Abstract:Humic acid plays an important role in the distribution of heavy metals in the environment. The aims of this study were conducted to evaluate the spectroscopic characteristics and aluminum (Al) adsorption of humic acids which were extracted from four composts. The functional groups were determined by Fourier transform infrared spectroscopy (FTIR) and solid-state 13 C nuclear magnetic resonance spectroscopy ( 13 C-NMR). The results showed that the aromatic groups were all found in the humic acids of the four com… Show more
“…As indicated in Table 1, humin is rich in -OH and -COOH functional groups and these groups, especially the -COOH group, has been known for a long time as the most reactive in attracting metal cations [18][19]. This finding has also been confirmed by more recent studies [16,20]. The amount of un-ionized -COOH functional groups in humic substances decreases with the increasing of medium pH.…”
The responsible mechanism and performance of peat soil humin for the sorption of methylene blue (MB) and p-nitrophenol (p-NP) have been investigated. Humin was obtained from peat soil of Siantan, West Kalimantan, Indonesia, after removing the content of humic and fulvic acids into a NaOH solution using the recommended procedure of International Humic Substances Society (IHSS). The obtained humin was then purified by rigorous stirring in a mixed solution of HCl 0.1 M and HF 0.3 M. Ash content in humin after the purification abruptly decreased from 36.84 to 1.26 wt.% indicating that minerals and other inorganic impurities were mostly removed. Phenolic –OH and carboxyl (–COOH) functional groups contributing to the acidity of humin were in the level of 3.44 and 2.10 mmol/g, respectively. At optimum medium pH of 6.20 for MB and 7.00 for p-NP, –COO– as the deprotonated product of –COOH was the most responsible active site in sorbing MB and p-NP through electrostatic interaction and hydrogen bonding, respectively. The homogeneity of –COO– as the active site for the sorption of MB and p-NP implied that the surface of humin sorbent was energetically uniform and thereby the sorption of both MB and p-NP followed better the Langmuir than the Freundlich isotherm model with sorption capacity of 0.19 and 0.26 mmol/g and sorption energy of 32.92 and 27.27 kJ/mol, respectively.
“…As indicated in Table 1, humin is rich in -OH and -COOH functional groups and these groups, especially the -COOH group, has been known for a long time as the most reactive in attracting metal cations [18][19]. This finding has also been confirmed by more recent studies [16,20]. The amount of un-ionized -COOH functional groups in humic substances decreases with the increasing of medium pH.…”
The responsible mechanism and performance of peat soil humin for the sorption of methylene blue (MB) and p-nitrophenol (p-NP) have been investigated. Humin was obtained from peat soil of Siantan, West Kalimantan, Indonesia, after removing the content of humic and fulvic acids into a NaOH solution using the recommended procedure of International Humic Substances Society (IHSS). The obtained humin was then purified by rigorous stirring in a mixed solution of HCl 0.1 M and HF 0.3 M. Ash content in humin after the purification abruptly decreased from 36.84 to 1.26 wt.% indicating that minerals and other inorganic impurities were mostly removed. Phenolic –OH and carboxyl (–COOH) functional groups contributing to the acidity of humin were in the level of 3.44 and 2.10 mmol/g, respectively. At optimum medium pH of 6.20 for MB and 7.00 for p-NP, –COO– as the deprotonated product of –COOH was the most responsible active site in sorbing MB and p-NP through electrostatic interaction and hydrogen bonding, respectively. The homogeneity of –COO– as the active site for the sorption of MB and p-NP implied that the surface of humin sorbent was energetically uniform and thereby the sorption of both MB and p-NP followed better the Langmuir than the Freundlich isotherm model with sorption capacity of 0.19 and 0.26 mmol/g and sorption energy of 32.92 and 27.27 kJ/mol, respectively.
“…Liming is a commonly applied soil treatment to restrict the occurrence of toxic aluminium forms ( Alvarez et al, 2012;Auxtero et al, 2012). Application of organic amendments also plays an important supporting role in immobilizing toxic Al ions by forming stable organic-mineral complexes involving aluminium and humic acids (Lin & Su, 2010;Qina et al, 2010).…”
Under the conditions of a long‐term fertilizer experiment, this study aimed to determine the contents of total and exchangeable aluminium in soil as well as the Al concentration in the soil solution. Additionally, Al speciation was evaluated with the use of the MINTEQA2 software. The results obtained indicated that under the conditions of long‐term application of different mineral fertilizers or farmyard manure, the soil reaction changed to a great extent (pH 3.58–6.78). At the same time, the content of total Al in soil fluctuated from 18.85 to 22.13 g/kg and that of exchangeable Al ranged from 1.42 to 102.66 mg/kg. The concentration of Al in the soil solution was highly differentiated (5.19–124.07 μmol/L) as well as that of free aluminium ions (Al3+) (0–16.9 μmol/L). In acidic soils, aluminium complexes with organic matter are the predominant forms of Al in the soil solution. In soils with neutral soil reaction, there were no free aluminium ions. Soil liming and addition of organic amendment were the treatments that restricted the presence of toxic aluminium forms in soil.
“…The -COOH group as the most reactive functional group in attracting metal cations has been confirmed also by recent studies [11,28]. The amount of unionized -COOH functional groups in HAs decreases as the pH increases.…”
Section: Effect Of Medium Phmentioning
confidence: 52%
“…Humic acid (HA) comprises the fraction that is insoluble at low pH, fulvic acid (FA) is the fraction that is soluble over a wide pH range, and humin is the fraction that is insoluble at any pH value [9]. For the HA extracted from peat soil, its excellent performance as an adsorbent has been confirmed for a variety of metals, such as Ag(I) [10], Al(III) [11], Cd(II) [12][13], Cr(III) [14][15], Cu(II) [16][17], Fe(III) [18], Mn(II) [19] and Ni(II) [20]. This performance is even higher after immobilizing the HA on silica gel [21], chitin [15,20], chitosan [12,22] and bentonite [23].…”
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