生物多样性 ›› 2014, Vol. 22 ›› Issue (3): 302-310. DOI: 10.3724/SP.J.1003.2014.13141
所属专题: 海洋生物多样性
收稿日期:
2013-06-24
接受日期:
2013-12-09
出版日期:
2014-05-20
发布日期:
2014-06-04
基金资助:
Received:
2013-06-24
Accepted:
2013-12-09
Online:
2014-05-20
Published:
2014-06-04
Contact:
Zhang Jinghuai
摘要:
利用2006年7-8月(夏季)、2007年4-5月(春季)和2007年10-12月(秋季)珠江丰水期、平水期和枯水期3个航次在南中国海北部珠江口附近海域4条由河口、近岸到深水区调查断面的数据, 研究大型底栖动物多样性由河口-近岸-深水的变化趋势及与环境因子的关系。春季、夏季和秋季分别获得大型底栖动物273、256和148种, 各季节均以环节动物种类最多, 节肢动物次之。大型底栖动物种类数、丰度、生物量和Shannon-Wiener多样性指数均由河口向近岸海域升高, 再由近岸向外海深水区降低。Pielou均匀度深水区最高, 其次为近岸。河口和深水区大型底栖动物k-优势度曲线位于近岸浅水域曲线之上, 表明生物多样性由河口向近岸升高, 而由近岸向深水则降低。大型底栖动物与环境因子Pearson相关性分析表明, 春、秋季大型底栖动物种类数、丰度和生物量与水深呈显著的负相关, 秋季种类多样性指数和均匀度也与水深呈显著的负相关性, 而夏季仅生物量与水深呈显著的负相关; 春、秋季大型底栖动物种类数、生物量、丰度、多样性指数和种类均匀度与盐度的相关性不显著, 但是夏季大型底栖动物种类数、丰度、多样性指数和种类均匀度与盐度呈显著正相关。单位面积(0.2 m2)内, 珠江口及邻近海域大型底栖动物在近岸浅水区较深水区和河口生物多样性高, 且生物量丰富。
张敬怀 (2014) 珠江口及邻近海域大型底栖动物多样性随盐度、水深的变化趋势. 生物多样性, 22, 302-310. DOI: 10.3724/SP.J.1003.2014.13141.
Jinghuai Zhang (2014) The variation of biodiversity of macrobenthic fauna with salinity and water depth near the Pearl Estuary of the northern South China Sea. Biodiversity Science, 22, 302-310. DOI: 10.3724/SP.J.1003.2014.13141.
断面 Transect | 站位 Station | 沉积类型 Sediment | 水深 Water depth | 春季 Spring | 夏季 Summer | 秋季 Autumn | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
BWS | H' | J' | BWS | H' | J' | BWS | H' | J' | ||||||
T1 | T1-01 | 细沙或泥 Silver sand or mud | 15.5 | 34.0 | 3.44 | 0.72 | 31.5 | 2.00 | 1.00 | 31.4 | 4.14 | 0.93 | ||
T1-02 | 泥沙 Mud sand | 48.1 | 34.3 | 3.41 | 0.90 | 34.3 | 4.22 | 0.82 | 33.1 | 3.48 | 0.87 | |||
T1-03 | 泥沙 Mud sand | 97.5 | 34.4 | 3.92 | 0.94 | 34.5 | 2.81 | 0.70 | 34.2 | 2.32 | 1.00 | |||
T1-04 | 泥沙 Mud sand | 259 | 34.5 | 1.58 | 1.00 | 34.5 | 1.37 | 0.86 | 34.5 | NC | NC | |||
T1-05 | 沙 Sand | 314 | 34.5 | 1.79 | 0.90 | 34.5 | 2.99 | 0.94 | 34.5 | 0.00 | 1.00 | |||
T2 | T2-01 | 泥沙 Mud sand | 8.5 | 13.7 | 1.91 | 0.95 | 0.8 | 2.15 | 0.83 | 15.0 | 1.45 | 0.72 | ||
T2-02 | 泥沙 Mud sand | 10.7 | 10.5 | 1.00 | 1.00 | 1.6 | 0.00 | 1.00 | 15.6 | 0.00 | 1.00 | |||
T2-03 | 泥沙 Mud sand | 7.7 | 18.0 | 2.13 | 0.92 | 6.0 | 2.25 | 0.97 | 17.0 | 2.11 | 0.75 | |||
T2-04 | 泥沙 Mud sand | 9.8 | 32.2 | 3.75 | 0.68 | 18.0 | 1.50 | 0.95 | 21.6 | 1.36 | 0.68 | |||
T2-05 | 泥 Mud | 9.0 | 32.5 | 4.04 | 0.81 | 19.8 | 2.05 | 0.79 | 26.5 | 2.59 | 1.00 | |||
T2-06 | 泥 Mud | 6.0 | 31.9 | 0.20 | 0.06 | 9.8 | 2.92 | 0.92 | 27.9 | 3.39 | 0.98 | |||
T2-07 | 泥 Mud | 7.9 | 31.1 | 2.71 | 0.78 | 28.1 | 2.93 | 0.93 | 29.1 | 3.07 | 0.89 | |||
T2-08 | 泥沙 Mud sand | 16.8 | 33.4 | 4.65 | 0.88 | 30.3 | 4.24 | 0.93 | 32.8 | 4.00 | 0.85 | |||
T2-09 | 泥 Mud | 31.0 | 34.4 | 4.14 | 0.92 | 34.3 | 3.67 | 0.92 | 32.9 | 3.12 | 0.90 | |||
T2-10 | 泥沙 Mud sand | 41.6 | 34.4 | 4.61 | 0.93 | 34.31 | 4.02 | 0.96 | 33.6 | 3.68 | 0.97 | |||
T2-11 | 泥沙 Mud sand | 54.0 | 34.4 | 3.72 | 0.95 | 34.4 | 4.31 | 0.98 | 34.0 | 3.80 | 0.89 | |||
T2-12 | 泥沙 Mud sand | 70.8 | 34.4 | 3.17 | 1.00 | 34.4 | 4.08 | 0.87 | 34.1 | 4.28 | 0.98 | |||
T2-13 | 泥沙 Mud sand | 92.4 | 34.4 | 3.48 | 0.94 | 34.4 | 3.67 | 0.94 | 34.2 | 2.95 | 0.98 | |||
T2-14 | 泥沙 Mud sand | 131 | 34.6 | 2.86 | 0.90 | 34.5 | 2.52 | 0.98 | 34.3 | 1.00 | 1.00 | |||
T2-15 | 泥沙 Mud sand | 486 | 34.4 | 3.52 | 0.93 | 34.5 | 2.41 | 0.93 | 34.4 | 2.65 | 0.94 | |||
T3 | T3-01 | 泥沙 Mud sand | 36 | 34.5 | 4.91 | 0.89 | 34.3 | 2.25 | 0.52 | 33.6 | 3.93 | 0.86 | ||
T3-02 | 泥沙 Mud sand | 43.6 | 34.5 | 4.72 | 0.88 | 34.3 | 4.54 | 0.96 | 33.8 | 2.71 | 0.90 | |||
T3-03 | 泥沙 Mud sand | 72.0 | 34.5 | 3.99 | 0.91 | 34.4 | 3.56 | 0.91 | 34.1 | 3.68 | 0.97 | |||
T3-04 | 泥沙 Mud sand | 127 | 34.6 | 3.73 | 0.98 | 34.5 | 3.73 | 0.98 | 34.1 | 2.50 | 0.97 | |||
T3-05 | 泥沙 Mud sand | 814 | 34.5 | 1.24 | 0.62 | 34.5 | 1.58 | 1.00 | 34.4 | NC | NC | |||
T4 | T4-01 | 泥 Mud | 13.5 | 31.5 | 3.18 | 0.71 | 34.3 | 3.36 | 0.81 | 31.9 | 2.41 | 0.58 | ||
T4-02 | 泥沙 Mud sand | 42.0 | 34.3 | 4.93 | 0.91 | 34.4 | 4.98 | 0.94 | 33.7 | 4.56 | 0.91 | |||
T4-03 | 泥沙 Mud sand | 65.5 | 34.4 | 3.00 | 1.00 | 34.4 | 4.66 | 0.98 | 34.1 | 2.95 | 0.98 | |||
T4-04 | 泥沙 Mud sand | 90.0 | 34.5 | 3.50 | 0.95 | 34.5 | 3.58 | 0.97 | 34.1 | 1.59 | 1.00 | |||
T4-05 | 泥沙 Mud sand | 157 | 34.6 | NC | NC | 34.6 | 1.79 | 0.90 | 34.5 | 1.50 | 0.95 | |||
T4-06 | 泥沙 Mud sand | 455 | 34.4 | NC | NC | 34.4 | 2.42 | 0.94 | 34.4 | NC | NC |
表1 珠江口及邻近海域大型底栖动物Shannon-Wiener多样性指数(H')、Pielou均匀度(J')和环境因子
Table 1 Shannon-Wiener index (H'), Pielou’s evenness (J') of macrobenthic fauna and environmental factors near the Pearl Estuary of the northern South China Sea
断面 Transect | 站位 Station | 沉积类型 Sediment | 水深 Water depth | 春季 Spring | 夏季 Summer | 秋季 Autumn | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
BWS | H' | J' | BWS | H' | J' | BWS | H' | J' | ||||||
T1 | T1-01 | 细沙或泥 Silver sand or mud | 15.5 | 34.0 | 3.44 | 0.72 | 31.5 | 2.00 | 1.00 | 31.4 | 4.14 | 0.93 | ||
T1-02 | 泥沙 Mud sand | 48.1 | 34.3 | 3.41 | 0.90 | 34.3 | 4.22 | 0.82 | 33.1 | 3.48 | 0.87 | |||
T1-03 | 泥沙 Mud sand | 97.5 | 34.4 | 3.92 | 0.94 | 34.5 | 2.81 | 0.70 | 34.2 | 2.32 | 1.00 | |||
T1-04 | 泥沙 Mud sand | 259 | 34.5 | 1.58 | 1.00 | 34.5 | 1.37 | 0.86 | 34.5 | NC | NC | |||
T1-05 | 沙 Sand | 314 | 34.5 | 1.79 | 0.90 | 34.5 | 2.99 | 0.94 | 34.5 | 0.00 | 1.00 | |||
T2 | T2-01 | 泥沙 Mud sand | 8.5 | 13.7 | 1.91 | 0.95 | 0.8 | 2.15 | 0.83 | 15.0 | 1.45 | 0.72 | ||
T2-02 | 泥沙 Mud sand | 10.7 | 10.5 | 1.00 | 1.00 | 1.6 | 0.00 | 1.00 | 15.6 | 0.00 | 1.00 | |||
T2-03 | 泥沙 Mud sand | 7.7 | 18.0 | 2.13 | 0.92 | 6.0 | 2.25 | 0.97 | 17.0 | 2.11 | 0.75 | |||
T2-04 | 泥沙 Mud sand | 9.8 | 32.2 | 3.75 | 0.68 | 18.0 | 1.50 | 0.95 | 21.6 | 1.36 | 0.68 | |||
T2-05 | 泥 Mud | 9.0 | 32.5 | 4.04 | 0.81 | 19.8 | 2.05 | 0.79 | 26.5 | 2.59 | 1.00 | |||
T2-06 | 泥 Mud | 6.0 | 31.9 | 0.20 | 0.06 | 9.8 | 2.92 | 0.92 | 27.9 | 3.39 | 0.98 | |||
T2-07 | 泥 Mud | 7.9 | 31.1 | 2.71 | 0.78 | 28.1 | 2.93 | 0.93 | 29.1 | 3.07 | 0.89 | |||
T2-08 | 泥沙 Mud sand | 16.8 | 33.4 | 4.65 | 0.88 | 30.3 | 4.24 | 0.93 | 32.8 | 4.00 | 0.85 | |||
T2-09 | 泥 Mud | 31.0 | 34.4 | 4.14 | 0.92 | 34.3 | 3.67 | 0.92 | 32.9 | 3.12 | 0.90 | |||
T2-10 | 泥沙 Mud sand | 41.6 | 34.4 | 4.61 | 0.93 | 34.31 | 4.02 | 0.96 | 33.6 | 3.68 | 0.97 | |||
T2-11 | 泥沙 Mud sand | 54.0 | 34.4 | 3.72 | 0.95 | 34.4 | 4.31 | 0.98 | 34.0 | 3.80 | 0.89 | |||
T2-12 | 泥沙 Mud sand | 70.8 | 34.4 | 3.17 | 1.00 | 34.4 | 4.08 | 0.87 | 34.1 | 4.28 | 0.98 | |||
T2-13 | 泥沙 Mud sand | 92.4 | 34.4 | 3.48 | 0.94 | 34.4 | 3.67 | 0.94 | 34.2 | 2.95 | 0.98 | |||
T2-14 | 泥沙 Mud sand | 131 | 34.6 | 2.86 | 0.90 | 34.5 | 2.52 | 0.98 | 34.3 | 1.00 | 1.00 | |||
T2-15 | 泥沙 Mud sand | 486 | 34.4 | 3.52 | 0.93 | 34.5 | 2.41 | 0.93 | 34.4 | 2.65 | 0.94 | |||
T3 | T3-01 | 泥沙 Mud sand | 36 | 34.5 | 4.91 | 0.89 | 34.3 | 2.25 | 0.52 | 33.6 | 3.93 | 0.86 | ||
T3-02 | 泥沙 Mud sand | 43.6 | 34.5 | 4.72 | 0.88 | 34.3 | 4.54 | 0.96 | 33.8 | 2.71 | 0.90 | |||
T3-03 | 泥沙 Mud sand | 72.0 | 34.5 | 3.99 | 0.91 | 34.4 | 3.56 | 0.91 | 34.1 | 3.68 | 0.97 | |||
T3-04 | 泥沙 Mud sand | 127 | 34.6 | 3.73 | 0.98 | 34.5 | 3.73 | 0.98 | 34.1 | 2.50 | 0.97 | |||
T3-05 | 泥沙 Mud sand | 814 | 34.5 | 1.24 | 0.62 | 34.5 | 1.58 | 1.00 | 34.4 | NC | NC | |||
T4 | T4-01 | 泥 Mud | 13.5 | 31.5 | 3.18 | 0.71 | 34.3 | 3.36 | 0.81 | 31.9 | 2.41 | 0.58 | ||
T4-02 | 泥沙 Mud sand | 42.0 | 34.3 | 4.93 | 0.91 | 34.4 | 4.98 | 0.94 | 33.7 | 4.56 | 0.91 | |||
T4-03 | 泥沙 Mud sand | 65.5 | 34.4 | 3.00 | 1.00 | 34.4 | 4.66 | 0.98 | 34.1 | 2.95 | 0.98 | |||
T4-04 | 泥沙 Mud sand | 90.0 | 34.5 | 3.50 | 0.95 | 34.5 | 3.58 | 0.97 | 34.1 | 1.59 | 1.00 | |||
T4-05 | 泥沙 Mud sand | 157 | 34.6 | NC | NC | 34.6 | 1.79 | 0.90 | 34.5 | 1.50 | 0.95 | |||
T4-06 | 泥沙 Mud sand | 455 | 34.4 | NC | NC | 34.4 | 2.42 | 0.94 | 34.4 | NC | NC |
图2 珠江口及邻近海域不同季节大型底栖动物种类组成。ANN, 环节动物; ART, 节肢动物; MOL, 软体动物; ECH, 棘皮动物; OSP, 其他类生物
Fig. 2 Species component of macrobenthic fauna near the Pearl Estuary of the northern South China Sea. ANN, Annelida; ART, Arthropoda; MOL, Mollusca; ECH, Echinodermata; OSP, Other species
图3 不同季节珠江口及邻近海域大型底栖动物种类、丰度和生物量分布
Fig. 3 Distribution of species richness, abundance and biomass of macrobenthic fauna near the Pearl Estuary of the northern South China Sea
图4 珠江口及邻近海域T2断面大型底栖动物k-优势度曲线。A, 区域A (水深≤100 m); B, 区域B (水深>100 m); E, 河口(T2-01站至T2-07站)。
Fig. 4 k-dominance curve of macrobenthic fauna on the T2 transect near the Pearl Estuary of the northern South China Sea. A, areas A (water depth ≤ 100 m); B, areas B (water depth> 100 m); E, estuary (T2-01 to T2-07).
季节 Seasons | 项目 Items | ||||
---|---|---|---|---|---|
S | ABU | BIO | H' | J' | |
春季 Spring (n=29) | |||||
水深 Water depth (m) | -0.443* | -0.524** | -0.428* | -0.306 | -0.248 |
底层海水水温 Water temperature in the bottom of water column (°C) | 0.528** | 0.413* | 0.421* | 0.447* | 0.319 |
底层海水盐度 Salinity in the bottom of water column | 0.228 | 0.184 | 0.195 | 0.099 | -0.121 |
底层海水溶解氧 Dissolved oxygen in the bottom of water column (mg/L) | 0.643** | 0.672** | 0.481** | 0.494** | 0.371* |
底层海水pH pH in the bottom of the water column | 0.470** | 0.351 | 0.324 | 0.324 | 0.074 |
底层海水碱度 Alkalinity in the bottom of water column (mmol/L) | 0.096 | -0.013 | 0.003 | 0.023 | -0.160 |
底层海水悬浮物 Suspended substance in the bottom of water column (mg/L) | -0.076 | 0.230 | 0.226 | -0.141 | -0.013 |
底层海水叶绿素a Chlorophyll a concentration in the bottom of water column (mg/m3) | 0.556** | 0.642** | 0.506** | 0.352 | 0.220 |
夏季 Summer (n=31) | |||||
水深 Water depth (m) | -0.136 | -0.17 | -0.520** | 0.082 | 0.212 |
底层海水水温 Water temperature in the bottom of water column (°C) | 0.152 | 0.146 | 0.379* | -0.094 | -0.246 |
底层海水盐度 Salinity in the bottom of water column | 0.469** | 0.372* | -0.038 | 0.603** | 0.547** |
底层海水溶解氧 Dissolved oxygen in the bottom of water column (mg/L) | 0.373* | 0.27 | 0.362* | 0.342 | 0.208 |
底层海水pH pH in the bottom of the water column | 0.677** | 0.532** | 0.146 | 0.836** | 0.723** |
底层海水碱度 Alkalinity in the bottom of water column (mmol/L) | 0.487** | 0.386* | 0.001 | 0.659** | 0.614** |
底层海水悬浮物 Suspended substance in the bottom of water column (mg/L) | -0.348 | -0.241 | 0.230 | -0.588** | -0.588** |
底层海水叶绿素a Chlorophyll a concentration in the bottom of water column (mg/m3) | 0.031 | 0.16 | 0.481** | -0.199 | -0.295 |
秋季 Autumn (n=27) | |||||
水深 Water depth (m) | -0.618** | -0.651** | -0.633** | -0.524** | -0.490** |
底层海水水温 Water temperature in the bottom of water column (°C) | 0.670** | 0.661** | 0.607** | 0.633** | 0.626** |
底层海水盐度 Salinity in the bottom of water column | 0.048 | -0.016 | -0.119 | 0.126 | 0.089 |
底层海水溶解氧 Dissolved oxygen in the bottom of water column (mg/L) | 0.710** | 0.658** | 0.570** | 0.717** | 0.699** |
底层海水pH pH in the bottom of the water column | 0.415* | 0.311 | 0.144 | 0.484** | 0.453* |
底层海水碱度 Alkalinity in the bottom of water column (mmol/L) | -0.043 | -0.099 | -0.225 | 0.030 | 0.001 |
底层海水悬浮物 Suspended substance in the bottom of water column (mg/L) | 0.261 | 0.348 | 0.306 | 0.099 | 0.039 |
底层海水叶绿素a Chlorophyll a concentration in the bottom of water column (mg/m3) | 0.655** | 0.714** | 0.647** | 0.532** | 0.456** |
表2 珠江口及邻近海域大型底栖动物种类数(S)、丰度(ABU)、生物量(BIO)、Shannon-Wiener指数(H')、Pielou均匀度(J')和环境因子的Pearson相关性
Table 2 Pearson correlation between species richness (S), abundance (ABU), biomass (BIO), Shannon-Wiener index (H'), Pielou’s evenness (J') of macrobenthic fauna and environmental factors near the Pearl Estuary of the northern South China Sea
季节 Seasons | 项目 Items | ||||
---|---|---|---|---|---|
S | ABU | BIO | H' | J' | |
春季 Spring (n=29) | |||||
水深 Water depth (m) | -0.443* | -0.524** | -0.428* | -0.306 | -0.248 |
底层海水水温 Water temperature in the bottom of water column (°C) | 0.528** | 0.413* | 0.421* | 0.447* | 0.319 |
底层海水盐度 Salinity in the bottom of water column | 0.228 | 0.184 | 0.195 | 0.099 | -0.121 |
底层海水溶解氧 Dissolved oxygen in the bottom of water column (mg/L) | 0.643** | 0.672** | 0.481** | 0.494** | 0.371* |
底层海水pH pH in the bottom of the water column | 0.470** | 0.351 | 0.324 | 0.324 | 0.074 |
底层海水碱度 Alkalinity in the bottom of water column (mmol/L) | 0.096 | -0.013 | 0.003 | 0.023 | -0.160 |
底层海水悬浮物 Suspended substance in the bottom of water column (mg/L) | -0.076 | 0.230 | 0.226 | -0.141 | -0.013 |
底层海水叶绿素a Chlorophyll a concentration in the bottom of water column (mg/m3) | 0.556** | 0.642** | 0.506** | 0.352 | 0.220 |
夏季 Summer (n=31) | |||||
水深 Water depth (m) | -0.136 | -0.17 | -0.520** | 0.082 | 0.212 |
底层海水水温 Water temperature in the bottom of water column (°C) | 0.152 | 0.146 | 0.379* | -0.094 | -0.246 |
底层海水盐度 Salinity in the bottom of water column | 0.469** | 0.372* | -0.038 | 0.603** | 0.547** |
底层海水溶解氧 Dissolved oxygen in the bottom of water column (mg/L) | 0.373* | 0.27 | 0.362* | 0.342 | 0.208 |
底层海水pH pH in the bottom of the water column | 0.677** | 0.532** | 0.146 | 0.836** | 0.723** |
底层海水碱度 Alkalinity in the bottom of water column (mmol/L) | 0.487** | 0.386* | 0.001 | 0.659** | 0.614** |
底层海水悬浮物 Suspended substance in the bottom of water column (mg/L) | -0.348 | -0.241 | 0.230 | -0.588** | -0.588** |
底层海水叶绿素a Chlorophyll a concentration in the bottom of water column (mg/m3) | 0.031 | 0.16 | 0.481** | -0.199 | -0.295 |
秋季 Autumn (n=27) | |||||
水深 Water depth (m) | -0.618** | -0.651** | -0.633** | -0.524** | -0.490** |
底层海水水温 Water temperature in the bottom of water column (°C) | 0.670** | 0.661** | 0.607** | 0.633** | 0.626** |
底层海水盐度 Salinity in the bottom of water column | 0.048 | -0.016 | -0.119 | 0.126 | 0.089 |
底层海水溶解氧 Dissolved oxygen in the bottom of water column (mg/L) | 0.710** | 0.658** | 0.570** | 0.717** | 0.699** |
底层海水pH pH in the bottom of the water column | 0.415* | 0.311 | 0.144 | 0.484** | 0.453* |
底层海水碱度 Alkalinity in the bottom of water column (mmol/L) | -0.043 | -0.099 | -0.225 | 0.030 | 0.001 |
底层海水悬浮物 Suspended substance in the bottom of water column (mg/L) | 0.261 | 0.348 | 0.306 | 0.099 | 0.039 |
底层海水叶绿素a Chlorophyll a concentration in the bottom of water column (mg/m3) | 0.655** | 0.714** | 0.647** | 0.532** | 0.456** |
图5 珠江口及邻近海域大型底栖动物相似性聚类分析。A, 区域A (水深≤100 m); B, 区域B (水深>100 m); E, 河口 (T2-01站至T2-07站)。
Fig. 5 The Similarity-cluster analysis on macrobenthic fauna near the Pearl Estuary of the northern South China Sea. A, areas A (water depth≤100 m); B, areas B (water depth>100 m); E, estuary (T2-01 to T2-07).
[28] | Shen GY (沈国英), Huang LF (黄凌风), Guo F (郭丰), Shi BZ (施并章) (2010) Marine Ecology, 3rd edn. (海洋生态学). Science Press, Beijing. (in Chinese) |
[29] | Zhang JH (张敬怀), Gao Y (高阳), Fang HD (方宏达), Xu ZB (徐志斌) (2009a) Ecological characteristics of macrobenthic communities in Pearl River Estuary.Acta Ecologica Sinica(生态学报), 29, 2989-2999. (in Chinese with English abstract) |
[30] | Zhang JH (张敬怀), Zhou JJ (周俊杰) , Bai J (白洁), Fang HD (方宏达) (2009b) Characters of macrobenthic community in southeast sea of the Pearl River Estuary.Marine Science Bulletin(海洋通报), 28(6), 26-33. (in Chinese with English abstract) |
[31] | Zhang ZN (张志南), Tu LH (图立红), Yu ZS (于子山) (1990) Preliminary study on the macrofauna in the Huanghe River Estuary and its adjacent waters. I. The biomass.Journal of Ocean University of Qingdao(青岛海洋大学学报), 20, 37-45. (in Chinese with English abstract) |
[1] | Brian M, Graham B (2001) South China Sea.Marine Pollution Bulletin, 48, 1236-1263. |
[2] | Cai LZ (蔡立哲) (2006) Progress on marine benthic ecology and biodiversity.Journal of Xiamen University (Natural Science)(厦门大学学报(自然科学版)), 45(Suppl.2), 83-89. (in Chinese with English abstract) |
[3] | Cai LZ (蔡立哲), Chen XW (陈昕韡), Wu C (吴辰), Peng X (彭欣), Cao J (曹婧), Fu SJ (傅素晶) (2011) Temporal and spatial variation of macrofaunal communities in Shenzhen Bay intertidal zone between 1995 and 2010.Biodiversity Science(生物多样性), 19, 702-709. (in Chinese with English abstract) |
[4] | Coleman N, Gason A, Poore GCB (1997) High species richness in the shallow marine waters of south-east Australia.Marine Ecology Progress Series, 154, 17-26. |
[5] | Du FY (杜飞雁), Zhang HH (张汉华), Li CH (李纯厚), Wang XH (王雪辉), Jia XP (贾晓平) (2008) Species composition and diversity of macrobenthic fauna in Daya Bay.Journal of Fishery Sciences of China(中国水产科学), 15, 252-259. (in Chinese with English abstract) |
[6] | Etter RJ, Grassle JF (1992) Patterns of species diversity in the deep-sea as a function of sediment particle size diversity.Nature, 360, 576-578. |
[7] | Gage JD (1996) Why are there so many species in deep-sea sediments? Journal of Experimental Marine Biology and Ecology, 200, 257-286. |
[8] | Grassle JF (1989) Species diversity in deep-sea communities.Trends in Ecology and Evolution, 4, 12-15. |
[9] | Grassle JF (1991) Deep-sea benthic biodiversity.BioScience, 41, 464-469. |
[10] | Grassle JF, Maciolek NJ (1992) Deep-sea species richness: regional and local diversity estimates from quantitative bottom samples.The American Naturalist, 139, 313-341. |
[11] | Gray JS (1994) Is the deep sea really so diverse? Species diversity from the Norwegian continental shelf.Marine Ecology Progress Series, 112, 205-209. |
[12] | Gray JS (1997) Marine biodiversity: patterns, threats and conservation needs.Biodiversity and Conservation, 6, 153-175. |
[13] | Gray JS (2000) The measurement of marine species diversity, with an application to the benthic fauna of the Norwegian continental shelf.Journal of Experimental Marine Biology and Ecology, 250, 23-49. |
[14] | Gray JS (2001) Marine diversity: the paradigms in patterns of species richness examined.Scientia Marina, 65(Suppl.2), 41-56. |
[15] | Gray JS, Poore GCB, Ugland KI, Wilson RS, Olsgard F, Johannessen Ø (1997) Coastal and deep-sea benthic diversities compared.Marine Ecology Progress Series, 159, 97-103. |
[16] | Hobbie JE (translated by Meng W (孟伟), Lei K (雷坤), Zheng BH (郑炳辉)) (2005) Estuarine Science: A Synthetic Approach to Research and Practice (河口科学—研究与实践的综合方法). China Ocean Press, Beijing. (in Chinese) |
[17] | Jumars PA (1976) Deep-sea species diversity: Does it have a characteristic scale? Journal of Marine Research, 34, 217-246. |
[18] | Lambshead PJD, Platt HM, Shaw KM (1983) The detection of differences among assemblages of marine benthic species based on an assessment of dominance and diversity. Journal of Natural History, 17, 859-874. |
[19] | Laprise R, Dodson JJ (1993) Nature of environmental variability experienced by benthic and pelagic animals in the St. Lawrence Estuary, Canada. Marine Ecology Progress Series, 94, 129-139. |
[20] | Levin L, Gage J (1998) Relationships between oxygen, organic matter and the diversity of bathyal macrofauna.Deep-Sea Research II, 45, 129-163. |
[21] | Li RG (李荣冠) (2003) Macrobenthos on the Continental Shelves and Adjacent Waters of China Seas ( 中国海陆架及邻近海域大型底栖生物 ). China Ocean Press, Beijing. (in Chinese) |
[22] | Li XZ (李新正) (2011) An overview of studies on marine macrobenthic biodiversity from Chinese waters: principally from the Yellow Sea.Biodiversity Science(生物多样性), 19, 676-684. (in Chinese with English abstract) |
[23] | Liu LS (刘录三), Li XZ (李新正) (2002) Distribution of macrobenthos in spring and autumn in the East China Sea.Biodiversity Science(生物多样性), 10, 351-358. (in Chinese with English abstract) |
[24] | Miller JM, Crowder LB, Moser ML (1985) Migration and utilization of estuarine nurseries by juvenile fishes: an evolutionary perspective.Contributions in Marine Science, 27, 338-352. |
[25] | Pearson TH, Rosenberg R (1978) Macrobenthic succession in relation to organic enrichment and pollution of the marine environment.Oceanography and Marine Biology Annual Review, 16, 229-311. |
[26] | Poore GCB, Wilson GDF (1993) Marine species richness. Nature, 361, 597-598. |
[27] | Sanders HL (1968) Marine benthic diversity: a comparative study.The American Naturalist, 102, 243-282. |
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