SPECTRAL CHARACTERISTICS AND SOURCE ANALYSIS OF SOIL DISSOLVED ORGANIC MATTER IN KARST MOUNTAINOUS AREA
-
摘要: 采用紫外-可见光谱(UV-vis)与三维荧光光谱(EEMs),结合平行因子分析(PARAFAC)方法,对贵州省典型喀斯特山区土壤溶解性有机质(SDOM)的特征、来源及组成进行分析。结果表明:土壤溶解性有机碳(SDOC)含量因土地利用类型不同而存在差异,其中草地表层SDOC含量显著高于林地。利用PARAFAC模型解析出3种荧光组分,C1(类腐殖质)、C2(类色氨酸)和C3(类酪氨酸),3种组分含量间存在显著正相关(P<0.01),且在不同土地利用方式下的分布有所差异。紫外特征参数显示:草地表层SDOM 相对分子质量小于林地,旱地SDOM中芳香物质和疏水性组分较多。荧光特征参数显示:研究区SDOM总体腐殖化程度较低、稳定性较弱,且不同土地利用类型SDOM来源存在差异。林地以微生物源输入为主,旱地兼具微生物源与陆源共同作用,但以新生自生源为主。草地表层SDOM来源特征与旱地相同,亚表层则以微生物源输入为主。随着海拔升高,组分C1占比增加,C3占比降低,SDOM腐殖化程度增强,微生物源贡献减弱。SDOM荧光与吸光特征可有效表征喀斯特山地SDOM组分与来源特性,可作为区域土地利用与环境决策的评价指标。Abstract: The characteristic, source, and composition of soil dissolved organic matter (SDOM) in typical karst mountainous area of Guizhou Province were studied by using ultraviolet-visible absorption spectrum (UV-vis) and three-dimensional fluorescence excitation-emission matrix (EEMs) combined with parallel factor analysis (PARAFAC). The results showed that SDOC content varied with the land-use type, and the SDOC content of grassland surface layer was significantly higher than that of woodland. Three fluorescent components, C1 (humic-like), C2 (tryptophan-like), and C3 (tyrosine-like), were derived from SDOM using the PARAFAC model. There was a significant positive correlation among the three components (P<0.01), and these three components were distributed differently in different land-use types. UV-vis spectral characteristics indicated that the relative molecular weight of SDOM in the grassland surface layer was smaller than that in the woodland, and SDOM in arid land contained more aromatic substances and hydrophobic components. The fluorescence characteristic index indicated that SDOM in the study area had a low humification degree and weak stability, and there were differences in SDOM sources among different land-use types. SDOM in woodland was mainly derived from autochthonous sources. SDOM in arid land was derived from autochthonous and terrigenous sources. The SDOM source characteristic of grassland surface layer was the same as those of arid land, while SDOM in the subsurface layer was mainly derived from autochthonous sources. With the increase in altitude, the proportion of component C1 increased, the proportion of C3 decreased, the humification degree of SDOM increased, and the contribution of microbial sources decreased. The study indicated that SDOM fluorescence and absorption characteristics can effectively track the composition and source characteristics of the SDOM in karst mountains, and be used as an evaluation index for regional land use and environmental decision-making.
-
[1] RIZZUTO S, JONES K C, ZHANG H, et al. Critical assessment of an equilibrium-based method to study the binding of waterborne organic contaminants to natural dissolved organic matter (DOM)[J]. Chemosphere, 2021, 285: 131524. [2] JIANG T, KAAL J, LIANG J, et al. Composition of dissolved organic matter (DOM) from periodically submerged soils in the three gorges reservoir areas as determined by elemental and optical analysis, infrared spectroscopy, pyrolysis-gc-ms and thermally assisted hydrolysis and methylation[J]. Science of the Total Environment, 2017, 603/604: 461-471. [3] TANG J M, LIANG S X, SUN H W, et al. Analysis of dissolved organic matters in Fu river of baoding using three dimensional fluorescence excitation-emission matrix[J]. Spectroscopy and Spectral Analysis, 2014, 34(2): 450-454. [4] DING Y, SHI Z Q, YE Q T, et al. Chemodiversity of soil dissolved organic matter[J]. Environmental Science and Technology, 2020, 54(10): 6174-6184. [5] 肖骁, 何小松, 席北斗, 等. 垃圾填埋水溶性有机物组成、演化及络合重金属特征[J]. 环境科学, 2017, 38(9): 3705-3712. [6] YUAN D H, AN Y C, HE X S, et al. Fluorescent characteristic and compositional change of dissolved organic matter and its effect on heavy metal distribution in composting leachates[J]. Environmental Science and Pollution Research, 2018, 25(19): 18866-18878. [7] INAMDAR S, FINGER N, SINGH S, et al. Dissolved organic matter (DOM) concentration and quality in a forested mid-atlantic watershed, USA[J]. Biogeochemistry, 2012, 108(1): 55-76. [8] ZHAO C, GAO S J, ZHOU L, et al. Dissolved organic matter in urban forestland soil and its interactions with typical heavy metals: a case of Daxing district, Beijing[J]. Environmental Science and Pollution Research, 2019, 26(3): 2960-2973. [9] TANG J F, WANG W D, YANG L, et al. Variation in quantity and chemical composition of soil dissolved organic matter in a peri-urban critical zone observatory watershed in eastern China[J]. Science of the Total Environment, 2019, 688: 622-631. [10] 秦纪洪, 王姝, 刘琛, 等. 海拔梯度上川西高山土壤溶解性有机质(DOM)光谱特征[J]. 中国环境科学, 2019, 39(10): 4321-4328. [11] HUANG X F, ZHOU Y C, ZHANG Z M. Carbon sequestration anticipation response to land use change in a mountainous karst basin in China[J]. Journal of Environmental Management, 2018, 228: 40-46. [12] BAI Y X, ZHOU Y C. The main factors controlling spatial variability of soil organic carbon in a small karst watershed, Guizhou Province, China[J]. Geoderma, 2020, 357: 113938. [13] AHMED A R, PICHLER V, HOMOLÁK M, et al. High organic carbon stock in a karstic soil of the middle-european forest province prsists after centuries-long agroforestry management[J]. European Journal of Forest Research, 2012, 131(6): 1669-1680. [14] KINDLER R, SIEMENS J, KAISER K, et al. Dissolved carbon leaching from soil is a crucial component of the net ecosystem carbon balance[J]. Global Change Biology, 2011, 17(2): 1167-1185. [15] 杨威杉, 李猛, 孙笑蕾, 等. 不同海拔下青海草甸土中溶解性有机质的荧光光谱特征[J]. 光谱学与光谱分析, 2019, 39(5): 1477-1482. [16] 丁卫红, 莫世江, 张鹏飞. 贵州韭菜坪石林形态差异性分析[J]. 毕节学院学报, 2007,25(4): 94-99. [17] NELSON D A, SOMMERS L. Total carbon, organic carbon, and organic matter[J]. Methods of Soil Analysis: Part 2 Chemical and Microbiological Properties, 1983, 9: 539-579. [18] HUANG M, LI Z Y, HUANG B, et al. Investigating binding characteristics of cadmium and copper to DOM derived from compost and rice straw using eem-parafac combined with two-dimensional FTIR correlation analyses[J]. Journal of Hazardous Materials, 2017, 344: 539-548. [19] DILLING J, KAISER K. Estimation of the hydrophobic fraction of dissolved organic matter in water samples using uv photometry[J]. Water Research, 2002, 36(20): 5037-5044. [20] HANSEN A M, KRAUS T E, PELLERIN B A, et al. Optical properties of dissolved organic matter (DOM): effects of biological and photolytic degradation[J]. Limnology and Oceanography, 2016, 61(3): 1015-1032. [21] LI P H, HUR J. Utilization of uv-vis spectroscopy and related data analyses for dissolved organic matter (DOM) studies: a review[J]. Critical Reviews in Environmental Science and Technology, 2017, 47(1/2/3/4/5/6): 131-154. [22] LAVONEN E E, KOTHAWALA D N, TRANVIK L J, et al. Tracking changes in the optical properties and molecular composition of dissolved organic matter during drinking water production[J]. Water Research, 2015, 85: 286-294. [23] HUGUET A, VACHER L, RELEXANS S, et al. Properties of fluorescent dissolved organic matter in the gironde estuary[J]. Organic Geochemistry, 2009, 40(6): 706-719. [24] MURPHY K R, HAMBLY A, SINGH S, et al. Organic matter fluorescence in municipal water recycling schemes: toward a unified parafac model[J]. Environmental Science & Technology, 2011, 45(7): 2909-2916. [25] 纪美辰, 李思佳, 常明, 等. 二龙湖表层水体有色溶解有机物的光学特性及来源[J]. 环境科学研究, 2020, 33(8): 1821-1829. [26] 许金鑫, 王初, 姚东京, 等. 崇明东滩湿地土壤溶解性有机质的光谱特征分析[J]. 环境工程, 2020, 38(11): 218-225. [27] HELMS J R, STUBBINS A, RITCHIE J D, et al. Absorption spectral slopes and slope ratios as indicators of molecular weight, source, and photobleaching of chromophoric dissolved organic matter[J]. Limnology and Oceanography, 2008, 53(3): 955-969. [28] 梁俭, 江韬, 卢松, 等. 淹水条件下三峡库区典型消落带土壤释放DOM的光谱特征:紫外-可见吸收光谱[J]. 环境科学, 2016, 37(7): 2496-2505. [29] WU H H, XU X K, CHENG W G, et al. Antecedent soil moisture prior to freezing can affect quantity, composition and stability of soil dissolved organic matter during thaw[J]. Scientific Reports, 2017, 7(1): 1-12. [30] ZHANG X, LI Z, NIE X D, et al. The role of dissolved organic matter in soil organic carbon stability under water erosion[J]. Ecological Indicators, 2019, 102: 724-733. [31] FOUCHÉ J, CHRISTIANSEN C T, LAFRENIōRE M, et al. Canadian permafrost stores large pools of ammonium and optically distinct dissolved organic matter[J]. Nature Communications, 2020, 11(1): 4500. [32] GAO J K, LIANG C L, SHEN G Z, et al. Spectral characteristics of dissolved organic matter in various agricultural soils throughout China[J]. Chemosphere, 2017, 176: 108-116. [33] 李帅东, 张明礼, 杨浩, 等. 昆明松华坝库区表层土壤溶解性有机质(DOM)的光谱特性[J]. 光谱学与光谱分析, 2017, 37(4): 1183-1188. [34] 张博, 王书航, 姜霞, 等. 太湖五里湖水体悬浮物中水溶性有机质(WSOM)的荧光光谱组分鉴别及其与氮形态的关系[J]. 湖泊科学, 2018, 30(1): 102-111. [35] STEDMON C A, MARKAGER S. Resolving the variability in dissolved organic matter fluorescence in a temperate estuary and its catchment using parafac analysis[J]. Limnology & Oceanography, 50(2): 686-697. [36] MCKNIGHT D M, BOYER E W, WESTERHOFF P K, et al. Spectrofluorometric characterization of dissolved organic matter for indication of precursor organic material and aromaticity[J]. Limnology and Oceanography, 2001, 46(1): 38-48. [37] OHN O, TSUTOM U. Fluorescence inner-filtering correction for determining the humification index of dissolved organic matter[J]. Environmental Science & Technology, 2002, 36(4): 742-746. [38] XI M, ZI Y Y, WANG Q Q, et al. Assessment of the content, structure, and source of soil dissolved organic matter in the coastal wetlands of Jiaozhou Bay, China[J]. Physics & Chemistry of the Earth Parts A/B/C, 2018, 103: 35-44. [39] 宋亚辉, 张娇阳, 刘鸿飞, 等. 管理措施对黄土高原油松人工林土壤水溶性碳氮及其三维荧光特征的影响[J]. 环境科学, 2020, 41(2): 905-913. [40] QUIDEAU S, BOCKHEIM J. Biogeochemical cycling following planting to red pine on a sandy prairie soil[R]: Wiley Online Library, 1997, 26(4): 1167-1175. [41] GREGORICH E G, LIANG B C, Drury C F, et al. Elucidation of the source and turnover of water soluble and microbial biomass carbon in agricultural soils[J]. Soil Biology and Biochemistry, 2000, 32(5): 581-587. [42] LEENHEER J A, CROUÉ J P. Peer reviewed: characterizing aquatic dissolved organic matter[J]. Environmental Science & Technology, 2003, 37(1): 18-26. [43] JAFARIAN Z, KAVIAN A. Effects of land-use change on soil organic carbon and nitrogen[J]. Communications in Soil Science and Plant Analysis, 2013, 44(1): 339-346. [44] 李璐璐, 江韬, 卢松, 等. 利用紫外-可见吸收光谱估算三峡库区消落带水体、土壤和沉积物溶解性有机质(DOM)浓度[J]. 环境科学, 2014, 35(9): 3408-3416. [45] 彭志刚, 刘晓庆. 不同深度土壤中水溶性有机物荧光光谱特征研究[J]. 现代农业科技, 2011(5): 272-273. [46] MANN P J, SPENCER R G, HERNES P J, et al. Pan-arctic trends in terrestrial dissolved organic matter from optical measurements[J]. Frontiers in Earth Science, 2016, 4: 25. [47] KAISER K, GUGGENBERGER G, HAUMAIER L. Changes in dissolved lignin-derived phenols, neutral sugars, uronic acids, and amino sugars with depth in forested haplic arenosols and rendzic leptosols[J]. Biogeochemistry, 2004, 70(1): 135-151. [48] 訾园园, 孔范龙, 郗敏, 等. 胶州湾滨海湿地土壤溶解性有机质的三维荧光特性[J]. 应用生态学报, 2016, 27(12): 3871-3881. [49] 王齐磊, 江韬, 赵铮, 等. 三峡库区典型农业小流域水体中溶解性有机质的光谱特征[J]. 环境科学, 2016, 37(6): 2082-2092. [50] WANG X W, LIU Z Q, XIONG K N, et al. Soil organic carbon distribution and its response to soil erosion based on eem-parafac and stable carbon isotope, a field study in the rocky desertification control of south China karst[J]. International Journal of Environmental Research and Public Health, 2022, 19(6): 3210.
点击查看大图
计量
- 文章访问数: 68
- HTML全文浏览量: 4
- PDF下载量: 6
- 被引次数: 0