干旱区研究 ›› 2025, Vol. 42 ›› Issue (11): 2071-2082.doi: 10.13866/j.azr.2025.11.10
王理德1,2,3(
), 李浩3, 何静3(
), 陈思航1, 王景瑞1,2, 李诗涵3, 司静怡3
收稿日期:2025-04-24
修回日期:2025-09-01
出版日期:2025-11-15
发布日期:2025-12-13
通讯作者:
何静. E-mail: hejing268@aliyun.com作者简介:王理德(1969-),男,博士,研究员,主要从事生物多样性及水土保持与荒漠化防治研究. E-mail: 460025211@qq.com
基金资助:
WANG Lide1,2,3(
), LI Hao3, HE Jing3(
), CHEN Sihang1, WANG Jingrui1,2, LI Shihan3, SI Jingyi3
Received:2025-04-24
Revised:2025-09-01
Published:2025-11-15
Online:2025-12-13
摘要: 为探究双龙沟矸石山不同修复年限人工沙棘林地植物物种多样性及土壤养分的变化规律。以修复3 a、6 a和11 a人工沙棘林地为研究对象,并以未修复的矸石荒山为对照(CK),通过实地调查植被生长情况与土壤养分测定,采用时空替代法探究植物-土壤间的相关性。结果表明:(1) 在修复过程中,样地内出现24科48属65种植物,其中菊科植物占比最大。(2) 随修复年限增加,植物个体数量、物种数、Simpson优势度指数和Margalef丰富度指数整体呈现上升趋势,在修复11 a样地达到最大值,分别为1234株、34种、0.277和3.213; Pielou均匀度指数与Shannon多样性指数整体呈下降趋势。(3) 随土层加深,土壤全氮、全磷、有机质、铵态氮和速效磷显著降低,表聚现象突出;随修复年限延长,全磷、硝态氮和铵态氮含量显著提升。(4) 植物物种多样性与土壤养分密切相关,植物个体数与硝态氮、铵态氮呈极显著正相关,与速效磷呈极显著负相关;植物物种数与土壤pH、全磷、硝态氮、铵态氮呈极显著正相关。Simpson优势度、Margalef丰富度与全磷、硝态氮、铵态氮显著正相关,Pielou均匀度则与速效磷显著正相关,表明土壤全磷、硝态氮、铵态氮和速效磷是影响该区域植物物种多样性的关键养分因子。随着人工修复年限延长,显著提升了双龙沟矸石山地植物物种多样性和土壤养分含量,为废弃矿区生态系统的恢复提供科学依据。
王理德, 李浩, 何静, 陈思航, 王景瑞, 李诗涵, 司静怡. 人工沙棘林地物种多样性及土壤养分变化——以双龙沟矸石山为例[J]. 干旱区研究, 2025, 42(11): 2071-2082.
WANG Lide, LI Hao, HE Jing, CHEN Sihang, WANG Jingrui, LI Shihan, SI Jingyi. Plant species diversity and soil nutrient alter characteristics of artificial Hippophae rhamnoides forests with different restoration years: A case study of Shuanglonggou Gangue Mountain[J]. Arid Zone Research, 2025, 42(11): 2071-2082.
表1
不同修复年限人工沙棘林地样地基本状况"
| 样地编号 | 修复年限/a | 海拔/m | 纬度 | 经度 | 群落优势种 |
|---|---|---|---|---|---|
| CK-1 | 0 | 3113 | 37°22′14″N | 102°22′54″E | 砾地毛茛(Ranunculus glareosus)、臭蒿(Artemisia hedinii)、车前(Plantago asiatica)、沼生繁缕(Stellaria palustris) |
| CK-2 | 0 | 3050 | 37°22′17″N | 102°22′53″E | |
| CK-3 | 0 | 3052 | 37°22′13″N | 102°22′7″E | |
| 3 a-1 | 3 | 3048 | 37°22′16″N | 102°23′9″E | 猪毛蒿(Artemisia scoparia)、蕨麻(Potentilla anserina)、沙棘(Hippophae rhamnoide)、垂穗披碱草(Elymus nutans) |
| 3 a-2 | 3 | 3048 | 37°22′16″N | 102°23′9″E | |
| 3 a-3 | 3 | 3048 | 37°22′15″N | 102°23′9″E | |
| 6 a-1 | 6 | 3003 | 37°22′6″N | 102°23′45″E | 黄白火绒草(Leontopodium ochroleucum)、草地早熟禾(Poa pratensis)、沙棘(Hippophae rhamnoide)、银露梅(Potentilla glabra) |
| 6 a-2 | 6 | 2966 | 37°22′49″N | 102°23′47″E | |
| 6 a-3 | 6 | 2663 | 37°22′7″N | 102°23′12″E | |
| 11 a-1 | 11 | 2959 | 37°22′18″N | 102°23′55″E | 垂穗披碱草(Elymus dahuricus )、金露梅(Dasiphora fruticosa)、沙棘(Hippophae rhamnoide)、早熟禾 (Poa annua) |
| 11 a-2 | 11 | 2868 | 37°22′26″N | 102°23′23″E | |
| 11 a-3 | 11 | 2652 | 37°22′49″N | 102°23′15″E |
表2
植物物种组成特征"
| 编号 | 科 | 属数 | 占总属数比例/% | 物种数 | 占总物种数比例/% |
|---|---|---|---|---|---|
| 1 | 菊科 (Asteraceae) | 10 | 20.833 | 13 | 20.00 |
| 2 | 蔷薇科 (Rosaceae) | 5 | 10.417 | 10 | 15.39 |
| 3 | 禾本科 (Poaceae) | 4 | 8.333 | 6 | 9.231 |
| 4 | 毛茛科 (Ranunculaceae) | 3 | 6.25 | 4 | 6.154 |
| 5 | 蓼科 (Polygonaceae) | 3 | 6.25 | 3 | 4.615 |
| 6 | 十字花科 (Brassicaceae) | 2 | 4.168 | 3 | 4.615 |
| 7 | 石竹科 (Caryophyllaceae) | 2 | 4.168 | 2 | 3.077 |
| 8 | 唇形科 (Lamiaceae) | 2 | 4.168 | 2 | 3.077 |
| 9 | 苋科 (Amaranthaceae) | 2 | 4.168 | 3 | 4.615 |
| 10 | 胡颓子科 (Elaeagnaceae) | 1 | 2.083 | 2 | 3.077 |
| 11 | 莎草科 (Cyperaceae) | 1 | 2.083 | 2 | 3.077 |
| 12 | 堇菜科 (Violaceae) | 1 | 2.083 | 2 | 3.077 |
| 13 | 忍冬科 (Caprifoliaceae) | 1 | 2.083 | 2 | 3.077 |
| 14 | 车前科 (Plantaginaceae) | 1 | 2.083 | 1 | 1.538 |
| 15 | 伞形科 ((Apiaceae) | 1 | 2.083 | 1 | 1.538 |
| 16 | 牻牛儿苗科 (Geraniaceae) | 1 | 2.083 | 1 | 1.538 |
| 17 | 鸢尾科 (Iridaceae) | 1 | 2.083 | 1 | 1.538 |
| 18 | 龙胆科 (Gentianaceae) | 1 | 2.083 | 1 | 1.538 |
| 19 | 柳叶菜科 (Onagraceae) | 1 | 2.083 | 1 | 1.538 |
| 20 | 茜草科 (Rubiaceae) | 1 | 2.083 | 1 | 1.538 |
| 21 | 通泉草科 (Mazaceae) | 1 | 2.083 | 1 | 1.538 |
| 22 | 瑞香科 (Thymelaeaceae) | 1 | 2.083 | 1 | 1.538 |
| 23 | 豆科 (Fabaceae) | 1 | 2.083 | 1 | 1.538 |
| 24 | 荨麻科 (Urticaceae) | 1 | 2.083 | 1 | 1.538 |
| 合计 | 24 | 48 | 100 | 65 | 100 |
表4
植物物种多样性与土壤养分相关性分析"
| 指标 | pH值 | 全氮 | 全磷 | 有机质 | 硝态氮 | 铵态氮 | 速效磷 | 有效钾 |
|---|---|---|---|---|---|---|---|---|
| 个体数(N) | 0.25 | 0.11 | 0.55 | -0.19 | 0.72** | 0.73** | -0.74** | -0.48 |
| 物种数(S) | 0.71** | 0.43 | 0.71** | 0.08 | 0.81** | 0.76** | -0.40 | -0.42 |
| Shannon多样性指数 | 0.52 | 0.30 | 0.12 | 0.16 | 0.06 | 0.11 | 0.23 | 0.30 |
| Pielou均匀度指数 | -0.01 | 0.36 | -0.46 | 0.17 | -0.52 | -0.52 | 0.68* | 0.77** |
| Simpson优势度指数 | 0.45 | 0.37 | 0.65* | 0.03 | 0.76* | 0.71* | -0.44 | -0.44 |
| Margalef丰富度指数 | 0.35 | 0.53 | 0.67* | 0.21 | 0.72* | 0.70* | -0.14 | -0.14 |
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