生物多样性 ›› 2021, Vol. 29 ›› Issue (7): 875-886. DOI: 10.17520/biods.2020416
收稿日期:
2020-11-04
接受日期:
2021-05-12
出版日期:
2021-07-20
发布日期:
2021-07-26
通讯作者:
* 王海珍 E-mail: whzzky@163.com
基金资助:
Jiapeng Kang1, Lu Han2, Chunhui Feng2, Haizhen Wang2,*()
Received:
2020-11-04
Accepted:
2021-05-12
Online:
2021-07-20
Published:
2021-07-26
Contact:
* Haizhen Wang E-mail: whzzky@163.com
摘要:
为解释塔里木荒漠河岸林群落构建和物种多度分布格局形成的机理, 本文以塔里木荒漠河岸林2个不同生境(沙地、河漫滩) 4 ha固定监测样地为研究对象, 基于两样地物种调查数据, 采用统计模型(对数级数模型、对数正态模型、泊松对数正态分布模型、Weibull分布模型)、生态位模型(生态位优先占领模型、断棍模型)和中性理论模型(复合群落零和多项式模型、Volkov模型)拟合荒漠河岸林群落物种多度分布, 并用K-S检验与赤池信息准则(AIC)筛选最优拟合模型。结果表明: (1)随生境恶化(土壤水分降低), 植物物种多度分布曲线变化减小, 群落物种多样性、多度和群落盖度降低, 常见种数减少。(2)选用的3类模型均可拟合荒漠河岸林不同生境群落物种多度分布格局, 统计模型和中性理论模型拟合效果均优于生态位模型。复合群落零和多项式模型对远离河岸的干旱沙地生境拟合效果最好; 对数正态模型和泊松对数正态模型对洪水漫溢的河漫滩生境拟合效果最优; 中性理论模型与统计模型无显著差异。初步推断中性过程在荒漠河岸林群落构建中发挥着主导作用, 但模型拟合结果只能作为推断群落构建过程的必要非充分条件, 不能排除生态位过程的潜在作用。
康佳鹏, 韩路, 冯春晖, 王海珍 (2021) 塔里木荒漠河岸林不同生境群落物种多度分布格局. 生物多样性, 29, 875-886. DOI: 10.17520/biods.2020416.
Jiapeng Kang, Lu Han, Chunhui Feng, Haizhen Wang (2021) Species abundance distribution in two riparian forests under contrasting environmental regimes in the Tarim Desert. Biodiversity Science, 29, 875-886. DOI: 10.17520/biods.2020416.
沙地生境 Sandy habitat | 河漫滩生境 Floodplain habitat | P | t | |
---|---|---|---|---|
土壤质量含水率 Soil mass water content (%) | 0.62 ± 0.11A | 21.95 ± 1.23B | < 0.01 | 2.01 |
电导率 Electrical conductivity (μS/cm) | 1,819.87 ± 272.90a | 1,105.93 ± 293.60a | 0.09 | 2.05 |
pH | 8.02 ± 0.03A | 8.20 ± 0.03B | < 0.01 | 2.05 |
土壤有机质 Soil organic matter (g/kg) | 2.48 ± 0.30a | 2.74 ± 0.73a | 0.96 | 2.12 |
全氮 Total nitrogen (g/kg) | 0.18 ± 0.03a | 0.22 ± 0.05a | 0.68 | 2.14 |
全磷 Total phosphorus (g/kg) | 7.22 ± 0.50a | 7.43 ± 0.38a | 0.97 | 2.20 |
碱解氮 Available nitrogen (mg/kg) | 6.46 ± 2.74a | 6.95 ± 1.06a | 0.30 | 2.20 |
有效磷 Available phosphorus (mg/kg) | 105.40 ± 15.07a | 109.62 ± 6.30a | 0.68 | 2.12 |
速效钾 Available potassium (mg/kg) | 203.56 ± 32.83a | 180.69 ± 34.23a | 0.54 | 2.12 |
表1 荒漠河岸林不同生境的土壤特征(平均值 ± 标准差)
Table 1 Soil characteristics of two different habitats in desert riparian forest (mean ± SD)
沙地生境 Sandy habitat | 河漫滩生境 Floodplain habitat | P | t | |
---|---|---|---|---|
土壤质量含水率 Soil mass water content (%) | 0.62 ± 0.11A | 21.95 ± 1.23B | < 0.01 | 2.01 |
电导率 Electrical conductivity (μS/cm) | 1,819.87 ± 272.90a | 1,105.93 ± 293.60a | 0.09 | 2.05 |
pH | 8.02 ± 0.03A | 8.20 ± 0.03B | < 0.01 | 2.05 |
土壤有机质 Soil organic matter (g/kg) | 2.48 ± 0.30a | 2.74 ± 0.73a | 0.96 | 2.12 |
全氮 Total nitrogen (g/kg) | 0.18 ± 0.03a | 0.22 ± 0.05a | 0.68 | 2.14 |
全磷 Total phosphorus (g/kg) | 7.22 ± 0.50a | 7.43 ± 0.38a | 0.97 | 2.20 |
碱解氮 Available nitrogen (mg/kg) | 6.46 ± 2.74a | 6.95 ± 1.06a | 0.30 | 2.20 |
有效磷 Available phosphorus (mg/kg) | 105.40 ± 15.07a | 109.62 ± 6.30a | 0.68 | 2.12 |
速效钾 Available potassium (mg/kg) | 203.56 ± 32.83a | 180.69 ± 34.23a | 0.54 | 2.12 |
模型类型 Model type | 模型名称 Model name | 沙地生境 Sandy habitat | 河漫滩生境 Floodplain habitat | ||||
---|---|---|---|---|---|---|---|
AIC | D | P | AIC | D | P | ||
统计模型 Statistical model | 对数级数模型 Log-series model | 59.80 | 0.20 | 1.00 | 227.10 | 0.36 | 0.46 |
对数正态模型 Log-normal model | 63.08 | 0.20 | 1.00 | 220.80 | 0.18 | 1.00 | |
泊松对数正态分布模型 Poisson lognormal distribution model | 62.82 | 0.20 | 1.00 | 220.80 | 0.18 | 1.00 | |
Weibull分布模型 Weibull distribution model | 62.57 | 0.20 | 1.00 | 222.70 | 0.18 | 1.00 | |
生态位模型 Niche model | 断棍模型 Broken stick model | 63.31 | 0.40 | 0.87 | 251.40 | 0.55 | 0.07 |
生态位优先占领模型 Niche preemption model | 63.95 | 0.40 | 0.87 | 241.50 | 0.55 | 0.07 | |
中性理论模型 Neutral theory model | 复合群落零和多项式模型 Metacommunity zero-sum multinomial distribution model | 58.70 | 0.20 | 1.00 | 226.10 | 0.36 | 0.48 |
Volkov模型 Volkov model | 60.44 | 0.20 | 1.00 | 222.50 | 0.18 | 1.00 |
表2 荒漠河岸林不同生境物种多度分布模型的拟合优度检验
Table 2 Goodness of fit test of species abundance distribution models at different habitats in desert riparian forest
模型类型 Model type | 模型名称 Model name | 沙地生境 Sandy habitat | 河漫滩生境 Floodplain habitat | ||||
---|---|---|---|---|---|---|---|
AIC | D | P | AIC | D | P | ||
统计模型 Statistical model | 对数级数模型 Log-series model | 59.80 | 0.20 | 1.00 | 227.10 | 0.36 | 0.46 |
对数正态模型 Log-normal model | 63.08 | 0.20 | 1.00 | 220.80 | 0.18 | 1.00 | |
泊松对数正态分布模型 Poisson lognormal distribution model | 62.82 | 0.20 | 1.00 | 220.80 | 0.18 | 1.00 | |
Weibull分布模型 Weibull distribution model | 62.57 | 0.20 | 1.00 | 222.70 | 0.18 | 1.00 | |
生态位模型 Niche model | 断棍模型 Broken stick model | 63.31 | 0.40 | 0.87 | 251.40 | 0.55 | 0.07 |
生态位优先占领模型 Niche preemption model | 63.95 | 0.40 | 0.87 | 241.50 | 0.55 | 0.07 | |
中性理论模型 Neutral theory model | 复合群落零和多项式模型 Metacommunity zero-sum multinomial distribution model | 58.70 | 0.20 | 1.00 | 226.10 | 0.36 | 0.48 |
Volkov模型 Volkov model | 60.44 | 0.20 | 1.00 | 222.50 | 0.18 | 1.00 |
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