互花米草盐沼土壤有机碳库组分及结构特征

在江苏盐城互花米草(Spartina alterniflora)盐沼建立以下样地:光滩(Mudflat)、互花米草建群1a(S.alterniflora flat 2011)、5a(S.alterniflora flat 2007)、12a(S.alterniflora flat 2000)、23a(S.alterniflora flat 1989)以及碱蓬(Suaeda salsa flat 1989),采集表层土壤样品,分析土壤中的活性有机碳(可溶性有机碳、微生物量碳)特征,并利用核磁共振波谱法测定土壤总有机碳的结构图谱,研究互花米草盐沼土壤有机碳库组分及结构特征。结果表明:(1)互花米草建群后,盐沼表层土壤有机碳含量显著增加(P0.05),在0.82—7.6 g/kg之间,各样地表层土壤有机碳含量为:互花米草滩(5.57 g/kg)碱蓬滩(2.4 g/kg)光滩(1.05 g/kg);可溶性有机碳含量为:互花米草滩(36.08 mg/kg)碱蓬滩(17.43 mg/kg)光滩(6.92 mg/kg);微生物量碳含量为:互花米草滩(52.51 mg/kg)碱蓬滩(18.27 mg/kg)光滩(13.56 mg/kg)。互花米草建群后,土壤中活性碳库含量显著增加(P0.05)。(2)土壤有机碳结构以烷氧碳和芳香碳为主,其中芳香碳的平均比例(35.85%)最高,其次为烷氧碳(32.83%)和羧基碳(20.62%),烷基碳的平均比例(10.36%)最低,其中建群5a的互花米草样地(SAF2007)土壤芳香碳、烷氧碳、烷基碳含量最高,建群23a的互花米草样地(SAF1989)土壤羧基碳含量最高。(3)互花米草盐沼土壤中烷基碳/烷氧碳为:SAF2007(0.44)SSF1989(0.43)SAF2000(0.28)SAF2011(0.27)SAF1989(0.22);疏水碳/亲水碳为:SAF2007(0.97)SSF1989(0.87)SAF2000(0.85)SAF2011(0.83)SAF1989(0.81)。烷基碳/烷氧碳在建群5a后达到最高值0.44,烷基化程度最高;疏水碳/亲水碳达到最高值0.97,土壤碳库稳定性高于其它样地。     

互花米草生物量变化对盐沼沉积物有机碳的影响

以江苏王港典型互花米草(Spartina alterniflora)盐沼湿地为研究对象,分析光滩及互花米草滩沉积物中有机碳的水平和垂向分布特征,了解互花米草生物量的季节动态变化,探讨二者之间的相互关系,在此基础上研究互花米草生物量分布和季节变化对沉积物中有机碳(TOC)含量的影响。结果表明,互花米草枯落物中的有机碳数量在两个月内衰减了40%,而表层沉积物中TOC含量及其中互花米草来源TOC所占比例的变化,均与互花米草地表枯落物量的季节变化存在两个月的"相位差",这与枯落物快速分解时间大致吻合,说明枯落物是表层沉积物中TOC的重要来源。高达60%的互花米草地下生物量分布在0—20cm深度内,该深度范围内沉积物中TOC含量较高,且TOC主要来源于互花米草。此外,不同深度TOC含量与地下生物量之间存在良好的正相关关系,说明地下生物量是影响沉积物TOC含量的重要因子。研究区互花米草年固碳能力为2274g m-2a-1,盐沼沉积物中TOC埋藏速率达到了470 g m-2a-1,是地表一个重要的碳汇;同时研究区每年向近岸水域输出大量的TOC,是近岸海域生态系统的一个重要碳源。     

互花米草海向入侵对土壤有机碳组分、来源和分布的影响

在江苏盐城新洋港互花米草(Spartina alterniflora)盐沼选择光滩(MF),互花米草入侵la(SAF-1),3a(SAF-3),5a(SAF-5)和12a(SAF-12)样地,采集0-20 cm表层土壤样品,分别测定土壤有机碳(SOC)、顽固性有机碳(RC)和活性有机碳(LC)含量,碳氮比(C/N),土壤有机碳和顽固性有机碳的δ13C值,分析互花米草海向入侵过程中土壤有机碳组分、分布及来源变化.结果表明:(1)SOC、RC、LC含量分别介于0.82-7.60 mg/g,0.58-4.02 mg/g和0.23-3.58 mg/g,由海向陆呈递增趋势:SAF-5＞SAF-12＞SAF-3＞MF＞SAF-1.入侵12 a的SAF-12样地表土SOC储量最大,年均碳汇积累速率为1.8 t/hm2.(2)互花米草来源SOC、RC和LC含量分别为0.06-3.01 mg/g、0.04-1.06 mg/g和0.03-2.00 mg/g,各占5.75％-47.40％、6.77％-31.77％和3.20％-64.40％.互花米草来源SOC、RC、LC由海向陆均呈递增趋势:SAF-12＞SAF-5＞SAF-3＞ SAF-1＞ MF.(3)互花米草植物来源SOC、RC、LC含量、比例与入侵时间显著正相关(P＜0.01).互花米草入侵对LC的影响较大,对RC的影响较小.(4)随着入侵时间的增长,互花米草来源有机碳的输入显著改变了土壤SOC组分.以上结果表明,短期内互花米草海向入侵能够提高土壤碳汇能力.     

中国盐沼湿地蓝碳碳汇研究进展

滨海蓝碳主要指被红树林、盐沼湿地、海草床等蓝碳生态系统所固定的碳,这部分碳对于减缓气候变暖意义重大。其中盐沼湿地作为我国面积最大、分布广泛的滨海湿地,受到人类活动的扰动较多,其碳汇估算的数据缺乏系统性与完整性。通过收集我国的盐沼湿地相关研究与数据,本文对我国盐沼湿地的分布现状及其碳储量、碳埋藏、碳来源、温室气体通量进行了总结,其中我国盐沼湿地的分布面积为(1.27~3.43)×10⁵hm²,总碳储量为(7.5±0.6) Tg,碳埋藏速率为7~955 g C/(m²·a),非CO₂温室气体通量分别为23.6~986 μg CH₄/(m²·h)和1.58~110 μg N₂O/(m²·h)。本文系统梳理了有关我国盐沼湿地碳汇功能的研究,指出我国盐沼湿地碳循环研究仍需加深对机制机理的解析和关键调控因子的探究,以期让盐沼湿地蓝碳为我国的碳达峰与碳中和战略做出更大贡献。     

盐度和淹水对长江口潮滩盐沼植物碳储量的影响

盐生植物是盐沼有机碳储存的"临时库",也是土壤有机碳累积的主要来源,其碳储量大小对盐沼生态系统"碳汇"功能的发挥十分重要。以长江口潮滩本地种芦苇(Phragmites australis)和海三棱藨草(Scirpus mariqueter),及入侵种互花米草(Spartina alterniflora)为研究对象,采用单因素盆栽实验,模拟分析淹水盐度(0、5、10、15、25和35)、淹水深度(0、10、20、40、60cm和80cm)和淹水频率(每天、每3天、每7天、每10天和每15天)变化对各盐生植物地上、地下和总体碳储量大小的影响。研究结果表明,随着淹水盐度增加,芦苇、互花米草和海三棱藨草地上部分与总体碳储量均显著降低。土壤盐度可分别解释其地上部分碳储量变异的47.2%、66.5%和72.7%,与总体碳储量变异的34.7%、45.0%和62.0%。随着淹水深度增加,芦苇地上部分、总体碳储量和海三棱藨草地上部分碳储量均显著降低,其变异的68.6%、28.5%和71.1%可由淹水深度变化(10—80cm)解释。互花米草在80cm淹水深度下仍有较高的地上部分碳储量和总体碳储量。3种盐生植物碳储量对淹水频率变化的响应差异均不显著,所有处理地下部分碳储量差异也未达到显著水平。总体而言,互花米草对水盐胁迫的耐受性要强于本地种芦苇和海三棱藨草。尽管互花米草和芦苇具有相对较高的碳储量,但水盐胁迫对其碳储量的显著抑制作用不容忽视。海三棱藨草碳储量本就不高,输入土壤的有机碳量较为有限,海平面上升及盐水入侵等逆境胁迫会使其对盐沼"碳汇"贡献更加微弱。     

互花米草凋落物有机碳在不同发育阶段盐沼中的分解动态

采用分解袋法,在江苏盐城新洋港互花米草(Spartina alterniflora)盐沼,根据盐沼发育阶段,从海向陆设置以下5个样地:建群3年互花米草盐沼(SAF2011)、5年互花米草盐沼(SAF2009)、11年互花米草盐沼(SAF2003)、25年互花米草盐沼(SAF1989)以及互花米草-碱蓬(Suaeda salsa)盐沼(SAF-SS),研究互花米草凋落物分解过程中总有机碳、惰性有机碳及活性有机碳动态变化。结果表明:(1)各样地凋落物经过1年的分解,其总有机碳、惰性有机碳、活性有机碳残留率逐月下降,惰性有机碳残留率高于活性有机碳残留率,有机碳各组分分解残留率随盐沼建群时间增加而增加;(2)各样地凋落物有机碳分解速率有明显季节变化,总有机碳、惰性有机碳和活性有机碳分解速率分别在8、1和6月最高,总有机碳和活性有机碳分解速率在10和2月较低,惰性有机碳分解速率在12和2月较低;活性有机碳分解速率高于惰性有机碳;凋落物总有机碳和活性有机碳分解速率均随着互花米草盐沼建群时间的增加而下降,建群3年盐沼中凋落物惰性有机碳分解速率最高;(3)凋落物分解后,总有机碳中惰性有机碳比重增高,活性有机碳比重降低,总有机碳中活性有机碳的分解比例大于惰性有机碳;(4)各样地凋落物总有机碳年分解量分别为0.3167、0.2632、0.2608、0.2380和0.2583 g·g-1,建群3年的盐沼中凋落物有机碳分解量高于其余样地。盐沼发育程度对凋落物的分解动态有显著影响。     

闽江口潮滩湿地不同植被带土壤及间隙水中硅的分布特征

以闽江口潮滩湿地为研究对象,由岸及海方向对芦苇、短叶茳芏、互花米草(潮沟内)和互花米草(潮沟外)4种湿地土壤生物硅和土壤间隙水氮硅营养盐含量及其随深度变化的特征进行为期1a的季度观测。结果显示:互花米草(外)、短叶茳芏、芦苇和互花米草(内)带湿地土壤生物硅的年均含量依次降低,分别为14.33、10.40、9.98、7.50 mg/g;互花米草(外)、互花米草(内)、短叶茳芏和芦苇带湿地土壤间隙水活性硅酸盐年均含量依次降低,分别为407、359、344、323μmol/L;湿地各植被带土壤及间隙水含硅量均呈现夏秋季节高于冬春季节的趋势。统计分析表明:间隙水活性硅酸盐与土壤生物硅含量、距潮沟的距离之间的正相关性均比较显著(P0.05),温度对土壤中硅含量的影响也有一定的正相关性,说明湿地植被、温度和潮汐作用是影响闽江口湿地硅分布的重要因素。与土著种对比,互花米草入侵在一定程度上改变了闽江口潮滩湿地土壤硅分布的格局。     

杭州湾滨海湿地土壤有机碳含量及其分布格局

通过研究杭州湾自然潮滩湿地和围垦湿地土壤有机碳含量及其分布格局,揭示湿地植被演替、外来物种入侵和围垦活动对土壤有机碳分布的影响.结果表明:潮滩湿地土壤表层有机碳含量在4.41～8.58 g·kg-1,平均值6.45 g·kg-1.不同植被类型下表层土壤有机碳表现为:芦苇(8.56±0.04 g·kg-1)＞互花米草(7.31±0.08 g·kg-1)＞海三棱蔗草(5.48±0.29 g·kg-1)＞光滩(4.47±0.09 g·kg-1);围垦湿地表层土壤有机碳表现为:20世纪60年代(7.46±0.25 g·kg-1)＞2003年(5.12±0.16 g·kg-1)＞20世纪80年代(1.96±0.46 g·kg-1),即土壤有机碳含量随围垦时间延长表现为先降低后升高的趋势;土壤有机碳在垂直剖面上均表现为由表向下逐渐降低的趋势.潮滩湿地和围垦湿地的土壤有机碳与pH呈显著负相关,与总氮呈显著正相关,表明在土壤中氮主要以有机氮的形态存在.潮滩湿地有机碳与碳氮比相关性不明显,而围垦湿地具有显著正相关性,说明围垦利用对湿地土壤碳氮比产生了一定影响.研究表明,潮滩湿地土壤固碳能力随着植物群落演替逐步增强,而外来入侵种互花米草的大量入侵和扩散将有可能降低潮滩湿地生态系统土壤的储碳功能.围垦引起的土壤水分、颗粒组成的变化以及耕作、土地利用和利用历史是影响围垦湿地土壤有机碳分布的主要原因.     

福建罗源湾潮间带大型底栖动物的次级生产力

根据2009年罗源湾潮间带大型底栖动物调查资料, 应用Brey公式对大型底栖动物的次级生产力、生产量/生物量系数（P/B)及其空间分布进行估算.结果表明： 该区域大型底栖动物的年次级生产力为18.58 g AFDM(无灰干质量)·m^-2·a^-1, P/B系数为0.97; 潮间带上部互花米草盐沼区域的年次级生产力（8.97 g AFDM·m^-2·a^-1）低于下部光滩区域（28.19 g AFDM·m^-2·a^-1）.与20世纪80年代末互花米草生长前相比, 潮间带的年次级生产力约增加4倍.栖息在光滩下部区域的凸壳肌蛤对次级生产力的贡献达66.4%.若除去该蛤拓殖因素, 则盐沼区域的次级生产力显著高于光滩区域, 并且25年来次级生产力的变化较小.互花米草加速了细颗粒物质的沉降, 为蛤类拓殖提供了重要条件; 凸壳肌蛤的摄食活动可增加沉积物中叶绿素a含量.大型底栖动物的次级生产力与沉积物中叶绿素a和有机碳含量显著相关.盐沼植物对潮间带生态系统的影响涉及物理和生物等多种因素     

中国草地生态系统碳库及其变化

准确评估草地生态系统碳库及其年际变化, 对揭示草地在中国陆地生态系统碳循环中的作用以及合理利用有限的草地资源有着极为重要的意义. 虽然中国学者在研究草地碳库及其动态变化方面已开展了很多工作, 但目前仍缺乏对中国草地生态系统碳库及其动态变化特征的全面认识. 通过综述当前中国草地碳循环研究的最新进展, 结合本研究组的工作, 试图全面评价中国草地生态系统碳库(植被生物量碳库和土壤有机碳库)及其动态变化. 结果显示: (1) 不同研究得到的中国草地生物量碳密度(单位面积生物量)存在较大差异, 为215.8~348.1 g C/m², 平均值为 300.2 g C/m². 同样, 对中国草地土壤有机碳密度(单位面积土壤碳库)的估算也存在显著差异, 在8.5~15.1 kg C/m²之间变动, 但考虑到8.5 kg C/m²的估算值是基于近千个土壤剖面的实测数据计算得到, 全国平均水平的土壤碳密度一般不会超过此值. 因此, 若采用目前最广泛使用的草地面积(331×104 km²), 那么中国草地生态系统碳库约为29.1 Pg C(1 Pg=1×10¹⁵ g), 其中96.6%的碳储存于土壤有机质中. (2) 文献报道的近20年中国草地生物量和土壤有机碳库的变化方向和变化量均存在差异. 按照最新的估算, 中国草地生物量和土壤有机碳库在过去20年里没有发生显著变化, 即中国草地生态系统处于中性碳汇状态. (3) 中国草地生物量的时空变异与降水量的变化关系密切. 土壤有机碳库的空间变异主要受与降水量密切相关的土壤水分的影响, 但土壤质地等因素也起一定作用. 此外, 放牧与围封等人类活动将对草地生物量和土壤碳库及其动态变化产生强烈影响.     

潮汐作用和干湿交替对盐沼湿地碳交换的影响机制研究进展

潮汐盐沼湿地具有高的碳积累速率和低的CH_4排放量,是地球上最密集的碳汇之一。同时,气候变暖和海平面上升可能使得盐沼湿地更迅速的捕获和埋藏大气中的CO_2,因此盐沼湿地的"蓝碳"在减缓气候变化方面扮演着重要角色。潮汐盐沼湿地与其他湿地类型最大的区别和最显著的特征是在周期性潮汐作用下出现淹没和暴露,同时伴随盐分表聚与淋洗的干湿交替,可能是控制盐沼湿地碳交换过程和碳收支平衡的关键因素。但是,当前潮汐水动力过程及其周期性干湿交替对盐沼湿地碳交换关键过程和碳汇形成机制的影响尚不十分清楚。另外,以往相关研究通常孤立地考虑垂直方向上CO_2或CH_4交换或横向方向上的可溶性有机碳(DOC)、可溶性无机碳(DIC)、颗粒有机碳(POC)交换通量对盐沼湿地碳平衡进行评估,显然不够准确。因此,为了精确评估和预测盐沼湿地蓝碳的吸存能力,必须系统研究潮汐不同阶段对盐沼湿地碳交换过程的影响;深入分析潮汐作用下盐沼湿地碳交换的微生物机制;关注潮汐水动力作用对盐沼湿地DOC、DIC和POC产生、释放以及向邻近水体输出的影响;阐明潮汐作用对盐沼湿地碳汇形成机制的影响;纳入潮汐水动力过程作为变量,建立盐沼湿地碳循环模型。     

Contribution of unvegetated tidal flats to coastal carbon flux

Unvegetated flats occupy a large area in the intertidal zone. However, compared to vegetated areas, the carbon sequestration of unvegetated tidal flats is rarely quantified, even though these areas are highly threatened by human development and climate change. We determined benthic maximum gross primary production (GPP_m), net primary production (NPP) and total respiration (TR) during emersion on seven tidal flats along a latitudinal gradient (from 22.48°N to 40.60°N) in winter and summer from 2012 to 2016 to assess the spatial and temporal variability of carbon dioxide flux. In winter, these processes decreased by 89%–104% towards higher latitudes. In summer, however, no clear trend was detected across the latitudinal gradient. Quadratic relationships between GPP_m, NPP and TR and sediment temperature can be described along the latitudinal gradient. These curves showed maximum values of GPP_m and NPP when the sediment temperatures reached 28.7 and 26.6°C respectively. TR increased almost linearly from 0 to 45°C. The maximum daily NPP across the latitudinal gradient averaged 0.24 ± 0.28 g C m^?2 day^?1, which was only 10%–20% of the global average of NPP of vegetated coastal habitats. Multiplying with the global area of unvegetated tidal flats, our results suggest that the contribution of NPP on unvegetated tidal flats to the coastal carbon cycle is small (11.04 ± 13.32 Tg C/year). If the land cover of vegetated habitats is continuously degraded to unvegetated tidal flats, the carbon sequestration capacity in the intertidal zone is expected to reduce by at least 13.10 Tg C/year, equivalent to 1% of global carbon emissions from land‐use change.     

Long‐term organic carbon sequestration in tidal marsh sediments is dominated by old‐aged allochthonous inputs in a macrotidal estuary

Tidal marshes are vegetated coastal ecosystems that are often considered as hotspots of atmospheric CO₂ sequestration. Although large amounts of organic carbon (OC) are indeed being deposited on tidal marshes, there is no direct link between high OC deposition rates and high OC sequestration rates due to two main reasons. First, the deposited OC may become rapidly decomposed once it is buried and, second, a significant part of preserved OC may be allochthonous OC that has been sequestered elsewhere. In this study we aimed to identify the mechanisms controlling long‐term OC sequestration in tidal marsh sediments along an estuarine salinity gradient (Scheldt estuary, Belgium and the Netherlands). Analyses of deposited sediments have shown that OC deposited during tidal inundations is up to millennia old. This allochthonous OC is the main component of OC that is effectively preserved in these sediments, as indicated by the low radiocarbon content of buried OC. Furthermore, OC fractionation showed that autochthonous OC is decomposed on a decadal timescale in saltmarsh sediments, while in freshwater marsh sediments locally produced biomass is more efficiently preserved after burial. Our results show that long‐term OC sequestration is decoupled from local biomass production in the studied tidal marsh sediments. This implies that OC sequestration rates are greatly overestimated when they are calculated based on short‐term OC deposition rates, which are controlled by labile autochthonous OC inputs. Moreover, as allochthonous OC is not sequestered in‐situ, it does not contribute to active atmospheric CO₂ sequestration in these ecosystems. A correct assessment of the contribution of allochthonous OC to the total sedimentary OC stock in tidal marsh sediments as well as a correct understanding of the long‐term fate of locally produced OC are both necessary to avoid overestimations of the rate of in‐situ atmospheric CO₂ sequestration in tidal marsh sediments.     

Dynamics of biogenic Si in freshwater tidal marshes: Si regeneration and retention in marsh sediments (Scheldt estuary)

The sequestration and recycling of biogenic silica (BSi) in freshwater tidal marshes was modelled through the combination of short-term year round sediment trap data with a long-term sedimentation model, MARSED. The modelling was implemented through the complete evolution from a young rapidly rising marsh to a marsh with an elevation close to mean high water. BSi in imported suspended matter was higher in summer (10.9 mg BSi g⁻¹ sediment) than winter (7.6 mg BSi g⁻¹ sediment). However, the deposition of BSi on the marsh surface was higher in winter compared to summer, due to the higher sedimentation rates. Deposition of BSi was correlated to the suspended matter deposition. In the old marsh, yearly about 40 g BSi m⁻² was deposited, while in the young marsh deposition could rise up to 300 g m⁻². Young marshes retained up to 85% of the imported biogenic silica. Recycling efficiency (60%) increased drastically for older marshes. The study shows that marshes act as important sinks for BSi along estuaries. The recycling of the imported BSi to DSi in summer and spring is most likely an essential factor in the buffering role of tidal marshes for estuarine DSi concentrations.     

Tidal freshwater forest accretion does not keep pace with sea level rise

Soil properties, accretion, and accumulation were measured in tidal freshwater forests (tidal forests) of the Ogeechee, Altamaha, and Satilla rivers of the South Atlantic (Georgia USA) coast to characterize carbon (C) sequestration and nutrient (nitrogen‐N, phosphorus‐P) accumulation in these understudied, uncommon, and ecologically sensitive wetlands. Carbon sequestration and N and P accumulation also were measured in a tidal forest (South Newport River) that experiences saltwater intrusion to evaluate the effects of sea level rise (SLR) and saltwater intrusion on C, N and P accumulation. Finally, soil accretion and accumulation of tidal forests were compared with tidal fresh, brackish and salt marsh vegetation downstream to gauge how tidal forests may respond to SLR. Soil accretion determined using ¹³⁷C and ²¹⁰Pb averaged 1.3 and 2.2 mm yr^?1, respectively, and was substantially lower than the recent rate of SLR along the Georgia coast (3.0 mm yr^?1). Healthy tidal forest soils sequestered C (49–82 g m^?2 yr^?1), accumulated N (3.2–5.3 g m^?2 yr^?1) and P (0.29–0.56 g m^?2 yr^?1) and trapped mineral sediment (340–650 g m^?2 yr^?1). There was no difference in long‐term accretion, C sequestration, and nutrient accumulation between healthy tidal forests and tidal forests of the South Newport River that experience saltwater intrusion. Accelerated SLR is likely to lead to decline of tidal forests and expansion of oligohaline and brackish marshes where soil accretion exceeds the current rate of SLR. Conversion of tidal forest to marshes will lead to an increase in the delivery of some ecosystem services such as C sequestration and sediment trapping, but at the expense of other services (e.g. denitrification, migratory songbird habitat). As sea level rises in response to global warming, tidal forests and their delivery of ecosystem services face a tenuous future unless they can migrate upriver, and that is unlikely in most areas because of topographic constraints and increasing urbanization of the coastal zone.     

The distribution and interconversion of ammonium and nitrate in the Skallingen salt marsh (Denmark) and their exchange with the adjacent coastal water

The potential nitrogen sources for the primary production in the intertidal area are nitrogen compounds obtained from mineralization in the sediment and the water column, nitrogen fixation, outflow from rivers and groundwater seeping from the mainland. The available inorganic nitrogen in the adjacent coastal waters decreases from 50–80 μmol NO₃ ^-/l and 6–15 μmol NH₄ ⁺/l in early spring to ca one tenth during the growing season. In the sediment of the tidal flats available ammonia and nitrate vary between 50 and 100 μmol/1 pw. In the salt marsh available ammonia increases from 200–300 nmol NH₄ ⁺/g fwt to approximately double the amount, and the available nitrate varies from 100–300 nmol NO₃ ^-/g fwt (250–750 μmol NO₃ ^-/l pw) to ca one third during the growing season. The exchange of NH₄ ⁺, NO₂ ^- and NO₃ ^- across the sediment water interface has been estimated during tidal cycles under light and dark conditions on the tidal flats. The flux of nitrogen was dependent on the flora and fauna as well as the time of the year. The tidal activity, frequency and length of inundation are considered the driving force in a two-way process between salt marshes and adjacent coastal waters. The role of marsh sediment, tidal water and sediments of the tidal flats as sites of accumulation, consumption and remineralization of organic matter is emphasized. The possible exchange of ammonia and nitrate between the salt marsh and the different compartments of the tidal water is discussed.     

Carbon flux between an estuary and the ocean: a case for outwelling

The classical outwelling hypothesis states that small coastal embayments (e.g. estuaries, wetlands) export their excess production to inshore marine waters. In line with this notion, the present study tested whether the Swartkops estuary acts as source or sink for carbon. To this end, concentrations of dissolved inorganic carbon (DIC), dissolved organic carbon (DOC) and particulate organic carbon (POC) were determined hourly during the first monthly spring and neap tides over one year in the tidal waters entering and leaving the estuary. Each sampling session spanned a full tidal cycle, yielding a total of 936 concentration estimates. Carbon fluxes were calculated by integrating concentrations with water flow rates derived from a hydrodynamic model calibrated for each sampling datum. Over the year, exports to marine waters markedly exceeded imports to the estuary for all carbon species: on the basis of total spring tidal drainage area, 1083 g m^–2 of DIC, 103 g m^–2 of DOC, and 123 g m^–2 of POC left the estuary annually. Total carbon export from the estuary to the ocean amounted to 4755 tonnes, of which 83% was in the inorganic form (DIC). Thus, the bulk of carbon moving in the water column is inorganic - yet, DIC seems to be measured only rarely in most flux studies of this nature. Salt marshes cover extensive areas in this estuary and produce some carbon, particularly DOC, but productivity of the local Spartina species is low (P:B=1.1). Consequently, the bulk of carbon exported from the estuary appears to originate from the highly productive macroinvertebrate and the phytoplankton component and not from the salt marsh plants.     

中国滨海盐沼湿地碳收支与碳循环过程研究进展

滨海盐沼湿地由于其较高的初级生产力和较缓慢的有机质降解速率而成为缓解全球变暖的有效蓝色碳汇,近年来引起全球范围内的热切关注.我国滨海盐沼湿地分布较广,国内学者对滨海盐沼湿地碳循环及碳收支研究取得了一定进展,深入研究滨海盐沼湿地碳循环有助于对全球碳循环及全球变化的理解,并为利用滨海湿地进行碳的增汇减排提供科学依据.主要从我国滨海盐沼湿地碳循环主要观测方法、碳收支与碳循环过程及特点、碳库的组成与影响因素、气态碳的输入输出、潮汐作用对其碳收支的影响这5个方面出发,对国内的滨海盐沼湿地碳循环与碳收支的研究进展进行了归纳总结,并对今后的研究方向给出如下建议:(1)加强滨海盐沼湿地土壤碳库在深度上和广度上的研究;(2)标准化滨海盐沼湿地碳储量、碳通量的量化方法和观测技术;(3)在研究尺度上要宏观、微观并重,同时加强长期原位监测湿地碳通量的变化与室内模拟研究;(4)量化在潮汐影响下滨海盐沼湿地碳与邻近生态系统之间的横向交换通量.只有对我国滨海盐沼湿地碳库收支进行更准确的评估和长期的碳库动态变化监测,方可进一步认识我国盐沼湿地对全球气候变化的影响及其反馈作用,这对于预测全球变化及制定湿地碳储备功能的提升策略具有重要的意义.     

Total ecosystem carbon stocks at the marine‐terrestrial interface: Blue carbon of the Pacific Northwest Coast,United States

The coastal ecosystems of temperate North America provide a variety of ecosystem services including high rates of carbon sequestration. Yet, little data exist for the carbon stocks of major tidal wetland types in the Pacific Northwest, United States. We quantified the total ecosystem carbon stocks (TECS) in seagrass, emergent marshes, and forested tidal wetlands, occurring along increasing elevation and decreasing salinity gradients. The TECS included the total aboveground carbon stocks and the entire soil profile (to as deep as 3 m). TECS significantly increased along the elevation and salinity gradients: 217 ± 60 Mg C/ha for seagrass (low elevation/high salinity), 417 ± 70 Mg C/ha for low marsh, 551 ± 47 Mg C/ha for high marsh, and 1,064 ± 38 Mg C/ha for tidal forest (high elevation/low salinity). Soil carbon stocks accounted for >98% of TECS in the seagrass and marsh communities and 78% in the tidal forest. Soils in the 0–100 cm portion of the profile accounted for only 48%–53% of the TECS in seagrasses and marshes and 34% of the TECS in tidal forests. Thus, the commonly applied limit defining TECS to a 100 cm depth would greatly underestimate both carbon stocks and potential greenhouse gas emissions from land‐use conversion. The large carbon stocks coupled with other ecosystem services suggest value in the conservation and restoration of temperate zone tidal wetlands through climate change mitigation strategies. However, the findings suggest that long‐term sea‐level rise effects such as tidal inundation and increased porewater salinity will likely decrease ecosystem carbon stocks in the absence of upslope wetland migration buffer zones.     

氮输入对滨海盐沼湿地碳循环关键过程的影响及机制

滨海盐沼湿地是缓解全球变暖的有效蓝色碳汇, 但是近岸海域富营养化导致的大量氮输入对盐沼湿地稳定性和碳汇功能构成严重威胁。潮汐作用下大量氮输入对盐沼湿地植物光合碳输入、植物-土壤碳分配和土壤碳输出等碳循环关键过程产生深刻影响, 进而影响盐沼湿地碳汇功能评估的准确性。该文从植物光合固碳、植物-土壤系统碳分配、土壤有机碳分解、土壤可溶性有机碳释放、盐沼湿地土壤碳库5个方面综述了氮输入对盐沼湿地碳循环关键过程的影响。在此基础上, 针对当前研究的不足, 提出今后的研究中, 需要进一步探究氮输入对盐沼湿地植物光合固碳及碳分配过程的影响、盐沼湿地土壤有机碳分解的微生物机制、盐沼湿地土壤可溶性有机碳产生和横向流动的影响、以及氮类型对盐沼湿地土壤碳库的影响。以期为揭示氮输入对盐沼湿地碳汇形成过程与机制提供基础资料和理论依据, 为评估未来近岸海域水体富营养化影响下滨海盐沼湿地碳库的潜在变化提供新思路。