古尔班通古特沙漠生物土壤结皮对土壤氮库垂直分布特征的影响

生物土壤结皮在干旱区氮素地球化学循环中具有重要作用,研究不同生物土壤结皮下不同形态氮素含量的变化,解析生物土壤结皮对土壤养分影响过程和范围,有助于进一步理解生物土壤结皮的生态功能。本研究以古尔班通古特沙漠藻-地衣混生结皮和藓类结皮两种生物土壤结皮为研究对象,以裸沙为对照,测定生物土壤结皮层和0—100 cm内8个土层全氮、无机氮、可溶性有机氮、游离态氨基酸氮、微生物生物量氮等氮库含量,和土壤脲酶、硝酸盐还原态酶、亮氨酸氨基肽酶等土壤胞外酶活性。结果表明：1)结皮层各形态氮素含量和各土壤酶活性显著高于其下层土壤,结皮层和结皮下各层土壤氮库整体上表现为藓类结皮>藻-地衣混生结皮>裸沙;土壤氮库各形态氮素含量和土壤酶活性在垂直分布上均呈现先显著下降(0—20 cm)后稳定(20—100 cm)的趋势;在20—30 cm土层,除裸沙的无机氮、铵态氮以及藻-地衣混生结皮的硝态氮外,其余速效氮(无机氮、硝态氮、铵态氮)含量具有增加的特点。2)土壤各氮库含量与全磷、有机碳、电导率、土壤脲酶和亮氨酸氨基肽酶活性呈正相关,与pH、土壤含水率呈负相关。3)利用氮循环相关指标建立土壤氮循环多功能...     

古尔班通古特沙漠生物结皮不同发育阶段中藻类的变化

通过在古尔班通古特沙漠南缘相同的地貌部位,选择裸沙、藻结皮、地衣结皮和苔藓结皮4种不同演替阶段中的生物结皮,研究了藻类的种类组成、优势种和生物量的变化.结果表明:(1)在结皮的不同演替阶段,藻类种类组成不同,其常见物种有一定的差异,如裸沙中藻类常见种是脆杆藻2(Fragilaria sp.2)、威利颤藻(Oscillatoria willei)和奥克席藻(Phormidium okenii),藻结皮的常见种是小聚球藻(Synechococcus parvus)、颗粒常丝藻 (Tychonema granulatum)、韧氏席藻(Phormidium retzli);同时在不同发育阶段亦存在一些特有种.(2)在裸沙发育到成熟生物结皮的过程中,藻类的优势物种也发生相应的变化.裸沙、藻结皮、地衣结皮和苔藓结皮的优势种分别是脆杆藻1(Fragilaria sp.1)、具鞘微鞘藻(Microcoleus vaginatus)、具鞘微鞘藻、眼点伪枝藻(Scytonema ocellatum)或集球藻(Palmellococcus miniatus).(3)藻类生物量在生物结皮不同演替阶段差异极显著(P<0.01),在裸沙中藻类生物量最低,随着生物结皮的逐渐发育,藻类生物量明显升高,地衣结皮最高,约是裸沙的8.3倍,当发育至苔藓结皮时,藻类生物量又有所下降.(4)在裸沙中基本为松散的沙粒,随着生物结皮的演替,丝状种类占明显的优势,尤其是具鞘微鞘藻,另外真菌菌丝和苔藓假根分别在地衣结皮和苔藓结皮中起着重要作用.     

毛乌素沙地生物结皮覆盖区土壤水分收支变化特征

探究半干旱生态系统生物土壤结皮对土壤水文过程的影响,并量化生物结皮覆盖下土壤水分收支状况,可为荒漠地区植被恢复与重建提供理论依据。本研究基于2018—2020年生长季(5—10月)对毛乌素沙地不同类型生物结皮(如藻类和苔藓)覆盖区土壤水分的连续观测,以裸沙为对照,分析了生物结皮对0～40 cm土壤水分收支的影响。结果表明: 与裸沙相比,藻类结皮和苔藓结皮显著降低了降雨对40 cm以下土壤水分的补充,增加了土壤水分的蒸发损失。在相对湿润年份(2018年),裸沙和不同类型生物结皮覆盖土壤的水分支出量(渗漏量+蒸发量)均低于降雨量,土壤水分状况为收入;在相对干旱年份(2019和2020年),藻类结皮和苔藓结皮覆盖土壤的水分支出量高于降雨量,土壤水分产生亏缺,但是裸沙相反。可见,生物结皮导致其下覆0～40 cm土壤水分收支不平衡,在相对干旱年份出现了水分亏缺,这可能驱动该区域植被群落向浅根系植物演替。     

腾格里沙漠东南缘不同类型生物土壤结皮对土壤有机碳矿化的影响

生物土壤结皮(BSCs)是荒漠生态系统的重要组成部分,是该区土壤碳循环及碳平衡的关键影响因素。研究了腾格里沙漠东南缘不同类型生物土壤结皮覆盖下土壤碳矿化过程及其对温度(10℃、25℃和35℃)和水分(土壤含水量10%和25%)变化响应特征,分析了土壤碳矿化过程与土壤理化性质的关系。结果表明:(1)结皮的形成和发育显著影响土壤有机碳矿化过程,藻类、地衣和藓类结皮覆盖的土壤碳矿化速率和CO_2-C累积释放量均显著高于去除结皮的土壤,不同类型BSCs覆盖土壤和去除结皮土壤之间均表现为藓类结皮土壤地衣结皮土壤藻类结皮。(2)含结皮层土壤的平均和最大矿化速率均随温度升高和水分增加而逐渐增大,有结皮覆盖的土壤和去除结皮的土壤对温度和水分变化的响应规律相同。(3)有结皮土壤和去除结皮土壤碳矿化速率的温度敏感性(Q_(10))与结皮类型密切相关,均表现为藓类结皮地衣结皮藻类结皮。结果表明生物土壤结皮由以藻类为主向以藓类为主的演变进一步促进了土壤碳矿化过程,结皮对土壤碳循环的调控作用受水热等环境因子的共同影响。     

古尔班通古特沙漠生物土壤结皮对土壤种子库多样性与分布特征的影响

古尔班通古特沙漠地表广泛分布着生物土壤结皮,研究其覆盖下的土壤种子库,有利于了解生物土壤结皮的生态功能及当地植被更新与恢复的潜力。本文研究了该地区3种生物土壤结皮(藻结皮、地衣结皮、苔藓结皮)对土壤种子库分布特征和多样性的影响。结果表明:在种子库水平分布上,相比于裸沙,生物土壤结皮增加了种子库密度,且不同结皮类型对种子库的影响程度不同。地衣结皮土壤种子库的密度最大(5905±778粒·m~(-3)),其对种子的捕获作用最为明显,其次是苔藓结皮(1138±380粒·m~(-3)),藻结皮与裸沙无显著差异;水平分布上的差异与结皮的发育程度、种子的形态、不同生物土壤结皮空间分布的异质性有关。在垂直分布方面,结皮发育土壤,种子库集中分布在土壤浅层(0~2 cm),这与裸沙种子库的垂直分布特征基本一致,说明结皮的存在并没有显著改变种子库的垂直分布格局。此外,从裸沙到苔藓结皮,土壤种子库和地上植被的相似性不高(0.14~0.29),土壤种子库中的物种多样性和丰富度指数不及地上植被高。该研究区土壤种子库在植被恢复中的潜力可能较小,但相对于裸沙,生物土壤结皮的存在有益于土壤种子库的保持,对荒漠生态系统物种多样性的维持和稳定具有重要意义。     

沙坡头地区生物土壤结皮的固氮活性及其对水热因子的响应

氮是除水分之外影响干旱区生态系统生物活性的关键因子。生物土壤结皮是干旱半干旱荒漠地表景观的重要组成部分, 也是荒漠生态系统氮素的主要贡献者。通过野外调查采样, 利用开顶式生长室, 模拟不同降水梯度, 采用乙炔还原法连续测定了沙坡头地区典型生物土壤结皮(藻类结皮、地衣结皮和藓类结皮)在其主要固氮活跃期(6-10月, 湿润期)的固氮活性, 及其对水热因子的响应特征。结果表明, 试验期三类生物土壤结皮的固氮活性介于2.5 × 10³-6.2 × 10⁴ nmol C₂H₄·m^-2·h^-1之间, 其中藻类结皮的最高(平均达2.8 × 10⁴ nmol C₂H₄·m^-2·h^-1), 地衣结皮的次之(2.4 × 10⁴ nmol C₂H₄ ·m^-2·h^-1), 藓类结皮的最低(1.4 × 10⁴ nmol C₂H₄·m^-2·h^-1), 差异显著(p < 0.001)。在模拟降水3 mm时, 三类结皮均可达到最大固氮速率, 当发生> 3 mm的降水事件时, 它们的固氮速率无显著增加; 不同结皮的固氮活性与温度均呈显著的负相关关系(r_藻类结皮 = -0.711, r_地衣结皮 = -0.732, r_藓类结皮 = -0.755, p < 0.001), 藻类和藓类结皮的固氮活性的最适温度区间为25-30 ℃, 地衣结皮为20-30 ℃。三类结皮之间的这种固氮差异主要归因于结皮组成生物体即隐花植物的差异, 藻类结皮主要成分为大量的蓝细菌和一些绿藻, 地衣结皮也由大量的固氮藻和真菌共生形成, 而藓类结皮的主要组成部分苔藓植物并不具有固氮作用, 其微弱的固氮量是结皮中混生的少量蓝细菌或地衣所致。     

实验室条件下两种生物土壤结皮对荒漠植物种子萌发的影响

生物土壤结皮广泛分布在干旱、半干旱区,深刻影响着土壤表层特性,进而对植物种子散布、萌发和定居产生极大的影响。到目前为止,生物土壤结皮与植物关系的研究很少见到,并且这些有限的研究所得出的结论存在着争议。研究了不同年龄的两种生物土壤结皮（苔藓结皮和藻类结皮）对油蒿（Artemisia ordosica）和雾冰藜（Bassia dasyphylla）种子萌发的影响,同时也研究了这两种结皮在失去活性前后对油蒿、雾冰藜和小画眉草（Eragrostis poaeoides）种子萌发的影响。苔藓和藻类结皮的出现对油蒿和雾冰藜种子的萌发均有显著的促进作用,而结皮年龄对植物种子的萌发没有显著的差异。对于不同的植物种,结皮类型和活性对种子的萌发具有不同的作用。雾冰藜在两种结皮上的萌发有显著的差异而油蒿和小画眉草在两种结皮上的萌发没有显著差异。活藻类显著地增加了三种植物的种子萌发,活苔藓仅增加了油蒿和雾冰藜种子萌发量而对小画眉草种子的萌发没有作用,研究表明,生物土壤结皮对一些植物种子萌发具有明显的促进作用。     

干燥对人工生物土壤结皮固氮酶活性恢复过程的影响

本文研究了不同演替阶段的人工生物土壤结皮其光合和固氮酶活性恢复过程对干燥时长的响应.生物土壤结皮通过人工接种丝状土壤蓝藻诱导形成,并根据藻类和苔藓丰度的不同划分为蓝藻结皮、藻-藓结皮、藓-藻结皮和苔藓结皮等4个演替阶段.经不同时长干燥处理的结皮,复水后测定其光合活性(F_v/F_m)和固氮酶活性(NA)的恢复过程.结果表明,苔藓结皮F_v/F_m的恢复速率与干燥时长呈负相关,但其他演替阶段结皮的F_v/F_m恢复速率几乎不受干燥时长的影响.早期演替阶段的结皮(藻结皮、藻-藓结皮和藓-藻结皮)显示出相同的NA活性恢复模式和不同的NA速率,而苔藓结皮NA活性的恢复较慢.光照条件下,干燥时长不超过8天时,则干燥时间越长,早期演替阶段结皮的NA活性越低,但在此较短的干燥时长范围内,苔藓结皮NA活性的恢复并不受干燥时长的影响;黑暗条件下,不同演替阶段结皮干燥两天后固氮酶活性均较低.相反,较长时间的干燥后(4~6个月),所有结皮均恢复了较高的NA活性.结果表明,不同演替阶段的人工生物土壤结皮其生理活性对干燥有不同的耐受性.     

生物土壤结皮对荒漠土壤种子库和种子萌发的影响

研究了腾格里沙漠东南缘在不同自然条件（风、温度、水分）下,人工固沙植被区（24龄、41龄、50龄）和相邻天然植被区的两种生物土壤结皮对荒漠土壤种子库和种子萌发的影响。结果表明,荒漠土壤种子库在苔藓结皮上的储量显著高于藻类结皮。随着生物土壤结皮的发育,种子萌发量在苔藓结皮上增加,在藻类结皮上减少。生物土壤结皮层的含水量对种子萌发有显著的影响（p〈0.05）,植物种子在湿润处理的生物土壤结皮上的萌发量高于干燥处理的生物土壤结皮上的种子萌发量。生物土壤结皮表层温度和亚表层温度对荒漠植物种子萌发无显著影响（p〉0.05）,但总体而言,对于苔藓结皮,植物种子在较高温度下的萌发量略高于在较低温度下的萌发量,而对于藻类结皮,植物种子在较低温度下的萌发量略高。     

生物土壤结皮的生态功能

荒漠化土壤或多或少地存在着结皮现象 ,导致结皮的产生有物理、化学和生物的因素 ,其中由不同种类的苔藓、地衣、藻类、真菌以及细菌等生物组成成分与其下层很薄的土壤共同形成的一个复合的生物土壤层 ,也就是所谓的生物土壤结皮在荒漠地区最具生态意义。组成生物土壤结皮的藻类、苔藓和地衣是常见的先锋拓殖植物 ,不仅能在严重干旱缺水、营养贫瘠、生境条件恶劣的环境中生长繁殖 ,并且能通过其生活代谢方式影响并改变环境 ,在防风固沙、防止土壤侵蚀、改变水分分布状况等方面更是扮演着重要角色。土壤的生态演替过程 ,往往是组成物种由低等…     

Strategies for restoring the structure and function of lichen‐moss biocrust communities

Biological soil crusts (biocrusts) are crucial components of dryland ecosystems, but they are slow to recover following disturbance. Herein, we evaluated several methods for restoring lichen‐moss biocrusts that included factorial applications of moss fragments in a water‐slurry (1) with and without lichen fragments (to restore biocrust taxonomic structure), (2) with and without clay (to facilitate establishment), and (3) with and without jute ground cloth (to facilitate establishment). Three and four years after inoculation, moss and lichen cover was up to five and eight times higher on jute ground cloth than on bare ground, respectively. Lichen cover was six times higher in plots where lichen fragments were added. Clay amendments did not increase moss or lichen establishment. To understand the effects of biocrust recovery on soil properties, we measured soil inorganic nitrogen, microbial biomass carbon, and soil water availability in restoration and control plots. Restored biocrusts decreased inorganic NH₄‐N availability by 67% when compared to controls 3 years after inoculation, but did not influence the availability of inorganic NO₃‐N, soil water, or microbial biomass carbon. Our results demonstrate that adding a biocrust inoculant to jute ground cloth can expedite recovery of lichen‐moss biocrust and reestablish its influence on soil properties within a few years.     

沙坡头地区生物结皮覆盖区土壤种子库组成及垂直分布特征

采用野外随机取样和室内萌发试验相结合的方法,对沙坡头人工植被区的藓类结皮、地衣结皮和裸沙覆盖区土壤种子库的组成及垂直分布特征进行了研究。结果表明:1)人工植被区土壤种子库的物种组成简单,以1年生草本为主,相较于裸沙,两种生物结皮的存在显著增加了土壤种子库的密度(P0.01),但降低了土壤种子库的物种多样性及其与地上植被的相似性;2)两种生物结皮覆盖区土壤种子库的总密度虽无显著差异,但在0—2 cm土层中,地衣结皮土壤种子库的密度显著高于藓类结皮(P0.05),而在2—5 cm和5—10 cm土层中,藓类结皮土壤种子库的密度高于地衣结皮,但差异不显著;3)不同生物结皮覆盖区土壤种子库的垂直分布特征存在差异,藓类结皮覆盖土壤中有活力的种子主要分布在0—5 cm土层中,而地衣结皮和裸沙覆盖土壤中有活力的种子主要分布在0—2 cm土层中,且随着深度的增加,土壤中有活力的种子急剧减少。该研究表明,相较于裸沙,生物结皮的存在不仅增加了土壤种子库的大小,还改变了土壤种子库的垂直分布格局。生物结皮层下仍有相当比例有活力的小种子,这些种子欠缺萌发条件,对地上植被的贡献作用较小,但它们的存在对荒漠生态系统健康及可持续发展具有重要意义。     

黄土丘陵区生物结皮群落组成与水分入渗的关系

黄土丘陵区坡面尺度生物结皮多是由藻、藓和地衣等以不同比例、不同方式组合的一个复杂群落结构,显著影响水分入渗,但目前混合生物结皮水分入渗与其群落结构之间的关系仍不清楚,妨碍了对坡面尺度生物结皮土壤渗透性的评估。本研究测定了藻结皮、藓结皮及藓结皮盖度分别为<15%、15%～30%、30%～45%、45%～60%、＞60% 5个不同藻藓比例的混合生物结皮的稳定入渗速率,采用主成分分析和通径分析揭示混合生物结皮水分稳定入渗速率的影响因素,明确混合生物结皮水分稳定入渗速率与群落结构之间的关系。结果表明: 藻结皮和藓结皮土壤饱和导水率分别为0.66和2.40 mm·min^-1。藓结皮盖度从<15%到>60%的混合生物结皮的稳定入渗速率为0.80～2.30 mm·min^-1。混合生物结皮水分稳定入渗速率主要与藓结皮盖度和藓结皮改善的土壤孔隙结构密切相关,相关系数分别为0.636(P=0.011)和0.835(P=0.000)。通过藻结皮和藓结皮土壤饱和导水率与盖度加权预测的混合生物结皮水分入渗量(y)与混合生物结皮实测水分入渗量(x)具有极显著相关关系(r=0.945),二者拟合的线性函数为y=0.85x(R²=0.98,P<0.05)。本研究明确了混合生物结皮水分入渗与单一组成生物结皮水分入渗之间的关系,为准确评估该区生物结皮水文过程提供了科学依据。     

Elucidating the microbial resuscitation cascade in biological soil crusts following a simulated rain event

Biological soil crusts (biocrusts) are photosynthetic mats formed through an association of prokaryotic and eukaryotic microorganisms with soil particles. Biocrusts are found in virtually any terrestrial ecosystem where vascular plant coverage is abiotically limited, with drylands comprising the primary habitat for them. We studied the dynamics of the active bacterial community in two biocrusts from an arid and a hyperarid region in the Negev Desert, Israel, under light‐oxic and dark‐anoxic incubation conditions after simulated rainfall. We used H₂¹⁸O for hydrating the crusts and analysed the bacterial community in the upper and lower parts of the biocrust using an RNA‐stable isotope probing approach coupled with 454‐pyrosequencing. In both biocrusts, two distinct bacterial communities developed under each incubation condition. The active anaerobic communities were initially dominated by members of the order Bacillales which were later replaced by Clostridiales. The aerobic communities on the other hand were dominated by Sphingobacteriales and several Alphaproteobacteria (Rhizobiales, Rhodobacterales, Rhodospirillales and Rubrobacteriales). Actinomycetales were the dominant bacterial order in the dry crusts but quickly collapsed and accounted for < 1% of the community by the end of the incubation. Our study shows that biocrusts host a diverse community whose members display complex interactions as they resuscitate from dormancy.     

Unexpected side effects in biocrust after treating non‐native plants using carbon addition

Carbon addition has been proposed as an alternative to herbicide and manual removal methods to treat non‐native plants and reduce non‐target effects of treatments (e.g. impacts on native plants; surface disturbance). On Mojave Desert pavement and biocrust substrates after experimental soil disturbance and carbon addition (1,263 g C/m² as sucrose), we observed declines in lichens and moss cover in sucrose‐treated plots. To further explore this unforeseen potential side effect of using carbon addition as a non‐native plant treatment, we conducted biocrust surveys 5 and 7 years after treatments, sampled surface soils to observe if treatments additionally affected soil filamentous cyanobacteria, and conducted laboratory trials testing the effects of different levels of sucrose on cyanobacteria and desert mosses. Sucrose addition to biocrust plots reduced lichen and moss cover by 33–78% and species richness by 40–80%. Sucrose reduced biocrust cover in biocrust plots to levels similarly detected in pavement plots (<1%). While cyanobacteria in the field did not appear to be affected by sucrose, laboratory tests showed negative effects of sucrose on both cyanobacteria and mosses. Cyanobacteria declined by 41% 1 month after exposure to 5.4 g C/m² equivalent solutions. We detected injury to photosynthesis in mosses after 96 hour exposure to 79–316 g C/m² equivalent solutions. Caution is warranted when using carbon addition, at least in the form and concentration of sucrose, as a treatment for reducing non‐native plants on sites where conserving biocrust is a goal.     

Plant recovery techniques do not ensure biological soil‐crust recovery after gypsum quarrying: a call for active restoration

Biological soil crusts (biocrusts) are a key component of dryland ecosystems worldwide. However, large extensions of biocrusts are disturbed by human activities, gypsum quarry being an outstanding example. Restoration techniques applied have offered satisfactory results for vascular plants but they could greatly differ in promoting biocrust recovery. A basic question remains unaddressed: can measures for plant recovery accelerate or promote the recovery of biological crusts? We have examined eight different situations: undisturbed natural habitat, five treatments with no restoration measures (overgrazed area, abandoned quarry, topsoil removal from natural habitat, and two areas filled with gypsum mining spoil), and 2 areas receiving restoration measures (manual sowing and hydroseeding). We took 40 soil cores to determine cover of lichen, moss, and cyanobacteria. Biocrust richness and cover were higher in the undisturbed habitat, with remarkable differences for the different components among treatments. Cyanobacteria were well represented in all the cores (restored and non‐restored). Mosses were promoted the most by hydroseeding. Lichen cover was remarkably higher in undisturbed samples, very low in the quarry abandoned in 1992, and 0 in the rest. Complete spontaneous recovery of biocrusts was inefficient in the 25‐year period examined. Plant restoration measures could speed up its recovery comparing with non‐restored areas. Cyanobacteria and mosses can spontaneously recover fairly well. However, promoting them would accelerate the appearance of lichen. For lichen, inoculation or translocation of lichen thalli might be proposed. Therefore, our results call for the inclusion of active restoration measures of biocrust components in recovery plans, especially for lichens.     

古尔班通古特沙漠生物土壤结皮对氨氧化微生物生态位的影响

生物结皮作为荒漠地表的重要覆被类型, 在荒漠生态系统的氮素循环中扮演重要角色。融雪期为古尔班通古特沙漠生物结皮的复苏和生长提供了充足的水分, 也成为该沙漠氮素固定和转化的重要时期, 但该时期生物结皮如何影响驱动氨氧化转化的微生物群落动态尚未明确。因此, 我们利用荧光定量PCR (fluorescent quantitative PCR, qPCR)方法分析融雪期生物结皮与去除结皮不同土层(0-2, 2-5, 5-10和10-20 cm)氨氧化菌群丰度特征, 结合潜在硝化速率和土壤理化参数, 探究融雪期生物结皮对荒漠土壤氮素转化作用。结果表明: 氨氧化古菌(ammonia-oxidizing archaea, AOA)是古尔班通古特沙漠土壤优势氨氧化菌, 生物结皮对0-2 cm层土壤中AOA、氨氧化细菌(ammonia-oxidizing bacteria, AOB) amoA基因丰度具有显著抑制作用(P < 0.01), 对10-20 cm层土壤中AOA amoA基因丰度具有显著促进作用(P < 0.01)。冗余分析(redundancy analysis, RDA)表明, AOA、AOB amoA基因丰度主要受土壤含水量和铵态氮含量的影响, 占总条件效应的54.90%。氨氧化速率分析发现, 去除生物结皮显著降低古尔班通古特沙漠土壤硝化作用潜力(P < 0.001), 证实生物结皮对荒漠土壤氮素转化具有重要的调控作用。综上所述, 古尔班通古特沙漠氨氧化微生物的分布规律受环境因子调控, 特别是生物结皮可以通过调节土壤含水量和铵态氮含量影响AOA和AOB的空间生态位分化, 促进沙漠土壤的硝化作用。     

黄土高原蓝藻和藓类生物结皮对草本植物多样性及生物量的影响

生物结皮在干旱和半干旱气候区占据了广阔的生态位，深刻影响草本植物的空间格局，但其影响程度和作用途径目前仍存有争议。分别以黄土高原风沙土和黄绵土上的蓝藻结皮和藓结皮为对象，以无结皮为对照，通过样方法调查并测定了生物结皮与无结皮样地中草本植物的多样性和生物量，继而结合灰色关联分析和结构方程模型，对比分析了两类生物结皮对草本植物多样性和生物量的影响程度及作用途径。结果表明：（1）风沙土上，无结皮样地的优势科为禾本科和菊科，蓝藻结皮样地的优势科为藜科，藓结皮样地的优势科为禾本科，而黄绵土上无结皮样地的优势科为菊科、禾本科和豆科，蓝藻结皮样地的优势科与无结皮相似，藓结皮样地的优势科为禾本科和菊科；（2）与无结皮相比，风沙土上蓝藻结皮和藓结皮样地中多年生草本的株数分别增加了30%和16%，而黄绵土上两类生物结皮样地中多年生草本株数则分别增加了44%和减少了46%；（3）与无结皮相比，风沙土上蓝藻结皮和藓结皮样地中草本植物的Patrick和Shannon指数分别降低了1.0、0.2和3.4、0.5；而黄绵土上蓝藻结皮和藓结皮样地中两种多样性指数分别降低了4.8、0.2和4.2、0.4；（4）风沙土上蓝藻结皮和藓结皮样地的草本植物生物量比无结皮减少了111.5 g/m²和145.0 g/m²，而在黄绵土上则分别减少了127.8 g/m²和172.2 g/m²；（5）灰色关联分析显示，土壤穿透阻力对草本植物的多样性影响最大（关联系数分别为0.960和0.996），而NH₄⁺-N和NO₃^--N含量对草本植物的生物量影响最大（两种土壤上关联系数分别为0.727和0.752）。综上，黄土高原生物结皮显著降低了草本植物的多样性和生物量，其途径为通过增加土壤穿透阻力以降低草本植物的种子萌发几率并限制幼苗根系伸展，同时通过土壤氮竞争限制了草本植物生长。     

Revegetation modifies patterns of temporal soil respiration responses to extreme-drying-and-rewetting in a semiarid ecosystem

Aims

The artificial cultivation of biocrusts may represent a new low-cost and highly efficient solution to erosion control. However, establishment under varying field environmental conditions is understudied. We tested a variety of methods, arriving at a set of technical recommendations for rapid establishment of moss biocrusts on disturbed slopes, and the industrialization of this process.

Methods

In multiple field experiments, aimed at moss biocrust cultivation and establishment, we considered the following factors: nutrient solutions (control and weekly addition); water-retaining agent (control and addition); plant growth regulator (control and biweekly addition); shading (0, 50%, 70% and 90%); dispersal method (broadcast and spray application). In all cases, we initially inoculated soils with 700 g/m² of moss biocrust materials. We monitored dynamic changes of the coverage and density of moss biocrusts during the cultivation period, and their biomass at the end.

Results

We successfully cultured moss biocrusts in a field setting in as little as two months. Specifically, we found:(1) Regardless of the dispersal method, the nutrient solutions and some degree of shading both increased the coverage, plant density and biomass of moss biocrusts, whereas the water-retaining agent and plant growth regulator had little influence on these parameters. The shading treatments improved the survival rates of moss biocrusts, with the shade rating of 70% exhibiting the best performance. Further, the nutrient solutions had a more positive effect under shaded conditions. (2) The growth of mosses dispersed in the fall exceeded that of mosses dispersed in the summer. (3) Under both dispersal techniques, the maximal coverage of the moss biocrusts exceeded 90%, and the maximal plant density of moss biocrusts reached 120 stems/cm²under broadcast dispersal, and 150 stems/cm², under spray dispersal.

Conclusions

The rapid restoration of moss biocrusts can best be achieved by spray-dispersal or broadcast-dispersal, while also applying Hoagland solution to supply nutrients and maintaining soil moisture at 15–25%. Fall inoculation appears more likely to lead to better moss establishment, in fact, high moss mortality occurred in summer unless shading was used. We have some evidence, observational in fall, and experimental in summer, that moderate shading favors establishment. This technique could feasibly be up scaled and adopted to restore some ecological functions on various types of engineered disturbed surfaces. Over a longer period, the survivorship, succession and sustainability of artificial moss biocrusts should be explored specifically.

     

Response of biological soil crusts to raindrop erosivity and underlying influences in the hilly Loess Plateau region,China

Biological soil crusts (biocrusts) are ubiquitous living covers in arid and semiarid regions, playing a critical role in soil erosion control in semiarid regions. So far, research separating the multiple mechanisms of erosion control by biocrusts has been limited. It was problematic to link the influence of biocrusts to existing erosion models. In the present study, the response of biocrusts of different successional stages to raindrop erosivity and underlying influences was investigated. Using single drop simulated rainfall, the erosion controlling capacities of biocrusts were analyzed from an energetic perspective. The results showed that biocrusts caused a dramatic improvement of soil erosion resistance, which depended on species composition and increased considerably with higher succession stages. While the accumulated raindrop kinetic energy sustained by dark cyanobacterial crusts was 0.93 J (~15 times higher than that of bare soil), that of 60 % moss covered crusts reached values up to 20.18 J (~342 times higher than that of bare soil) and for 80 % moss covered crusts even 24.59 J were measured. Besides the composition and successional stages, the resistance of biocrusts to raindrop erosivity was related to the substrate soil moisture, soil texture, slope gradients and seasonal variation. The accumulated raindrop kinetic energy measured for cyanobacterial crusts was highest on silty, followed by loamy and sandy soil. For moss-dominated crusts raindrop kinetic energy was highest on sandy, followed by silty and loamy soil. Dry biocrust samples reached significantly higher accumulated raindrop kinetic energies compared to moist biocrusts, whereas the moisture content within moist crusts did not have a significant influence. Erosion resistance increased significantly with higher slope gradients. The resistance capacities of biocrusts during monsoon and post-monsoon were significantly higher than these of pre-monsoon biocrusts. Our results suggest that the influence of biocrusts can be included into erosion models from an energy point of view. The raindrop kinetic energy resistance capacity provides a potential bridge between biocrust succession and soil erodibility in commonly used erosion models.