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作 者:王文亮[1] 陈建芳[1] 金海燕[1] 刘际弟[1] 金明明[1] 卢勇[1] 薛斌[1] 李宏亮[1] 王奎[1]
机构地区:[1]国家海洋局第二海洋研究所,国家海洋局海洋生态系统与生物地球化学重点实验室,浙江杭州310012
出 处:《海洋学研究》2009年第2期32-41,共10页Journal of Marine Sciences
基 金:国家重点基础研究发展规划资助项目(2006CB400603);国家自然科学基金资助项目(40403013);国家海洋局第二海洋研究所基本科研业务费专项资助项目(JT0707、JG0723)
摘 要:根据2006年7月至9月"海监49号"科学考察船夏季航次的调查数据,分析了长江口及邻近海域水体中磷形态的平面分布特征及其影响因素,结果表明,调查海域水体各种形态磷平均浓度均为底层高于表层,并呈现出由河口向邻近海域降低的趋势。杭州湾及最大混浊带部分区域水体中以颗粒态磷为主,且颗粒态无机磷为磷的主要存在形态;长江口门及江苏东部近海区域水体中以溶解态磷为主,溶解态无机磷为磷的主要存在形态;舟山群岛东部外海区表层水体以溶解态磷为主,溶解态有机磷为磷的主要存在形态,而底层水体中溶解态磷浓度略高于颗粒态磷,以溶解态无机磷为磷的主要存在形态。水体中颗粒态无机磷与颗粒态有机磷、颗粒总磷与总磷、总磷与悬浮颗粒物均呈非常显著的正相关,说明悬浮颗粒物是颗粒态磷的主要影响因素。调查海域外海区域绝大部分站位水体中溶解态无机磷表层浓度接近或小于浮游植物生长限制的动力学最低阈值,是磷限制或潜在的磷限制区域。Based on field observations from July to September in 2006, the distribution characteristics and influence factor of some species phosphorus in waters of the Changjiang Estuary were discussed in this paper. The results showed that the concentrations of some species phosphorus were slightly higher in the bottom than in the surface, and decreased greatly from the estuary to the adjacent waters. The average of TP was 3.93 μmol/dma in the surface water and 5. 09 μmol/dma in the bottom water. The average of TDP was 1.40 μmot/dina in the surface water and 1. 56 μmol/dma in the bottom water. The average of PP was 2. 53μmol/dma in the surface water and 3. 55μmol/dm3 in the bottom water. The average of DIP was 0. 71 μmol/dma in the surface water and 0.90 μmol/dma in the bottom water. The average of DOP was 0.69 μmol/dma in the surface water and 0.72 μmol/dma in the bottom water. The average of PIP was 1.60 μmol/dma in the surface water and 2.42 μmol/dma in the bottom water. The average of POP was 0.93 μmol/dma in the surface water and 1.12μmol/dma in the bottom water. In A, PP was the main factor which affect the distribution of TP and account for 76.6% in the surface water and 83.2% in the bottom water, and PIP was the main existing forms of the TP and accounted for 50.8% in the surface water and 57.9% in the bottom water. In B, TDP was the main factor which affect the distribution of TP and accounted for 62.7% in the surface water and 64.3% in the bottom water, and DIP which was the main existing forms of the TP accounted for 36.7% in the surface water and 37.50//oo in the bottom water. In C, TDP was the main factor which affect the distribution of TP and accounted for 68.7% in the surface water and 52.3% in the bottom water, DOP was the main existing forms of the TP and accounted for 46.3% in the surface water; TDP was slightly higher than PP (47.7%) in the bottom water, DIP (30. 2%) and PIP (31. 4%) was the main existing forms of the TP. The positive correlations between PIP and POP, between
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