土壤溶解有机碳的研究进展

系统地综述DOC的来源、组成、性质、影响因素、环境效应及测定方法等。尽管关于土壤DOC的研究目前还不完善，至今对DOC的组成，性质等问题都不是很清楚，但现有的研究已经表明，DOC是土壤圈中一种非常活跃的化学物质，它对土壤中化学物质的溶解、吸附、解吸、迁移和毒性等行为均有显著的影响。     

胶州湾滨海湿地土壤溶解性有机碳淋溶特征

[目的]在山东省青岛市胶州湾滨海湿地采集光滩、碱蓬、芦苇和米草4种不同植被类型土壤,探究滨海湿地土壤溶解性有机碳淋溶特征。[方法]通过室内土柱淋溶试验,测定土壤淋出液溶解性有机碳(DOC)浓度,利用紫外—可见分光光度法对土壤淋出液DOC结构进行分析。[结果]土壤淋出液DOC浓度随土层深度增加而增加;芦苇湿地的土壤淋出液DOC浓度最高,为23.12mg/L,其次分别为碱蓬湿地,米草湿地和光滩湿地,分别为15.22mg/L,14.44mg/L与8.38mg/L。4种土壤淋出液DOC光谱特征值存在一定的差异性,碱蓬湿地土壤淋出液DOC的芳香性和腐殖化程度最高,米草湿地土壤淋出液DOC的分子量和团聚化最大;随土层深度的增加土壤淋出液DOC的芳香性、腐殖化程度增大,分子量以及团聚化程度逐渐减小。[结论]植被残体的分解以及土壤的解吸附能力的差异是造成不同土层土壤淋出液DOC浓度差异的主要原因;而植被类型是影响土壤淋出液DOC结构变化的关键因素。     

江苏下蜀林区土壤溶解有机碳与土壤因子的关系

采用TOC-5000A总有机碳仪测定了江苏下蜀森林土壤溶解有机碳(DOC)的含量,分析了土壤DOC与土壤因子的关系。结果表明:酸性森林土壤中,DOC与有机C、全N、碱解N、有效P等养分因子之间呈极显著或显著的正相关关系,土壤DOC与土壤肥力状况关系密切,因而可以作为评价土壤肥力性状的生物学指标。土壤DOC与土壤中有机络合态Fe、有机络合态Al和活性羟基Al之间呈极显著或显著的正相关。土壤中有机C的运输是调整土壤中Al和Fe的溶出及迁移的一个重要因子。土壤DOC与交换性Al、pH值、全P、速效K之间无相关关系。     

淹水条件下水稻田中磷的淋溶研究

采用地下垂直埋入钢管收集土壤淋溶液的方法，在江苏宜兴对水稻生长季节内稻田土壤中P向下迁移作了研究，重点主要集中在淋溶液中P的浓度、渗漏速度以及P的淋溶量测定几个方面。结果表明，在整个水稻生长季中淋溶液的溶解P与全P浓度均不高，溶解P的浓度维持在0．02mg／L以下，全P的浓度则在0．03-0．08mg／L之间；土壤直渗速度为0．53cm／天；本实验方法测得的淋溶量中，整个水稻生长季在施P量为30kg/hm^2的条件下，P的淋溶量为3．77kg/hm^2，其各土壤层次中土壤表层淋溶量所占比例最大，占各层总淋溶量的36％。     

红壤稻田土壤溶解有机碳含量动态及其生物降解特征

本通过田间采样分析和室内培育试验,研究了不同利用年限的3种红壤水田土壤中溶解有机C(DOC)的含量动态和生物降解特征。结果表明：土壤DOC的含量随土壤深度而降低,二具有显负相关性。0-30cm土壤DOC的含量及其占总C比例随土壤有机C含量的升高而增大。DOC的季节变化明显,主要与气候因素有关：降雨和灌水可显提高DOC的含量,是落干时含量的1．44-2．50倍。淋溶试验结果表明,从试验开始,淋滤液中DOC的浓度呈增加趋势,至2l天时达到最大,其后又趋下降。在49天的培养期内,DOC的分解速率为3l％-58％,其中低分子量组分能在数天内降解掉。不同土壤间DOC的分解速率有明显差异。     

桂林毛村岩溶区与非岩溶区几种果树土壤溶解有机碳空间变化

土壤溶解有机碳是当前环境学的研究热点之一。从土壤溶解有机碳的空间变化的角度出发,研究了果树在岩溶区与非岩溶区土壤溶解有机碳的表现。结果表明,不同区域、不同树种、不同取样深度的土壤溶解有机碳的含量均不同,非岩溶区、20cm的土壤溶解有机碳含量较岩溶区、50cm为高,不同树种在不同区域不同深度有不同的表现。低pH对应较高的土壤溶解有机碳含量。     

喀斯特石漠化过程对土壤活性有机碳的影响

以贵州省花江峡谷区典型喀斯特石漠化小流域为研究区域,对潜在、轻度、中度、强度石漠化等级样地代表性土壤活性有机碳进行了测试分析.分析结果表明,随着石漠化程度的增加,土壤微生物生物量碳(sMBc)、轻组有机碳(LFOC)、可矿化碳(MC)、微生物商(qSMBC)呈下降趋势,微生物呼吸商(qCO2)呈上升趋势,与石漠化过程有一致性,能较好体现石漠化过程中土壤退化的本质.开垦序列土壤活性有机碳库的周转速率和土壤微生物碳库的下降速率大于樵采序列,使得开垦序列土壤即使在高的生物归还量下,形成土壤有机碳的比例相对较小.土壤SMBC,LFOC,MC,易氧化有机碳(LOC),qSMBC,qCO2等生物学性质除了与人为干扰方式有关外,还与植被生物量有关,可以体现土壤质量发展的方向,是石漠化过程土壤退化及恢复评价的敏感指标.     

不同有机物料还田对华北农田土壤固碳的影响及原因分析

中国农业面临着废弃物数量大、污染严重,农田土壤生产力低的现实问题。该研究以增加农田土壤固碳为目标对砂质农田进行有机物料还田,将秸秆、猪粪、沼渣和生物炭4种物料用尿素调节等氮还田,对农田土壤有机碳、颗粒有机碳、可溶性有机碳和微生物量碳的含量进行测定,并探究不同有机物料还田对土壤有机碳的影响原因。研究结果表明:物料还田3a后,生物炭、猪粪和沼渣处理土壤有机碳(SOC)比秸秆处理分别高262.4%、26.8%和20.7%;2014—2015年生物炭处理的土壤微生物量碳(MBC)较秸秆处理降低2.9%~35.5%,猪粪处理和沼渣处理的土壤可溶性有机碳(DOC)分别提高17.1%~60.1%和7.2%~64.8%;2014—2015年生物炭、猪粪和沼渣处理土壤颗粒有机碳(POC)较秸秆处理提高10.8%~148.2%、9.5%~58.3%和11.3%~57.6%;物料还田后,土壤总有机碳(TOC)和POC呈极显著的回归关系(R2=0.67,P0.001),土壤DOC与MBC有极显著相关性(R2=0.52,P0.001)。与秸秆还田相比,生物炭还田有利于土壤POC的累积进而促进土壤有机碳的提升,猪粪和沼渣则通过提高土壤MBC、DOC和POC的含量,促进土壤有机碳的周转和固定。从农田土壤固碳角度而言,生物炭,猪粪和沼渣还田优于秸秆还田。     

有机物料添加对内蒙古河套灌区碱化土壤可溶性有机碳的影响

通过研究不同有机物料添加对内蒙古河套灌区碱化土壤可溶性有机碳含量变化的影响,寻找合理高效的增碳方式,降低碱化土壤有机碳损失。以内蒙古河套灌区轻度、中度盐碱土为对象进行田间试验,设置生物炭（BC）添加、羊粪（GM）添加,对照（CK）3个处理,对比和分析不同有机物料添加后土壤有机碳（SOC）、可溶性有机碳（DOC）、土壤理化性质的变化。结果表明：（1）与CK相比,轻度碱化土壤BC、GM处理土壤DOC含量分别增加3.28%,20.66%,SOC含量增加5.40%,10.30%,中度碱化土壤BC和GM处理下可溶性碳增加41.32%,74.10%,土壤SOC含量增加60.24%,79.16%;（2）轻度碱化土壤BC和GM处理土壤DOC含量与SOC含量呈负相关,中度碱化土壤BC和GM处理下呈正相关;（3）盐碱土壤SOC、DOC含量主要与土壤pH、电导率的变化有关;BC处理较GM处理相比土壤电导率低约1.93%~29.15%,而GM处理土壤pH、碱化度比BC处理低0.31%~1.53%,7.10%~24.63%。总体来看,有机物料添加后均能使土壤中SOC、DOC含量提高,不同程度地降低土壤碱化程度,且羊粪添加较生物炭略好,因此羊粪添加对河套灌区碱化土壤碳含量的提高比生物炭添加更有效,土壤改良效果更好,土壤理化性质改善更明显。     

有机物料输入稻田提高土壤微生物碳氮及可溶性有机碳氮

土壤微生物量碳、氮和可溶性有机碳、氮是土壤碳、氮库中最活跃的组分,是反应土壤被干扰程度的重要灵敏性指标,通过设置相同有机碳施用量下不同有机物料处理的田间试验,研究了有机物料添加下土壤微生物量碳（soil microbial biomass carbon,MBC）、氮（soil microbial biomass nitrogen,MBN）和可溶性有机碳（dissolved organic carbon,DOC）、氮（dissolved organic nitrogen,DON）的变化特征及相互关系。结果表明化肥和生物碳、玉米秸秆、鲜牛粪或松针配施下土壤微生物量碳、氮和可溶性有机碳、氮显著大于不施肥处理（no fertilization,CK）和单施化肥处理,分别比不施肥处理和单施化肥平均高23.52%和12.66%（MBC）、42.68%和24.02%（MBN）、14.70%和9.99%（DOC）、22.32%和21.79%（DON）。化肥和有机物料配施处理中,化肥+鲜牛粪处理的微生物量碳、氮和可溶性有机碳、氮最高,比CK高26.20%（MBC）、49.54%（MBN）、19.29%（DOC）和32.81%（DON）,其次是化肥+生物碳或化肥+玉米秸秆处理,而化肥+松针处理最低。土壤可溶性有机碳质量分数（308.87 mg/kg）小于微生物量碳（474.71 mg/kg）,而可溶性有机氮质量分数（53.07 mg/kg）要大于微生物量氮（34.79 mg/kg）。与不施肥处理相比,化肥和有机物料配施显著降低MBC/MBN和DOC/DON,降低率分别为24.57%和7.71%。MBC和DOC、MBN和DON随着土壤有机碳（soil organic carbon,SOC）、全氮（total nitrogen,TN）的增加呈显著线性增加。MBC、MBN、DOC、DON、DOC+MBC和DON+MBN之间呈极显著正相关（P<0.01）。从相关程度看,DOC+MBC和DON+MBN较MBC、DOC、MBN、DON更能反映土壤中活性有机碳和氮库的变化,成为评价土壤肥力及质量的更有效指标。结果可为提高洱海流域农田土壤肥力,增强土壤固氮效果,减少土壤中氮素流失,保护洱海水质安全提供科学依据。     

水稻品种和砷污染对土壤溶解性有机碳氮的影响

选取有机质含量和pH不同的2种水稻土(黄泥田和红泥田),通过盆栽实验研究砷(As)污染条件下,种植9个水稻品种对土壤溶解性有机碳(DOC)和溶解性有机氮(DON)含量的影响,分析水稻品种、As污染和土壤类型的相对影响与交互作用.结果表明,水稻品种显著影响了土壤DOC和DON的变化,在水稻收获后,DOC平均含量的大小顺序为杂交稻(41.09±0.92 mg kg-1)＞籼稻(38.10±1.53 mg kg-1)＞粳稻(37.74± 1.37 mg kg-1);DON平均含量的大小顺序为粳稻(2.94± 0.40 mg kg-1)＞杂交稻(2.61±0.42 mg kg-1)＞籼稻(1.45± 0.17 mg kg-1).As污染降低了土壤DOC和DON的含量,但不同品种水稻的响应不同.与对照相比,As污染条件下,黄泥田和红泥田中DOC平均含量分别下降了14.4％和11.1％,DON平均含量分别下降了65.0％和44.7％;DOC在种植杂交稻后降幅最小,而DON在种植籼稻后降幅最小.在两种水稻土中,黄泥田的DOC和DON平均含量高于红泥田,在没有As污染条件下,分别高22.4％和45.8％,这与黄泥田有机质含量和pH高有关.水稻品种、As污染和土壤类型对DOC和DON变化的影响不同,3个因子对DOC变化的相对贡献率分别为7.7％、15.5％和27.6％,对DON变化的相对贡献率分别为14.7％、24.2％和2.0％.     

不同植被类型对滨海盐碱土壤有机碳库的影响

对江苏滨海盐碱地5种不同植被类型土壤（0 ~ 40 cm）有机碳（SOC）含量、密度和表层（0 ~ 20 cm）土壤微生物量碳（SMBC）、可溶性有机碳（DOC）含量及其占总有机碳（TOC）的比例进行了分析。结果显示,随土层深度的增加,SOC含量降低,表层SOC密度占整个剖面的54.6% ~ 75.8%。表层SOC含量和密度分别介于2.02 ~ 9.61 g/kg和5.87 ~ 21.54 t/hm2,平均值分别为4.77 g/kg和12.56 t/hm2。随着原生植被群落的演替（光滩→盐蒿→茅草）,SOC、SMBC和DOC含量均依次增加。茅草荒地围垦后,稻-油轮作地和菊芋地表层SOC密度分别比茅草地的增加了55%（5.77 t/hm2）和107%（11.15 t/hm2）;稻-油轮作地的SMBC含量及SMBC/TOC比值下降,而菊芋地的上升;围垦后土壤DOC含量及DOC/TOC比值都明显下降。结果表明,滨海盐碱地SOC主要分布在表层,原生植被群落的顺行演替使SOC库容增加且活性增强,在盐荒地围垦初期（3年）,SOC库容增加但活性有所减弱。经估算,滨海盐碱非耕地具有较大的固碳潜力,但需要合理的耕作管理措施来保证农业生产的可持续发展并实现增汇减排的目标。     

Direct effects of litter decomposition on soil dissolved organic carbon and nitrogen in a tropical rainforest

To clarify how litter decomposition processes affect soil dissolved organic carbon (DOC) and soil dissolved nitrogen (DN) dynamics, we conducted a field experiment on leaf litter and collected DOC and DN from the underlying soil in a tropical rainforest in Xishuangbanna, southwest China. Principal components analysis (PCA) showed the first PCA axis (corresponding to degraded litter quantity and quality) explained 61.3% and 71.2% of variation in DOC and DN concentrations, respectively. Stepwise linear regression analysis indicated that litter carbon mass controlled DOC and hemicellulose mass controlled DN concentrations. Litter decomposition was the predominant factor controlling surface-soil DOC and DN dynamics in this tropical rainforest.     

长期施肥对黄壤有机碳平衡及玉米产量的影响

基于长期定位试验,以黔中典型黄壤为研究对象,采用单因素方差分析、可持续性指数、稳定性指数等方法对长期定位试验获取的数据进行分析和比较,以探讨长期不同施肥处理对黄壤有机碳含量、有机碳平衡量、玉米产量稳定性、可持续性及其相互关系的影响。结果表明:(1)与施化肥和对照处理相比,施有机肥处理土壤有机碳含量明显升高,按大小排序依次为:MMNPK1/2M+1/2NPK1/4M+3/4NPK;(2)施有机肥处理黄壤有机碳平衡量为正值,且随有机肥施用量增加而增加,相反,施化肥和对照处理均为负值,大小依次为:MNPK、M1/2M+1/2NPK1/4M+3/4NPKNPKNKNPN、CKPK,各处理差异显著;(3)有机肥与化肥配施、有机肥单施及氮磷钾化肥协调施用更有利于提高玉米产量,排序为:MNPK1/4M+3/4NPK、1/2M+1/2NPKNPK、MNPNK、PK、NCK;(4)适量有机肥与化肥配施可提高玉米产量稳定性和可持续性(可持续性指数0.6,变异系数0.3),其中,1/4M+3/4NPK处理玉米产量稳定性和持续性最好;(5)玉米年产量与黄壤有机碳平衡量相关度较高,而玉米可持续性、稳定性则主要受有机碳含量影响。综上,有机肥与化肥配施有利于黄壤有机碳含量提升、玉米维持高产稳产。按适量"减肥"原则,以25%有机肥配施75%氮磷钾化肥效果最佳。     

Experimental evaluation of methods to quantify dissolved organic nitrogen (DON) and dissolved organic carbon (DOC) in soil

A significant proportion of the total nutrient in soil solution can be bound to organic molecules and these often constitute a major loss from soil to freshwater. Our purpose was to determine whether chemical extractants used for measuring inorganic N could also be used to quantify dissolved organic nitrogen (DON) and carbon (DOC) in soil. In a range of soils, DOC and DON were extracted with either distilled water or 2 M KCl and the amount recovered compared with that present in soil solution recovered by centrifugal-drainage. The recovery of DON and DOC from soil was highly dependent upon the method of extraction. Factors such as soil sampling strategy (number of samples over space and time), sample preparation (sieving and drying), soil storage, extraction temperature, shaking time, and soil-to-extractant volume ratio all significantly affected the amount of DOC and DON extracted from soil. To allow direct comparison between independent studies we therefore propose the introduction of a standardized extraction procedure: Replicate samples of unsieved, field-moist soil extracted as soon as possible after collection with distilled water, 0.5 M K₂SO₄ or 2 M KCl at a 1:5 w/v ratio for 1 h at 20 °C.     

水溶性有机物在土壤中的化学行为及其对环境的影响

水溶性有机物(Dissolved organic matter,DOM)是能够溶解于水的有机化合物的统称。尽管目前对于陆地生态系统中DOM的研究尚不完善,对其性质、组成和分类方法等问题的看法还没有达成一致,但现有研究结果已经表明DOM是一种十分活跃的重要化学组分。DOM进入土壤后将发生吸附、解吸、迁移、转化等一系列化学过程,进而对土壤及环境产生一系列重要影响:一方面,DOM可以与土壤胶体结合,形成有机无机结合体,从而改善土壤性质,DOM还可以通过其自身的分解产生养分离子,从而提高土壤肥力;另一方面,DOM也可能亲合土壤中原来与土壤胶体结合的养分,使之与DOM一起进入土壤溶液,从而增加土壤中养分离子被淋失的风险,并造成土壤养分的损失以及水体的富营养化,DOM还有可能活化土壤中重金属离子,增加土壤中重金属离子的毒性,并使土壤中的重金属离子向地下水迁移。由于其对土壤和环境的多种效应,水溶性有机物近年来已经逐渐成为土壤学、环境科学、生态学等学科的研究热点之一。     

Impacts of particulate organic carbon and dissolved organic carbon on removal of polycyclic aromatic hydrocarbons, organochlorine pesticides, and nonylphenols in a wetland

Background, aim, and scope  The potential of wetlands for controlling point- and nonpoint-source pollution in surface water has attracted increasing interest. The partitioning process of organic contaminants between water, particulate organic carbon (POC) and dissolved organic carbon (DOC), impacts their behaviors in the aquatic environments. Meantime, the partitioning process of organic contaminants is closely related to their physicochemical properties, such as hydrophobicity (or K _ow), and their fates in wetlands may vary greatly depending on physicochemical properties. The aim of this study was to examine fates and removals of polycyclic aromatic hydrocarbons (PAHs), organochlorine pesticides (OCPs) and nonylphenols (NPs) in a wetland in Beijing, China, and provide useful information for ecological remediation. Materials and methods  Water samples, collected at five sites from inlet to outlet of the wetland once a month in summer 2006, were immediately filtered within 2 days through 0.45-μm glass fiber prefilters and enriched by solid-phase extraction. The filtered particulates were collected as the total suspended particulates (TSPs), freeze-dried, and Soxhlet-extracted. After extraction, samples were purified following a clean-up procedure and analyzed by GC-MS. Results  TSPs could be removed efficiently with a removal rate of 97.4%, and DOC could be moderately removed with a removal rate of 44.7% from inlet to outlet. The total removals of target contaminants varied widely from null to 82.0%. A good correlation between logK _ow and logK _oc (organic-carbon-normalized suspended-particulate partition coefficient) was observed (r ² = 0.84 for PAHs and r ² = 0.86 for OCPs, p < 0.01). Ratios of the POC-bound fraction of target contaminants (or DOC-bound fraction) to the freely dissolved fraction increased with their K _ow values. The removal of the POC fraction contributed more than 50% to the total removal for the contaminants with logK _ow > 5.0. Only a small portion of the removal was attributed to the removal of the freely dissolved fraction. Discussion  Hydrophobic compounds such as PAHs and OCPs with higher K _ow values would show stronger POC or DOC preference. Their removal depended greatly on their K _ow values and the removal of total suspended particulates. On the other hand, concentrations of NPs decreased little in the wetland, probably due to their production through degradation of their precursors and relatively low hydrophobicity. Conclusions  POC and DOC play essential roles on the fates and removals of hydrophobic organic contaminants in the wetland. The removal of target contaminants with a high K _ow should be mainly through association with the suspended particulates which were precipitated and retained in the wetland. The fates of the organic contaminants in the wetland greatly depended on their hydrophobicities. Recommendations and perspectives  Further work should be done to study the influence of hydraulic retention time and some other environmental factors, e.g., temperature, on removals and fates of organic contaminants. Behavior of NPs and their precursors in the wetland should also be investigated more thoroughly.     

黑碳添加对土壤有机碳矿化的影响

通过室内培养试验,向土壤中分别添加不同温度制备的黑碳,热解温度分别为350℃(T350)、600℃(T600)和850℃(T850),研究了黑碳添加对土壤有机碳矿化的影响。结果表明,不同温度条件制备的黑碳在15℃和25℃培养条件下,土壤CO2释放速率总的趋势是前期分解速率快,后期缓慢。在整个培养过程中(112天),随着培养时间的延长,土壤CO2释放速率下降趋势逐渐降低,CO2释放速率相对值的大小随着培养温度的的升高而增大。在不同温度培养条件下,添加黑碳后土壤CO2-C累计量均是T350>T600>T850,T350土壤CO2-C累计量最高分别为415.26 mg/kg和733.82 mg/kg。添加不同黑碳后,土壤有机碳矿化增加率存在极显著差异(p<0.01),表明不同温度制备的黑碳对土壤有机碳矿化的影响显著。     

土壤有机质对有效磷及水提取磷含量的影响

为了解土壤有机质对有效磷与总磷、水提取磷与有效磷关系的影响,采用田间调查的方法,对洛阳市郊主要农田4种土壤耕作层土壤进行取样调查,并采用常规土壤测试方法,分别测定土样有机质、金磷、有效磷和水提取磷含量.根据有机质含量(高于或低于16.0 g·kg-1)把土样分成两组,对两组土样的总磷与有效磷、有效磷与水提取磷分别做相关关系分析.结果表明:与低有机质土样组相比,高有机质土样组有效磷与总磷相关方程的斜率较大,水提取磷与有效磷相关方程的斜率较小,这一趋势在以Olsen法和Mehlich-3法测定有效磷时均相同.表明在缺磷环境中,有机质增加条件下,虽然磷的生物有效性降低,但有助于在土壤溶液中维持相对较高的磷酸根浓度,这可能是由于磷的周转加快;随着土壤磷含量增加,有机质增加有助于更快提高磷的生物有效性,但土壤溶液中维持相对较低的磷酸根浓度,这可能有助于减轻农田磷的渗漏流失.     

Effective retention of litter-derived dissolved organic carbon in organic layers

This study aimed to gain insight into the generation and fate of dissolved organic carbon (DOC) in organic layers. In a Free Air CO₂ Enrichment Experiment at the alpine treeline, we estimated the contribution of ¹³C-depleted recent plant C to DOC of mor-type organic layers. In an additional laboratory soil column study with 40 leaching cycles, we traced the fate of ¹³C-labelled litter-DOC (22 and 45 mg l⁻¹) in intact Oa horizons at 2 and 15 °C. Results of the field study showed that DOC in the Oa horizon at 5 cm depth contained only 20 ± 3% of less than six-year-old C, indicating minor contributions of throughfall, root exudates, and fresh litter to leached DOC. In the soil column experiment, there was a sustained DOC leaching from native soil organic matter. Less than 10% of totally added litter-DOC was leached despite a rapid breakthrough of a bromide tracer (50 ± 7% within two days). Biodegradation contributed only partly to the DOC removal with 18-30% of added litter-DOC being mineralized in the Oa horizons at 2 and 15 °C, respectively. This was substantially less than the potential 70%-biodegradability of the litter-DOC itself, which indicates a stabilization of litter-DOC in the Oa horizon. In summary, our results give evidence on an apparent ‘exchange’ of DOC in thick organic layers with litter-DOC being retained and ‘replaced’ by ‘older’ DOC leached from the large pool of indigenous soil organic matter.