A comparative study on the chemical composition of humic acids from forest soil,agricultural soil and lignite deposit: Bound lipid,carbohydrate and amino acid distributions

Base- and acid-hydrolysable fractions of humic acids (HAs) isolated from a forest soil, an agricultural soil and a lignite deposit were analysed, and comparisons were made between the base hydrolysable lipid (bound lipid), carbohydrate and amino acid signatures of the different humic acids.Bound lipids differ depending on the humic acid origin. Their composition were rather similar for the two soil humic acids, with three main lipid classes identified: (i) aliphatic components, (ii) aromatic components and (iii) sterols and triterpenols. The aliphatic subfraction was the most abundant and consisted predominantly of cutin- and suberin-derived moieties some of which could be clearly related to the vegetation. A minor bacterial input was indicated by the presence of short chain α- and β-hydroxyalkanoic acids. Aromatic subfraction contributed to a low amount to the total base hydrolysates and consisted mainly of lignin-derived methoxyphenols. Present in trace amounts, sterols and triterpenols are mainly of higher plant origin. The base hydrolysate from lignite humic acid markedly differs. Bound lipids released from lignite HA comprised almost exclusively aliphatic components, largely dominated by long chain alkanoic acids. Lignin-derived moieties, hardly detected, consisted solely of vanillic and 4-hydroxybenzoic acids indicating a much higher degree of lignin alteration in lignite humic acid. Sterols and triterpenols were absent.Although the composition of monosaccharides released upon acid hydrolysis was rather uniform irrespective of the humic acid origin, the distribution changed with the degree of humification of the HAs. Ratios of (Galactose+Mannose) to (Xylose+Arabinose) increased from soil to lignite humic acids. The high values of the ratios indicate that carbohydrates are primarily of microbial origin.In all humic acids neutral and acidic protein amino acids dominated. Non protein amino acids were only minor components consisting mainly of hydroxy proline and ornithine. The amino acid distributions of both soil HAs were similar. The amino acid distribution of lignite HA resembled that of soil HAs except for the following differences: (1) the absence of hydroxy proline and the greater abundance of ornithine suggesting a higher microbial contribution to the amino acids as the degree of humification increases, (2) the higher contribution of polar amino acids suggesting a preferential preservation of these amino acids possibly by interaction with the humic acid surface through hydrogen bonds.     

不同施肥条件土壤胡敏酸级分变异及性质的研究

以１７年长期定位试验土壤为材料,在研究土壤有机质氧化稳定性基础上,采用酒精沉淀分级方法,对不同施肥处理土壤胡敏酸的级分及光学性质进行了研究,并对胡敏酸及其级分的类型进行了划分。结果表明长期施用有机（堆肥及秸秆）土壤有机质含量明显增加,有机质的氧化稳定系数降低,土壤胡敏酸组成分布中心向高浓度酒精析出的级分偏移,颗粒小的级分比例增大,土壤胡敏酸的Ｅ４,Ｅ６值减小Ｅ４／Ｅ６增大,而单施化肥则有相反趋势。     

Effect of soil pollution with polycyclic aromatic hydrocarbons on the properties of humic acids

Purpose

Interestingly, soil is the component of the natural environment in which most hydrophobic organic pollution including polycyclic aromatic hydrocarbons (PAHs) gets accumulated. The aim of the present paper was to determine the effect of soil pollution with PAHs on the elemental composition, spectral properties, and hydrophobic and hydrophilic properties of humic acids. The research was performed on different types of soil samples that were artificially polluted with selected PAHs (anthracene, pyrene, fluorene and chrysene).

Materials and methods

The soil samples were polluted with selected PAHs in an amount corresponding to 10 mg PAHs kg^?1. The PAHs-polluted soil samples were incubated for 180 and 360 days at a temperature of 20–25 °C and fixed moisture (50 % of field water capacity). Humic acids (HAs) were extracted from the soil samples prior to the incubation (additionally, soils not polluted with PAHs) and after 180 and 360 days of incubation. For isolated HAs, the following analyses were performed: elemental composition, UV–Vis and IR spectra, susceptibility to oxidation, and hydrophilic (HIL) and hydrophobic (HOB) properties were determined using high-performance liquid chromatography.

Results and discussion

The research demonstrated that introducing anthracene, fluorene, pyrene and chrysene to soil samples resulted in a change in some of the quality parameters of humic acids. However, the intensity and the direction of those changes were determined by soil properties. The changes of the parameters, once PAHs were introduced, that did not depend on the soil properties were ΔA _665u and ΔA _465u (susceptibility to oxidation at wavelengths of 465 and 665 nm) as well as HIL/ΣHOB. The same tendency in changes in the structure of humic acids, once PAHs were introduced, was also observed based on the Fourier transform infrared spectra pattern.

Conclusions

A single pollution of soils with PAHs that leads to changes in the quality parameters of humic acids shows that, as for the soils permanently exposed to pollution with those compounds, significant changes can occur in the properties of humic acids. As a result, it can lead to a change in the functions played by humic acids in the environment.     

Humic acids buffer the effects of urea on soil ammonia oxidizers and potential nitrification

Humic acids (HAs) play an important role in the global nitrogen cycle by influencing the distribution, bioavailability, and ultimate fate of organic nitrogen. Ammonium oxidation by autotrophic ammonia-oxidizing bacteria (AOB) is a key process in ecosystems and is limited, in part, by the availability of NH₄⁺. We evaluated the impact of HAs on soil AOB in microcosms by applying urea (1.0%, equal to 10 mg urea/g soil) with 0.1% bHA (biodegraded lignite humic acids, equal to 1 mg/g soil), 0.1% cHA (crude lignite humic acids) or no amendment. AOB population size, ammonium and nitrate concentrations were monitored for 12 weeks after urea and HA application. AOB densities (quantified by real-time PCR targeting the amoA) in the Urea treatments increased about ten-fold (the final abundance: 5.02 × 10⁷ copies (g of dry soil)⁻¹) after one week of incubation and decreased to the initial density after 12 weeks incubation; the population size of total bacteria (quantified by real-time PCR with a universal bacterial probe) decreased from 1.12 × 10¹⁰ to 2.59 × 10⁹ copies (g of dry soil)⁻¹ at week one and fluctuated back to the initial copy number at week 12. In the Urea + bHA and Urea + cHA treatments, the AOB densities were 4 and 6 times higher, respectively, than the initial density of approximately 5.07 × 10⁶ copies (g of dry soil)⁻¹ at week 1 and did not change much up to week 4; the total bacteria density changed little over time. The AOB and total bacteria density of the controls changed little during the 12 weeks of incubation. The microbial community composition of the Urea treatment, based on T-RFLP using CCA (canonical correspondence analysis) and pCCA (partial CCA) analysis, was clearly different from those of other treatments, and suggested that lignite HAs buffered the change in diversity and quantity of total bacteria caused by the application of urea to the soil. We hypothesize that HAs can inhibit the change in microbial community composition and numbers, as well as AOB population size by reducing the hydrolysis rate from urea to ammonium in soils amended with urea.     

Effect of aerial oxidation pretreatment on composition and effectiveness of a Nigerian lignite sample as soil organic matter amendment

Abstract

A Nigerian lignite sample was analyzed for its nutrient element and organic components. The effect of two oxidation procedures, namely, oven‐oxidation and wet‐oxidation on the composition and extractability of organic fraction with 0.1 M sodium hydroxide (NaOH), was also studied. A pot experiment was conducted to investigate effect of the oxidized lignite samples on the growth of Gmelina arborea seedlings. The lignite sample is very acidic in reaction with a pH of 2.0, and has low quantity of macro‐ and micronutrient elements with a carbon (C):nitrogen (N) ratio of 103. It, however, has over 90% organic matter with more than 78% extractable humic substances. All these components were either increased, decreased, or unaffected by the oxidation pretreatments. Compared to the control, both the unoxidized and differently oxidized lignite samples, generally depressed growth of 12‐week‐old Gmelina arborea seedlings in the Alfisols while their addition to the Oxisols enhanced the growth of the seedlings. Wet‐oxidized lignite stimulated growth of the seedlings more than either unoxidized or oven‐oxidized sample while the latter performed the poorest of the three.     

Impact of flue gas desulfurization gypsum and lignite humic acid application on soil organic matter and physical properties of a saline-sodic farmland soil in Eastern China

Purpose

Appropriate land management is important for improving the soil quality and productivity of the saline-sodic farmland. A recent study has revealed that flue gas desulfurization (FGD) gypsum and lignite humic acid application enhanced the salt leaching and crop production. The purpose of this study was to investigate the effects of applied FGD gypsum and lignite humic acid (powder) on the soil organic matter (SOM) content and physical properties.

Materials and methods

This study was based on a field experiment of five consecutive rapeseed-maize rotations in a saline-sodic farmland soil (Aquic Halaquepts) at coastal area of North Jiangsu Province, China. The soil is sandy clay loam texture with pH of 8.43 and clay content of 185 g kg^?1. Six treatments included three FGD gypsum rates (0, 1.6, and 3.2 Mg ha^?1) and two lignite humic acid rates (0 and 1.5 Mg ha^?1). The amendments were incorporated into 0–20 cm soil depth manually every year. Soil samples were collected from each treatment and analyzed for soil organic matter, water-stable aggregates (wet sieving method), bulk density (clod method), water retention capacity (pressure plate apparatus), total porosity (calculated from bulk density and particle density), and microporosity (calculated from water content at 0.01 MPa).

Results and discussion

After 5 years, the SOM and soil physical properties were significantly (P?<?0.05) affected by the application of FGD gypsum and lignite humic acid, especially at the 0–20 cm soil depth. The highest amount of SOM with best soil physical condition was observed in the field which was treated with FGD gypsum at 3.2 Mg ha^?1 with lignite humic acid, and the SOM, total porosity (TP), microporosity (MP), mean weight diameter (MWD), water-stable macroaggregate (WSMA), and available water content (AWC) were increased by 22.8, 6.34, 23.2, 48.1, 55.5, and 15.8 %, respectively, while the bulk density (BD) was decreased by 5.9 % compared to no amendments applied. The generalized linear regression analysis showed that the SOM explained 42.9, 55.0, 48.5, and 54.2 % of the variability for BD, MWD, WSMA, and MP, respectively.

Conclusions

This study illustrates the benefits of applying FGD gypsum and lignite humic acid for increasing the soil organic matter content and improving the soil physical properties and suggests a great potential for ameliorating saline-sodic farmland soil (Aquic Halaquepts) by using combined amendment of FGD gypsum with lignite humic acid.

     

施用生物质炭对黑土腐殖质组成及水稳性团聚体分布的影响

为探究生物炭对土壤腐殖质组成和团聚体特征的影响，以东北黑土区植烟土壤为研究对象，设置了3个处理，2019-2020年连续施用低量生物炭5t/hm2（C1）；高量生物炭25t/hm2（C2）和不施生物炭（CK），分析了不同用量生物炭对土壤腐殖质组分及水稳性团聚体分布的影响，并利用傅里叶红外光谱(FTIR)和13C核磁共振光谱(13C-NMR)对土壤胡敏酸化学结构进行表征。结果表明：C1和C2处理分别使富里酸减少了16.90%和40.85%，胡敏酸含量显著增加了14.86%和33.78%，胡敏酸在腐殖酸中所占比例（PQ值）也显著增加；FTIR和13C-NMR分析表明，C2处理的土壤胡敏酸的2920/1620值降低了11.82%，脂族C/芳香C比值降低了13.04%，表明高量生物炭使胡敏酸芳构化程度增强，脂肪结构比例降低；生物炭的添加促使土壤大团聚体（>0.25mm）比例增加，C2处理提升大团聚体的作用更显著。结合相关性分析发现，胡敏酸含量与2~0.25mm大团聚体含量显著正相关，胡敏酸分子的脂肪族官能团特征与>2mm粒级团聚体显著正相关。此外，C1和C2处理显著提高了烟叶产量。从而表明，生物炭能提升土壤腐殖质中胡敏酸含量和结构，有利于土壤大团聚体形成，提高土壤固碳潜力，对作物有一定的增产效果。     

土壤腐殖质分组研究

采用Pallo法对两种耕地土壤腐殖质进行分组,初步研究了各组分的数量和结构特征。结果表明:焦磷酸钠提取的胡敏酸(HAp)是胡敏酸(HA)的主要组分;游离富里酸(FAf)是富里酸(FA)的主要组分;胡敏素(HM)的主要组分为非溶解性胡敏素(ISHM),而溶解性胡敏素(SHM)含量较低。通常随土层深度增加,HA、HM各组分的绝对数量和相对数量都下降;FA各组分的绝对数量也下降,而相对数量增加;HA/FA比值下降。一般来看,焦磷酸钠提取的富里酸(FAp)、氢氧化钠提取的富里酸(FAs)比相应的HAp、氢氧化钠提取的胡敏酸(HAs)的分子结构简单,铁结合胡敏素(HMi)比粘粒结合胡敏素(HMc)的分子结构简单;随土层深度增加,HAp、HAs的分子结构变简单,而HMi、HMc的分子结构变复杂。     

活化过硫酸钠氧化土壤对挥发性有机污染物吸附特性的影响

活化过硫酸钠(Sodium persulfate,SPS)氧化技术是一种新型的土壤修复技术。为了更科学地评价化学氧化处理后土壤的环境风险,本文通过亚铁离子活化过硫酸钠法对有机质(Organic matter,OM)含量存在显著差别的两种土壤进行氧化处理,比较了活化过硫酸钠氧化前后两种土壤样品对3种挥发性有机污染物的吸附特性。结果表明,亚铁活化的SPS能够氧化土壤中腐殖酸和胡敏素类的有机质。对OM含量较高的1号土,SPS氧化对有机质的去除率为71.9%。而对OM含量较低的2号土,SPS氧化对有机质的去除率为49.9%。1号土样对3种挥发性有机物的吸附以分配作用为主,氧化后的1号土样对3种物质的吸附机制不变,但吸附量有所增加;2号土样对3种挥发性有机污染物的吸附有一定的非线性,而氧化后的2号土样对3种物质的吸附线性特征增强。吸附数据用对数形式的Freundlich方程拟合得到分配系数lg Kf值,比较有机碳标化后的分配系数lg Kfoc,氧化后的土壤有机质对3种挥发性有机污染物的吸附特性有所提高。分析表明,SPS氧化了有机质中较多的极性组分(如羧基及羟基等),从而使处理后的土壤中有机质的非极性增强,强化了对非极性化合物的吸附。     

The effects of acid nitrogen and acid sulphur deposition on CH4 oxidation in a forest soil: a laboratory study

Sieved soil and soil core experiments were performed to determine the potential sensitivity of forest soil CH₄ oxidation to oxidised N, reduced N and oxidised S atmospheric deposition. Ammonium sulphate was used to simulate reduced N deposition, HNO₃ oxidised N deposition and H₂SO₄ oxidised S deposition. The effects of NH₄⁺, NO₃⁻, SO₄²⁻ and H⁺ on soil CH₄ flux were shown to be governed by the associated counter-anion or cation of the investigated ions. Ammonium sulphate, at concentrations greater than those that would be experienced in polluted throughfall, showed a low potential to cause inhibition of CH₄ oxidation. In contrast, HNO₃ strongly inhibited net CH₄ oxidation in sieved soils and also in soil cores. In addition, soil CO₂ production was inhibited and the organic and mineral soil horizons acidified in HNO₃ treated soil cores. This suggested that the HNO₃ effect on CH₄ flux might be indirectly mediated through aluminium toxicity. Sulphuric acid only inhibited CH₄ oxidation when added at pH 1. At concentrations more representative of heavily polluted throughfall, H₂SO₄ had no effect on soil CH₄ flux or CO₂ production from soil cores, even after 210 days of repeated addition. In contrast to HNO₃ additions, acidification of the soil was not marked and was only significant for the mineral soil. The findings suggest that the response of forest soil CH₄ oxidation to atmospheric acid deposition is strongly dependent on the form of acid deposition.     

Analysis of polynuclear aromatic and aliphatic components in soil humic acids using ruthenium tetroxide oxidation

Although condensed aromatic components are considered to be one of the major structural units of soil humic acids (HAs) and to be responsible for the dark colour of HAs, their amount and composition remain largely unknown. In ruthenium tetroxide oxidation (RTO), condensed aromatic components are detectable as their degradation products, mainly benzenepolycarboxylic acids (BPCAs). We applied this technique to soil HAs with various degrees of humification (darkening). The yields of water‐ and dichloromethane‐soluble products from HAs upon RTO after methylation ranged from 210 to 430 mg g⁻¹ and 10–40 mg g⁻¹, respectively. Eight kinds of BPCAs with two to six carboxyl groups, and seven kinds of BPCAs with additional side chains (tentative assignment) were obtained as methylated counterparts. The yield of each BPCA and the sum of the yields of BPCAs (12–85 mg g⁻¹ HAs) increased with increasing degree of humification and aromatic C content. The compositions of BPCAs indicated that the degree of condensation was greater in the HAs with greater degrees of humification. The sum of the yields of aliphatic compounds ranged from 0.1 to 6.5 mg g⁻¹, and decreased with increasing degree of humification. The C₁₂ to C₃₀ monocarboxylic acid methyl esters accounted for > 56% of the aliphatic compounds assigned, which may be present mainly as end alkyl groups in the HA molecules. We also obtained the methylated counterparts of C₁₄ to C₂₄ dicarboxylic acids; these were possibly derived from polymethylene bridges between adjacent aromatic rings.     

Effect of humic amendments on inorganic N, dehydrogenase and alkaline phosphatase activities of a Mediterranean soil

Dehydrogenase activity, alkaline phosphatase activity and NH₄ ⁺, NO₂ ⁻ and NO₃ ⁻ concentrations were monitored in an aridisol treated with three commercially available humic amendments. The materials were of plant residue, lignite and peat origins. The humus plant residues, fulvic acids, with a high content of Kjeldahl-N, sustained high enzyme activities and highest levels of NH₄ ⁺, NO₂ ⁻ and NO₃ ⁻. Humus lignite (mainly humic acids) produced the highest dehydrogenase activity, whereas the alkaline phosphatase activity was not as high as that amendment with humus plant residues. The lower activity of alkaline phosphatase could not be attributed to the higher P content of humus lignite. Nitrification was also low, probably due to the low N content of this fertilizer. The amendment of humus peat origin (only humic acids) did not increase enzyme activity or inorganic N concentrations of soil. Our results show that although these materials are widely utilized and recommended as microbial and plant activators, they all behave very differently, and the effects on soil microbiological activity cannot be predicted solely on the basis of their humic and/or fulvic acid contents.     

不同分子量腐植酸的结构特征及其对土壤镉有效性的影响

为探究不同分子量腐植酸组分的结构特征,本研究利用褐煤粉提取腐植酸进行超滤分级,获得四个不同分子量的腐植酸组分。研究发现,分子量大于50 kDa和小于1 kDa的腐植酸分别占总腐植酸的49.66%、47.07%,中间两个组分占比很小；腐植酸的理化性质和功能主要是由1 kDa以下的腐植酸和50 kDa以上的腐植酸所决定的。1 kDa以下的腐植酸总酸性基、羧基和酚羟基官能团含量最高,酚羟基占总酸性基的比例也较高,腐植酸的芳香化程度、缩合度随分子量的增大而增大,含氧官能团含量、E4/E6值随分子量的增大而减少。通过盆栽试验,探索了不同分子量腐植酸对土壤镉有效性的影响,土壤对镉的吸附量随腐植酸分子量的增大而减少,各处理均在500 mg/L时达到吸附平衡；土壤镉的解吸量亦随腐植酸分子量的增大而减少。小分子量腐植酸的酸性官能团丰富,对土壤重金属的吸附络合能力更强,可以降低土壤对镉的吸持能力,提高其移动性和生物有效性；大分子腐植酸则主要起吸持和固定作用,降低重金属的移动性和生物有效性。     

Retention of added copper by two soils as affected by organic matter,CaCO3, and exchangeable ions

The effects of addition and removal of organic matter and CaCO₃ and of saturating a loam and a loamy sand soil with hydrogen (HCl treated), with calcium and with sodium on the retention of added copper were studied. Removal of organic matter reduced the copper-retaining capacity in soils, while addition of 1 to 4% humic acid to H₂O₂-treated soils increased the retention. Soil organic matter had higher specific copper retaining as well as fixing capacity than the added humic acid. Humic acid fixed about 62 and 49% of the copper it retained, while soil organic matter fixed about 65 and 61% in the loam and loamy sand respectively, which could not be extracted with 0.1 N HCl. About 30% extra copper retained by the added humic acid was exchangeable. Saturating the soils with hydrogen (HCl treatment) decreased the retention of added copper considerably but addition of CaCO₃ up to 8% increased the retention by increasing the pH of the soil system. The CaCO₃ induced retention was lower than caused by humic acid additions. The specific copper retention by native CaCO₃ was slightly higher than that of added CaCO₃. However, other changes associated with the pre-treatment of the soil may have caused those differences in specif is copper retention. Although CaCO₃ had as high a copper fixing capacity as organic matter its contribution towards exchangeable copper was negligible.     

Quantitative and qualitative characterisation of humic products with spectral parameters

Purpose

The application of different humic products for the treatment of soils and plants has increased in recent years. The characteristics of humic products, such as the content and composition of organic carbon and the maturity, provide valuable information which is essential for an adequate application. Such information is crucial for manufacturers, business consultants and users involved in the production, distribution and implementation of humic products. This article presents the correlation between the quantitative indicators of commercial humic products and their spectral characteristics via measurements in the ultraviolet spectrum at 300 nm, in the visible area at 445 and 665 nm and in the near-infrared spectrum at 850 nm.

Materials and methods

We evaluated humic products (liquid and solid) of different origins. Via wet combustion, the content of total organic carbon in humic products can be determined. The precipitation of humic acids from the starting solution determines the composition of the humic products in terms of humic acids (HAs) and fulvic acids (FAs). The dissolution of HAs determines their concentration by titration, while the specific extinction can be assessed via spectrophotometry via measuring the absorption of HAs spectra at the following wavelengths: 300, 465, 665 and 850 nm. The degree of aromaticity and condensation of humic products determines the optical density of the HAs via the E₄/E₆ ratio.

Results and discussion

The content of total organic carbon varied widely from 0.55 to 37.5% across all groups. The content of carbon in HAs, as a percentage of the total carbon in fulvic-type humic products, ranged from 1.29 to 16.00%, while in humic-type products, it ranged from 51.43 to 91.92%. The minimum value of the E₄/E₆ ratio was 2.97, while the maximum value was 6.35. We observed a direct relationship between the dominant type of acids in humic products and the E₄/E₆ ratio.

Conclusions

The optical density of HAs indicates their quality characteristics. The presented optical characteristics for humic products show that there is a direct relationship, especially between HAs/FAs and E₄/E₆ ratios. Measurement at 300 nm (E₃₀₀) in the near-ultraviolet area and at 850 nm (E₈₅₀) in the near-infrared area can increase the range of the spectral study.

     

Conformational changes of humic substances induced by some hydroxy-, keto-, and sulfonic acids

We studied the effect of organic acids of plant, microbial, or anthropic origin on the molecular size distribution of dissolved humic acids (HAs). High Performance Size Exclusion Chromatography (HPSEC) was used to evaluate size changes in four different HAs upon addition of hydroxy- (glycolic and malic), keto- (glyoxylic), and sulfonic (benzenesulfonic and methanesulfonic) acids. All humic substances showed a decrease of peaks absorbance when the pH of HAs dissolved in HPSEC mobile phase was lowered from 7 to 3.5 by acid addition before analysis. This effect, combined with an increase of peaks elution volumes in most cases, was interpreted as a disruption of supramolecular humic associations into smaller-size but energy-richer conformations brought about by the formation of mixed intermolecular hydrogen bonding upon acid treatment. The extent of size variation was related to the pKa of acids and also to the chemical and stereochemical affinity of humic components with the chemical structure of the acids. Dicarboxylic malic acid was the most effective in modifying humic conformations in all HAs whereas the aromatic-rich superstructure of HA from an oxidized coal was effectively disrupted by the relatively small methanesulfonic acid and the chemically akin benzenesulfonic acid. These results suggest that the conformational association of humus dissolved in the soil solution may be systematically altered by organic acids present in the rhizosphere and might have effects on plant and microbial activities.     

腐殖酸对矿物结合汞活性的影响──Ⅰ.腐殖酸对矿物结合汞挥发活性的影响

挥发试验结果表明,试验条件下,富里酸能极显著地促进Ｆｅ２Ｏ３－Ｈｇ,ＭｎＯ２－Ｈｇ与高岭土结合汞的挥发,对膨润土结合汞和碳酸钙结合汞的挥发则表现抑制作用。棕色胡敏酸参促进各矿物结合汞的挥发。灰色胡敏酸影响最为微弱。腐殖酸对矿物结合态汞挥发性的影响与其对汞的络合容量与络合稳定性,矿物对汞的吸持特性的以及矿物与腐殖酸的作用特性密切相关。     

Humus composition and humification degree of humic acids of alpine meadow soils in the northeastern part of the Qinghai–Tibet Plateau

The characteristics of humus composition are important for understanding the mechanism of carbon storage in the Qinghai–Tibet Plateau. The aim of this study was to characterize the quality of soil organic matter (SOM) in this region. Soil samples from four soil profiles in fenced study sites in the alpine grassland were collected at altitudes of 4200, 4000, 3800, and 3400 m, along the southwest facing slope in the Qilian Mountains. The humus composition and humification degree of the humic acid (HA) were determined by two methods: (1) extraction with 0.5% sodium hydroxide (NaOH) followed by 0.1 M sodium pyrophosphate (Na₄P₂O₇) (OH-PP method); and (2) treating once with 0.1 M hydrochloric acid (HCl) followed by extracting with 0.5% NaOH (Cl-OH method). Physico-chemical analysis revealed higher exchangeable cation content and higher base saturation ratios could be related to slightly acidic to neutral soils, which could be regarded as calcium (Ca)-rich soils. The amounts of combined-form HAs obtained by HCl pretreatment (HA_Cl – HA_OH; ?HA_Cl) were remarkably higher than those extracted with Na₄P₂O₇ (HA_PP), indicating that the combined form of HAs is mainly Ca. In addition, the proportion of HA_PP in the total HAs extracted with both NaOH and Na₄P₂O₇ (HA_OH + HA_PP) obtained in the OH-PP method increased with soil depth and decreasing elevation, indicating that HAs associated with aluminum (Al) and iron (Fe) were distinguished in the subsoils of lower elevation. Therefore, the formation of the organo-mineral complex may contribute to stabilizing SOM in the Qinghai–Tibet Plateau. Moreover, Type A-HA with the highest degree of humification was obtained from the deeper horizons with the Cl-OH method and almost all horizons by extraction with Na₄P₂O₇ in the OH-PP method. Further studies using various spectroscopic analyses are necessary to elucidate the chemical properties of SOM in this region.     

溶液体系中非生物因素对胡敏酸还原汞的影响

As a global pollutant process,the reduction of mercury(Hg)is especially important.One pathway is through an abiotic reduction with humic acids(HAs),which is controlled by different factors,including initial Hg and HA concentrations,pH,temperature and light.In this study,three humic acids were selected to illustrate the Hg~(2+)abiotic reduction mechanisms by HAs,and to identify the key limiting factors for reduction rates and amounts.In addition,the initial status of the HAs as a solid or in an aqueous solution were also compared,to help explain why HAs show different dominant characteristics(e.g.complexation or reduction)in the reaction process with Hg.Results indicated that HAs were able to reduce Hg abiotically.Higher initial Hg,higher HA concentrations and either high(8.1)or low(3.6)solution pH decreased the HA reduction capacity.In addition,Hg°production rates increased with increasing temperature,and the same trend was observed with light exposure.Humic acids added as an aqueous solution resulted in significantly greater Hg°production than addition as a bulk solid.Finally,the Hg reduction rate and capacity varied significantly(P0.05)with HAs from different sources.These findings helped to explain why HAs showed different dominant characteristics(e.g.complexation or reduction)in the reaction process with Hg,and evidentially demonstrated the existence of a possible pathway of Hg~(2+)reduction,which indicated that humic substances in natural environments,especially in water bodies,could act either as a sink or a source for Hg.