187 resultados para Mowing


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Four methods to control the smooth cordgrass Spartina (Spartina alterniflora) and the footwear worn by treatment personnelat several sites in Willapa Bay, Washington were evaluatedto determine the non-target impacts to eelgrass (Zostera japonica). Clone-sized infestations of Spartina were treated bymowing or a single hand-spray application of Rodeo® formulatedat 480 g L-1acid equivalence (ae) of the isopropylaminesalt of glyphosate (Monsanto Agricultural Co., St. Louis, MO;currently Dow AgroSciences, Indianapolis, IN) with the nonionic surfactant LI 700® (2% v/v) or a combination of mowing and hand spraying. An aerial application of Rodeo® with X-77 Spreader® (0.13% v/v) to a 2-ha meadow was also investigated. Monitoring consisted of measuring eelgrass shoot densities and percent cover pre-treatment and 1-yr post-treatment. Impacts to eelgrass adjacent to treated clones were determined 1 m from the clones and compared to a control 5-m away. Impacts from footwear were assessed at 5 equidistant intervals along a 10-m transect on mudflat and an untreated control transect at each of the three clone treatment sites. Impacts from the aerial application were determined by comparing shoot densities and percent cover 1, 3 and 10 m from the edge of the treated Spartina meadow to that at comparable distances from an untreated meadow. Methods utilized to control Spartina clones did not impact surrounding eelgrass at two of three sites. Decreases in shoot densities observed at the third site were consistent across treatments. Most impacts to eelgrass from the footwear worn by treatment personnel were negligible and those that were significant were limited to soft mud substrate. The aerial application of the herbicide was associated with reductions in eelgrass (shoot density and percent cover) at two of the three sampling distances, but reductions on the control plot were greater. We conclude that the unchecked spread of Spartina is a far greater threat to the survival and health of eelgrass than that from any of the control measures we studied. The basis for evaluating control measures for Spartina should be efficacy and logistical constraints and not impacts to eelgrass. PDF is 7 pages.

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羊草是高品质的牧草,羊草草地是优良的割草场,刈割是人类对草地的主要利用手段之一,其对羊草草地造成的影响一直受到学者和生产管理者的关注并开展了大量研究。但以往刈割的相关研究主要集中在整个草地的水平上,羊草个体对刈割的响应迄今还没有深入研究。随着畜牧业的发展对草场质量要求的不断提高,发掘耐刈割的羊草种质势在必行,而羊草在不同时期对刈割的响应状况及不同生态型羊草对刈割的响应则是其中必不可少的研究环节。 本文以羊草为实验材料,对其在不同发育时期进行了刈割研究,主要以高度作为动态研究的手段,包括四个部分: 实验1,羊草在苗期对刈割的响应,结果表明,苗期进行的刈割,对羊草第1片叶生长速率没有影响。 实验2,两种生态型羊草在三四叶期及七八叶期两次刈割的响应,表明三四叶期进行的刈割,羊草能达到85.1%的恢复,灰绿型比黄绿型多恢复8.5%。七八叶期进行的刈割,刈除茎尖使羊草停滞生长。三四叶期的刈割能导致灰绿型增加1个分株,黄绿型则减少1个分株。 实验3,四年生羊草草地对不同程度刈割的响应,表明羊草草地在重度刈割后所受影响更严重,但每株羊草分蘖数目会增加1。 实验4,赖草属十一个物种生长期刈割响应,表明羊草对刈割的恢复性明显高于所研究的赖草属其他物种,达到超补偿水平。 在对羊草草原合理利用时,适度刈割是关键的,刈割的频次及程度关系重大。羊草生态型的选择也有举足轻重的作用,选用适应性强的灰绿型羊草对于提高羊草草地具有一定的积极作用。

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第一部分:内蒙古锡林河流域草原植物种群和群落热值的时空变异研究 热值的研究是评价生态系统能量固定、传输和转化的基础,也是评价植物光合作用效率和植物营养值的有用参数。同种植物热值会随着植物部位、光照、养分条件、季节、土壤类型和气候条件的不同而发生变化。不同的种类和类群之间热值也存在差异。本项研究以内蒙古锡林河流域中段草原植物群落为对象,研究了植物种群和群落热值的时空变异规律。 对内蒙古羊草草原群落不同植物种群热值的时问动态研究结果表明,42种植物地上部分的热值在13.16土1.14 kJ.g-l和18.14土0.53 kJ.g-1之间变动,所有物种的平均热值为16.90土0,84 kJ.g-1,种间变异系数4.9%。小叶锦鸡儿(Caraganamicrophylla)具有最高的热值。禾草的平均热值高于杂草。根据生活型和生长型,草本物种被进一步分组,热值从高到低的排列顺序为:高禾草>豆科植物>矮禾草>其余杂草>半灌木>一二年生植物。 主要植物种群地下部分热值的分布范围为15.05-16.41 kJ.g-1。其中根茎型草地下部分热值较高。不同种类植物地下部分热值差异并不与地上部分一致。根茎型禾草地上、地下部分热值差异较小,而须根型植物差异较大。不同种群的植物地上部分热值随植物物候期的不同而波动,其变化规律是与植物种群本身的生物学特性相联系的。不同植物种群热值的年际波动规律有所不同,羊草(Leymuschinensis)、大针茅(Stipa grandis)和洽草(Koeloria cristata)的年际热值波动相关显著,但与生长季降水量和生长季累积日照时数之间无明显相关性。在某种程度上,植物热值的种内变化反映了植物生长状况的差异。 42种植物的热值和它们在群落中的相对生物量存在显著正相关关系。表现为优势种(17.74 kJ.g-1)>伴生种(17.24 kJ.g-l)>偶见种(16.65 kJ.g-1)。高热值的植物更具竞争力,在群落中通常占据优势地位,而低热值的植物竞争力通常较弱,构成草原群落的伴生种或偶见种。 以内蒙古锡林河流域3个草原群落类型(羊草典型草原,大针茅典型草原,羊草草甸草原)的放牧退化梯度系列(包括未退化,轻度退化,中度退化和重度退化4个强度)为研究对象,对主要植物种群和群落热值随草原类型和退化梯度的空间变异规律及热值与其他群落和土壤性质的相关性进行了研究。 结果表明,研究区出现的60个植物种平均热值为17.25土0.92 kJ.g-1,变异系数5.4%.热值大于18.00 kJ.g-1的高能植物包括3种优势高禾草(羊草、大针茅和羽茅(A. sibiricum))和一些有毒植物,热值小于17.00 kJ.g-1的低能值植物包括多数一年生杂草;热值在17.00-18.00 kJ.g-1之间的中能值植物包括大多数多年生杂草和矮禾草。 按照生活型分类,灌木的热值最高,多年生禾草显著高于一二年生植物,半灌木和多年生杂草介于二者之间。按照水分生态类型分类,旱生植物、中旱生、旱中生和中生植物之间在热值上没有明显差异。不同科之间热值存在显著差异,禾本科、豆科、菊科植物热值较高,藜科植物平均热值最低。 二因素方差分析结果表明,主要优势物种热值在不同草原类型之间存在显著差异,表现为羊草草甸草原>羊草典型草原>大针茅典型草原。对于大多数优势禾草,热值没有随退化梯度发生明显变化,洽草(K. cristata)、冰草(A.ctistatum)和所有优势杂草随退化程度的增强热值趋于下降。对于大多数优势物种,热值随不同草原类型的空间变异大于放牧退化所导致的空间变异。 不同草原类型的群落热值为羊草草甸草原>羊草典型草原>大针茅典型草原,群落平均热值表现出随退化强度的增加而下降的趋势,这主要归因于沿退化梯度不同物种构成比例的变化,即随退化程度的加剧,高能值植物在群落中的比例下降。其次是特定物种热值随退化梯度的变化。在同一草原区,放牧对群落热值的影响大于立地条件之间的差异。 群落和主要物种热值均表现出与某些群落特征和土壤性质的相关性。 关键词:内蒙古,锡林河流域,羊草草原;物种和群落热值,时空变异,退化梯度,草原类型,土壤性质 第二部分内蒙古羊草草原17年刈割演替过程中功能群组成动态及其对群落净初级生产力稳定性的影响 基于17年的野外实验数据,研究了内蒙古羊草草原群落刈割演替过程中的功能群组成动态,探索功能群组成变化与群落净初级生产力(ANPP)之间的关系,分析结构参数怎样影响功能参数。结果显示:在17年的割草演替过程中,群落的结构与功能均发生了变化。随着羊草群落刈割演替的进行,群落的功能群组成发生了显著变化,根茎禾草在群落中的优势地位相继被一二年生植物,高丛生禾草,矮丛生禾草所取代。到17年末,群落变成根茎禾草,矮丛生禾草,高丛生禾草共同建群的群落。在对照群落中ANPP与年降水量显著相关,但在刈割群落中二者则不相关。年降水量解释对照群落ANPP变异的62%,而连年的刈割干扰则是刈割群落中ANPP动态的主要驱动因子。群落净初级生产则显出对刈割干扰的抵抗能力,在刈割干扰的前几年,依靠群落内功能群组成的不断调节,保持相对稳定的水平,当刈割进行5年之后,群落结构的变化积累到一定程度,净初级生产迅速下降到一个较低的水平,此后依靠群落结构的不断调节来维持这一功能水平。因此,群落结构是以渐变的方式改变的,而群落功能的下降则是以跃变的形式完成的。群落依赖于结构的不断调整来保持功能的相对稳定,但结构变化到一定程度也会导致功能的衰退。 关键词:内蒙古,羊草草原;刈割演替;功能群组成;净初级生产;群落;稳定性

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通量测量点的能量收支总是表现出不平衡,即使在地势平坦、植被分布均一、稀疏植被下垫面的情况下也有约30%的能量失衡状况。能量平衡闭合 (EBC) 问题在验证涡度相关系统质量方面,得到了广泛的关注。实验在内蒙古草原3个地点,通过涡度相关系统附近移动能量平衡系统的测定手段,采用能量平衡余项法和最小二乘 (OLS) 线性回归法,研究了土壤热通量、净辐射及可供能量空间变异对能量平衡闭合的影响。 结果显示,EBC 在三个研究点的平均余项为8~19 W m-2,OLS 斜率为0.83~0.96。EBC 在土壤湿润情况的站点要高于干旱站点。 土壤热通量的空间变异三站点平均为白天48 W m-2 (占同时间 Rn 的13%),夜间15 W m-2 (34%),平均29 W m-2 (24%)。通过8个工作站的测量,这个变异会造成9% (从0.93到1.01) 的 OLS 斜率差别。夜间的能量平衡不闭合可以由土壤热通量的空间变异解释。如果在本研究的的三个草原站点上忽略了土壤热通量,则会造成较大的余项 (峰值时110 W m-2) 产生,从而使 OLS 斜率增大23%。特别是通量板埋置在地面以下30 mm处时,上层的土壤热储部分占到全部土壤热通量的50%,这不仅影响到 EBC 的大小,更起到调节土壤热通量与“真实的波形” 相一致的作用。如果该部分热储被忽略掉,EBC 余项会增加60 W m-2,OLS 斜率也会变化 (减少) 9%。用大尺度多点测量与涡度塔附近的小尺度测定相比较,后者表现出稍高的闭合率,即 OLS 斜率增加4%。 相对于土壤热通量,净辐射的空间变异较小,三站点平均为白天17 W m-2 (5%),夜间7 W m-2 (13%),平均 12 W m-2 (5%)。可以引起3% (从0.88到0.91) 的 OLS 斜率差异。研究结果还表明,风速校正应该在 Q7.1 净辐射仪中应用,校正后的结果与 CNR1 的结果在白天有吻合较好,但在其它时段仍有较大差异,特别是在夜间,风速校正基本不起作用,使得两种仪器间差异达20 W m-2。比较表明,风速校正可以提高白天 Rn 的6%,仅降低夜间0.3%。因此,无论是用余项法还是用 OLS 线性回归法,在比较使用不同仪器的站点间的闭合状况时 (本研究的结果适用于草地 Q7.1 与 CNR1 间的比较),可以用9:00-15:00 h 时段的数据进行比较,这样可以避免因使用不同仪器的差异所造成的影响。用该时段的数据进行比较,仪器间的差异余项法小于6 W m-2,OLS 法小于3%。 受可供能量空间变异影响,三个站点平均 EBC 的不确定性为白天66 W m-2 (19%),夜间23 W m-2 (50%),平均42 W m-2 (36%);或者改变 OLS 斜率11%。用最大值和最小值来衡量,EBC 最大不确定性,正午时在站点 I、II 和 III 中分别为81,114和91 W m-2。故在探讨能量平衡和能量平衡闭合问题时,必须充分考虑到这种不确定性,否则会产生偏差,或者得出错误结论。 研究还表明,即使考虑到白天所有可供能量的最大不确定性,仍然不能使能量平衡闭合。中午 (12:00 h),站点 I,II 和 III 仍然有14±15,48±12和47±14 W m-2 的失衡不能够归因于可供能量的空间不确定性。因此,其它影响因素也需进行细致的探讨。 在两站点不同测量深度土壤热通量结果的差异性比较实验中,无论在站点 I 还是 III,均表现出一致的结论,即随通量板布置深度加深,其测量结果会越高,与浅层布置的相比,差别可高达150 W m-2。深层土壤热通量的计算仍是个难题,需进一步研究。 在不同植被结构对净辐射测定影响的实验中发现,随刈割强度增加,一天中大部分时间净辐射均减少。正午依次为413,395和388 W m-2。无论正午还是全天合计,重度刈割地点的净辐射均比不刈割对照处理少6%,而且,在整个生长季也少6%,约合40,000 W m-2。测量高度不同,不同处理间对测定结果影响不同:刈割处理中,由于下垫面较均一,结果相差不显著;而对照则表现出较高的差异,用两配对样本T检验表明差异达到极显著 (P<0.000,9:30-15:00 h data)。当使用不同新旧程度的 domes 时,对净辐射结果会产生明显的影响。新 domes 的测量结果白天明显高,晚上明显低,使用了11个月的旧 domes,峰值时,白天低估25 W m-2,晚上高估10 W m-2。说明该差异在进行能量平衡闭合计算时,不能忽略。而全用新的和全用旧的进行比较,晚上仅有2-3 W m-2差异。 考虑生态系统中非生物因子对干扰条件下生物多样性动态和功能的影响,有助于更精确地阐明生物多样性-稳定性功能的关系。为此,设计了一个单因子刈割实验——内蒙古地区一种广泛存在的土地利用方式。主要目的是研究不同强度刈割影响下,微气候变量特别是能量平衡各分量和群落结构的变化及二者的关系。连续4年刈割,占第一位的优势种明显由低矮半灌木冷蒿 (Artemisia frigida) 取代了高大丛生禾草克氏针茅 (Stipa kylovii)。重度刈割下,针茅的盖度、生物量和丛重,群落叶面积、绿色生物量、凋落物量和群落高度一致低于轻度刈割/不刈割处理。微气候由于群落特征的这些变化也呈规律性变化。与对照相比,重度刈割降低了生长季土壤含水量的47.5%,但中午和日均土壤表面温度分别增加了7.4和1.2 °C,并且增加地表下2 cm土壤温度日较差 (日最高与最低温度之差) 4.2 °C。刈割处理由于凋落物少、反射强而表现出较低的净辐射,但土壤热通量显著提高,表现为土层加热和冷却快。因此,重度刈割处理较对照降低了可供能量8%,约合52,000 W m-2 。不同刈割强度间来看,NPP 或 LAI 与土壤热通量和净辐射的比值 (G/Rn) 以及波文比 (H/LE) 间呈负相关。重度刈割处理感热通量显著提高,但潜热通量在处理间差异不显著,表明未刈割处理虽然冠层伸展大,但是并没有导致更大的水分亏缺。未刈割处理增加了抵抗物种改变的能力,而刈割处理在连续一年一割的第四年显著增加了物种数,可能与因刈割影响而导致的群落结构与微气候的改变有关。本研究表明,未刈割处理可以减轻高温干旱季节的高温和干旱胁迫,表现出对环境变化的高抵抗性。未刈割处理的凋落物层和较高的垂直结构所形成的遮荫,可以形成一个阻挡蒸发的篱笆,这是维持其水分的保证。因此,为了恢复退化草原生态系统功能,需要修复能导致微气候变化的植物群落结构,否则难以成功。 本研究立足于原创性的实验研究,在中国特有的自然草原生态系统上开展,结合不同温度梯度的三地区涡度相关系统进行了能量平衡闭合的移动比较实验,以及结合常用土地利用方式的定点能量平衡实验。在翔实的数据基础上,为涡度相关方法的陆地表面能量平衡失衡问题提供了解释。增加了对两个主要能量流——土壤热通量和净辐射空间变异规律的认识,研究对于能量平衡和湍流通量相关研究是有价值的。在三个代表性地区首次利用多个净辐射仪和土壤热通量板的结果与三个标准的涡度相关系统进行了比较,这类量化失衡原因的相关研究应受到高度重视并进一步拓展,以提高对能量失衡的认识,进而推进水热和碳循环研究向更深层次发展。

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随着温室气体的大量排放、土地利用方式的改变以及气温的逐步升高,全球变化对自然生态系统的影响也日益加强,全球变化背景下植物群落物种组成的改变能够引起整个生态系统功能的变化。本论文的研究以内蒙古多伦县十三里滩全球变化多因子实验基地为依托,研究割草、施肥、増雨以及红外加热对内蒙古温带典型草原群落物种组成的影响。本研究采用传统的植物调查方法,比较样方中所有物种和功能型的变化,最终揭示植物群落结构对上述四个处理的响应状况。 研究结果表明:氮素作为中国北方典型草原生产力的重要限制因子,增加了禾草优势物种克氏针茅和冰草的盖度,提高了禾草植物盖度和群落总盖度。施磷提高了群落中豆科植物的盖度。 种群水平上,割草提高了乳白花黄芪、苔草和冷蒿等矮小植物盖度;群落水平上,提高了群落总盖度,增加了群落的物种数。但是仅仅在施氮处理下,割草显著地影响了种群和群落水平的指标。 除了氮以外,土壤水分含量也是草原生态系统的限制因素之一。虽然不同增雨方式之间对群落的影响无显著差异,但是增雨都显著地增加了群落中禾草植物和群落的总盖度。在氮肥处理样地,增雨对禾草植物的正效应更加显著。增雨单独对群落的物种丰富度没有显著的影响。 加热减少了土壤水分含量,降低了群落物种数和群落的总盖度。加热提高了群落中非禾草杂类草的比例,降低了群落中禾草植物的比例。 总之,土壤水分和活性氮含量左右了草原植物群落的物种组成。全球变化的四个主要驱动因子正是通过影响生态系统中水分和氮的有效含量来影响群落结构。施氮和增雨降低了土壤水分和氮含量的限制,割草、加热增强了土壤水分和氮的限制。基于四个驱动因子对草原生态系统相反的作用和影响,有必要进行长期的控制实验,充分了解全球变化下,内蒙古典型草原群落物种组成的变化规律。

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自然界中资源的异质性是普遍存在的,既有自然因素导致的,也有人类干扰导致的。在内蒙古草原,植物经常处在地上部异质性的干扰生境和地下异质性的养分生境中。植物的生物量生产反映了植物对不同生境的适应能力,而资源的分配策略是链接进化生态学和功能生态学的纽带。在变化的生境中植物可以通过改变资源分配的格局而适应环境的变化,获得较高的生物产量。但是,关于草原植物在生物量生产和资源分配上如何对异质性的生境做出响应迄今研究尚少。为此在中国科学院内蒙古草原生态系统定位研究站的长期围封样地(1983年围封),设计了氮素添加和刈割处理的小区实验,使植物处于不同的养分和干扰生境中。我们选择羊草(Leymus chinensis ,根茎禾草,群落优势种)、大针茅(Stipa grandis ,丛生禾草,群落优势种)、糙隐子草(Cleistogenes squarrosa , C4 植物,群落常见伴生种)、木地肤(Kochia prostrate ,藜科半灌木,群落常见伴生种)、猪毛菜(Salsola collina,藜科一年生植物,群落常见伴生种)为对象对这一问题进行了研究。同时,以1979 年围封的羊草样地为对照,选择了比邻的刈割草场,就草原植物对长期刈割干扰的响应策略进行了研究。结果显示: 1. 氮素添加使植物群落生物量显著提高,而且高氮生境下群落生物量增加的幅度最大。从季节动态看,植物群落生物量对氮素添加的响应存在滞后现象,在植物进入快速生长期后,氮素添加的效应日趋明显。 2. 不同植物种群对氮素添加的响应不同,按照植物种群生物量的变化可以分为三种类型:极其敏感型 、敏感型和不敏感型。极其敏感型代表植物是羊草,氮素添加后其种群生物量显著增加。敏感型代表植物是糙隐子草和猪毛菜,前者种群生物量在中氮生境下显著增加,后者种群生物量在低氮生境下显著增加。不敏感型代表植物是大针茅和木地肤,氮素添加后,二者的种群生物量均无显著变化。 3.从生物量向地上和地下器官的分配来看,添加氮素后,一年生植物猪毛菜向地上器官分配的生物量的比例均显著增加;多年生草本植物羊草、大针茅和糙隐子草向地上器官分配的比例均没有发生变化;多年生灌木木地肤在中氮生境下向地上器官的分配比例增加。从生殖分配来看,多年生的C3植物羊草和大针茅和一年生的C4植物猪毛菜的生殖分配格局相对稳定,均未因氮素的添加而发生显著改变。多年生C4植物糙隐子草和木地肤在低氮生境中生殖分配比例显著增加。 4. 不同时间刈割对草原群落生物量影响不同。在牧草快速生长期刈割,群落生物量显著降低,当季能恢复,但影响翌年群落水平的生物量生产;而在牧草生物量最大期刈割,当季难恢复,但对第二年的植物的生长影响较小。 5. 刈割对不同植物的影响存在显著差异:C4植物<C3植物,一年生植物<多年生植物,牧草快速生长期刈割<牧草生物量最大期刈割。 6. 面对不同时间的刈割干扰,草原植物的响应不同。在生物量向地上器官和地下器官分配方面:C3植物大针茅、羊草面对刈割干扰生物量分配分配格局相对稳定,变异较小;而C4植物的资源分配对刈割干扰响应敏感,因不同刈割时间其生物量分配格局不同。在生物量生殖分配方面:多年生植物(如羊草、大针茅、糙隐子草、木地肤)资源分配格局相对稳定,面对刈割干扰其生物量生殖分配格局无显著变化,而一年生植物猪毛菜对刈割干扰敏感,因刈割时间不同其生殖分配格局将随之发生变化。 7.长期刈割干扰下大针茅的种群生物量维持不变;而糙隐子草的种群生物量表现为显著增长的趋势。由于大针茅的株丛生物量显著降低,糙隐子草无显著变化,长期刈割干扰下两种植物种群生物量的维持或增加都是因为密度的显著提高。因此,密度调节是两种植物实现种群调节的重要机制。 8. 长期刈割干扰下大针茅的丛面积和单株分蘖数均无显著变化,表明大针茅非生殖株丛密度的增加不是以降低单个非生殖株丛的大小为代价的,而是通过减少生殖株丛的密度来实现的。而糙隐子草丛面积降低,但是单株分蘖数无显著变化,说明糙隐子草密度增加的过程中,单个株丛占据的营养面积减少了,但株丛的生长状况没有受到显著影响。 9.面对长期刈割干扰,两种植物对无性繁殖和有性繁殖过程采取了截然相反的调整策略。大针茅显著提高了非生殖株丛的密度和相对密度,显著降低了生殖株丛的相对密度,而且降低了对有性生殖过程的生物量分配的比例。糙隐子草显著增加了生殖株丛的密度和相对密度,而且增加了对有性生殖过程的生物量分配的比例。面对刈割干扰两个植物种在繁殖策略上的逆向调节,可能是它们在刈割干扰梯度上能够相互取代的重要原因。

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我国北方温带草原地处干旱半干旱区,是欧亚大陆草原生物区系的重要组成部分,也是我国重要的畜牧业生产基地。土壤氮素作为陆地植物生长和生态系统初级生产力的主要限制因子之一,了解其矿化和可利用性对各种人为干扰因素的响应,有助于我们充分认识草地退化机理,维持草场生产力并进一步促进畜牧业的可持续发展,为草地恢复、重建和维护提供理论依据。本实验在中国科学院内蒙古草原生态系统定位研究站的多年围封退化样地,分别实施了火烧、施肥、刈割及其交互作用的人为干扰处理,利用原状土野外培养的方法,在两年时间中,研究不同的人为干扰因素(火烧、施肥、刈割及其交互处理)对土壤净氮矿化作用的影响。 火烧显著影响草原的氮循环过程,季节和年际的气候变化参与调节氮循环对火烧处理的响应。多年围封后的初次人工火烧处理显著降低了第一个生长季(2006 年生长季)和其后冬季的土壤净氮矿化速率,但是,火烧处理仅在冬季对土壤无机氮含量产生显著降低作用;2007 年生长季,火烧处理对土壤净氮矿化速率和土壤无机氮含量没有显著作用,但是在个别月份,不同的火烧频率对土壤净氮矿化速率和无机氮含量的影响表现出差异。2006 年生长季,未火烧样地和火烧样地净氮矿化积累量分别为3.07±0.26 g N m-2 和2.18±0.21 g N m-2;冬季,未火烧样地和火烧样地净氮矿化积累量分别为1.18±0.25 g N m-2 和0.51±0.08 g N m-2;2007 年生长季,未火烧样地(BC)、每年火烧样地(B1)和两年一烧样地(B2)净氮矿化积累量分别为1.32±0.21 g N m-2、0.54±0.30 g N m-2 和 0.77±0.24 g N m-2。较为湿润的2006 年生长季的净氮矿化积累量显著高于较为干旱的2007 年生长季,冬季也存在相当丰富的净氮矿化积累量。我们推论,长时间围封后的单次火烧处理对土壤净氮矿化作用的影响可能是短效的,但是年际间气候变化对土壤净氮矿化作用影响显著。 施肥显著提高了土壤的无机氮含量,并且与施肥梯度呈显著正相关关系。施肥对土壤无机氮含量的影响具有累加效应,第一次施肥和第二次施肥后的首次取样,+N5.25 、+N17.5 、+N28.0 三个施肥梯度的样地土壤无机氮含量比未施肥样地分别高出56%、219%、1054%和514%、891%、1811%。施肥处理在2006 年和2007 年对土壤净氮矿化作用都没有显著影响,仅在2007 年的个别月份有一定效果。以上结果说明,无机氮肥的添加可以明显提高土壤中无机氮的含量,满足植物生长的需求,但对于土壤氮转化过程的影响可能还要受其它环境和生物因子的制约。 刈割对土壤无机氮含量和净硝化速率没有显著作用,对土壤净氮矿化速率仅在个别月份表现显著效果。2007 年生长季,未刈割样地和刈割样地净氮矿化积累量分别为1.32±0.21 g N m-2 和1.08±0.35 g N m-2,不存在显著差异。我们推论,长期围封后的单次刈割处理在短期内对生长季的土壤氮动态仅有微弱影响,并且这种效果还可能受水分因素的制约。 火烧、施肥、刈割的交互处理在2007 年生长季对土壤无机氮含量产生显著作用,但是,对土壤净氮矿化速率和净硝化速率没有显著效果,然而,在不同的取样时间,火烧、施肥、刈割的交互处理对土壤无机氮含量、净氮矿化速率和净硝化速率的影响存在显著差异,说明火烧、施肥、刈割的交互处理对土壤无机氮和净氮矿化作用的影响可能受各种环境因子的制约,尤其是在水分相对缺乏的半干旱内蒙古草原,非生物因子和生物因子可能共同影响着土壤中的氮平衡。 本研究初步分析了长期围封后火烧、施肥、刈割及其交互处理对土壤净氮矿化的影响,初步探究了人为干扰和环境气候变化对土壤可利用性氮的调节作用,为科学地进行禁牧、割草、人工养份添加等草原管理提供了数据支持。

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Bees are believed to be in decline across many of the world's ecosystems. Recent studies on British bumblebees proposed alternative theories to explain declines. One study suggested that greater dietary specialization among the rarer bumblebee species makes them more susceptible to decline. A second study disputed this theory and found that declines in British bumblebees were correlated with the size of species' European ranges, leading to the suggestion that climate and habitat specialization may be better indicators of the risk of decline. Here we use a new and independent dataset based on Irish bumblebees to test the generality of these theories. We found that most of the same bumblebee species are declining across the British Isles, but that, within Ireland, a simple food-plant specialization model is inadequate to explain these declines. Furthermore, we found no evidence of a relationship between declines in Irish bumblebees and the size of species' European ranges. However, we demonstrate that the late emerging species have declined in Ireland (and in Britain), and that these species show a statistically significant westward shift to the extremity of their range, probably as a result of changing land use. Irish data support the finding that rare and declining bumblebees are later nesting species, associated with open grassy habitats. We suggest that the widespread replacement of hay with silage in the agricultural landscape, which results in earlier and more frequent mowing and a reduction in late summer wildflowers, has played a major role in bumblebee declines. (C) 2006 Elsevier Ltd. All rights reserved.

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Since dwarf napiergrass (Pennisetum purpureum Schumach.) must be propagated vegetatively due to lack of viable seeds, root splitting and stem cuttings are generally used to obtain true-to-type plant populations. These ordinary methods are laborious and costly, and are the greatest barriers for expanding the cultivation area of this crop. The objectives of this research were to develop nursery production of dwarf napiergrass in cell trays and to compare the efficiency of mechanical versus manual methods for cell-tray propagation and field transplanting. After defoliation of herbage either by a sickle (manually) or hand-mowing machine, every potential aerial tiller bud was cut to a single one for transplanting into cell trays as stem cuttings and placed in a glasshouse over winter. The following June, nursery plants were trimmed to a 25–cm length and transplanted in an experimental field (sandy soil) with 20,000 plants ha^(−1) either by shovel (manually) or Welsh onion planter. Labour time was recorded for each process. The manual defoliation of plants required 44% more labour time for preparing the stem cuttings (0.73 person-min. stemcutting^(−1)) compared to using hand-mowing machinery (0.51 person-min. stem-cutting^(−1)). In contrast, labour time for transplanting required an extra 0.30 person-min. m^(−2) (14%) using the machinery compared to manual transplanting, possibly due to the limited plot size for machinery operation. The transplanting method had no significant effect on plant establishment or plant growth, except for herbage yield 110 days after planting. Defoliation of herbage by machinery, production using a cell-tray nursery and mechanical transplanting reduced the labour intensity of dwarf napiergrass propagation.

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In the northeastern United States, grassland birds regularly use agricultural fields as nesting habitat. However, birds that nest in these fields regularly experience nest failure as a result of agricultural practices, such as mowing and grazing. Therefore, information on both spatial and temporal patterns of habitat use is needed to effectively manage these species. We addressed these complex habitat use patterns by conducting point counts during three time intervals between May 21, 2002 and July 2, 2002 in agricultural fields across the Champlain Valley in Vermont and New York. Early in the breeding season, Bobolinks (Dolichonyx oryzivorus) used fields in which the landscape within 2500 m was dominated by open habitats. As mowing began, suitable habitat within 500 m became more important. Savannah Sparrows (Passerculus sandwichensis) initially used fields that contained a high proportion of suitable habitat within 500 m. After mowing, features of the field (i.e., size and amount of woody edge) became more important. Each species responded differently to mowing: Savannah Sparrows were equally abundant in mowed and uncut fields, whereas Bobolinks were more abundant in uncut fields. In agricultural areas in the Northeast, large areas (2000 ha) that are mostly nonforested and undeveloped should be targeted for conservation. Within large open areas, smaller patches (80 ha) should be maintained as high-quality, late-cut grassland habitat.

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In Britain, managed grass lawns provide the most traditional and widespread of garden and landscape practices in use today. Grass lawns are coming under increasing challenge as they tend to support a low level of biodiversity and can require substantial additional inputs to maintain. Here we apply a novel approach to the traditional monocultural lawnscape by replacing grasses entirely with clonal perennial forbs. We monitored changes in plant coverage and species composition over a two year period and here we report the results of a study comparing plant origin native, non-native and mixed) and mowing regime. This allows us to assess the viability of this construct as an alternative to traditional grass lawns. Grass-free lawns provided a similar level of plant cover to grass lawns. Both the mowing regime and the combination of species used affected this outcome, with native plant species seen to have the highest survival rates, and mowing at 4cm to produce the greatest amount of ground coverage and plant species diversity within grass-free lawns. Grass-free lawns required over 50% less mowing than a traditionally managed grass lawn. Observations suggest that plant forms that exhibited: a) a relatively fast growth rate, b) a relatively large individual leaf area, and c) an average leaf height substantially above the cut to be applied, were unsuitable for use in grass-free lawns. With an equivalent level of ground coverage to grass lawns, increased plant diversity and a reduced need for mowing, the grass-free lawn can be seen as a species diverse, lower input and potentially highly ornamental alternative to the traditional lawn format.

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The grass-free lawn is a novel development in modern ornamental horticulture where the traditional monoculture of grass is replaced by a variety of mowing-tolerant clonal forbs. It brings floral aesthetics and a diverse species approach to the use of lawn space. How the number of constituent forb species affects the aesthetic and structural performance of grass-free lawns was investigated using grass-free lawns composed of four, six and twelve British native clonal perennial forb species. Lawn productivity was seen to increase with increasing species number but the relationship was not linear. Plant cover was dynamic in all lawn types, varied between years and was not representative of individual species' floral performance. The behaviour of component species common to all lawns suggested that lawns with 12 species show greater structural stability than the lawns with a lower species number. Visual performance in lawns with the greatest species number was lower than in lawns with fewer species, with increasing variety in floral size and individual species floral productivity leading to a trade-off between diversity and floral performance. Individual species were seen to have different aesthetic functions in grass-free lawns either by providing flowers, ground coverage or both.

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The integration of ecological principles into agricultural systems presents major opportunities for spreading risk at the crop and farm scale. This paper presents mechanisms by which diversity at several scales within the farming system can increase the stability of production. Diversity of above- and below-ground biota, but also genetic and phenotypic diversity within crops, has an essential role in safeguarding farm production. Novel mixtures of legume-grass leys have been shown to potentially provide significant benefits for pollinator and decomposer ecosystem services but to realise the greatest improvements carefully tailored farm management is needed such as mowing or grazing time, and the type and depth of cutivation. Complex farmland landscapes such as agroforestry systems have the potential to support pollinator abundance and diversity and spread risk across production enterprises. At the crop level, early results indicate that the vulnerability of pollen development, flowering and early grain set to abiotic stress can be ameliorated by managing flowering time through genotypic selection, and through the buffering effects of pollinators. Finally, the risk of sub-optimal quality in cereals can be mitigated through integration of near isogenic lines selected to escape specific abiotic stress events. We conclude that genotypic, phenotypic and community diversity can all be increased at multiple scales to enhance resilience in agricultural systems.

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Insect diversity may be declining even more rapidly than in plants and vertebrates, particularly in areas where indigenous habitats are replaced by an anthropogenic one. The most common component of anthropogenic greenspace is the ornamental lawn. Intensively managed and offering limited habitat opportunities for both plants and insects, lawns are biodiversity poor and ecologically insensitive. An alternative lawn format that positively influences biodiversity and reduces management requirements would be a useful tool in eco-friendly urban greenspace management. In investigating the potential for a forb-only alternative to the grass lawn we sampled both trial grass-free lawn formats and turf lawns to identify any influence that lawn composition and grass-free lawn specific mowing regimes might have on the abundance and diversity of insect families. In addition to the mowing regimes, both the composition and origin of lawn flora were found to significantly influence insect abundance and diversity and these factors rarely interacted. Native-only and mixed origin grass-free lawns hosted greater numbers of adult insects than found in turf and an equivalent diversity of insect families, however the mowing regime applied was distinct from traditional turf lawn management by being substantially less intensive and our results suggest that there is the potential for even greater abundance and diversity via the grass-free format that may offer additional resources to insectivorous garden species such as birds. When the composition of grass-free lawns included native forbs the diversity of insect families was found be sufficiently different from turf lawns to form distinct assemblages and in so doing contribute to beta diversity within urban greenspace. In sum, grass-free lawns may be a useful and aesthetically appropriate tool for adding value to the generally biodiversity poor urban lawnscape.

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Landscape scale habitat restoration has the potential to reconnect habitats in fragmented landscapes. This study investigates landscape connectivity as a key to effective habitat restoration in lowland agricultural landscapes and applies these findings to transferable management recommendations. The study area is the Stonehenge World Heritage Site, UK, where landscape scale chalk grassland restoration has been implemented. Here, the ecological benefits of landscape restoration and the species, habitat and landscape characteristics that facilitate or impede the enhancement of biodiversity and landscape connectivity were investigated. Lepidoptera were used as indictors of restoration success and results showed restoration grasslands approaching the ecological conditions of the target chalk grassland habitat and increasing in biodiversity values within a decade. Restoration success is apparent for four species with a broad range of grass larval host plants (e.g. Melanargia galathea, Maniola jurtina) or with intermediate mobility (Polyommatus icarus). However, two species with specialist larval host plants and low mobility (Lysandra bellargus), are restricted to chalk grassland fragments. Studies of restoration grassland of different ages show that recent grassland restoration (1 or 2 years old) may reduce the functional isolation of chalk grassland fragments. A management experiment showed that mowing increases boundary following behaviour in two species of grassland Lepidoptera; Maniola jurtina and Zygaena filipendulae. Analysis of the landscape scale implications of the grassland restoration illustrates an increase in grassland habitat network size and in landscape connectivity, which is likely to benefit the majority of grassland associated Lepidoptera. Landscape and habitat variables can be managed to increase the success of restoration projects including the spatial targeting of receptor sites, vegetation structure and selection of seed source and management recommendations are provided that are transferrable to other species-rich grassland landscape scale restoration projects. Overall results show restoration success for some habitats and species within a decade. However, additional management is required to assist the re-colonisation of specialist species. Despite this, habitat restoration at the landscape scale can be an effective, long term approach to enhance butterfly biodiversity and landscape connectivity.