沙埋与水分对科尔沁沙地主要固沙植物出苗的影响

蒿属半灌木乌丹蒿(Artemisia wudanica)、白沙蒿(A. sphaerocephala)、差不嘎蒿(A. halodendron)是科尔沁沙地的主要固沙植物。其中乌丹蒿和差不嘎蒿是科尔沁沙地的本土植物,白沙蒿为来自于库布齐沙漠、毛乌素沙地的飞播植物。设置了 5个沙埋深度(0.5、1.0、1.5、2.0和3.0 cm)和 4个水分梯度(86、171、257和 342 mL,分别模拟每月25、50、75和100 mm的降雨量),以探讨3种植物幼苗出土对沙埋和水分的响应。结果表明,沙埋与水分均显著影响着3种蒿属植物的幼苗出土(P < 0.001)。3种植物最适沙埋深度在0.5-1.5 cm范围内,萌发出土时适宜水量要高于当地种子萌发期的平均降水量(50 mm/月)。两种固沙先锋植物乌丹蒿和白沙蒿的种子出苗率均显著高于差不嘎蒿,乌丹蒿较白沙蒿也明显为高,尤其在水分缺乏时,表现出两种先锋植物种子出苗对干旱有更好的适应性。协方差分析表明,乌丹蒿幼苗死亡率显著高于白沙蒿和差不嘎蒿(P < 0.05),在达到75 mm/月降水量时,3种植物的出苗较好,但不能满足乌丹蒿幼苗生长对水分的需求,而实际种子萌发期的降水量平均只有50 mm/月。因而降水的缺乏导致乌丹蒿种群更新出现问题,加之飞播植物的竞争,使得近几年科尔沁沙地较多乌丹蒿种群出现衰退。     

沙埋对两种沙生植物幼苗生长的影响及其生理响应差异

为了解沙埋对沙生植物生长的影响及其生理响应特征, 比较不同沙生植物耐沙埋能力及其机制, 2010年在内蒙古科尔沁沙地研究了不同深度沙埋下沙蓬(Agriophyllum squarrosum)和盐蒿(Artemisia halodendron)幼苗的存活率、株高等生长特性及其渗透调节物质含量, 保护酶活性和膜透性的变化, 得到以下结果: 沙蓬和盐蒿幼苗均具有较强的耐沙埋能力, 其中沙蓬幼苗最大耐沙埋深度超过幼苗10 cm, 盐蒿幼苗最大耐沙埋深度超过其株高8 cm; 随着沙埋深度增加, 沙蓬和盐蒿幼苗的存活率和株高均显著下降, 沙蓬的下降幅度显著小于盐蒿; 沙埋处理下两种植物均未表现出受水分胁迫, 沙埋导致其光合面积下降, 幼苗顶土困难, 是影响其存活和高生长的主要生态机制; 随着沙埋深度增加, 沙蓬幼苗丙二醛(MDA)含量显著增加, 盐蒿幼苗MDA含量下降, 虽然二者膜透性均呈增加趋势, 但沙蓬膜透性增加幅度显著低于盐蒿, 说明细胞膜受损是导致二者幼苗存活率下降和生长受到抑制的主要生理机制, 沙蓬膜透性受损程度较低是其耐沙埋能力较强的主要生理机制; 沙埋胁迫下, 虽然两种植物都通过提高过氧化物酶活性和脯氨酸含量减轻细胞膜受损程度, 但沙蓬体内超氧化物歧化酶也表现出重要协调作用, 使之酶促系统在保护细胞膜免受胁迫损伤过程中的作用更有效。     

沙埋对西鄂尔多斯珍稀植物种子萌发和幼苗出土的影响

采用不同沙埋深度(0、1、2、3、5、7、10 cm埋深)处理,对内蒙古西鄂尔多斯4种珍稀植物霸王(Zygophyllum xanthoxylum)、沙冬青(Ammopiptanthus mongolica)、蒙古扁桃(Prunus mongolica)和长叶红砂(Reaumuria trigyna)种子萌发及幼苗出土情况进行研究,以揭示其种子萌发特性.结果表明:表层沙土(0 cm埋深)的种子几乎不萌发;除霸王外,其他3种植物在不同沙埋深度处理下的种子萌发率差异显著(P＜0.05);沙埋对4种珍稀植物的幼苗出土均有显著影响,出苗率随着沙埋深度的增加而降低,且遵循指数方程.霸王在2 cm沙埋深度的出苗率最高,其他物种在1 cm沙埋深度的出苗率最高.沙埋深度对幼苗生物量的影响不显著.     

毛乌素沙地4种沙生植物种子萌发及出苗对沙埋及单次供水的响应

飞播固沙作为一项快速而有效的现代化治沙措施,已成为毛乌素沙地植被恢复与重建的重要手段。但此项技术仍存在一些问题,如飞播后成苗率较低等。以毛乌素沙地优势植物柠条（Caragana korshinskii）、羊柴（Hedysarum laeve）、油蒿（Artemisia ordosica）与籽蒿（Artemisia sphaerocephala）为研究对象,人工控制7个沙埋深度和9个水分梯度,研究4种植物种子萌发和幼苗出土对沙埋和单次供水的响应,阐明多大的单次降雨才能保证种子萌发与幼苗出土及出土幼苗的维持时间。结果表明,对于柠条和羊柴质量相对较大的种子而言．种子主要在供水量10．20mm,埋藏深度为0．5．2cm的条件下出苗,但在埋藏深度为5cm时这两个物种仍有少量种子能够出苗;而对于油蒿和籽蒿质量相对较小的种子而言,种子主要在供水量10．20mm,埋藏深度为0．5cm时出苗,当埋藏深度为1．5cm和2cm时不能顺利出苗。沙埋深度0．5cm条件下,4个物种具有最高的出苗率和出苗速率。在试验期内（30d）,柠条、羊柴和油蒿出土幼苗分别在单次供水量为5、7．5mm和7．5mm时全部死亡,在单次供水量高于15mm时4个种的出土幼苗死亡率大多低于50％,且随供水量的增加出土幼苗死亡率降低。结合毛乌素沙地降雨特点与本次实验结果,0．5cm的沙埋及7．5mm以上的单次降雨是上述4种植物自然条件下出苗较好的重要条件。     

沙埋和种子大小对固沙禾草沙鞭的种子萌发与幼苗出土的影响

该文研究了野外条件下不同深度的沙埋对沙鞭(Psammochloa villosa)种子萌发和幼苗出土的影响,以及温室条件下种子大小对不同深度沙埋后的种子萌发和幼苗出土的影响。结果表明,沙埋深度显著影响沙鞭的种子萌发率、幼苗出土率和种子休眠率。沙子表面的种子不能萌发。2 cm的浅层沙埋时的种子萌发率和幼苗出土率最高,1 cm 沙埋的种子萌发率和幼苗出土率次之。沙埋深度超过2 cm之后,沙鞭的种子萌发率和幼苗出土率与沙埋深度呈负相关。2 cm的种子休眠率最低。从2 ~12 cm,种子休眠率随着沙埋深度的增加而增加。在幼苗能够出土的深度(1~6 cm),幼苗首次出土所需的时间随着沙埋深度的增加而延长。种子大小对沙鞭的种子萌发率没有显著影响。但是在深层沙埋(6 cm)时,与小种子相比,大种子产生的幼苗的出土率较高。从2~6 cm,大种子形成的幼苗的茎长度都较长。     

沙埋对醉马草种子萌发和幼苗生长的影响

为探讨醉马草(Achnatherum inebrians)种群繁殖和扩散机理,并为其防控和开发利用提供理论基础,研究了不同沙埋深度(0、1、2、3、4和5cm)对醉马草种子萌发和幼苗生长的影响。结果表明:埋深对醉马草幼苗出土率、首次出苗时间、幼苗生长高度以及生物量的分配均有极显著影响(P<0.001);种子萌发和幼苗出土率在2cm沙埋下达到最高(92%),在5cm沙埋下最低(58.7%);幼苗最大高度(10.8cm)出现在3cm的沙埋,最小高度(6.3和7.1cm)出现在0和5cm的埋深;埋深为2cm时,地上和地下生物量最大,埋深5cm时地上和地下生物量均最小;最大根长(约5cm)和最小根长(1cm)分别出现在2～3cm和5cm的埋深。2～3cm的埋深是醉马草种子萌发和幼苗生长的最佳深度。     

沙埋和种子大小对柠条锦鸡儿种子萌发、出苗和幼苗生长的影响

研究了沙埋深度和种子大小对内蒙古毛乌素沙地植被群落中占优势的柠条锦鸡儿(Caragana korshinskii Kom.)种子萌发、出苗、幼苗存活和生长的影响.结果表明,沙埋深度显著影响柠条锦鸡儿的种子萌发率、休眠率、出苗率、幼苗存活率及生物量.在0.5-2cm的浅层沙埋下,种子萌发率、出苗率、幼苗存活率及生物量最高,休眠率最低;沙埋深度≥4 cm时,柠条锦鸡儿的种子萌发率、出苗率、幼苗存活率及生物量随着沙埋深度增加显著降低,而休眠率却显著升高;沙埋深度≥12 cm时,柠条锦鸡儿种子不能够出苗,幼苗也不能够存活.种子大小对柠条锦鸡儿种子萌发率没有显著影响,但对出苗率、幼苗存活率及生物量影响显著.在各个沙埋深度下,不同大小的柠条锦鸡儿种子间的萌发率没有显著差异.当沙埋深度≤6 cm时,不同大小的柠条锦鸡儿种子在同一沙埋深度下的出苗率间没有显著差异;但当沙埋深度≥8 cm时,在同一沙埋深度下,大种子的出苗率显著高于中种子和小种子的出苗率,而中种子和小种子出苗率间没有显著差异.0.5-10 cm的沙埋深度中,除6 cm和8 cm深度下中种子和小种子萌发幼苗的生物量间没有显著差异外,其余深度下,大种子萌发的幼苗的存活率及生物量显著高于同一沙埋深度下中种子萌发的幼苗的存活率及生物量,后者又显著高于小种子萌发的幼苗的存活率及生物量.可能正是种子萌发对沙埋环境的忍耐或响应能力以及种子的多态性提高了柠条锦鸡儿在毛乌素沙地的适合度,为其在流动或半流动沙丘环境中成功定居并形成优势群落奠定了基础.     

沙埋对花棒种子萌发和幼苗生长的影响

为探讨花棒(Hedysarum scopariium)种子萌发和幼苗生长对沙埋的响应,并为固沙造林、水土保持提供理论基础,研究了6种沙埋深度(0、1、2、3、4和5cm)对花棒种子萌发和幼苗生长的影响.结果表明,埋深对花棒幼苗出土率、首次出苗时间、单株叶片数、幼苗生长高度以及生物量的分配均有极显著影响(P<0.001).种子出苗率在2 cm沙埋下达到最高(95.6%),在5cm沙埋下最低(43.4%);幼苗最大高度(11.6cm)、绝对株高(13.9cm)和最大地上生物量(26.7mg)均出现在2cm的埋深,幼苗最小高度(3.3cm)、最小根长(4.3cm)和最小地上生物量(5.3mg)出现在5cm的埋深;生物量分配随沙埋深度增大而更多地分配给地下部分.2cm的沙埋是花棒种子萌发和幼苗生长的最佳深度.     

五种荒漠植物幼苗出土及生长对沙埋深度的响应

研究了红砂、泡泡刺、花棒、白刺和沙拐枣5种荒漠优势植物的幼苗出土和生长对沙埋的响应,判断了幼苗的生长特征能否预测植物的定植能力。进行了0、1、2、3、5cm和8cm等6个沙埋深度处理,每个处理5个重复。结果表明：每种植物的出苗率都随着沙埋深度的增加而降低,而且遵循着指数方程关系。红砂种子的最佳沙埋深度应为0-1cm,3cm已是出苗和存活的最大沙埋深度;泡泡刺、花棒和白刺种子的最佳深埋深度为0—3cm;沙拐枣在0—8cm各个深度都有出苗现象,且出苗率没有显著差异,但8cm深度的出苗率只有4％,最佳沙埋深度约为5cm。幼苗的生长高度受沙埋深度的影响显著,在同一时间,幼苗的最大生长高度并不在0cm表层,但红砂幼苗除外。泡泡刺、花棒和白刺在0—3cm的沙埋深度的幼苗生长高度大于5-8cm沙埋深度的生长高度,但沙拐枣幼苗在5cm深度的生长高度最大。5种荒漠植物幼苗的生物量受沙埋深度的影响不显著。在同一沙埋深度下,红砂的绝对高度生长率明显低于其余4种植物,沙拐枣的绝对高度生长率高于其余4种植物幼苗;5种植物的相对高度生长率对沙埋深度的响应并不敏感。绝对高度生长率与相对高度生长率并不能预示幼苗存活成功率。     

差巴嘎蒿幼苗对沙埋的生态适应和生理响应

沙埋对于沙漠植物存活和生长影响的研究文献已有很多,但迄今有关沙漠植物对于沙埋生理生态适应的研究还很少见有报道。差巴嘎蒿(Artemisia halodendron)广泛分布于我国半干旱沙地中,是流动半流动沙地的优势种。为了解沙生植物对沙埋的生态适应及其生理响应,2010—2011年在内蒙古科尔沁沙地研究了不同沙埋深度下差巴嘎蒿幼苗的存活率、株高等生长特性和渗透调节物质含量,保护酶活性和膜透性的变化,得到以下结果:沙埋对差巴嘎蒿幼苗的存活与生长有着显著影响,特别是沙埋深度超过其株高后,其存活率和高生长受到严重抑制,但和非沙生植物相比,差巴嘎蒿幼苗具有很强的耐沙埋能力,即使沙埋深度达到其株高的200%时仍有部分幼苗存活。随着沙埋深度的增加,差巴嘎蒿幼苗叶片含水量没有显著变化,但过氧化物歧化酶活力降低,过氧化物酶活性增强,过氧化氢酶活性变化不明显,脯氨酸含量增加,可溶性糖含量下降,丙二醛含量下降,膜透性增强。和水分、盐分胁迫不同,沙埋并未造成差巴嘎蒿幼苗的水分亏缺,沙埋胁迫下差巴嘎蒿幼苗死亡率增加、生长受到抑制的主要原因是沙埋导致植物光合面积下降,沙埋叶片无法进行正常呼吸和部分幼苗无法破土生长,但沙埋胁迫下脯氨酸含量的和过氧化物酶活性增强分别在渗透调节和保护细胞膜免受损伤中起到了关键作用。     

苜蓿种子萌发和幼苗生长对温度、光照和埋深的响应

紫花苜蓿(Medicago sativa)是世界人工草地重要的优良牧草。研究其种子萌发和幼苗生长对温度、光照及埋深等环境因子的响应,对苜蓿草地的种植及管理具有重要的实践指导意义。采用室内控制实验,分析了紫花苜蓿种子萌发和幼苗生长对恒温(10、15、20、25、30℃)、变温(6/15、10/20、15/25、15/30、20/30℃)、光照(12 h光照/12 h黑暗、24 h黑暗)以及埋深(1、2、3、4、5 cm)等环境因子的响应特征。结果表明,苜蓿种子的萌发温度范围宽,在供试的10种恒温和变温下萌发率为50%~88%,且温度处理对苜蓿种子的萌发率没有显著的影响;黑暗对苜蓿种子萌发有抑制作用,12 h光照/12 h黑暗条件下,苜蓿种子萌发率为69%~88%,而24 h全暗条件下为50%~77%,其中10、15、30、10/20和15/30℃温度下,光照处理均显著高于全暗处理。埋深1~5 cm的苜蓿种子出苗率没有显著差异,且幼苗株高、干重、鲜重均没有受到显著影响;埋深对苜蓿根生长存在显著影响,埋深1~2 cm根长度及重量均显著高于其他埋深处理。以上结果表明,苜蓿种子萌发的温度范围宽,恒温和变温下都有较高的萌发率,适合播种季节要求宽泛;黑暗显著抑制紫花苜蓿种子的萌发,田间种植苜蓿的最佳埋深为1~2 cm。     

Effects of burial in sand and water supply regime on seedling emergence of six species

BACKGROUND AND AIMS: Air seeding has long been regarded as a quick and successful measure for vegetation rehabilitation in China. However, seedling emergence of often-used species including Agriophyllum squarrosum, Artemisia sphaerocephala, Artemisia ordosica, Hedysarum fruticosum, Caragana korshinskii and Medicago sativa is low. Experiments were conducted under controlled conditions to study the effects of sowing depth and water supply on seedling emergence, in order to understand the requirements for increasing seedling emergence. METHODS: Seeds were exposed to different environments of burial and water supply regimes in PVC pots (7 cm in diameter and 11 cm in height) under the same light intensity and alternating temperature regimes in a growth chamber. KEY RESULTS: Seedlings of three species (Agriophyllum squarrosum, Artemisia sphaerocephala, Artemisia ordosica) with relatively light seeds emerged well at a 0.5 cm sowing depth under a 7.5 and 10 mm water supply regime. However, few seedlings of these species emerged when the sowing depth was over 1 cm or when water supply was 5 mm. Seedlings of Caragana korshinskii, Hedysarum fruticosum and Medicago sativa emerged from sowing depths of 0.5-4 cm, 0.5-3 cm, and 0.5-4 cm, respectively, under both 7.5 and 10 mm water supply regimes. Under a 5 mm water supply regime, seedlings of these species also emerged at over 1 cm sowing depth. Seeds of all six species sown on the surface of sand did not germinate, and seedlings did not emerge when they were sown at depths greater than 6 cm. CONCLUSIONS: Based on these experiments, a 0.5 cm sowing depth resulted in the highest seedling emergence and it is concluded that this is the optimal sowing depth for seedling emergence of all six species.     

Seed germination and seedling emergence of three annuals growing on desert sand dunes in China

BACKGROUND AND AIMS: Information on the initial growth characteristics of annuals found in Chinese deserts is very limited. The aim of this study was to investigate seed germination and interactive effects of irrigation and seed burial depth in sand on seedling emergence and seedling survival in three annuals (Agriophyllum squarrosum, Bassia dasyphylla and Aristida adscensionis) commonly growing on sand dunes in these regions. METHODS: Effects of temperature, light and polyethylene glycol-6000 on seed germination were examined by irrigating seeds sown on filter paper in Petri dishes. Seedling emergence was examined for seeds sown on the surface of, or at different depths (5, 10, 20, 30, 40 and 50 mm) in, sand-filled pots, which were irrigated under different regimes. For seeds buried at a depth of 50 mm, seed viability was examined after irrigation of the pots. KEY RESULTS: Seeds of three species germinated at most temperatures recorded between spring and autumn in their native habitats. No seed dormancy was found in any species. For all three species, seedling emergence was most favoured when seeds were buried at a depth of 10 mm. When seeds sown on the sand surface were irrigated, seed germination was considerably suppressed due to water deficiency, but many seeds remained viable. For A. squarrosum and B. dasyphylla, many seeds that were deeply buried and irrigated remained ungerminated but viable, while for A. adscensionis deeply buried seeds germinated, but the seedlings did not emerge due to unfavourable seedling growth in deep sand. CONCLUSIONS: Precipitation is the most crucial factor in determining the seasonal emergence of seedlings of the three tested species in the field. The vertical distribution of seeds in sand determines the proportion of seeds that germinate after precipitation and acts to maintain seed banks over multiple years.     

Germination and emergence of annual species and burial depth: Implications for restoration ecology

Due to the high content of viable seeds, topsoil is usually spread on ground left bare during railway and motorway construction to facilitate the regeneration of vegetation cover. However, during handling of the topsoil, seeds are often buried deeply and they cannot germinate or the seedlings cannot emerge from depth. This study experimentally explores the predictive value of seed mass for seed germination, mortality and seedling emergence at different burial depths for 13 common annual species in semiarid Mediterranean environments. We separate the effect of burial depth on germination and emergence by means of two experiments. In the germination experiment, five replicates of 20 seeds for each species were buried at depths ranging from 0 to 4 cm under greenhouse conditions. Germinated and empty or rotten seeds were counted after 8 weeks. In the emergence experiment, five replicates of four newly-germinated seeds per species were buried at the same depths under controlled conditions and emergence was recorded after 3 weeks. The effect of burial depth on percentage of germination and seedling emergence was dependent on seed size. Although all species showed a decrease in germination with burial depth, this decrease was greater for small-than large-seeded species. Percentage of emergence was positively related to seed mass but negatively related to burial depth. Seed mortality was higher for small-than large-seeded species, but there was no general effect of burial depth on this variable. Thus, the current practice of spreading 30 cm deep layers of topsoil in post-construction restoration projects is unadvisable. In this restoration scenario, thinner layers of topsoil should be used to achieve the maximum potential of the topsoil for germination and seedling establishment.     

沙埋对沙米幼苗生长及生理过程的影响

2010-2011年在科尔沁沙地,研究了不同沙埋深度下沙米幼苗生长特性及其逆境生理指标的变化.结果表明: 沙米幼苗的耐沙埋能力较强,当埋深超过其株高后生长才会受到严重抑制,而埋深超过其株高1.66倍时仍有部分幼苗存活.当埋深未超过株高时,其幼苗丙二醛含量和膜透性的变化不显著;随着埋深进一步增加,其膜质过氧化加剧,细胞膜受损.沙埋胁迫下,沙米幼苗的超氧化物歧化酶(SOD)、过氧化物酶(POD)活性及脯氨酸含量均显著增加,过氧化氢酶(CAT)活性和可溶性糖含量下降.沙埋使植株光合面积减少、细胞膜受损,导致沙米幼苗死亡率增加、生长受抑,但是SOD和POD活性的增强及脯氨酸含量的增加对于减轻沙埋危害将起到一定的作用.     

Effects of sand burial depth and seed mass on seedling emergence and growth of Nitraria sphaerocarpa

A greenhouse experiment was conducted to test the effects of sand burial depth and seed mass on seedling emergence and growth of Nitraria sphaerocarpa. Seeds of Nitraria sphaerocarpa were sorted into three size-classes (large, medium, small) and artificially buried at 0, 1, 2, 3, 4, 5 and 6 cm depths in plastic pots filled with unsterilized sand. In the seven treatments, the percent emergence, seedling mass and seedling height, significantly affected by both burial depth and seed size, were highest at the optimal burial depth of 2 cm burial depth, and decreased with increasing burial depth in each seed size-class. Although seedling mass was usually greatest for large seeds and least for small seeds at each burial depth, little difference was observed in seedling height at shallow burial depths of 0–3 cm. In each seed size-class, with increasing burial depth, both root-mass ratio and aboveground stem-mass ratio decreased, while belowground stem-mass ratio increased. In each burial depth, with decreasing seed size, belowground stem-mass ratio increased, while root-mass ratio decreased.