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1.
【目的】通常恒温恒湿培养下土壤有机碳矿化强度随时间延长逐渐衰减，而干湿交替和阶段性扰动（如人为破碎、见光风干等）是否会改变这一趋势？【方法】设置多重干湿交替培养试验，并辅以人为破碎和见光风干阶段性扰动措施，分析多循环干湿交替下土壤有机碳矿化的动态特征，探讨人为破碎和见光风干对干湿交替培养下土壤有机碳矿化的影响。【结果】与恒湿（淹水和好气）处理相比，常规干湿交替每次复水和排水后对土壤有机碳矿化均有显著的激发效应，这种激发效应随着干湿交替次数增多逐步减弱，培养结束时土壤有机碳累积矿化量分别提高了72.09%和128.48%；见光风干相较于避光风干土壤有机碳矿化速率峰值和土壤有机碳累积矿化量分别提高了26.29%和16.15%，而人为破碎对土壤有机碳矿化特征无显著影响。各阶段难分解有机碳矿化的比例随着干湿交替次数逐渐增加。【结论】循环干湿交替并未改变土壤有机碳矿化强度随时间延长阶段性衰减的趋势，但衰减幅度有所减缓；见光风干阶段性扰动进一步减缓了衰减趋势，建议用于土壤有机碳矿化培养试验的土壤样品应尽量避光风干和保存。  相似文献   

2.
冻融交替对水稻土水溶性有机碳含量及有机碳矿化的影响   总被引：4，自引：2，他引：4  
郝瑞军  李忠佩  车玉萍 《土壤通报》2007,38(6):1052-1057
冻融交替影响土壤水分的有效性及土壤团聚体稳定性,进而影响土壤中微生物的活性及土壤有机碳的矿化。通过室内冻融模拟(即分别在-7℃和28℃下处理土壤)及培养实验,研究了不同冻融交替循环处理下土壤水溶性有机碳(WSOC)、微生物生物量及土壤有机碳矿化的变化规律。结果表明,1到3次冻融交替处理会增加土壤中水溶性有机碳的含量,其中经过1次冻融交替处理的2种土壤其WSOC含量分别增加了25%,20%;但在本实验条件下如果继续增加冻融交替次数则会使土壤水溶性有机碳含量减少。冻融交替处理降低土壤微生物生物量,因此也会影响土壤有机碳的矿化。冻融交替处理对培养第1天的土壤有机碳矿化具有激发效应,激发能力:1次冻融交替>3次冻融交替>6次冻融交替,经过1次冻融交替处理后的土壤其呼吸速率与对照相比增加了17%～40%;其后,冻融交替处理土壤呼吸速率迅速下降,在培养后期甚至低于对照处理。  相似文献   

3.
长期施肥对水稻土碳氮矿化与团聚体稳定性的影响   总被引：3，自引：2，他引：1  
水稻土有机碳、氮矿化过程对水稻土质量和作物养分吸收具有重要的作用,但是它们对施肥措施的响应及其与土壤结构之间的关系尚不清楚。本研究基于红壤性水稻土长期施肥定位试验,分析了不施肥(CK)、施用常量化肥(NPK)、2倍化肥(NPK2)和常量化肥配施有机肥(NPKOM)等处理下水稻土碳氮矿化特征,并研究了其与土壤团聚体稳定性的关系。结果表明NPKOM处理显著提高了土壤有机碳和全氮含量(P0.05),而单施化肥处理(NPK2和NPK)则同CK处理没有显著差异。土壤有机碳矿化速率、累积矿化量和矿化率均为NPKOMNPK2NPKCK处理,其中NPKOM处理显著高于其他处理(P0.05),而后3个处理间没有显著差异。土壤氮矿化速率、累积矿化量和矿化率同土壤碳矿化的规律一致,NPKOM、NPK2和NPK处理累积矿化氮量较CK处理分别提高110.0%、29.4%和8.8%,矿化率分别提高110.8%、25.6%和13.0%。单施化肥处理(NPK和NPK2)的平均质量直径(MWD)分别降低了17.1%和15.5%,而NPKOM处理则增加了19.4%。相关分析表明,土壤碳氮矿化主要取决于土壤有机碳氮含量,而与土壤团聚体水稳定性无直接关系。在今后研究中,应重点分析土壤孔隙结构与有机碳氮周转的关系。  相似文献   

4.
地处干旱半干旱区的黄灌区干湿交替过程中引起土壤环境因素的周期性变化,从而影响农田生态系统关键过程。通过连续测定黄河上游宁夏引黄灌区稻田在灌溉淹水和落干过程中的土壤pH,研究在水稻生育期内表层土壤pH在高频次灌溉排水干湿交替过程中的变化规律。结果表明:在灌水之后淹水过程中,表层土壤pH升高;相反在淹水之后落干过程中表层土壤pH降低;但在最后一次灌水之后,经过长时间的落干烤田过程,土壤pH随表层土壤表层盐分积累过程逐渐升高。土壤电导率(EC)与土壤pH在灌溉淹水和落干过程中具有相同的变化趋势,具有显著正相关性(p0.05),土壤氧化还原电位(Eh)与pH呈极显著负线性相关(p0.01),而灌溉量、施肥量、降水、地表5 cm土壤温度对表层土壤pH的影响均不显著。  相似文献   

5.
干湿交替对土壤碳库和有机碳矿化的影响   总被引：15，自引：0，他引：15  
水分是影响土壤活性碳库和惰性碳库周转过程的主导因子,而土壤有机碳的周转速率会对气候变化造成潜在的重要影响。以农田水稻土为供试土壤,通过培育试验研究了干湿交替过程对土壤有机碳矿化的影响,并利用两库叠加模型对土壤不同碳库及其降解动力学进行初步评估。结果表明:干湿交替激发了土壤呼吸,增加了土壤微生物代谢活性。三次湿润过程对土壤呼吸的激发量分别为119.3%、159.5%和87.3%,激发效应随干湿交替频率的增加先升高后降低。多次干湿交替后,土壤累积CO2释放量低于恒湿土壤,湿润所引起的激发的矿化量不足以弥补干旱期降低的矿化量。在湿润的数小时内,土壤溶解性有机碳含量先升高后降低。干湿交替提升了土壤活性碳库的降解速率,降低了惰性碳库的降解速率,湿润后土壤活性碳库显著增加。多次干湿交替降低了土壤真菌/细菌比,使土壤微生物群落结构发生变化,细菌成为优势种群。  相似文献   

6.
不同培养温度下长期施肥红壤水稻土有机碳矿化特征研究   总被引：4，自引：2，他引：2  
陈晓芬  吴萌  江春玉  刘明  李忠佩 《土壤》2019,51(5):864-870
以长期不同施肥处理红壤水稻土为研究对象,布置不同温度下(15、25和35℃)的室内培养试验,研究有机碳矿化的温度敏感性及施肥对土壤有机碳矿化的影响,并分析土壤有机碳矿化与土壤理化性质和不同形态碳素之间的关系。结果表明,培养前期(0～7 d),土壤有机碳矿化速率快速下降,之后逐渐降低并最终趋于稳定。温度升高提高了土壤有机碳矿化速率、累积矿化量和矿化率。磷肥和有机肥的施用提高了土壤有机碳累积矿化量。各处理土壤有机碳矿化的温度敏感性系数Q10为1.31～1.75,施肥提高了土壤有机碳矿化的温度敏感性。Q10与有机碳、全量和速效氮磷、微生物生物量碳、易氧化有机碳和胡敏酸碳呈显著或极显著的正相关关系。3种培养温度下土壤有机碳累积矿化量均与pH呈显著负相关,与有机碳和全氮呈显著或极显著正相关。25℃和35℃培养时,土壤有机碳累积矿化量与微生物生物量碳、胡敏酸碳和富里酸碳显著或极显著正相关。  相似文献   

7.
盐胁迫对棉田土壤微生物量和土壤养分的影响   总被引：6，自引：0，他引：6  
以耐盐品种中棉所44为材料,模拟滨海混合盐土成分,研究了正常灌水(土壤相对含水量保持在75±5%)和轻度干旱(55±5%)下,不同程度盐胁迫(0,0.35%,0.60%,0.85%,1.00%)对棉田土壤微生物量和土壤养分的影响。结果表明,棉花产量及产量构成(铃数和铃重)、生物量、根重均随着盐浓度的升高而显著递减。棉田土壤微生物量C和N在棉花各个生育期内均随着盐浓度的升高而显著降低,花铃期达到最大,土壤有机质、全氮、速效N、有效P、速效K等养分含量的变化趋势与土壤微生物量C和N基本一致,但降幅较小。土壤微生物量碳与土壤有机碳的比值、土壤微生物量氮与全氮的比值均随着盐浓度的升高而呈现逐渐下降的趋势,表明了土壤微生物量碳氮受盐胁迫的影响大于土壤有机碳和全氮,也表明了土壤微生物对土壤有机碳和全氮转化效率的显著减低。正常灌水条件下各盐分处理的棉花生物量、铃数、铃重、根重、土壤微生物量和土壤养分含量均显著高于相应干旱处理,干旱加重了盐分对土壤微生物量和土壤养分的抑制效应。土壤微生物量C和N与土壤pH值之间存在显著负相关,与土壤有机质、全氮、速效N、有效P、速效K之间均存在显著正相关。  相似文献   

8.
长期施肥对红壤旱地玉米生物量及养分吸收的影响   总被引：5，自引：1，他引：4  
基于江西进贤旱地长期施肥定位试验田,研究不同施肥模式下玉米不同器官的生物量、养分吸收与分配及其与土壤养分的关系.结果表明:(1)长期施用化肥导致土壤pH值下降,不合理施肥使土壤养分含量有不同程度的下降,有机无机肥配施能有效缓解土壤酸化,显著提高土壤有机碳和有效养分含量.(2)与对照相比,N处理降低了玉米籽粒、穗轴、秸秆和根茬的生物量,而均衡施肥(NPK、2NPK)及有机肥处理(NPKOM、OM)使玉米籽粒增产1.1～2.9倍,并提高了其他器官的生物量.土壤酸碱度、有机质及N、P养分对玉米籽粒的产量影响显著,土壤K养分对玉米生物量影响相对较小.(3)玉米对N的吸收主要集中在籽粒和秸秆,分别占总吸N量的41.8％～61.3％和30.3％～48.4％,P在籽粒中的吸收量高达61.8％～73.9％,K的吸收主要集中在秸秆,占总吸K量的51.4％～67.9％.有机无机肥配施模式则显著促进了作物各器官对养分的吸收和提高作物产量.作物养分的收获指数为P＞N＞K.  相似文献   

9.
不同农田生态系统土壤微生物生物量碳的变化研究   总被引：18，自引：0，他引：18       下载免费PDF全文
试验研究不同农田生态系统土壤微生物生物量碳的变化结果表明,长期单施N、P肥处理对土壤有机碳和微生物生物量碳的影响不明显,施有机肥处理土壤微生物生物量碳及微生物生物量碳/有机碳值均高于其他施肥处理,轮作中引入豆科作物或豆科连作均对土壤微生物生物量碳的积累有显著作用。  相似文献   

10.
长期施用化肥和秸秆对水稻土碳氮矿化的影响   总被引：5，自引：0，他引：5  
闫德智  王德建 《土壤》2011,43(4):529-533
以长期定位试验的土壤为供试材料,通过室内培养试验,研究了长期施用化肥和秸秆对水稻土?C、N矿化和微生物生物量的影响。结果表明长期施用化肥和秸秆增加了土壤?C?矿化量,但降低了可矿化?C?在土壤有机?C?中的比例。长期施用化肥能够增加土壤?N?矿化量,而且增加了可矿化?N?在土壤全?N?中的比例,但配施秸秆不能继续增加?N?矿化量。长期施用化肥和秸秆能够显著增加土壤微生物生物量?C、N?含量,但微生物量在土壤中的比例变化不大。  相似文献   

11.
Rewetting a dry soil has long been known to cause a burst of respiration (the “Birch Effect”). Hypothesized mechanisms for this involve: (1) release of cellular materials as a result of the rapid increase in water potential stress and (2) stimulating C-supply to microbes via physical processes. The balance of these factors is still not well understood, particularly in the contexts of multiple dry/wet cycles and of how resource and stress patterns vary through the soil profile. We evaluated the effects of multiple dry/wet cycles on surface and subsurface soils from a California annual grassland. Treatments included 4, 6, and 12 cycles that varied the length of the drying period between rewetting events. Respiration was monitored after each wetting event while extractable C and N, microbial biomass, and microbial activity were assayed initially, after the first rewetting event, and at the end of the experiment. Initially, microbial biomass and activity (respiration, dehydrogenase, and N mineralization) in subsurface soils were ca. 10% and 20% of surface soil levels. After multiple cycles, however, subsurface soil microbial biomass and activity were enhanced by up to 8-fold, even in comparison to the constantly moist treatment. By comparison, surface soil microbial biomass and activity were either moderately (i.e. 1.5 times increase) or not affected by wetting and drying. Drying and rewetting led to a cascade of responses (soluble C release, biomass growth, and enhanced activity) that mobilized and metabolized otherwise unavailable soil carbon, particularly in subsurface soils.  相似文献   

12.
The effects of adding P and of drying and rewetting were studied in two acid forest soils from southeast Australia. The soils were a yellow podzolic with a low soil organic matter content (3.75% C) and a red earth with a high organic matter content (13.5% C). C and N mineralization and microbial C and N contents were investigated in a laboratory incubation for 151 days. Microbial C and N were estimated by a hexanol fumigation-extraction technique. Microbial C was also determined by substrate-induced respiration combined with a selective inhibition technique to separate the fungal and the bacterial biomass. The results obtained by the selective inhibition technique were not conclusive. Adding P to the soil and drying and rewetting the soil reduced microbial N. This effect was more pronounced in rapidly and frequently dried soils. Microbial C was generally less affected by these treatments. Compared with the control, the addition of P caused a reduction in respiration in the red earth (-13%) but an increase in the yellow podzolic soil (+12%). In the red earth net N mineralization was highest following the addition of P. In the yellow podzolic soil highest N mineralization rates were obtained when the soil was subjected to drying and rewetting cycles. In both soils increased N mineralization was associated with a decrease in microbial N, indicating that the mineralized N was of microbial origin. Nitrification decreased with rapid drying and rewetting. The addition of P promoted heterotrophic nitrification in both soils.  相似文献   

13.

Purpose

The aim of the research was to explore the effect of Chinese milk vetch (CM vetch) addition and different water management practices on soil pH change, C and N mineralization in acid paddy soils.

Materials and methods

Psammaquent and Plinthudult paddy soils amended with Chinese milk vetch at a rate of 12 g?kg?1 soil were incubated at 25 °C under three different water treatments (45 % field capacity, CW; alternating 1-week wetting and 2-week drying cycles, drying rewetting (DRW) and waterlogging (WL). Soil pH, dissolved organic carbon, dissolved organic nitrogen (DON), CO2 escaped, microbial biomass carbon, ammonium (NH4 +) and nitrate (NO3 ?) during the incubation period were dynamically determined.

Results and discussion

The addition of CM vetch increased soil microbial biomass concentrations in all treatments. The CM vetch addition also enhanced dissolved organic N concentrations in all treatments. The NO3–N concentrations were lower than NH4–N concentrations in DRW and WL. The pH increase after CM vetch addition was 0.2 units greater during WL than DRW, and greater in the low pH Plinthudult (4.59) than higher pH Paleudalfs (6.11) soil. Nitrogen mineralization was higher in the DRW than WL treatment, and frequent DRW cycles favored N mineralization in the Plinthudult soil.

Conclusions

The addition of CM vetch increased soil pH, both under waterlogging and alternating wet–dry conditions. Waterlogging decreased C mineralization in both soils amended with CM vetch. Nitrogen mineralization increased in the soils subjected to DRW, which was associated with the higher DON concentrations in DRW than in WL in the acid soil. Frequent drying–wetting cycles increase N mineralization in acid paddy soils.  相似文献   

14.
Drying and rewetting of soil is an important process in soil aggregation, soil organic matter (SOM) decomposition, and nutrient cycling. We investigated the source of the C and N flush that occurs upon rewetting of dry soil, and whether it is from microbial death and/or aggregate destruction. A moderately well drained Kennebec silt loam (Fine-silty, mixed, superactive, mesic Cumulic Hapludoll) was sampled to a 10 cm depth. Soil under constant water content (CWC) was compared with soil subjected to a series of four dry-wet (DW) cycles during the experimental period (96 d) and incubated at 25 °C. Mineralized C and N were measured during the drying and rewetting periods. Aggregate size distributions were studied by separating the soil into four aggregate size classes (>2000, 250-2000, 53-250, and 20-53 μm) by wet sieving. Repeated DW cycles significantly reduced cumulative N mineralization compared with CWC. The reduction in cumulative mineralized C resulting from DW compared with CWC increased as the DW treatments were subjected to additional cycles. The flush of mineralized C significantly decreased with repeated DW cycles. There was no significant effect on aggregate size distributions resulting from to the DW cycles compared with CWC treatment. Therefore, the flush of mineralized C and N seemed to be mostly microbial in origin in as much as aggregate distribution was unaffected by DW cycles.  相似文献   

15.
The effects of repeated soil drying and rewetting on microbial biomass N (Nbio) and mineral N (Nmin) were measured in incubation experiments simulating typical moisture and temperature conditions for soils from temperate climates in the post‐harvest period. After application of in vitro 15N‐labeled fungal biomass to a silty loam, one set of soils was exposed to two drying‐rewetting cycles (treatment DR; 14 days to decrease soil moisture to 20 % water‐holding capacity (WHC) and subsequently 7 days at 60 % WHC). A control set (treatment CM) was kept at constant moisture conditions (60 % WHC) throughout the incubation. Nbio and Nmin as well as the 15N enrichment of these N pools were measured immediately after addition of 15N‐labeled biomass (day 0) and after each change in soil moisture (day 14, 21, 35, 42). Drying and rewetting (DR) resulted in higher Nmin levels compared to CM towards the end of the incubation. Considerable amounts of Nbio were susceptible to mineralization as a result of soil drying (i.e., drying enhanced the turnover of Nbio), and significantly lower Nbio values were found for DR at the end of each drying period. Immediately after biomass incorporation into the soil (day 0), 22 % of the applied 15N was found in the Nmin pool. Some of this 15Nmin must have been derived from dead cells of the applied microbial biomass as only about 80 % of the microbes in the biomass suspension were viable, and only 52 % of the 15Nbio was extractable (using the fumigation‐extraction method). The increase in 15Nmin was higher than for unlabeled Nmin, indicating that added labeled biomass was mineralized with a higher rate than native biomass during the first drying period. Overall, the effect of drying and rewetting on soil N turnover was more pronounced for treatment DR compared to CM during the second drying‐rewetting cycle, resulting in a higher flush of mineralization and lower microbial biomass N levels.  相似文献   

16.
Drying and rewetting of soil can have large effects on carbon (C) and nitrogen (N) dynamics. Drying-rewetting effects have mostly been studied in the absence of plants, although it is well known that plant–microbe interactions can substantially alter soil C and N dynamics. We investigated for the first time how drying and rewetting affected rhizodeposition, its utilization by microbes, and its stabilization into soil (C associated with soil mineral phase). We also investigated how drying and rewetting influenced N mineralization and loss. We grew wheat (Triticum aestivum) in a controlled environment under constant moisture and under dry-rewetting cycles, and used a continuous 13C-labeling method to partition plant and soil organic matter (SOM) contribution to different soil pools. We applied a 15N label to the soil to determine N loss. We found that dry-rewetting decreased total input of plant C in microbial biomass (MB) and in the soil mineral phase, mainly due to a reduction of plant biomass. Plant derived C in MB and in the soil mineral phase were positively correlated (R2 = 0.54; P = 0.0012). N loss was reduced with dry rewetting cycles, and mineralization increased after each rewetting event. Overall drying and rewetting reduced rhizodeposition and stabilization of new C, primary through biomass reduction. However, frequency of rewetting and intensity of drought may determine the fate of C in MB and consequently into the soil mineral phase. Frequency and intensity may also be crucial in stimulating N mineralization and reducing N loss in agricultural soils.  相似文献   

17.
为了验证平衡施肥对长期缺施钾肥的南方红壤性水稻土的修复效果,通过2年盆栽试验,以五种不同施肥处理（NPK、NPKSi、NPKOM、NPhK、NPhKOM）,研究了长期缺施钾肥的水稻土的微生物特性,结果发现,在对照（NPK）基础上增施硅肥（NPKSi）、钾肥（NPhK）能促进细菌和放线菌数量的增长,提高微生物活度,加速微生物量N、P的转化,同时也能提高微生物量C。相反,在淹水条件下配施有机肥（NPKOM）,由于降低了水稻根际环境的氧化还原电位,使根际微生物生长萎缩,微生物活度、微生物量C无显著提高;虽然土壤微生物量N、P随之增加,但有机N的矿化减弱,植株可吸收的有效态养分减少。增施钾肥的同时配施有机肥（NPhKOM）具有增施钾肥的优点,即可提高微生物活度、提高微生物量C,加速有机N、P的矿化,但同时也会减少微生物数量。因此在缺钾水稻土的修复实践中,常规施肥的基础上对水稻增施硅肥、钾肥应是有效举措,而配施有机肥则须谨慎:有机肥或须适量酌施,或须结合增施钾（硅）肥。  相似文献   

18.
Soil drying and wetting impose significant influences on soil nitrogen (N) dynamics and microbial communities. However, effects of drying-wetting cycles, while common in vegetable soils, especially under greenhouse conditions, have not been well studied. In this study, two greenhouse vegetable soils, which were collected from Xinji (XJ) and Hangzhou (HZ), China, were maintained at 30% and 75% water-holding capacity (WHC), or five cycles of 75% WHC followed by a 7-day dry-down to 30% WHC (DW). Soil inorganic N content increased during incubation. Net N mineralization (Nmin), microbial activity, and microbial biomass were significantly higher in the DW treatment than in the 30% and 75% WHC treatments. The higher water content (75% WHC) treatment had higher Nmin, microbial activity, and microbial biomass than the lower water content treatment (30% WHC). Multivariate analyses of community-level physiological profile (CLPP) and phospholipid fatty acid (PLFA) data indicated that soil moisture regime had a significant effect on soil microbial community substrate utilization pattern and microbial community composition. The significant positive correlation between Nmin and microbial substrate utilization or PLFAs suggested that soil N mineralization had a close relationship with microbial community.  相似文献   

19.
Summary The effects of adding lime and/or phosphate to an acid, phosphate-deficient soil on microbial activity, enzyme activities and levels of biomass and extractable N, S and P were studied under laboratory conditions. Following rewetting there was, as expected, an initial flush in microbial growth and activity, as shown by large increases in CO2 evolution, in levels of biomass N, S and P and by accumulation of extractable mineral N and sulphate in the soil. Following rewetting, additions of lime and phosphate further stimulated mineralization of C, N and S. In the first 4 weeks of incubation, the mineralized N accumulated in the soil as ammonium N and there was a concomitant rise in soil pH. After this initial period, nitrification increased substantially and soil pH decreased again. Additions of lime generally increased protease and sulphatase activities but decreased phosphatase activity. Additions of phosphate decreased the activities of all three enzymes. The positive effect of liming on protease and sulphatase activities persisted for the duration of the experiment while accumulation of mineral N and sulphate effectively ceased after about 4 weeks. Furthermore, although phosphate additions decreased the activities of protease and sulphatase they increased the accumulation of mineral N and sulphate. Thus, protease and sulphatase activities were not reliable indicators of the relative amounts of mineral N and sulphate accumulated in the soil during incubation. Some uncertainty surrounded the validity of biomass S and P values estimated by the chloroform fumigation technique because differing proportions of the sulphate and phosphate released from the lysed cells may have been extracted from the different treatments.  相似文献   

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