

FOLLOWUS
1.Center for Marine Environmental Studies, Ehime University, Matsuyama 7908577, Japan
2.Key Laboratory of Marine Environment and Ecology, Ministry of Education, Ocean University of China, Qingdao 266100, China
3.College of Environmental Science and Engineering, Ocean University of China, Qingdao 266100, China
4.College of Marine and Environmental Sciences, Tianjin University of Science and Technology, Tianjin 300457, China
GUO Xinyu, guo.xinyu.mz@ehime-u.ac.jp
收稿:2016-08-30,
录用:2016-10-15,
网络首发:2016-11-16,
纸质出版:2018-01
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王玉成, 郭新宇, 赵亮. Simulating the responses of a low-trophic ecosystem in the East China Sea to decadal changes in nutrient load from the Changjiang (Yangtze) River[J]. 海洋湖沼学报(英文), 2018,36(1):48-61.
Yucheng WANG, Xinyu GUO, Liang ZHAO. Simulating the responses of a low-trophic ecosystem in the East China Sea to decadal changes in nutrient load from the Changjiang (Yangtze) River[J]. Chinese Journal of Oceanology and Limnology, 2018, 36(1): 48-61.
王玉成, 郭新宇, 赵亮. Simulating the responses of a low-trophic ecosystem in the East China Sea to decadal changes in nutrient load from the Changjiang (Yangtze) River[J]. 海洋湖沼学报(英文), 2018,36(1):48-61. DOI: 10.1007/s00343-017-6233-z.
Yucheng WANG, Xinyu GUO, Liang ZHAO. Simulating the responses of a low-trophic ecosystem in the East China Sea to decadal changes in nutrient load from the Changjiang (Yangtze) River[J]. Chinese Journal of Oceanology and Limnology, 2018, 36(1): 48-61. DOI: 10.1007/s00343-017-6233-z.
Using a three-dimensional coupled biophysical model
we simulated the responses of a lowtrophic ecosystem in the East China Sea (ECS) to long-term changes in nutrient load from the Changjiang (Yangtze) River over the period of 1960-2005. Two major factors affected changes in nutrient load:changes in river discharge and the concentration of nutrients in the river water. Increasing or decreasing Changjiang discharge induced different responses in the concentrations of nutrients
phytoplankton
and detritus in the ECS. Changes in dissolved inorganic nitrogen (DIN)
silicate (SIL)
phytoplankton
and detritus could be identified over a large area of the ECS shelf
but changes in dissolved inorganic phosphate (DIP) were limited to a small area close to the river mouth. The high DIN:DIP and SIL:DIP ratios in the river water were likely associated with the different responses in DIN
DIP
and SIL. As DIP is a candidate limiting nutrient
perturbations in DIP resulting from changes in the Changjiang discharge are quickly consumed through primary production. It is interesting that an increase in the Changjiang discharge did not always lead to an increase in phytoplankton levels in the ECS. Phytoplankton decreases could be found in some areas close to the river mouth. A likely cause of the reduction in phytoplankton was a change in the hydrodynamic field associated with the river plume
although the present model is not suitable for examining the possibility in detail. Increases in DIN and DIP concentrations in the river water primarily led to increases in DIN
DIP
phytoplankton
and detritus levels in the ECS
whereas decreases in the SIL concentration in river water led to lower SIL concentrations in the ECS
indicating that SIL is not a limiting nutrient for photosynthesis
based on our model results from 1960 to 2005. In both of the above-mentioned cases
the sediment accumulation rate of detritus exhibited a large spatial variation near the river mouth
suggesting that core sample data should be carefully interpreted.
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