and antioxidant enzymes of maize (Zea Mays L.) seedlings under NaCl stress. Plant Biol. 2019;21:643–51.

    Article  PubMed  CAS  Google Scholar 

  44. Nakano Y, Asada K. Hydrogen peroxide is scavenged by ascorbate-specific peroxidase in spinach chloroplasts. Plant Cell Physiol. 1981;22:867–80.

    CAS  Google Scholar 

  45. Knörzer OC, Burner J, Boger P. Alterations in the antioxidative system of suspension-cultured soybean cells (Glycine max) induced by oxidative stress. Physiol Plant. 1996;97:388–96.

    Article  Google Scholar 

  46. Habig WH, Pabst MJ, Jakoby WB. Glutathione S-transferases the first enzymatic step in mercapturic acid formation. J Biol Chem. 1974;249:7130–9.

    Article  PubMed  CAS  Google Scholar 

  47. Mauch F, Dudler R. Differential induction of distinct glutathione-S-transferases of wheat by xenobiotics and by pathogen attack. Plant Physiol. 1993;102:1193–201.

    Article  PubMed  PubMed Central  CAS  Google Scholar 

  48. Flohe L, Gunzler WA. Assay of glutathione peroxidase. Methods Enzymol J Academic Press New York. 104:114–7.

  49. Zhang JP, Wu ZL. Determination of glutathione peroxidase activity in several plants. J Guangxi Agric Sci. 2004;03:177–8.

    Google Scholar 

  50. Dubois M, Gilles KA, Hamilton JK, et al. Colorimetric method for determination of sugars and related substances. Anal Chem. 1956;28(3):350–6.

    Article  CAS  Google Scholar 

  51. Bradford MM. A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal Biochem. 1976;72:248–54.

    Article  PubMed  CAS  Google Scholar 

  52. Zhu YL, Zhang HS, Yang SF, Zhao XS, Xue HH. Analysis of protein content, compositions of amino acid and fatty acid in 18 kinds of soybean seeds. China Oils Fats. 2017;42:144–8.

    Google Scholar 

Download references

Acknowledgements

We thank all of the colleagues in our laboratory for providing useful discussions and technical assistance. We are very grateful to the editor and reviewers for critically evaluating the manuscript and providing constructive comments for its improvement.

Funding

The Project was Supported by the Foundation (No. 202001) of Qilu University of Technology of Cultivating Subject for Biology and Biochemistry.

Author information

Author notes

  1. Feng Ding and Xiaofeng Wei are co-first authors of the article.

Authors and Affiliations

  1. State Key Laboratory of Biobased Material and Green Papermaking (LBMP), College of Bioengineering, Qilu University of Technology (Shandong Academy of Sciences), Jinan, 250353, People’s Republic of China

    Feng Ding, Xiaofeng Wei, Yuanren Dao, Fei Zhao, Ruiming Wang & Piwu Li

Authors
  1. Feng Ding
    View author publications

    You can also search for this author in PubMed Google Scholar

  2. Xiaofeng Wei
    View author publications

    You can also search for this author in PubMed Google Scholar

  3. Yuanren Dao
    View author publications

    You can also search for this author in PubMed Google Scholar

  4. Fei Zhao
    View author publications

    You can also search for this author in PubMed Google Scholar

  5. Ruiming Wang
    View author publications

    You can also search for this author in PubMed Google Scholar

  6. Piwu Li
    View author publications

    You can also search for this author in PubMed Google Scholar

Contributions

F.D., P.L. conceived and designed the study. X.W., Y.D. and F.Z., conducted the experiments. X.W. performed the data and statistical analysis. F.D., P.L. wrote the manuscript, which was reviewed and edited by F.D., P.L. and R.W. The author(s) read and approved the final manuscript.

Authors’ information

Not applicable.

Corresponding authors

Correspondence to Feng Ding or Piwu Li.

Ethics declarations

Ethics approval and consent to participate

All methods were carried out in accordance with relevant local and national guidelines and regulations. All necessary permissions for planting and investigating this culti-var were obtained from Qilu University of Technology, and the collection and research of this cultivar have complied with the Convention on the Trade in Endangered Species of Wild Fauna and Flora.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Additional information

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.

Reprints and Permissions

About this article

Verify currency and authenticity via CrossMark

Cite this article

Ding, F., Wei, X., Dao, Y. et al. Use of fulvic acid-like compounds from pulp-derived black liquor for enhancing the selenium content of peanut buds. BMC Plant Biol 22, 546 (2022). https://doi.org/10.1186/s12870-022-03903-3

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: https://doi.org/10.1186/s12870-022-03903-3

Keywords

  • Fulvic acid-like substances
  • Peanut sprout
  • Selenite tolerance and selenium accumulation
  • Edible quality and food safety

BMC Plant Biology

ISSN: 1471-2229

Contact us