
生物多样性 ›› 2011, Vol. 19 ›› Issue (4): 441-452. DOI: 10.3724/SP.J.1003.2011.12287 cstr: 32101.14.SP.J.1003.2011.12287
所属专题: 昆虫多样性与生态功能
娄巧哲1,2, 徐养诚1,3, 马吉宏1,2, 吕昭智1,*(
)
收稿日期:2010-12-02
接受日期:2011-04-14
出版日期:2011-07-20
发布日期:2011-07-29
通讯作者:
吕昭智
作者简介:* E-mail: zhaozhi@ms.xjb.ac.cn基金资助:
Qiaozhe Lou1,2, Yangcheng Xu1,3, Jihong Ma1,2, Zhaozhi Lü1,*(
)
Received:2010-12-02
Accepted:2011-04-14
Online:2011-07-20
Published:2011-07-29
Contact:
Zhaozhi Lü
摘要:
为了解荒漠地表甲虫的多样性特点及其与环境的关系, 明确其环境指示作用, 评估沙漠工程对荒漠地表甲虫多样性的影响, 作者于2010年5-7月采用陷阱法调查了古尔班通古特沙漠南缘从沙漠腹地到沙漠绿洲交错区不同生境的地表甲虫物种多样性, 其中包括沙漠腹地公路防护体系的干扰生境。结果如下: (1)共捕获地表甲虫54,527头, 隶属于14科81种, 其中拟步甲科和象甲科占绝对优势, 数量分别占到93.65%和5.14%; 拟步甲科在沙漠腹地的活动密度远大于交错区, 而在交错区象甲科种类最多, 活动密度也最大; 漠王属(Platyope)的种类均表现出明显的风沙土的倾向性, 而阿苇长足甲(Adesmia aweiensis)和光滑胖漠甲(Trigonoscelis sublaevigata sublaevigata)则表现出明显的碱化灰漠土的倾向性; (2)不同生境间的丰富度、多样性指数、均匀度指数、优势度指数、活动密度总体上均具有显著性差异(df = 32, P<0.05); (3)分别基于地表甲虫群落与优势类群的生境除趋势对应分析(DCA排序)均表明, 沙漠边缘在研究区域中处于中间过渡地位, 坡上生境更接近沙漠腹地, 垄间更接近交错区; (4)荒漠地表甲虫群落的物种丰富度、多样性指数、均匀度指数、优势度指数与植被盖度、土壤含水量、有机质含量及全N、全P含量均存在显著线性相关(P<0.05), 其中与土壤含水量的相关性最好, 活动密度与所有环境因子的相关性最差, 且为负相关; (5)沙漠公路防护体系中的地表甲虫活动密度显著降低, 物种丰富度、多样性及均匀性均有所下降, 但没有达到显著性水平; 主要种的相对重要值也有较大变化。结论如下: 荒漠地表甲虫的多样性特点为丰富度低、多样性低、均匀度差, 但优势度高、活动密度高, 并且这一特点随着生境从荒漠绿洲交错区到沙漠腹地越趋明显; 荒漠地表甲虫在科、属与种的水平上均表现了一定的环境指示作用; 土壤类型在群落排序中起着主要作用; 活动密度与土壤含水量的负相关关系可能是局域尺度下荒漠地表甲虫多样性的一般性规律; 工程干扰对沙漠腹地的地表甲虫群落产生了一定的影响, 草方格、梭梭(Haloxylon ammodendron)、沙拐枣(Calligonum sp.)等人工植被可能是导致这一影响的主要因素。
娄巧哲, 徐养诚, 马吉宏, 吕昭智 (2011) 古尔班通古特沙漠南缘地表甲虫物种多样性及其与环境的关系. 生物多样性, 19, 441-452. DOI: 10.3724/SP.J.1003.2011.12287.
Qiaozhe Lou, Yangcheng Xu, Jihong Ma, Zhaozhi Lü (2011) Diversity of ground-dwelling beetles within the southern Gurbantunggut Desert and its relationship with environmental factors. Biodiversity Science, 19, 441-452. DOI: 10.3724/SP.J.1003.2011.12287.
图1 古尔班通古特沙漠南缘研究样地及陷阱布设示意图(地图仿自王雪芹和雷加强, 1998)。A: 沙漠腹地自然生境; B: 沙漠腹地干扰生境; C: 沙漠边缘自然生境; D: 沙漠绿洲交错区自然生境; AS, AN, AL: 沙丘的阳面、阴面和垄间; BNN, BNS, BSN, BSS: 沙丘背路面阴面、沙丘向路面阳面、沙丘向路面阴面和沙丘背路面阳面, 其中背路面仅为草方格机械固沙, 向路面为草方格+植被复合固沙; CS, CN, CL: 沙丘的阳面、阴面和垄间; DL: 平地。
Fig. 1 The sites of insect investigation on southern Gurbantunggut Desert and the distribution of traps within different plots. A, Natural habitat in desert hinterland; B, Disturbed habitat in desert hinterland; C, Natural habitat on desert edge; D, Natural habitat on desert-oasis ecotone; AS, AN, AL, Sunny slope of dune in A, Shady slope of dune in A, Interdune in A; BNN, BNS, BSN, BSS, Shady and outerside of dune in B, Sunny and interside of dune in B, Shady and interside of dune in B, Sunny and outerside in B; CS, CN, CL, Sunny slope of dune in C, Shady slope of dune in C, Interdune in C; DL, Flat land in D.
| 地点 Sites | 样地数 No. of plots | 小生境 Micro- habitat | 经度 Longitude (E) | 纬度 Latitude (N) | 海拔 Elevation (m) | 生境类型 Habitat type | 土壤类型 Soil type | 植被类型 Vegetation type |
|---|---|---|---|---|---|---|---|---|
| 沙漠腹地自然生境 Natural hinterland | 9 | AS | 88°19'41.2" | 44°30'58.4" | 515 | 偏东南走向的纵向半固定自然沙丘。 Natural semi-fixed longitudinal dune with a deviation to southeast. | 全部为风沙土, 土壤含水量很低。 Aeolian sandy soil with a lower soil water content. | 沙丘上主要为白梭梭群系; 垄间主要为蛇麻黄群系, 且生物结皮发育良好。 Haloxylon persicum community on dune, and Ephedra distachya community with well-developed biological crust on interdune. |
| AN | 88°19'41.9" | 44°31'00.0" | 513 | |||||
| AL | 88°19'40.5" | 44°30'57.2" | 508 | |||||
| AS | 88°18'01.1" | 44°32'26.2" | 526 | |||||
| AN | 88°18'02.4" | 44°32'27.4" | 525 | |||||
| AL | 88°18'03.4" | 44°32'28.8" | 519 | |||||
| AS | 88°18'05.0" | 44°32'22.8" | 524 | |||||
| AN | 88°18'06.1" | 44°32'23.8" | 520 | |||||
| AL | 88°18'08.4" | 44°32'25.4" | 515 | |||||
| 沙漠腹地干扰生境 Disturbed hinterland | 12 | BNN | 88°19'46.1" | 44°31'07.6" | 532 | 偏东南走向的横向半固定扰动沙丘。 Disturbed semi-fixed horizontal dune with a deviation to southeast. | 全部为风沙土, 土壤含水量很低。 Aeolian sandy soil with a lower soil water content. | 背路面有草方格固沙, 有一定草本植物入侵, 向路面除草方格固沙, 人工种植有梭梭和沙拐枣。 Just straw barrier on outside of dune, with a certain amount of invasive plant, while straw barrier with artificial plant (H. ammodendron and Calligonum sp.) on interside of dune. |
| BNS | 88°19'44.7" | 44°31'06.2" | 532 | |||||
| BSN | 88°19'42.4" | 44°31'03.5" | 517 | |||||
| BSS | 88°19'40.1" | 44°31'01.5" | 520 | |||||
| BNN | 88°17'55.8" | 44°32'18.8" | 525 | |||||
| BNS | 88°17'54.6" | 44°32'16.4" | 530 | |||||
| BSN | 88°17'59.1" | 44°32'09.9" | 518 | |||||
| BSS | 88°17'57.3" | 44°32'05.6" | 519 | |||||
| BNN | 88°17'52.2" | 44°32'19.2" | 532 | |||||
| BNS | 88°17'53.2" | 44°32'17.8" | 525 | |||||
| BSN | 88°17'50.4" | 44°32'12.0" | 530 | |||||
| BSS | 88°17'52.2" | 44°32'06.6" | 324 | |||||
| 沙漠边缘自然生境 Natural desert edge | 9 | CS | 87°51'50.5" | 44°24'16.1" | 429 | 偏东南走向的纵向半固定自然沙丘。 Natural semi-fixed longitudinal dune with a deviation to southeast. | 沙丘上为含水量较低的风沙土, 垄间为含水量较高的碱化灰漠土。 Aeolian sandy soil on dune, while alkaline desert soil on interdune. | 沙丘上主要为白梭梭群系; 垄间主要为梭梭群系, 且短命植物发育良好。 H. persicum community on dune while H. ammodendron community with well-developed ephemeral on interdune. |
| CN | 87°51'53.0" | 44°24'16.2" | 432 | |||||
| CL | 87°51'45.7" | 44°24'16.0" | 427 | |||||
| CS | 87°51'36.1" | 44°24'09.3" | 433 | |||||
| CN | 87°51'38.3" | 44°24'09.2" | 431 | |||||
| CL | 87°51'33.4" | 44°24'10.0" | 430 | |||||
| CS | 87°51'49.4" | 44°24'03.2" | 437 | |||||
| CN | 87°51'51.2" | 44°24'03.9" | 434 | |||||
| CL | 87°51'47.0" | 44°24'02.1" | 431 | |||||
| 交错区自然生境 Natural ecotone | 3 | DL | 88°08'18.6" | 44°21'19.9" | 484 | 平地 Flat land | 全部为碱化灰漠土, 含水量最高。 Alkaline desert soil, with a higher soil water content. | 主要为梭梭-红砂-草本群系。 H. ammodendron, Reaumuria songarica and herbal community. |
| DL | 88°08'19.2" | 44°21'16.7" | 486 | |||||
| DL | 88°08'09.7" | 44°21'09.7" | 482 |
表1 古尔班通古特沙漠南缘研究样地的地理位置、土壤特性及植被特征
Table 1 The geographical position, soil characteristics and vegetation type of plots on southern Gurbantunggut Desert
| 地点 Sites | 样地数 No. of plots | 小生境 Micro- habitat | 经度 Longitude (E) | 纬度 Latitude (N) | 海拔 Elevation (m) | 生境类型 Habitat type | 土壤类型 Soil type | 植被类型 Vegetation type |
|---|---|---|---|---|---|---|---|---|
| 沙漠腹地自然生境 Natural hinterland | 9 | AS | 88°19'41.2" | 44°30'58.4" | 515 | 偏东南走向的纵向半固定自然沙丘。 Natural semi-fixed longitudinal dune with a deviation to southeast. | 全部为风沙土, 土壤含水量很低。 Aeolian sandy soil with a lower soil water content. | 沙丘上主要为白梭梭群系; 垄间主要为蛇麻黄群系, 且生物结皮发育良好。 Haloxylon persicum community on dune, and Ephedra distachya community with well-developed biological crust on interdune. |
| AN | 88°19'41.9" | 44°31'00.0" | 513 | |||||
| AL | 88°19'40.5" | 44°30'57.2" | 508 | |||||
| AS | 88°18'01.1" | 44°32'26.2" | 526 | |||||
| AN | 88°18'02.4" | 44°32'27.4" | 525 | |||||
| AL | 88°18'03.4" | 44°32'28.8" | 519 | |||||
| AS | 88°18'05.0" | 44°32'22.8" | 524 | |||||
| AN | 88°18'06.1" | 44°32'23.8" | 520 | |||||
| AL | 88°18'08.4" | 44°32'25.4" | 515 | |||||
| 沙漠腹地干扰生境 Disturbed hinterland | 12 | BNN | 88°19'46.1" | 44°31'07.6" | 532 | 偏东南走向的横向半固定扰动沙丘。 Disturbed semi-fixed horizontal dune with a deviation to southeast. | 全部为风沙土, 土壤含水量很低。 Aeolian sandy soil with a lower soil water content. | 背路面有草方格固沙, 有一定草本植物入侵, 向路面除草方格固沙, 人工种植有梭梭和沙拐枣。 Just straw barrier on outside of dune, with a certain amount of invasive plant, while straw barrier with artificial plant (H. ammodendron and Calligonum sp.) on interside of dune. |
| BNS | 88°19'44.7" | 44°31'06.2" | 532 | |||||
| BSN | 88°19'42.4" | 44°31'03.5" | 517 | |||||
| BSS | 88°19'40.1" | 44°31'01.5" | 520 | |||||
| BNN | 88°17'55.8" | 44°32'18.8" | 525 | |||||
| BNS | 88°17'54.6" | 44°32'16.4" | 530 | |||||
| BSN | 88°17'59.1" | 44°32'09.9" | 518 | |||||
| BSS | 88°17'57.3" | 44°32'05.6" | 519 | |||||
| BNN | 88°17'52.2" | 44°32'19.2" | 532 | |||||
| BNS | 88°17'53.2" | 44°32'17.8" | 525 | |||||
| BSN | 88°17'50.4" | 44°32'12.0" | 530 | |||||
| BSS | 88°17'52.2" | 44°32'06.6" | 324 | |||||
| 沙漠边缘自然生境 Natural desert edge | 9 | CS | 87°51'50.5" | 44°24'16.1" | 429 | 偏东南走向的纵向半固定自然沙丘。 Natural semi-fixed longitudinal dune with a deviation to southeast. | 沙丘上为含水量较低的风沙土, 垄间为含水量较高的碱化灰漠土。 Aeolian sandy soil on dune, while alkaline desert soil on interdune. | 沙丘上主要为白梭梭群系; 垄间主要为梭梭群系, 且短命植物发育良好。 H. persicum community on dune while H. ammodendron community with well-developed ephemeral on interdune. |
| CN | 87°51'53.0" | 44°24'16.2" | 432 | |||||
| CL | 87°51'45.7" | 44°24'16.0" | 427 | |||||
| CS | 87°51'36.1" | 44°24'09.3" | 433 | |||||
| CN | 87°51'38.3" | 44°24'09.2" | 431 | |||||
| CL | 87°51'33.4" | 44°24'10.0" | 430 | |||||
| CS | 87°51'49.4" | 44°24'03.2" | 437 | |||||
| CN | 87°51'51.2" | 44°24'03.9" | 434 | |||||
| CL | 87°51'47.0" | 44°24'02.1" | 431 | |||||
| 交错区自然生境 Natural ecotone | 3 | DL | 88°08'18.6" | 44°21'19.9" | 484 | 平地 Flat land | 全部为碱化灰漠土, 含水量最高。 Alkaline desert soil, with a higher soil water content. | 主要为梭梭-红砂-草本群系。 H. ammodendron, Reaumuria songarica and herbal community. |
| DL | 88°08'19.2" | 44°21'16.7" | 486 | |||||
| DL | 88°08'09.7" | 44°21'09.7" | 482 |
| 科 Family | 沙漠腹地自然生境 Natural hinterland | 沙漠腹地干扰生境 Disturbed hinterland | 沙漠边缘自然生境 Natural desert edge | 交错区自然生境 Natural ecotone | 合计 Total | 百分比 (%) | ||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| AS | AN | AL | BNN | BNS | BSN | BSS | CS | CN | CL | DL | ||||||
| 拟步甲科 Tenebrionidae | 7,881 | 5,191 | 5,440 | 4,979 | 4,438 | 3,730 | 4,613 | 4,848 | 5,233 | 3,334 | 1,375 | 51,062 | 93.65 | |||
| 象甲科 Curculionidae | 59 | 48 | 100 | 106 | 109 | 253 | 77 | 124 | 96 | 107 | 1,721 | 2,800 | 5.14 | |||
| 金龟科 Scarabaeidae | 17 | 19 | 70 | 3 | 2 | 5 | 16 | 14 | 15 | 15 | 8 | 184 | 0.34 | |||
| 步甲科 Carabidae | 14 | 35 | 46 | 10 | 11 | 8 | 8 | 4 | 11 | 9 | 14 | 170 | 0.31 | |||
| 葬甲科 Silphidae | 4 | 13 | 10 | 6 | 14 | 12 | 11 | 6 | 2 | 4 | 10 | 92 | 0.17 | |||
| 芫菁科 Meloidae | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 3 | 13 | 45 | 65 | 0.12 | |||
| 阎甲科 Histeridae | 3 | 4 | 6 | 0 | 0 | 2 | 1 | 34 | 8 | 5 | 2 | 65 | 0.12 | |||
| 隐翅虫科 Staphylinidae | 16 | 14 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 0 | 33 | 0.06 | |||
| 吉丁科 Buprestidae | 2 | 11 | 0 | 0 | 1 | 1 | 2 | 1 | 0 | 0 | 5 | 23 | 0.04 | |||
| 丽金龟科 Rutelidae | 2 | 3 | 0 | 5 | 3 | 3 | 3 | 0 | 0 | 0 | 0 | 19 | 0.03 | |||
| 花金龟科 Cetoniidae | 0 | 1 | 0 | 0 | 4 | 0 | 5 | 0 | 0 | 0 | 0 | 10 | 0.02 | |||
| 叩甲科 Elateridae | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 2 | 0.00 | |||
| 犀金龟科 Dynastidae | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0.00 | |||
| 皮蠹科 Dermestidae | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0.00 | |||
| 合计 Total | 7,998 | 5,339 | 5,673 | 5,109 | 4,583 | 4,014 | 4,739 | 5,035 | 5,368 | 3,487 | 3,182 | 54,527 | 100.00 | |||
表2 古尔班通古特沙漠南缘不同生境地表甲虫群落的科组成和数量分布(2010年5-7月)
Table 2 The family composition and number of individuals of different ground-dwelling beetle communities in southern Gurbantunggut Desert (collected from May to July, 2010)
| 科 Family | 沙漠腹地自然生境 Natural hinterland | 沙漠腹地干扰生境 Disturbed hinterland | 沙漠边缘自然生境 Natural desert edge | 交错区自然生境 Natural ecotone | 合计 Total | 百分比 (%) | ||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| AS | AN | AL | BNN | BNS | BSN | BSS | CS | CN | CL | DL | ||||||
| 拟步甲科 Tenebrionidae | 7,881 | 5,191 | 5,440 | 4,979 | 4,438 | 3,730 | 4,613 | 4,848 | 5,233 | 3,334 | 1,375 | 51,062 | 93.65 | |||
| 象甲科 Curculionidae | 59 | 48 | 100 | 106 | 109 | 253 | 77 | 124 | 96 | 107 | 1,721 | 2,800 | 5.14 | |||
| 金龟科 Scarabaeidae | 17 | 19 | 70 | 3 | 2 | 5 | 16 | 14 | 15 | 15 | 8 | 184 | 0.34 | |||
| 步甲科 Carabidae | 14 | 35 | 46 | 10 | 11 | 8 | 8 | 4 | 11 | 9 | 14 | 170 | 0.31 | |||
| 葬甲科 Silphidae | 4 | 13 | 10 | 6 | 14 | 12 | 11 | 6 | 2 | 4 | 10 | 92 | 0.17 | |||
| 芫菁科 Meloidae | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 4 | 3 | 13 | 45 | 65 | 0.12 | |||
| 阎甲科 Histeridae | 3 | 4 | 6 | 0 | 0 | 2 | 1 | 34 | 8 | 5 | 2 | 65 | 0.12 | |||
| 隐翅虫科 Staphylinidae | 16 | 14 | 0 | 0 | 0 | 0 | 3 | 0 | 0 | 0 | 0 | 33 | 0.06 | |||
| 吉丁科 Buprestidae | 2 | 11 | 0 | 0 | 1 | 1 | 2 | 1 | 0 | 0 | 5 | 23 | 0.04 | |||
| 丽金龟科 Rutelidae | 2 | 3 | 0 | 5 | 3 | 3 | 3 | 0 | 0 | 0 | 0 | 19 | 0.03 | |||
| 花金龟科 Cetoniidae | 0 | 1 | 0 | 0 | 4 | 0 | 5 | 0 | 0 | 0 | 0 | 10 | 0.02 | |||
| 叩甲科 Elateridae | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 2 | 2 | 0.00 | |||
| 犀金龟科 Dynastidae | 0 | 0 | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0.00 | |||
| 皮蠹科 Dermestidae | 0 | 0 | 1 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 1 | 0.00 | |||
| 合计 Total | 7,998 | 5,339 | 5,673 | 5,109 | 4,583 | 4,014 | 4,739 | 5,035 | 5,368 | 3,487 | 3,182 | 54,527 | 100.00 | |||
| 物种 Species | 沙漠腹地自然生境 Natural hinterland | 沙漠腹地干扰生境 Disturbed hinterland | 沙漠边缘自然生境 Natural desert edge | 交错区自然生境 Natural ecotone |
|---|---|---|---|---|
| 中华漠王 Platyope proctoleuca chinensis | 55 | 55 | - | |
| 库氏东鳖甲 Anatolica kulzeri | 22 | 32 | 49 | - |
| 宽颈小鳖甲 Microdera laticollis | 11 | 3 | 9 | - |
| 维氏漠王 Platyope victori | 4 | 3 | - | |
| 戈壁琵甲 Blaps gobiensis | 3 | 2 | 4 | - |
| 列氏浑圆象 Epexochus lehmanni | - | 2 | - | |
| 漠王未定种 Platyope sp. | 19 | - | ||
| 阿苇长足甲 Adesmia aweiensis | 9 | 24 | ||
| 三北甜菜象 Bothynoderes securus | - | - | 16 | |
| 光滑胖漠甲 Trigonoscelis sublaevigata sublaevigata | - | - | 4 | 14 |
| 黑斑齿足象 Deracanthus grumi | - | - | 10 | |
| 筒喙象未定种 Lixus sp. | 8 | |||
| 甜菜象未定种1 Bothynoderes sp.1 | 8 | |||
| 黄褐纤毛象 Tanymecus urbanus | - | - | - | 4 |
| 甜菜象未定种2 Bothynoderes sp.2 | - | - | - | 3 |
表3 不同生境地表甲虫群落主要种的相对重要值(%)
Table 3 Index of relative importance (% of total specimens) of main species in different habitats
| 物种 Species | 沙漠腹地自然生境 Natural hinterland | 沙漠腹地干扰生境 Disturbed hinterland | 沙漠边缘自然生境 Natural desert edge | 交错区自然生境 Natural ecotone |
|---|---|---|---|---|
| 中华漠王 Platyope proctoleuca chinensis | 55 | 55 | - | |
| 库氏东鳖甲 Anatolica kulzeri | 22 | 32 | 49 | - |
| 宽颈小鳖甲 Microdera laticollis | 11 | 3 | 9 | - |
| 维氏漠王 Platyope victori | 4 | 3 | - | |
| 戈壁琵甲 Blaps gobiensis | 3 | 2 | 4 | - |
| 列氏浑圆象 Epexochus lehmanni | - | 2 | - | |
| 漠王未定种 Platyope sp. | 19 | - | ||
| 阿苇长足甲 Adesmia aweiensis | 9 | 24 | ||
| 三北甜菜象 Bothynoderes securus | - | - | 16 | |
| 光滑胖漠甲 Trigonoscelis sublaevigata sublaevigata | - | - | 4 | 14 |
| 黑斑齿足象 Deracanthus grumi | - | - | 10 | |
| 筒喙象未定种 Lixus sp. | 8 | |||
| 甜菜象未定种1 Bothynoderes sp.1 | 8 | |||
| 黄褐纤毛象 Tanymecus urbanus | - | - | - | 4 |
| 甜菜象未定种2 Bothynoderes sp.2 | - | - | - | 3 |
图2 不同生境地表甲虫群落(a)及最优势类群(b)的相对重要性-物种序列曲线
Fig. 2 Relative Importance-Species Rank curves of the different ground-dwelling beetle communities (a) and the most dominant beetle groups (b).
| 生境类型 Habitat type | 活动密度(AD) Activity density | 物种丰富度(S) Species richness | 多样性指数(H') Diversity index | 均匀度指数(J) Evenness index | 优势度指数(D) Dominance index |
|---|---|---|---|---|---|
| 沙漠腹地自然生境 Natural hinterland | 34.6 ± 3.9b | 19.6 ± 1.1a | 1.33 ± 0.04a | 0.45 ± 0.01a | 0.37 ± 0.02bc |
| 沙漠腹地干扰生境 Disturbed hinterland | 25.2 ± 2.4a | 17.5 ± 0.7a | 1.18 ± 0.04a | 0.41 ± 0.01a | 0.43 ± 0.02c |
| 沙漠边缘自然生境 Natural desert edge | 25.3 ± 1.8a | 25.1 ± 1.4b | 1.62 ± 0.09b | 0.50 ± 0.02b | 0.31 ± 0.03b |
| 交错区自然生境 Natural ecotone | 17.4 ± 1.9a | 36.7 ± 2.2c | 2.34 ± 0.06c | 0.65 ± 0.01c | 0.15 ± 0.01a |
表4 古尔班通古特沙漠南缘不同生境地表甲虫群落的活动密度、物种丰富度及物种多样性比较(平均值±标准误)
Table 4 Activity density, species richness and diversity indices of ground-dwelling beetle communities in different habitats in southern Gurbantunggut Desert (Mean ± SE)
| 生境类型 Habitat type | 活动密度(AD) Activity density | 物种丰富度(S) Species richness | 多样性指数(H') Diversity index | 均匀度指数(J) Evenness index | 优势度指数(D) Dominance index |
|---|---|---|---|---|---|
| 沙漠腹地自然生境 Natural hinterland | 34.6 ± 3.9b | 19.6 ± 1.1a | 1.33 ± 0.04a | 0.45 ± 0.01a | 0.37 ± 0.02bc |
| 沙漠腹地干扰生境 Disturbed hinterland | 25.2 ± 2.4a | 17.5 ± 0.7a | 1.18 ± 0.04a | 0.41 ± 0.01a | 0.43 ± 0.02c |
| 沙漠边缘自然生境 Natural desert edge | 25.3 ± 1.8a | 25.1 ± 1.4b | 1.62 ± 0.09b | 0.50 ± 0.02b | 0.31 ± 0.03b |
| 交错区自然生境 Natural ecotone | 17.4 ± 1.9a | 36.7 ± 2.2c | 2.34 ± 0.06c | 0.65 ± 0.01c | 0.15 ± 0.01a |
图3 古尔班通古特沙漠南缘不同生境地表甲虫群落及优势类群的除趋势对应分析(DCA)。: AS, AN and AL;: BNN, BNS, BSN and BSS;: CS, CN and CL。字母所代表的样地同图1。
Fig. 3 Detrended correspondence analysis (DCA) ordination performed on ground-dwelling beetle communities or Tenebrionidae or Curculionidae in 33 sampling sites in southern Gurbantunggut Desert. AS, AN and AL; BNN, BNS, BSN and SS; CS, CN and CL. The labels are given in Fig. 1.
| 土壤含水量 Soil water content | 土壤有机质含量 Soil nutrient content | 土壤全氮含量 Soil total N content | 土壤全磷含量 Soil total P content | 植被盖度 Vegetation coverage | |
|---|---|---|---|---|---|
| 物种丰富度 Species richness | 0.93** | 0.64* | 0.71* | 0.81** | 0.84** |
| 活动密度 Activity density | -0.63* | -0.54 | -0.56 | -0.66* | -0.75** |
| 优势度指数 Dominance index | -0.93** | -0.76** | -0.80** | -0.90** | -0.89** |
| 物种多样性指数 Diversity index | 0.97** | 0.71* | 0.78** | 0.92** | 0.89** |
| 均匀度指数 Evenness index | 0.96** | 0.72* | 0.78** | 0.92** | 0.88** |
表5 古尔班通古特沙漠南缘不同生境地表甲虫群落特征值与环境因子的相关性分析(Pearson线性相关性系数r)
Table 5 Correlation analysis of community characters and environmental factors in different habitats in southern Gurbantunggut Desert (Pearson’s r)
| 土壤含水量 Soil water content | 土壤有机质含量 Soil nutrient content | 土壤全氮含量 Soil total N content | 土壤全磷含量 Soil total P content | 植被盖度 Vegetation coverage | |
|---|---|---|---|---|---|
| 物种丰富度 Species richness | 0.93** | 0.64* | 0.71* | 0.81** | 0.84** |
| 活动密度 Activity density | -0.63* | -0.54 | -0.56 | -0.66* | -0.75** |
| 优势度指数 Dominance index | -0.93** | -0.76** | -0.80** | -0.90** | -0.89** |
| 物种多样性指数 Diversity index | 0.97** | 0.71* | 0.78** | 0.92** | 0.89** |
| 均匀度指数 Evenness index | 0.96** | 0.72* | 0.78** | 0.92** | 0.88** |
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