Passive restoration of vegetation and biological soil crusts following 80 years of exclusion from grazing across the Great Basin

Restoration targets for biological soil crusts are largely unknown. We surveyed seven 80‐year‐old grazing exclosures across northern Nevada for biocrusts to quantify reference conditions at relatively undisturbed sites. Exclosures were associated with the following plant communities: Wyoming big sagebrush, black sagebrush, and areas co‐dominated by winterfat and Wyoming big sagebrush. Cover of biocrusts and shrubs were generally higher than other plant groups at these sites, regardless of being inside or outside of the exclosures, suggesting these groups make up most of the native flora across the region. Important in forming soil structure, cyanobacteria of the order Oscillatoriales were less abundant and diverse in black sagebrush communities. Grazing had a negative effect on the abundance of Oscillatoriales but not the number of algal taxa, including cyanobacteria. Abundance of light algal crusts were not influenced by plant community or grazing. Dark algal crusts were generally less abundant on grazed sites. Influences of plant community and grazing were most apparent when accounting for reproductive rates of lichens and mosses based on establishment mechanisms. Abundance of shrubs, perennial grasses, Oscillatoriales, fast reproducing biocrusts and the number of algal and cyanobacterial taxa, varied by plant community, suggesting that restoration should be plant community specific. We demonstrate the affinity of rapidly reproducing biocrusts for winterfat‐Wyoming big sagebrush co‐dominated plant communities, regardless of grazing pressure. Across sites, the effects of grazing were most evident on the abundance of Oscillatoriales and slowly reproducing biocrusts following 80 years of cessation from grazing.     

黄土丘陵区生物土壤结皮表面糙度特征及影响因素

地表糙度是影响地表径流和侵蚀过程的重要属性.生物结皮在干旱半干旱区广泛分布,是地表糙度的影响因子之一.本文采用链条法测定了黄土丘陵区不同发育阶段生物结皮表面糙度特征,分析了不同发育阶段生物结皮表面糙度对坡向、土壤含水量和冻融作用的响应及其与各理化性质的相关性,初步探索了生物结皮对地表糙度的影响及其相关因素.结果表明: 生物结皮显著改变地表糙度,随着生物结皮从藻结皮向藓结皮演替,其糙度先降低后增加,生物结皮发育形成10年以后,其表面糙度基本趋于稳定;研究区早期形成的藻结皮表面糙度较裸土降低47.0%,深色藻结皮(藓类盖度<20%)较裸土降低20.4%,混生结皮(藓类盖度为20%～60%)和苔藓结皮(藓类盖度>70%)表面糙度与深色藻结皮基本一致;坡向对发育10年以上的生物结皮表面糙度的影响不显著;土壤含水量影响地表糙度特征.研究区浅色藻结皮表面糙度随水分变化较为剧烈;随着生物结皮发育,深色藻结皮、混生结皮和苔藓结皮表面糙度随水分的变化趋于平缓.冻融增加了生物结皮表面糙度.浅色藻结皮经两次冻融后表面糙度增加29.7%;深色藻结皮、混生结皮和藓结皮表面糙度的影响需经过反复冻融才有所体现.生物结皮表面糙度与藓结皮盖度呈显著正相关(P＜0.1).     

Microbial inoculum production for biocrust restoration: testing the effects of a common substrate versus native soils on yield and community composition

Human activities are causing unprecedented disturbances in terrestrial ecosystems across the globe. To reverse soil deterioration in drylands, a promising tool is the ex situ cultivation of biological soil crusts, topsoil geobiological assemblages that provide key ecosystem services. One approach is to transplant biocrusts cultivated in greenhouse nursery facilities into degraded sites to accelerate recovery. Lichen‐ and moss‐dominated biocrusts have been successfully grown using a common, sandy soil. We compared the use of a common, sandy soil versus native soils as a substrate for the cultivation of cyanobacteria‐dominated biocrusts. In greenhouse experiments, we inoculated natural biocrusts collected from three Southwestern USA dryland sites on to either a common, sandy soil or on their respective native soils. The common substrate resulted in a moderate enhancement of growth yield relative to native soils. While changes in bacterial phyla composition remained low in all cases, the use of a common substrate introduced larger shifts in cyanobacterial community composition than did using native soils. The shift increase attributable to the common, sandy soil was not catastrophic—and typical cyanobacteria of field biocrusts remained dominant—unless textural differences between the common substrate and native soils were marked. Because collecting native soils adds a significant effort to growing cyanobacterial biocrusts in greenhouses for restoration purposes, the use of a common, sandy substrate may be considered by land managers as a standard practice. But we recommend to regularly monitor the composition of the grown biomass.     

Nursing biocrusts: isolation,cultivation, and fitness test of indigenous cyanobacteria

Biological soil crusts (biocrust) are microbial communities that develop at the soil surface of drylands and play an important role in erosion control and fertility. Soil surface disturbance from a broad range of natural and human processes (e.g. fire, livestock grazing, off‐road traffic) cause significant losses in biocrust cover and associated ecosystems services. Hence, biocrust restoration is emerging as an important intervention strategy to rehabilitate degraded dryland soils. In a multistep process, we designed protocols for the establishment of “microbial nurseries” to produce photosynthetic cyanobacterial inoculum for biocrust seeding at scale. We first report on the strategy for isolation, directly from the target site, of a large culture collection of cyanobacteria that included multiple representatives of the five most common biocrust taxa. After genetic pedigreeing of these isolates, we could select those that best matched field populations genetically for scale‐up cultivation. We then developed protocols for effective cyanobacterial biomass production to obtain sufficient inoculum. This was followed by conditioning treatments (hardening off) to preacclimate this inoculum to the stressful conditions expected in the field. Finally, we show that the inoculum obtained was fit to thrive in its original soil under natural outdoor conditions if sufficient water was available. We repeated this process successfully for four sites, two in the hot Chihuanuan desert and two in the cooler Great Basin Desert, and on two textural types of soils in each. The cyanobacterial biocrust nursery approach represents a versatile, viable, and safe tool for the rehabilitation of dryland soils.     

Soil reconstruction after mining fails to restore soil function in an Australian arid woodland

The biogeochemical properties of soils drive ecosystem function and vegetation dynamics, and hence soil restoration after mining should aim to reinstate the soil properties and hydrological dynamics of remnant ecosystems. The aim of this study is to assess soil structure in two vegetation types in an arid ecosystem, and to understand how these soil properties compare to a reconstructed soil profile after mining. In an arid ecosystem in southeast Australia, soil samples were collected at five depths (to 105 cm) from remnant woodland and shrubland sites, and sites either disturbed or totally reconstructed after mining. We assessed soil physico‐chemical properties and microbial activity. Soils in the remnant arid ecosystem had coarse‐textured topsoils that overlay clay horizons, which allows water to infiltrate and avoid evaporation, but also slows drainage to deeper horizons. Conversely, reconstructed soils had high sand content at subsoil horizons and high bulk density and compaction at surface layers (0–20 cm). Reconstructed soils had topsoils with higher pH and electrical conductivity. The reconstructed soils did not show increased microbial activity with time since restoration. Overall, the reconstructed soil horizons were not organized in a way that allowed rainfall infiltration and water storage, as is imperative to arid‐zone ecosystem function. Future restoration efforts in arid ecosystems should focus on increasing sand content of soils near the surface, to reduce evaporative water loss and improve soil quality and plant health.     

Contrasting mechanisms underlie short‐ and longer‐term soil respiration responses to experimental warming in a dryland ecosystem

Soil carbon losses to the atmosphere through soil respiration are expected to rise with ongoing temperature increases, but available evidence from mesic biomes suggests that such response disappears after a few years of experimental warming. However, there is lack of empirical basis for these temporal dynamics in soil respiration responses, and for the mechanisms underlying them, in drylands, which collectively form the largest biome on Earth and store 32% of the global soil organic carbon pool. We coupled data from a 10 year warming experiment in a biocrust‐dominated dryland ecosystem with laboratory incubations to confront 0–2 years (short‐term hereafter) versus 8–10 years (longer‐term hereafter) soil respiration responses to warming. Our results showed that increased soil respiration rates with short‐term warming observed in areas with high biocrust cover returned to control levels in the longer‐term. Warming‐induced increases in soil temperature were the main drivers of the short‐term soil respiration responses, whereas longer‐term soil respiration responses to warming were primarily driven by thermal acclimation and warming‐induced reductions in biocrust cover. Our results highlight the importance of evaluating short‐ and longer‐term soil respiration responses to warming as a mean to reduce the uncertainty in predicting the soil carbon–climate feedback in drylands.     

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。     

腾格里沙漠不同组成生物结皮特征及其对土壤酶活性的影响

生物结皮在干旱半干旱地区生态系统中起着重要的作用。目前,有关生物结皮的存在对土壤酶活性的影响已有大量研究,而对生物结皮基本特征对土壤酶活性的研究较少。以流沙为对照,研究了不同组成生物结皮(藻结皮、地衣结皮、地衣-藓结皮、藓结皮)中以结皮厚度、叶绿素a含量、胞外多糖、胞外蛋白质及结皮中养分为特征的变化规律及其对结皮下土壤酶活性的影响。结果表明：(1)不同组成生物结皮的结皮厚度、叶绿素a、胞外多糖、胞外蛋白质、C、N、P、C/N、C/P、N/P的变化范围从藻结皮到藓结皮分别为：2.28—8.29 mm、1.79—8.05μg/cm~2、14.60—20.43 mg/kg、13.16—19.37 mg/kg、5.54—51.42 g/kg、0.44—3.36 g/kg、0.23—0.54 g/kg、9.62—15.32、24.07—94.98、1.92—6.23,且上述结皮特征均沿着藻结皮、地衣结皮、地衣-藓结皮、藓结皮方向显著增加(P<0.001),但胞外多糖和胞外蛋白质在地衣结皮、地衣-藓结皮和藓结皮间无显著差异(P>0.05);(2)相比于C和N,结皮的P含量具有较小的变异...     

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。