米槠人促更新林与杉木人工林叶片及凋落物溶解性有机物的数量和光谱学特征

选取中亚热带米槠人促更新林(CCF)和杉木人工林(CLP)内的鲜叶、未分解层(L层)和半分解层(F层)凋落物为研究对象进行室内淋溶,对其淋溶液中的溶解性有机碳(DOC)、溶解性有机氮(DON)和溶解性有机磷(DOP)含量,紫外吸收值(SUVA),腐殖化指标(HIX)和红外光谱(FTIR)等进行了比较分析,以揭示其淋溶液中溶解性有机物(DOM)的数量和光谱学特征。结果表明:随着淋溶时间的增加,不同样品的DOM含量呈现先上升后下降,或者有波动的上升的趋势,这是因为DOM的释放和反吸附共同控制着DOM的含量。两林分中,F层凋落物DOM的SUVA值显著高于鲜叶和L层凋落物(P0.05);从鲜叶到L层到F层凋落物,其HIX逐渐变大并且三者荧光强度最大值对应的波长由短波向长波移动,这是腐殖化程度越来越高、电子共轭体系逐渐增大的体现。两个林分6种样品的红外光谱显示了5个相似的吸收谱带,但不同样品各吸收带的相对比例不同,强度最大的吸收来自于H键键合的—OH的伸缩振动;同一林分内3种样品之间红外吸收的差异证明了鲜叶到L层再到F层凋落物,其DOM的芳香类物质含量逐渐升高,化学键力常数变小。总体上,与杉木人工林相比,米槠人促更新林的DOM养分含量更高,结构更复杂,因而更有利于有机质的积累。     

森林凋落物淋溶中的溶解有机物与紫外-可见光谱特征

对格氏栲(Castanopsis kawakamii)和杉木(Cunninghamia lanceolat)人工林新近凋落物、半分解层(F层)和分解层(H层)凋落物进行室内模拟淋洗实验,研究了凋落物淋溶过程中溶解有机碳(DOC)浓度变化及紫外-可见(UV-Vis.)光谱特征.结果表明,格氏栲和杉木人工林新近凋落物淋出液的DOC浓度较低,F层淋出液的DOC浓度较高;格氏栲凋落物淋出液的DOC浓度基本上随淋溶次数的增加而降低,杉木的则先升后降.淋出液中溶解有机物(DOM)的紫外吸收值均随波长的增加而减小,且UV-Vis.吸收曲线均在200nm附近出现吸收峰,不同来源DOM的E240/E420存在显著差异;同一样品各次淋出液的DOC浓度与E200有很好的线性关系(P2＞0.90),据此,可用E200值估算DOC浓度.     

亚热带地区竞争型和忍耐型树种叶片可溶性有机质数量及光谱学特征

气候变化下,不同生态策略的树种对环境变化有着不同的响应能力,影响其叶片淋溶产生的DOM(Dissolved organic matter)的数量和质量,进而影响土壤的养分循环。通过探究亚热带地区不同生态策略树种叶片DOM数量及光谱学特征的差异,评估不同数量和结构特征DOM输入到土壤对养分循环的影响。本研究选取6种树种鲜叶进行浸提,其中竞争型(Competitive,C)和忍耐型(Stress-tolerant,S)各3种(树参(Dendropanax dentiger),黄绒润楠(Machilus grijsii),黄牛奶树(Symplocos cochinchinensis(Lour.)),细柄阿丁枫(Altingia gracilipes),丝栗栲(Castanopsis fargesii)和罗浮栲(Castanopsis faberi))。通过溶解性有机碳(Dissolved organic carbon,DOC)、溶解性有机氮(Dissolved organic nitrogen,DON)表征DOM的数量特征,通过紫外吸收值(Special Ultraviolet-Visible Absorption,SUVA),腐殖化指标(Humification index,HIX)和傅里叶红外光谱(Fouriertransform infrared,FTIR)等光谱指标表征DOM质量特征。结果表明:不同生态策略树种的叶浸提液中可溶性有机碳浓度无显著差异,但是C策略树种浸提液中可溶性有机氮浓度大于S策略的DON浓度。此外,S策略的芳香化指数(Aromatic index,AI)和腐殖化指数(HIX)均高于C策略。C策略树种的发射荧光强度也高于S策略,说明C策略树种DOM腐殖化程度较低,易分解物质含量高;S策略难分解物质多,腐殖化程度较高。傅里叶红外光谱结果表明,各树种叶浸提的DOM存在相似的吸收峰,其中以H键键合的—OH伸缩振动最强且C策略树种结果相对简单,验证了荧光光谱的结果。总体而言,与C策略相比,S策略树种叶片浸提的DOM结构更复杂,养分含量更高。这可能是因为,S策略树种对环境变化具有更高的适应性。由于其DOM结构相对复杂,输入土壤后减缓土壤碳周转速率,在未来气候变化情景下,S策略树种可能有利于土壤碳汇的形成。     

红壤侵蚀区芒萁对土壤可溶性有机质光谱特征的影响

可溶性有机质(DOM)是森林生态系统能量循环的主要载体,在碳循环过程中发挥着重要的作用。为了深入了解植被恢复后土壤DOM的变化和结构特征,在典型红壤侵蚀区福建省龙岩市长汀县河田镇选取不同恢复年限的马尾松(Pinus massoniana)林为研究对象,利用光学技术对比分析了不同恢复年限(0年,13年,31年)马尾松林保留芒萁(Dicranopteris dichotoma)覆盖地、去除芒萁覆盖地和林下裸地土壤DOM光谱特征。结果表明:未治理地(Y0)、恢复13年(Y13)和恢复31年(Y31)马尾松林芒萁覆盖地土壤可溶性有机碳(DOC)含量分别是林下裸地的7.61倍、4.83倍和5.47倍,去除芒萁一年后,土壤DOC的含量显著下降,但仍分别是林下裸地的1.84倍、4.12倍和4.73倍;芒萁覆盖地土壤DOM的芳香化指数(AI)和腐殖化指数(HIX)均显著高于林下裸地,而波长在250 nm和365 nm处的紫外可见光光度值之比(E2:E3)的趋势与之相反,去除芒萁一年后,AI和HIX降低显著,表明芒萁覆盖地土壤DOM腐殖化和芳香化程度更高,分子量更大;林下裸地DOM红外光谱中特征峰明显不如林下芒萁覆盖地丰富,其含有更多的羟基、羧酸类,以及碳水化合物中的烷氧基等结构简单、易迁移的物质,去除芒萁一年后,DOM红外光谱特征峰无明显变化,表明芒萁是土壤DOM数量和结构的主要影响因素,而这种影响是一个长期缓慢的过程。从DOM光谱分析结果可知,芒萁覆盖下土壤DOM的分子量更大,结构更复杂,易于被土壤胶粒吸附,维持其化学稳定,利于土壤有机碳积累。由此可见,芒萁在土壤有机碳积累过程中具有积极的作用。     

盐度和淹水程度对短叶茳芏枯落物分解初期DOM含量及其组成结构的影响

选取闽江河口潮汐湿地短叶茳芏枯落物为研究对象,通过设置不同盐度(0、5、10、15)和淹水程度(不浸没分解袋,淹水Ⅰ和持续浸没分解袋,淹水Ⅱ)等处理,分析枯落物分解过程中可溶性有机物(DOM)的含量及组成结构的紫外光谱、荧光光谱和红外光谱学等变化特征。研究结果表明,在181 d的分解过程中,枯落物可溶性有机碳(DOC)、可溶性总氮(DTN)、可溶性无机氮(DIN)和可溶性有机氮(DON)等浓度在不同盐度和淹水处理下均有显著差异(P0.05)。盐度对DOC和DON影响不显著,但高盐组的DIN显著较低(P0.05);除淹水Ⅰ对照组外,各盐分处理组的芳香化指数(AI)随分解时间推移呈上升趋势。不同分解阶段对枯落物DOM组分和光谱特征有重要影响。分解前期(前89 d),淹水Ⅰ处理下,盐分升高可导致枯落物中的腐殖化指数(HIX_(syn), HIX_(em))降低。分解中、后期(120 d后),盐分较高条件下,腐殖质在枯落物中累积;而淹水Ⅱ处理下,盐分处理组在整个实验期内始终抑制枯落物的分解,腐殖化程度较高。淹水程度也会影响枯落物DOM的淋溶和腐殖化过程。在分解前期,淹水Ⅰ处理的AI和HIX_(em)显著高于淹水Ⅱ处理,而淹水Ⅱ处理下枯落物DOM较淹水Ⅰ处理更容易发生N的淋溶;分解中、后期,淹水Ⅱ处理下的厌氧环境反而抑制枯落物DOM中的腐殖质和芳香类物质析出。红外光谱分析表明,闽江河口短叶茳芏枯落物DOM中结构简单、容易分解的碳水化合物含量相对较高,但是不同淹水处理并未改变枯落物DOM的结构特征。     

侵蚀退化地植被恢复过程中芒萁对土壤可溶性有机碳的影响

林下植被是生态系统的重要组分。通过对比分析红壤侵蚀区植被恢复过程中,林下有无芒萁覆盖地的土壤可溶性有机碳(DOC,Dissolved Organic Carbon)含量及其与地下根系生物量、地上植被淋溶液DOC含量的关系。结果表明:林下植被芒萁覆盖增加了地上叶片和地下根系生物量,土壤DOC含量及储量也显著增加(P0.05),芒萁覆盖对表层土壤(0—20cm)DOC的影响大于深层土壤(20—100cm)(P0.05);相关分析结果表明,林下芒萁覆盖地土壤DOC储量与细根生物量的垂直变化呈显著的正相关关系(P0.05),且随植被恢复年限的增加相关性显著增加,地下根系的垂直分布直接影响各土层DOC储量。不同植被恢复时期,林下芒萁覆盖地土壤DOC与鲜叶(马尾松+芒萁)和枯落物(马尾松+芒萁)淋溶液DOC均呈显著的正相关关系(P0.01),而林下裸露地土壤DOC仅与鲜叶(马尾松)淋溶液DOC呈显著的相关性(P0.01),林下芒萁覆盖地相对于裸露地枯落物淋溶液对土壤DOC储量的影响大于鲜叶。植被恢复过程中芒萁覆盖地土壤微生物生物量碳和微生物熵显著高于林下裸露地。因此,在植被恢复进程中,芒萁能够提供更多底物参与土壤物质与养分循环,对土壤DOC的贡献较大,为侵蚀区马尾松林恢复提供了重要的养分再吸收来源;同时芒萁覆盖增加了微生物活性,促进了微生物对土壤DOC的同化作用,提高了微生物碳源的利用率,对土壤有机碳的积累起着重要的作用。     

广西主要人工林凋落物分解过程及其对淋溶水质的影响

为探讨不同人工林各组分凋落物分解过程特征及其释放物质对淋溶水质的影响,恒温(28 ℃)培养条件下,在室内人工定期淋水模拟自然环境中凋落物的淋溶过程,对1年生和4年生尾巨桉、7年生杂交相思、13年生马尾松以及软阔林5种人工林的凋落叶、凋落枝、凋落皮进行255 d的模拟淋溶.结果表明：1年生和4年生尾巨桉各组分凋落物分解0～105 d的淋溶液色度和化学需氧量（COD）、总N和总P含量显著高于杂交相思、马尾松、软阔林,淋溶液pH值显著低于其他3种林分人工林;至255 d,1年生和4年生尾巨桉凋落叶淋溶液的COD累积量（193.9和212.8 g·kg^-1）分别是杂交相思、马尾松、软阔林的4.2、4.0、4.3倍和5.3、4.4、4.7倍;1年生尾巨桉凋落叶质量损失率、N和P淋失率显著大于杂交相思、马尾松和软阔林,凋落皮显著大于马尾松,而凋落枝与后三者基本相当.1年生尾巨桉凋落叶和凋落皮比4年生尾巨桉更易被分解淋溶,但凋落枝差异不显著.5种林分凋落物不同组分间,凋落叶最易被分解淋溶,凋落枝难于被分解淋溶.尾巨桉凋落物淋溶液pH值与色度、COD含量呈显著负相关,COD与色度、总N和总P呈显著正相关.     

中亚热带森林转换对土壤可溶性有机质数量与光谱学特征的影响

选取中亚热带福建三明格氏栲天然林及其转换而成的木荷、锥栗及福建柏等3种人工林表层土壤(0—10 cm)可溶性有机质(DOM)为对象,对其数量和光谱学特征进行了研究,以探讨森林转换对土壤DOM的影响。结果表明,天然林转换成上述3种人工林后,0—5 cm土壤可溶性有机碳(DOC)浓度显著降低(P0.05),降低程度分别为66.1%,69.9%及29.4%,可溶性有机氮(DON)浓度也有所下降;除福建柏外,其余两种人工林5—10 cm土壤DOC及DON浓度均低于天然林。各林分0—5 cm土壤DOC及DON浓度均高于5—10 cm土层。两个土层中,天然林土壤DOM的芳香化及腐殖化程度均显著高于人工林(P0.05),但荧光效率值低于人工林;荧光光谱图显示,天然林土壤DOM在芳香性脂肪族及木质素类复杂结构荧光基团处的吸收大于人工林;各林分土壤DOM傅里叶红外光谱出现吸收谱带的位置相似,其中吸收强度最大的为形成氢键的—OH的伸缩振动,此外还有芳香性CC伸缩振动、有机羧酸盐COO-反对称伸缩振动、碳水化合物中烷氧基C—O的振动等,人工林土壤DOM中碳水化合物的比例增加是其结构简单的主要原因。土壤DOM中结构复杂、分子量大的组分不易向下迁移;天然林与人工林间土壤DOM数量及光谱学特征的差异主要与凋落物输入及营林措施的干扰有关;本研究所涉及的3种人工林中,福建柏更有利于土壤养分的累积。     

耕作扰动对喀斯特土壤可溶性有机质及其组分迁移淋失的影响

土壤可溶性有机质(DOM)及其组分淋失特征研究对深入理解干扰作用下土壤碳氮养分损失机制具有重要意义,本研究基于翻耕模拟试验,分析喀斯特石灰土可溶性有机碳(DOC)、可溶性有机氮(DON)、及DOM官能团组分的淋失动态特征及其对不同耕作频率的响应,并探讨其影响因子。结果表明:(1)土壤DOC与DON的淋失量均随翻耕频率的增加而增加,但4个官能团特征参数对翻耕频率响应均不显著;DOC/DON淋失比随翻耕频率的增大而减少,DON占淋溶水可溶性总氮(TDN)比例随翻耕频率增加而增加。(2)DOC和DON月淋失量同时受翻耕处理与季节变化及其交互作用的影响,4个官能团特征参数仅受季节变化的影响;翻耕处理实施后,DOC月淋失量表现为初期大、后期小,各处理间差异性逐渐降低;但DON月淋失量初期小、后期大,各处理间差异性逐渐增大。(3)DOC淋失量与4个官能团特征参数呈显著负相关(P0.05),与Ca~(2+)、NH_4~+-N的淋失量呈显著正相关;DON淋失量与4个官能团参数无显著相关关系,与Mg~(2+)淋失量呈显著正相关关系。以上结果表明耕作扰动会加剧土壤DOM淋失,但淋失组分中稳定性组分没有变化,意味着耕作干扰将导致土壤有机质的持续损失,且由于其淋失组分碳氮比(DOC/DON)随扰动频率增加而降低,DON/TDN比随扰动频率增加而增加,持续的耕作干扰将大大增加水体氮素污染风险。     

雪被期川西高山林线交错带凋落物可溶性有机碳的淋失特征

凋落物可溶性有机碳(dissolved organic carbon,DOC)是土壤DOC的主要来源之一,同时,凋落物DOC的淋失过程是生态系统碳循环的重要环节。本文采用凋落物分解袋法,于2012年10月—2013年5月,以川西高山林线交错带12种代表性植物的凋落物为材料,研究了冬季雪被期凋落物DOC在暗针叶林森林、高山林线和高山草甸3种分解生境中的淋失特征。结果表明:1)凋落物初始DOC含量为22.78~178.8 g·kg-1,物种间差异显著;2)经过一个雪被期(182 d),凋落物DOC淋失率为18.92%~62.33%,各物种DOC的淋失率对分解生境的响应差异较大;3)分解生境差异对凋落物DOC的淋失产生了显著影响,暗针叶林生境中凋落物DOC的淋失率显著高于林线和高山草甸生境;4)雪被是影响冬季高山林线交错带凋落物DOC淋失的主要环境因素。因此,高山林线交错上雪被期DOC淋失的空间变异性主要是景观尺度分布的雪被差异造成的,分解生境中较厚的雪被更利于凋落物DOC的淋失。     

Interannual variability of Aureococcus anophagefferens in Quantuck Bay, Long Island: natural test of the DON hypothesis

This study examined benthic and pelagic rate processes from the perspective of benthic dissolved organic matter (DOM) and its possible role in Aureococcus anophagefferens population dynamics. Sampling was conducted in Quantuck Bay, Long Island, New York, at three times in the summer of 2000 and two times in the summer of 2001. A. anophagefferens exhibited a large bloom between the May and July 2000 sample periods, but a smaller bloom was captured in the September 2000 sampling. Densities throughout 2001 were significantly lower than during 2000. There were few differences in most parameters measured between years, but the largest difference was the seasonal increase in both particulate (POM) and dissolved organic matter (DOM) during 2000 that was not observed during 2001. In particular, DOP accumulated the most, followed by DON and DOC, which resulted in significant seasonal decreases in the C:N:P ratios of the DOM pools. On the contrary, changes in elemental ratios of POM were not observed. The seasonal accumulation of DON appeared to be driven largely (50%) by the flux of DON from the benthos in 2000, but during 2001, all measured DON fluxes were into the sediment from the water column. This is consistent with the lack of accumulation during this year. There was little evidence for changes in microzooplankton grazing pressure between 2000 and 2001, and therefore the accumulation of DON and DOP during 2000 could have provided a competitive advantage to A. anophagefferens over other picoalgal species (e.g., Synechococcus) resulting in the significant blooms observed in 2000.     

杉木和米槠凋落叶DOM对土壤碳矿化的影响

DOM(Dissolved organic matter)是土壤微生物呼吸的重要底物,凋落物淋溶的DOM对土壤碳矿化具有重要影响。选择中亚热带地区具有代表性的杉木(Cunninghamia lanceolata)和米槠(Castanopsis carlesii)凋落叶作为研究对象,通过两个月的短期室内培养,把不同凋落叶浸提出的DOM添加到培养瓶中,定期测定土壤碳矿化速率,计算土壤碳累积矿化量,探讨两种等浓度等量DOM添加对土壤碳矿化的影响,并分析DOM化学性质在土壤碳矿化过程中的重要性。结果表明:米槠凋落叶浸提得到的DOC(Dissolved organic carbon)和DON(Dissolved organic nitrogen)浓度均显著高于杉木凋落叶的(P0.05),而杉木凋落叶浸提得到的DOM的UV吸收值(SUVA_(254))和HIX(Humification index)均显著低于米槠凋落叶的(P0.01)。添加等浓度等量杉木和米槠凋落叶DOM到土壤中均显著增加了土壤碳矿化速率,在第1天内分别比对照高198%和168%,3d后下降到61.8%和44.1%,14d后基本处于平稳状态,表明外源有机物添加对土壤碳矿化的前期影响较大。培养过程中,添加杉木和米槠凋落叶DOM的土壤碳矿化累积量均能采用双因素指数模型进行拟合(r~2=0.99),但添加两者凋落叶DOM后土壤碳矿化累积量没有显著差异。     

Response of dissolved organic matter in the forest floor to long-term manipulation of litter and throughfall inputs

Dissolved organic matter (DOM) contributes to organic carbon either stored in mineral soil horizons or exported to the hydrosphere. However, the main controls of DOM dynamics are still under debate. We studied fresh leaf litter and more decomposed organic material as the main sources of DOM exported from the forest floor of a mixed beech/oak forest in Germany. In the field we doubled and excluded aboveground litter input and doubled the input of throughfall. From 1999 to 2005 we measured concentrations and fluxes of dissolved organic C and N (DOC, DON) beneath the Oi and Oe/Oa horizon. DOM composition was traced by UV and fluorescence spectroscopy. In selected DOM samples we analyzed the concentrations of phenols, pentoses and hexoses, and lignin-derived phenols by CuO oxidation. DOC and DON concentrations and fluxes almost doubled instantaneously in both horizons of the forest floor by doubling the litter input and DOC concentrations averaged 82 mg C l⁻¹ in the Oe/Oa horizon. Properties of DOM did not suggest a change of the main DOM source towards fresh litter. In turn, increasing ratios of hexoses to pentoses and a larger content of lignin-derived phenols in the Oe/Oa horizon of the Double litter plots in comparison to the Control plots indicated a priming effect: Addition of fresh litter stimulated microbial activity resulting in increased microbial production of DOM from organic material already stored in Oe/Oa horizons. Exclusion of litter input resulted in an immediate decrease in DOC concentrations and fluxes in the thin Oi horizon. In the Oe/Oa horizon DOC concentrations started to decline in the third year and were significantly smaller than those in the Control after 5 years. Properties of DOM indicated an increased proportion of microbially and throughfall derived compounds after exclusion of litter inputs. Dissolved organic N did not decrease upon litter exclusion. We assume a microbial transformation of mineral N from throughfall and N mineralization to DON. Increased amounts of throughfall resulted in almost equivalently increased DOC fluxes in the Oe/Oa horizon. However, long-term additional throughfall inputs resulted in significantly declining DOC concentrations over time. We conclude that DOM leaving the forest floor derives mainly from decomposed organic material stored in Oe/Oa horizons. Leaching of organic matter from fresh litter is of less importance. Observed effects of litter manipulations strongly depend on time and the stocks of organic matter in forest floor horizons. Long-term experiments are particularly necessary in soils/horizons with large stocks of organic matter and in studies focusing on effects of declined substrate availability. The expected increased primary production upon climate change with subsequently enhanced litter input may result in an increased production of DOM from organic soil horizons.     

Land use and hydrologic flowpaths interact to affect dissolved organic matter and nitrate dynamics

The transport and transformation of dissolved organic matter (DOM) and dissolved inorganic nitrogen (DIN) through the soil profile impact down-gradient ecosystems and are increasingly recognized as important factors affecting the balance between accumulation and mineralization of subsoil organic matter. Using zero tension and tension lysimeters at three soil depths (20, 40, 60 cm) in paired forest and maize/soybean land uses, we compared dissolved organic C (DOC), dissolved organic N (DON) and DIN concentrations as well as DOM properties including hydrophilic-C (HPI-C), UV absorption (SUVA₂₅₄), humification index and C/N ratio. Soil moisture data collected at lysimeter locations suggest zero tension lysimeters sampled relatively rapid hydrologic flowpaths that included downward saturated flow through the soil matrix and/or rapid macropore flow that is not in equilibrium with bulk soil solution whereas tension lysimeters sampled relatively immobile soil matrix solution during unsaturated conditions. The effect of land use on DOC and DON concentrations was largely limited to the most shallow (20 cm) sampling depth where DOC concentrations were greater in the forest (only zero tension lysimeters) and DON concentrations were greater in the cropland (both lysimeter types). In contrast to DOC and DON concentrations, the effect of land use on DOM properties persisted to the deepest sampling depth (60 cm), suggesting that DOM in the cropland was more decomposed regardless of lysimeter type. DOC concentrations and DOM properties differed between lysimeter types only in the forest at 20 cm where soil solutions collected with zero tension lysimeters had greater DOC concentrations, greater SUVA₂₅₄, greater humification index and lower HPI-C. Our data highlight the importance of considering DOM quality in addition to DOC quantity, and indicate long-term cultivation reduced the delivery of relatively less decomposed DOM to all soil depths.     

Nutrient and mineralogical control on dissolved organic C, N and P fluxes and stoichiometry in Hawaiian soils

We measured DOM fluxes from the O horizon of Hawaiiansoils that varied in nutrient availability and mineralcontent to examine what regulates the flux ofdissolved organic carbon (DOC), nitrogen (DON) andphosphorus (DOP) from the surface layer of tropicalsoils. We examined DOM fluxes in a laboratory study from N, P and N+Pfertilized and unfertilized sites on soils that rangedin age from 300 to 4 million years old. The fluxesof DOC and DON were generally related to the % Cand % N content of the soils across the sites. Ingeneral, CO₂ and DOC fluxes were not correlatedsuggesting that physical desorption, dissolution andsorption reactions primarily control DOM release fromthese surface horizons. The one exception to thispattern was at the oldest site where there was asignificant relationship between DOC and CO₂flux. The oldest site also contained the lowestmineral and allophane content of the three sites andthe DOC-respiration correlation indicates arelationship between microbial activity and DOC fluxat this site. N Fertilization increased DON fluxes by50% and decreased DOC:DON ratios in the youngest,most N poor site. In the older, more N rich sites, Nfertilization neither increased DON fluxes nordecreased DOM C:N ratios. Similarly, short termchanges in N availability in laboratory-based soil Nand P fertilization experiments did not affect the DOMC:N ratios of leachate. DOM C:N ratios were similar tosoil organic matter C:N ratios, and changes in DOM C:Nratios with fertilization appeared to have beenmediated through long term effects on SOM C:N ratiosrather than through changes in microbial demand for Cand N. There was no relationship between DON andinorganic N flux during these incubations suggestingthat the organic and inorganic components of N fluxfrom soils are regulated by different factors and thatDON fluxes are not coupled to immediate microbialdemand for N. In contrast to the behavior of DON, thenet flux of dissolved organic phosphorus (DOP) and DOMC:P ratios responded to both long-term P fertilizationand natural variation in reactive P availability. There was lower DOP flux and higher DOM C:P ratiosfrom soils characterized by low P availability andhigh DOP flux and narrow DOM C:P ratios in sites withhigh P availability. DOP fluxes were also closelycorrelated with dissolved inorganic P fluxes. PFertilization increased DOP fluxes by 73% in theyoungest site, 31% in the P rich intermediate agesite and 444% in the old, P poor site indicating thatDOP fluxes closely track P availability in soils.     

氮沉降对杉木人工林土壤可溶性有机质数量和结构的影响

氮沉降作为现在乃至未来气候变化的趋势之一,其可能深刻影响土壤可溶性有机质的数量和结构。选取我国中亚热带杉木人工林不同深度土壤（0-10 cm和10-20 cm）进行氮沉降试验,利用光谱技术研究氮沉降对土壤可溶性有机质数量和结构的影响。试验设对照（CT,0 kg hm^-2 a^-1）、高氮（HN：80 kg hm^-2 a^-1）、低氮（LN：40 kg hm^-2 a^-1）3种处理。结果表明：（1）在0-10 cm和10-20 cm土层,HN、LN处理的土壤可溶性有机碳和可溶性有机氮含量显著高于CT。（2）在0-10 cm和10-20 cm土层,1月时HN、LN处理的芳香性指数和腐殖化程度都显著高于CT,而4月时HN、LN处理的芳香性指数和腐殖化程度都显著低于CT。除了氮含量的直接影响外,RDA （冗余分析）表明,两土层中土壤含水量、pH和土壤有机碳是驱动氮沉降对土壤DOM数量和结构的重要环境因子。因此,氮沉降对土壤DOM的影响是复杂的,未来尤其应该注重氮沉降对生态系统影响的季节模式。     

杉木人工林土壤可溶性有机质及其与土壤养分的关系

通过在福建省来舟林场对不同栽植代数杉木人工林土壤可溶性有机碳(DOC)和氮(DON)及土壤养分的研究,其结果表明,随着杉木栽植代数的增加林地土壤DOC和DON含量逐渐下降,在0～10cm土层内第3代杉木林土壤DOC和DON含量分别是第1代杉木林的83.9%和87.1%、第2代杉木林的90.6%和96.9%,在10～20cm土层内第3代杉木林土壤DOC和DON含量分别是第1代杉木林的80.2%和81.5%、第2代杉木林的81.8%和90.0%。在不同林地和土层内土壤DOC含量之间的差异性达到了显著或极显著水平,而DON含量之间的差异性不显著。不同栽植代数杉木林土壤养分的变化趋势与DOM一致,随着杉木连栽,土壤养分含量呈下降趋势。在0～10cm土层内第3代杉木林土壤全氮、全钾、铵态氮和速效钾含量分别是第1代杉木林的83.1%、60.4%、68.1%和44.3%,是第2代杉木林的84.6%、68.5%、74.4%和58.7%;在10～20cm土层内第3代杉木林土壤全氮、全钾、铵态氮和速效钾含量分别是第1代杉木林的74.0%、53.4%、57.6%和54.6%,是第2代杉木林的94.8%、59.5%、74.3%和65.5%。经相关性分析,在各土层内土壤DOC和DON含量与土壤全氮、全钾、铵态氮和速效钾等土壤养分含量存在着不同程度的相关性。