Effect of seasonal freeze–thaw cycle on net nitrogen mineralization of soil organic layer in the subalpine/alpine forests of western Sichuan,China

Nitrogen mineralization, a main way that soil organic nitrogen converts to mineral nitrogen, is one of the key processes in soil nitrogen cycle. The mineral nitrogen has an important role in plant growth in the growing season. It has been widely accepted that soil freezing in winter can kill a number of microorganisms, weakening soil nitrogen mineralization. However, more and more recent studies have documented that soil microorganisms still have high activity during the deep freezing period, and obvious nitrogen mineralization in winter. Seasonal freeze–thaw cycle is a common phenomenon in the subalpine/alpine forest region, which may have a strong effect on soil ecological processes. Furthermore, the changing pattern of seasonal freeze–thaw cycles might have a significant influence on soil nitrogen mineralization in this region in the scenarios of global warming. As yet, little attention has been given to nitrogen mineralization of soil organic layer as affected by changed seasonal freeze–thaw pattern, although the increasing studies have demonstrated that winter warming might give strong effects on the litter decomposition and microbial activity in the subalpine/alpine forest regions. Therefore, a method of intact soil core incubation in combination with natural environmental gradient was employed by transferring forest soils from 3582 m (A₁) of altitude to 3298 m (A₂) of altitude and 3023 m (A₃) of altitude in the subalpine/alpine forests of western Sichuan, respectively. The amounts and rates of net nitrogen mineralization in soil organic layer were measured. The incubation period included the growing season and the freeze–thaw season from May 24, 2010 to April 19, 2011. The results suggested that significant net nitrogen mineralization was only observed in soil organic layer at low altitude (A₃) during the whole incubation period. Forest soils at higher altitudes (A₁ and A₂) showed obvious soil nitrogen immobilization. In comparison with the growing season which showed remarkable nitrogen immobilization characteristic, the freeze–thaw season showed obvious nitrogen mineralization at lower altitudes (A₂ and A₃). In contrast, the nitrogen immobilization amounts at high altitude (A₁) in freeze–thaw period were less than those in the growing season. Besides, the maximum of net nitrogen mineralization amounts and rates at high altitude (A₁) in soil organic layer mainly occurred in the late stage of growing season and the onset of freezing, soil nitrogen mineralization at the middle altitude (A₂) mainly occurred in the onset of freezing and the deep freezing period, while the highest amount and rate of net nitrogen mineralization at low altitude (A₃) occurred in the early stage of thawing and the late stage of growing season. Furthermore, the amount and rate of soil net nitrogen mineralization during the freeze–thaw season were increasing with the decrease of altitude, which correlated with soil freeze–thaw cycle and freezing process at different altitudes. These results indicated that increasing soil temperature in the future could not only significantly enhance soil nitrogen mineralization in the freeze–thaw season, but also improve soil nitrogen mineralization by increasing freeze–thaw cycle times and shortening freeze–thaw period. However, the processes were significantly influenced by soil micro-environment of subalpine/alpine forest regions.     

亚高山/高山森林土壤有机层氨氧化细菌和氨氧化古菌丰度特征

为了解季节性冻融作用对川西亚高山/高山地区土壤氨氧化微生物群落的影响,采用qPCR技术,以氨单加氧酶基因的α亚基(amoA)为标记,在生长阶段、冻结阶段、融化阶段中的9个关键时期调查了该地区不同森林群落：岷江冷杉(Abies faxoniana)原始林(PF)、岷江冷杉(A. faxoniana)和红桦(Betula albosinensis)混交林(MF)、岷江冷杉次生林(SF)土壤有机层的氨氧化细菌(ammonia-oxidizing bacteria, AOB)和氨氧化古菌(ammonia-oxidizing archaea, AOA)丰度的特征。结果表明,三个森林群落土壤有机层中都具有相当数量的氨氧化细菌和古菌,均表现出从生长阶段至冻结阶段显著降低,在冻结阶段最低,但冻结阶段后显著增加,在融化阶段为全年最高的趋势。土壤氨氧化微生物类群结构(AOA/AOB)受负积温影响明显。冻结后期三个森林群落土壤负积温最大时,AOA数量明显高于AOB,但其他关键时期土壤氨氧化微生物类群结构与群落类型密切相关。高海拔的PF群落土壤有机层表现为AOA>AOB(冻结初期除外),低海拔的SF群落中表现为AOB>AOA(冻结后期除外),而MF群落则仅在融冻期和生长季节末期表现为AOB>AOA。这些结果为认识亚高山/高山森林及其相似区域的生态过程提供了一定的科学依据。     

川西亚高山/高山森林土壤氧化还原酶活性及其对季节性冻融的响应

川西亚高山/高山森林土壤通常具有明显的季节性冻融特征。为深入了解川西亚高山/高山森林冬季土壤生态过程,于2008年11月-2009年10月,在土壤初冻期、冻结期和融化期及生长季节,研究了不同海拔(3582 m、3292 m和3023 m)岷江冷杉林的土壤氧化还原酶活性及其对土壤冻融的响应。土壤冻结时间和冻融循环次数随海拔的增加而增加。冻融格局显著影响了土壤氧化还原酶活性,但不同土壤酶在不同海拔表现出明显差异。土壤过氧化物酶和脱氢酶活性受初冻期冻融循环和温度降低影响显著下降,而过氧化氢酶活性明显上升。3种土壤氧化还原酶活性在土壤温度相对稳定的冻结期变化不显著,但在融化期随着土壤温度急剧增加经历一个明显的活性高峰后快速降低,且冻结时间最长和冻融循环次数最多的3582 m变化更为显著。此外,海拔和土层的交互作用显著影响了过氧化物物活性,但对脱氢酶和过氧化氢酶活性不显著。脱氢酶活性与土壤温度极显著相关,但过氧化物酶和过氧化氢酶活性与土壤温度的相关性随海拔差异而不同。这些结果表明川西亚高山/高山森林冬季土壤氧化还原酶仍然具有较高的活性,但受到季节性冻融及其变化的显著影响。     

季节性冻结初期川西亚高山/高山森林土壤细菌多样性

高山/亚高山显著的季节性冻结过程可能对土壤细菌多样性产生重要影响。为了解季节性冻结初期土壤完全冻结前后川西亚高山/高山森林群落土壤细菌多样性变化特征,于2008年11月5日(土壤冻结前期)—11月25日(土壤完全冻结期)期间,采用PCR-DGGE技术同步研究了原始冷杉(Abies faxoniana)林(PF)、针阔混交林(MF)和次生冷杉林(SF)的土壤细菌群落多样性变化特征。土壤完全冻结后,3个森林群落仍然具有较高的土壤细菌多样性。3个森林的土壤细菌类群总数在土壤冻结前表现为MFSFPF,但在土壤完全冻结后表现为PFMFSF。土壤冻结明显降低了土壤细菌多样性,但提高了土壤细菌群落的优势度。冻结作用对土壤细菌群落的影响随着土壤深度增加而降低,随着海拔升高而降低。这些结果表明季节性冻结过程对亚高山/高山森林土壤细菌多样性有着显著的影响,这对深入认识冬季土壤生态过程具有重要意义。     

高山森林凋落物分解过程中的微生物生物量动态

凋落物分解过程中的微生物生物量动态对于深入了解森林凋落物分解机理具有重要意义。为了解高山森林典型树种凋落物分解过程中的微生物生物量特征,采用凋落物分解袋法,研究了土壤冻结期(3月)、融冻期(4月-5月)、生长季节(5-10月)和冻结初期(11月)红桦(Betula albosinensi)、岷江冷杉(Abies faxoniana)和粗枝云杉(Picea asperata)凋落物分解过程的微生物生物量C(MBC)、微生物生物量N(MBN)和微生物生物量P(MBP)动态。四个关键时期,凋落物的MBC、MBN以生长季节最高,但非生长季节的三个关键时期也检测出较高的MBC、MBN。在融冻期结束后,三类凋落物分解过程中MBC和MBN均出现爆发性增长。然而,MBP在生长季节中期(8月)、完全冻结期(3月)和冻结初期(11月)均相对较低,但在融冻期和生长季节后期(9月)相对较高。另外,红桦凋落物的MBC、MBN和MBP含量均高于岷江冷杉和粗枝云杉凋落物(除4月粗枝云杉凋落物MBP异常升高外)。这些结果为更加清晰地认识高寒森林凋落物分解过程及机理,以及进一步理解陆地生态系统结构和功能提供了一定基础数据。     

Seasonal dynamics of soil fauna in the subalpine and alpine forests of west Sichuan at different altitudes

The climate (especially temperature) often plays an important role in the structure, function as well as composition of soil organisms in different latitudes and altitudes. As one of the essential components of soil ecosystem, soil faunal community not only lays their roles as soil engineer in material cycling and energy flow, but also acts as the sensitive bio-indicator to environmental change. However, little information has been available on the responses of soil faunal community to the changed environment at different altitudes and seasons. In order to understand the seasonal dynamics of soil faunal diversity under different forests with varying altitudes, three fir (Abies faxoniana) forests were selected covering a 600 m vertical transition zone. The primary fir forest at 3600 m (A1) of altitude, mixed fir and birch forest at 3300 m (A2) of altitude, and secondary fir forest at 3000 m (A3) of altitude are representative forests in the subalpine and alpine region of west Sichuan. A 2 years study was conducted in the three subalpine and alpine forests from May in 2009 until October in 2010. Soil samples were collected in both the soil organic layer and mineral soil layer. Soil macro-fauna were picked up by hand in the fields. Meso/micro-fauna and damp living fauna were separated and collected from the soil samples by Baermann and Tullgren methods in laboratory, respectively. A total of 74,827 individuals were collected in the 2 years, belonging to seven phyla, 16 classes, 31 orders and 125 families by preliminary identification. Similar dominant groups were detected in different forests at different altitudes, consisting of Spirostreptida, Formicidae, Staphylinidae, Hesperinidae, Onychiuridae, Isotomidae, Oribatuloidae, Alicoragiidae, Secernentea, and Adenophorea. In contrast, the ordinary species of macro-fauna and the ratios of Acarina to Collembolan were obviously different. For instance, the ordinary species were dominated by Cydmaenidae and Mycetophilidae at the A1, Scaphidiidae and Helicinidae at the A2, and Lumbricida and Agelenidae at the A3, respectively. Both the individual density and the number of soil faunal groups were significantly higher in soil organic layer than those in mineral soil layer. The density and group of macro-, meso- and micro-fauna in different forests showed the order as A2 > A1 > A3, but the density of damp living fauna showed the order as A1 > A2 > A3. The functional groups of macro-fauna were mainly dominated by saprozoic. The highest density and group of macro-fauna was observed in August, while the highest value of meso/micro-fauna was detected in October. In addition, the Jacard similarity indices showed that the composition and structure of soil fauna were similar in the different forests varied with altitudes, but the Shannon–Wiener indices were significantly different. The highest values of Shannon–Wiener indices were observed in October at both the A1 and A3, and in August at the A2. The results suggested that soil faunal community kept a high diversity in the subalpine and alpine forests of west Sichuan, and their structures were significantly affected by the variation of altitudes, which provided important scientific evidences for understanding the ecological processes in the subalpine and alpine coniferous forests.     

Annual ecosystem respiration is resistant to changes in freeze–thaw periods in semi‐arid permafrost

Warming in cold regions alters freezing and thawing (F–T) of soil in winter, exposing soil organic carbon to decomposition. Carbon‐rich permafrost is expected to release more CO₂ to the atmosphere through ecosystem respiration (Re) under future climate scenarios. However, the mechanisms of the responses of freeze – thaw periods to climate change and their coupling with Re in situ are poorly understood. Here, using 2 years of continuous data, we test how changes in F–T events relate to annual Re under four warming levels and precipitation addition in a semi‐arid grassland with discontinuous alpine permafrost. Warming shortened the entire F–T period because the frozen period shortened more than the extended freezing period. It decreased total Re during the F–T period mainly due to decrease in mean Re rate. However, warming did not alter annual Re because of reduced soil water content and the small contribution of total Re during the F–T period to annual Re. Although there were no effects of precipitation addition alone or interactions with warming on F–T events, precipitation addition increased total Re during the F–T period and the whole year. This decoupling between changes in soil freeze – thaw events and annual Re could result from their different driving factors. Our results suggest that annual Re could be mainly determined by soil water content rather than by change in freeze – thaw periods induced by warming in semi‐arid alpine permafrost.     

冻融末期川西亚高山/高山森林土壤水解酶活性特征

冻融末期是连接冬季与生长季节的关键时期,期间强烈的温度变化可能深刻影响土壤生态过程.为了解冻融末期川西亚高山/高山森林土壤的生化过程,2009年3月5日-4月25日土壤融化期间,研究了该区典型冷杉原始林、针阔混交林和冷杉次生林土壤转化酶、脲酶和磷酸酶(中性、酸性和碱性磷酸酶)活性特征.结果表明:在土壤完全冻结期,3个森林群落各水解酶的活性仍相对较高.在土壤融化前期,随土壤温度升高,除中性磷酸酶外,其他水解酶活性均出现了一个爆发性增高然后迅速降低的过程.随后,除转化酶外,其他水解酶活性均随土壤温度的升高而持续增高.相对于矿质土壤层,冻融末期土壤有机层的水解酶活性更高,对土壤温度变化的响应更加明显.     

Contribution of Soil Fauna to Foliar Litter-Mass Loss in Winter in an Ecotone between Dry Valley and Montane Forest in the Upper Reaches of the Minjiang River

Litter decomposition during winter can provide essential nutrients for plant growth in the subsequent growing season, which plays important role in preventing the expansion of dry areas and maintaining the stability of ecotone ecosystems. However, limited information is currently available on the contributions of soil fauna to litter decomposition during winter in such ecosystems. Therefore, a field experiment that included litterbags with two different mesh sizes (0.04 mm and 3 mm) was conducted to investigate the contribution of soil fauna to the loss of foliar litter mass in winter from November 2013 to April 2014 along the upper reaches of the Minjiang River. Two litter types of the dominant species were selected in each ecosystem: cypress (Cupressus chengiana) and oak (Quercus baronii) in ecotone; cypress (Cupressus chengiana) and clovershrub (Campylotropis macrocarpa) in dry valley; and fir (Abies faxoniana) and birch (Betula albosinensis) in montane forest. Over one winter incubation, foliar litter lost 6.0%-16.1%, 11.4%-26.0%, and 6.4%-8.5% of initial mass in the ecotone, dry valley and montane forest, respectively. Soil fauna showed obvious contributions to the loss of foliar litter mass in all of the ecosystems. The highest contribution (48.5%-56.8%) was observed in the ecotone, and the lowest contribution (0.4%-25.8%) was observed in the montane forest. Compared with other winter periods, thawing period exhibited higher soil fauna contributions to litter mass loss in ecotone and dry valley, but both thawing period and freezing period displayed higher soil fauna contributions in montane forest. Statistical analysis demonstrated that the contribution of soil fauna was significantly correlated with temperature and soil moisture during the winter-long incubation. These results suggest that temperature might be the primary control factor in foliar litter decomposition, but more active soil fauna in the ecotone could contribute more in litter decomposition and its related ecological processes in this region.     

川西亚高山森林林窗不同时期土壤转化酶和脲酶活性的特征

为了解川西亚高山森林林窗对不同时期土壤生态过程的影响,于2012年6月—2013年5月期间,根据温度动态过程,对比研究了生长季节(土壤完全融化期、生长季节前期和生长季节后期)与非生长季节(冻结初期、深冻期和融化期)川西亚高山粗枝云杉(Picea asperata)人工林林窗中心、林缘和林下土壤有机层和矿质土壤层转化酶和脲酶活性变化过程。结果表明:林窗不同区域中,土壤有机层转化酶活性均高于矿质土壤层;在生长季节,土壤有机层和矿质土转化酶活性表现为:林窗中心林下林缘,而脲酶活性表现为:林窗中心林缘林下。冻结初期和深冻期林窗中心土壤转化酶活性均高于林缘和林下,而在融化期林下转化酶活性高于林窗中心和林缘;冻结初期和融化期林下土壤脲酶活性显著高于林窗中心和林缘,而在深冻期林窗不同区域土壤脲酶活性没有显著差异。林窗不同区域在不同时期对土壤转化酶和脲酶活性的响应有着深刻影响。     

海拔对高山峡谷区土壤微生物生物量和酶活性的影响

为了解土壤微生物生物量和酶活性随海拔的变化特征,以川西海拔1563 m到3994 m的高山峡谷区的干旱河谷、干旱河谷-山地森林交错带、亚高山针叶林、高山森林和高山草甸土壤为研究对象,采用原位培养法研究了5种不同海拔生态系统中有机层(0～15 cm)和矿质层(15～30 cm)土壤微生物生物量碳氮、土壤蔗糖酶、脲酶及酸性磷酸酶活性的变化.结果表明:有机层土壤中微生物生物量碳氮和3种土壤酶活性呈现出先增加后减少再增加的变化特征,从2158 m开始不断增加,到3028 m左右达到峰值后减少,在3593 m出现最小值后,逆势增加直到3994 m后再次减少;矿质层土壤的微生物生物量碳氮和3种土壤酶活性表现为亚高山针叶林(3028 m)>高山草甸(3994 m)>干旱河谷-山地森林交错带(2158 m)>高山森林(3593 m)>干旱河谷(1563 m).各海拔梯度土壤有机层的微生物生物量和酶活性显著高于矿质层.高山峡谷区土壤微生物生物量与土壤酶活性呈极显著正相关.土壤微生物生物量和土壤酶与土壤含水量、有机碳和全氮呈极显著正相关,土壤蔗糖酶与土壤全磷含量呈极显著正相关,土壤酸性磷酸酶与土壤全磷和土壤温度呈极显著正相关.可见,高山峡谷区海拔变化引起的植被和其他环境因子的变化显著影响了土壤生化特性.     

Soil Fauna Affects Dissolved Carbon and Nitrogen in Foliar Litter in Alpine Forest and Alpine Meadow

Dissolved organic carbon (DOC) and total dissolved nitrogen (TDN) are generally considered important active biogeochemical pools of total carbon and nitrogen. Many studies have documented the contributions of soil fauna to litter decomposition, but the effects of the soil fauna on labile substances (i.e., DOC and TDN) in litter during early decomposition are not completely clear. Therefore, a field litterbag experiment was carried out from 13th November 2013 to 23rd October 2014 in an alpine forest and an alpine meadow located on the eastern Tibetan Plateau. Litterbags with different mesh sizes were used to provide access to or prohibit the access of the soil fauna, and the concentrations of DOC and TDN in the foliar litter were measured during the winter (the onset of freezing, deep freezing and thawing stage) and the growing season (early and late). After one year of field incubation, the concentration of DOC in the litter significantly decreased, whereas the TDN concentration in the litter increased. Similar dynamic patterns were detected under the effects of the soil fauna on both DOC and TDN in the litter between the alpine forest and the alpine meadow. The soil fauna showed greater positive effects on decreasing DOC concentration in the litter in the winter than in the growing season. In contrast, the dynamics of TND in the litter were related to seasonal changes in environmental factors, rather than the soil fauna. In addition, the soil fauna promoted a decrease in litter DOC/TDN ratio in both the alpine forest and the alpine meadow throughout the first year of decomposition, except for in the late growing season. These results suggest that the soil fauna can promote decreases in DOC and TDN concentrations in litter, contributing to early litter decomposition in these cold biomes.     

亚高山森林林窗大小对凋落叶木质素降解的影响

木质素降解是认识高寒森林凋落物分解过程的关键环节,可能受到林窗大小及其在不同季节水热环境的影响。采用分解袋法,研究了川西亚高山森林不同面积大小林窗下红桦(Betula albo-sinensis)和岷江冷杉(Abies faxoniana)凋落叶在初冻期、深冻期、融化期、生长季节初期、生长季节中期和生长季节后期的木质素分解动态特征。研究结果表明,采样时间和林窗面积大小对两种凋落叶的木质素降解均有显著影响。经历1a分解,红桦凋落叶的木质素降解了21.53%—27.65%,而岷江冷杉凋落叶的木质素富集了7.95%—19.40%。较大林窗促进了冬季岷江冷杉凋落叶和生长季节红桦凋落叶木质素的降解,抑制了冬季红桦凋落叶木质素的降解;而生长季节岷江冷杉凋落叶木质素富集速率则为林下大林窗中林窗小林窗。逐步回归分析表明,凋落叶木质素的降解过程在冬季主要受到负积温和土壤冻融循环次数的影响(木质素结构的物理破碎),而在生长季节则主要受到平均温度和正积温的影响(木质素的生物降解)。可见,川西亚高山森林木质素降解受林窗格局变化的显著影响,且林窗大小对凋落叶木质素降解的影响与物种和分解时期有关。     

川西亚高山不同森林生态系统碳氮储量及其分配格局

森林采伐和恢复是影响森林碳氮储量的重要因素。以川西亚高山岷江冷杉原始林、粗枝云杉阔叶林、天然次生林和粗枝云杉人工林为研究对象,采用样地调查和生物量实测的方法,研究了不同森林生态系统各组分碳、氮储量及其分配特征。结果表明岷江冷杉原始林、粗枝云杉阔叶林、天然次生林和粗枝云杉人工林生态系统碳储量分别为611.18、252.31、363.07 tC/hm~2和239.06 tC/hm~2;氮储量分别为16.44、12.11、15.48 tN/hm~2和8.92 tN/hm~2。恢复林分与原始林碳储量在土壤—植被的分配格局发生了变化,而氮储量未发生变化。岷江冷杉原始林以植被碳储量为主,恢复林分以土壤为主,氮储量均以土壤为主。乔木层碳储量分别占生态系统总储量的56.65%、17.63%、13.57%和22.05%,土壤层(0—80 cm)分别占32.03%、69.87%、76.20%和72.12%;土壤层氮储量占生态系统总储量的76.80%—92.58%。植物残体碳氮储量分别占生态系统总储量的4.40%—9.83%和2.94%—7.08%,林下植被所占比例最小。空间格局上,岷江冷杉原始林植被部分具有较高的碳储量,应进行保护。3种恢复林分具有较高的碳汇潜力,且地上/地下碳储量较低,表明其碳汇潜力尤其表现在地上部分。天然次生林利于土壤有机碳的积累,而人工林乔木层碳储量较高。     

Impact of snowpack decrease on net nitrogen mineralization and nitrification in forest soil of northern Japan

Winter climate change is an important environmental driver that alters the biogeochemical processes of forest soils. The decrease in snowpack amplifies soil freeze–thaw cycles and decreases the snowmelt water supply to soil. This study examined how snow decrease affects nitrogen (N) mineralization and nitrification in forest soil in northern Japan by conducting an in situ experimental snowpack manipulation experiment and a laboratory incubation of soil with different moisture, temperature and freeze–thaw magnitudes. For the incubation studies, surface mineral soil (0–10 cm) was collected from a cool-temperate natural mixed forest and incubated using the resin core method during the winter. In the field, there were two treatments: 50 and 100 % snow removal and control plots. The increase in the soil freeze–thaw cycle increased net N mineralization and marginally decreased the net nitrification in soil. The dissolved organic carbon (DOC) and DOC/DON ratio in soil increased with the decrease in snowpack especially during the snow melt period. These results suggested that the change in substrate quality by the increase in freeze–thaw cycles caused the significant enhancement of microbial ammonium production in soil. The lower soil moisture and higher gross immobilization of inorganic N by soil microbes may be maintaining the slow net nitrification and low nitrate leaching in freeze–thaw cycles with less snowpack. The results indicate that winter climate change would strongly impact N biogeochemistry through the increase in ammonium availability in soil for plants and microbes, whereas it would be unlikely that nitrate loss from surface soil would be enhanced.     

川西亚高山不同森林类型土壤呼吸和总硝化速率的季节动态

川西亚高山原始林及其采伐后通过不同恢复措施形成的不同类型森林土壤呼吸和总硝化速率的对比分析及其耦合关系的研究相对匮乏。采用气压过程分离系统(Ba PS)技术研究了川西亚高山岷江冷杉原始林及其砍伐后恢复的粗枝云杉阔叶林、红桦-岷江冷杉天然次生林和粗枝云杉人工林土壤呼吸和总硝化速率的季节动态及其影响因素。结果表明:生长季内平均土壤呼吸速率和总硝化速率分别以粗枝云杉阔叶林和粗枝云杉人工林较高,均以岷江冷杉原始林较低。土壤呼吸和总硝化速率在生长季内具有明显的季节动态,呈以7月份最高的单峰趋势。土壤呼吸和总硝化速率与土壤温度显著相关,而与土壤水分相关性不显著,表明土壤温度是调控呼吸和总硝化作用季节动态的主要因子。土壤呼吸的温度敏感性(Q_(10))介于2.59—4.71,以岷江冷杉原始林最高,表明高海拔的岷江冷杉原始林可能更易受到气候变化的影响。林型间土壤呼吸和总硝化速率主要受凋落物量、p H和有机质的影响。不同林型间土壤呼吸和总硝化速率显著正相关,表明土壤呼吸和总硝化速率存在耦合关系。     

高山森林林窗对苔藓及土壤微量元素含量的影响

苔藓植物和土壤在森林元素循环过程中具有重要作用,其元素含量特征可能受林窗和生长基质的影响,但有关不同林窗位置对苔藓和土壤微量元素含量影响的研究尚未见报道。为理解林窗更新对森林苔藓和土壤微量元素含量及分布特征的影响,于2016年10月,调查研究了在川西高山岷江冷杉(Abies faxoniana)原始林林下、林缘、林窗和旷地中地表苔藓和石生苔藓Na、Zn、Mg、Mn、Ca、Fe元素含量以及对应土壤有机层和矿质土壤层的元素含量。结果表明:川西高山森林地表苔藓与石生苔藓的Na、Zn、Mg、Fe、Ca含量差异不显著,地表苔藓的Mn元素含量显著高于石生苔藓;土壤有机层的Zn、Mg、Mn和Ca元素含量显著高于矿质土壤层,但Fe元素含量则相反,Na元素含量差异不显著。林窗位置对地表苔藓和石生苔藓Na、Zn、Ca和Fe元素含量具有相似的影响,均以林窗和旷地相对较高;石生苔藓与地表苔藓的Mn含量对林窗的响应存在差异,石生苔藓的Mn含量以林下最高,而地表苔藓则以林窗中心最高。但是,林窗对苔藓植物Mg元素含量的影响不显著。森林林窗位置对土壤有机层和矿质土壤层微量元素含量具有相似的影响。Na元素含量以旷地土壤最高,而Zn、Mn、Ca和Fe含量以林窗中心的土壤最高;除元素Na,所有微量元素均以林缘的土壤最低。此外,地表苔藓的Na、Zn、Mn和Ca含量显著高于土壤,而土壤中的Fe含量显著高于苔藓植物;苔藓中Ca和Mn元素含量与土壤的Ca和Mn元素含量呈显著正相关。可见,高山森林林窗更新过程在不同程度上影响了森林地表苔藓和土壤对微量元素的吸存特征,为进一步了解林窗和苔藓植物在高山森林生态系统物质循环中的作用提供了新的角度。     

川西高山林线交错带土壤动物对岷江冷杉和高山杜鹃凋落物分解的贡献

土壤动物是调控凋落物分解的重要生物因素.为了探究川西高山林线交错带土壤动物对两个优势物种岷江冷杉和高山杜鹃凋落物分解的贡献,在3个海拔梯度(针叶林-林线-高山草甸)采用凋落物分解袋试验,通过不同孔径的网袋(0.04 mm,基本排除土壤动物;3 mm,允许土壤动物通过),研究了分解554 d(2013年5月—2014年11月)土壤动物对凋落物的影响.结果表明: 在整个林线交错带上,岷江冷杉的分解速率(k)为0.209～0.243,高山杜鹃的k为0.173～0.189,岷江冷杉的k大于高山杜鹃.土壤动物的参与显著加速了两种凋落叶分解,同时土壤动物对两种凋落物分解的作用和贡献随海拔升高而降低.自针叶林、高山林线至高山草甸,土壤动物对岷江冷杉分解的质量损失率为15.2%、13.2%、9.8%,对高山杜鹃分解的质量损失率为20.1%、17.5%、12.4%;土壤动物对岷江冷杉分解的平均日贡献率为0.17%、0.13%、0.12%,对高山杜鹃分解的平均日贡献率为0.26%、0.25%、0.23%,土壤动物对高山杜鹃的分解影响相对较大.海拔、凋落物自身性质及其交互作用对土壤动物作用下凋落物的质量损失率和贡献率均表现出显著影响.土壤动物的作用于岷江冷杉和高山杜鹃分解的平均日贡献率在当年生长季(0.25%和0.44%)和次年生长季(0.10%和0.19%)均高于雪被期(0.07%和0.12%).回归分析表明,环境因子(日平均气温、冻融循环次数以及雪被厚度)可以解释土壤动物作用于岷江冷杉和高山杜鹃质量损失率的42.7%和50.9%,贡献率的43.2%和55.6%,这对了解土壤动物在凋落物分解中的作用和深入认识高山生态系统物质循环具有重要意义.     

季节性冻融期间土壤动物对高山草甸两种凋落叶失重的贡献

季节性冻融期间高山草甸凋落叶的分解可为生长季节植物生长提供必要的养分,对于维持生态系统物质循环和养分平衡具有重要作用。然而,土壤动物对凋落叶分解是否具有明显的贡献仍然缺乏一致认识。因此,以高山草甸代表性植物黄花亚菊(Ajania nubigena)和黑褐苔草(Carex atrofusca)凋落叶为研究对象,采用不同孔径凋落叶袋排除土壤动物的方法,研究冬季不同冻融时期(冻结前期、冻结期和融化期)土壤动物对凋落叶失重的贡献。整个季节性冻融期间土壤动物对黄花亚菊和黑褐苔草两种凋落叶失重率的作用分别为12.07%和4.03%,总贡献率分别为46.39%和24.14%。土壤动物对两种凋落叶失重率的作用均在融化期最大,而土壤动物对黄花亚菊凋落叶失重率的作用在冻结初期最小,土壤动物对黑褐苔草凋落叶失重率的作用在冻结期最小。整个季节性冻融期,土壤动物对凋落叶失重率的作用和贡献率与正积温和凋落叶初始C、N浓度和C/N比均呈显著的正相关关系。因此,季节性冻融期间土壤动物对高山草甸凋落叶分解具有明显的贡献,但这些过程受冻融格局和凋落叶初始质量的调控。     

Correction to: The biogeochemical consequences of litter transformation by insect herbivory in the Subarctic: a microcosm simulation experiment

Northern forest ecosystems are projected to experience warmer growing seasons and increased soil freeze–thaw cycles in winter over the next century. Past studies show that warmer soils in the growing season enhance nitrogen uptake by plants, while soil freezing in winter reduces plant uptake and ecosystem retention of nitrogen, yet the combined effects of these changes on plant root capacity to take up nitrogen are unknown. We conducted a 2-year (2014–2015) experiment at Hubbard Brook Experimental Forest in New Hampshire, USA to characterize the response of root damage, nitrogen uptake capacity, and soil solution nitrogen to growing season warming combined with soil freeze–thaw cycles in winter. Winter freeze–thaw cycles damaged roots, reduced nitrogen uptake capacity by 42%, and increased soil solution ammonium in the early growing season (May–June). During the peak growing season (July), root nitrogen uptake capacity was reduced 40% by warming alone and 49% by warming combined with freeze–thaw cycles. These results indicate the projected combination of colder soils in winter and warmer soils in the snow-free season will alter root function by reducing root nitrogen uptake capacity and lead to transient increases of nitrogen in soil solution during the early growing season, with the potential to alter root competition for soil nitrogen and seasonal patterns of soil nitrogen availability. We conclude that considering interactive effects of changes in climate during winter and the snow-free season is essential for accurate determination of the response of nitrogen cycling in the northern hardwood forest to climate change.