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The study of spatial and temporal nutrient limitation in Meiliang Bay, Lake Taihu. Longyuan Yang 1 , Feizhou Chen 1 , Yunling Zhang 1 , Shixin Wang 2 (1 Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences; 2 Institute of Remote Sensing Applications, - PowerPoint PPT Presentation
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The study of spatial and temporal nutrient limitation in Meiliang Bay, Lake Taihu
Longyuan Yang1, Feizhou Chen1, Yunling Zhang1,
Shixin Wang2
(1 Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences;
2 Institute of Remote Sensing Applications,Chinese Academy of Sciences )
Purpose• To measure nitrogen and phosphorus concent
rations in Meiliang Bay, Lake Taihu, and analyze spatial and temporal variation of water quality parameters;
• To analyze the relationship between nutrient concentrations and dominant algae species.
• To study nutrient limitation status in Meiliang Bay, Lake Taihu.
Redfield Ratio• If N:P ratio > 16, there is P
limitation in the aquatic ecosystem;
• If N:P ratio < 16, there is N limitation in the aquatic
ecosystem.
Background about limitation factor research in Lake Taihu
• Phosphorus is the limitation factor in Lake Taihu (traditional opinion);
• There is nitrogen limitation sites in some seasons and in some aquatic area (Martin Dokulil et al. 2000);
• There is a limitation factor change phenomenon that from Liangxi river discharge area to the main body of Lake Taihu (McCarthy et al. 2007)
Sampling sitesRegular site: 25 (per 3 months)
Add specific site: 20 (2 times in 2004)
Total sites: 45
Distribution of sampling areaName Sites NL Range S Number
River discharge
L0 K5
B3 B4 B6 B7 B8
31.31-31.33 7
Inner bay L1 L2
K2 K3 K4 K6
B5 B9 B10 B11 B12
31.28-31.31 11
Outer bay L3 L4 K1 K7 K8
B1 B2 B13 B14 B15
31.24-31.28 10
Open area L5 L6 K9 K10 K11
K12 K19 K20
31.18-31.24 8
Central area L7 L8 L9 K13 K14
K15 K16 K17 K18
31.13-31.18 9
Function of Distribution
Name Function Distance
River Discharge
Pollution area by point source from Liangxi and Lvjing River
0 km
Inner B Near pollution source area of Bay
8 km
Outer B Fare pollution source and near open area of Bay
16 km
Open A Open area that connect with the Outer Bay
24 km
Central A Main body of Lake Taihu 36 km
Results
(Oct-2003 to Aug-2005)
For whole research area
Spatial and temporal variation calculate of nutrients
• Spatial variation in research area were calculated by average of all sites in one distribution area;
• Annual variation were calculated by all sites in same distribution area and separated seasons.
Interval to Average Index (IA Index)
I %=(Ci-Cm)*100/Cm
Where: I mean the IA index coefficient ;
Ci concentration of individual parameter;
Cm mean concentration of whole area
TN I ndex
-80. 0
-60. 0
-40. 0
-20. 0
0. 0
20. 0
40. 0
60. 0
80. 0
Wi n Spr Sum Fal l
Season
%
B1 B2 B3 B4 B5
TP I ndex
-60
-40
-20
0
20
40
60
Wi n Spr Sum Fal l
Season
%
B1 B2 B3 B4 B5
TN MB1
0
2
4
6
8
Wi nter Spr i ng Summer Fal l
C mg
/L
200320042005Mean
TN MB2
0
2
4
6
8
Wi nter Spr i ng Summer Fal l
C mg
/L
200320042005Mean
TN MB3
0123456
Wi nter Spr i ng Summer Fal l
C mg
/L
200320042005Mean
TN MB4
0
1
2
3
4
5
Wi nter Spri ng Summer Fal l
C mg
/L
200320042005Mean
TN MB5
0
12
34
5
Wi nter Spri ng Summer Fal l
C mg
/L200320042005Mean
MB1 TP
0. 00
0. 10
0. 20
0. 30
Wi nter Spr i ng Summer Fal l
C mg
/L
200320042005Mean
MB2 TP
0. 00
0. 10
0. 20
0. 30
Wi nter Spr i ng Summer Fal l
C mg
/L
200320042005Mean
MB3 TP
0. 00
0. 10
0. 20
0. 30
Wi nter Spr i ng Summer Fal l
200320042005Mean
MB4 TP
0. 00
0. 10
0. 20
0. 30
Wi nter Spr i ng Summer Fal l
C mg
/L
200320042005Mean
MB5 TP
0. 00
0. 10
0. 20
0. 30
Wi nter Spr i ng Summer Fal l
C mg
/L200320042005Mean
R (TN: TP)
0306090
120
MB1 MB2 MB3 MB4 MB5
R
Wi n Spr Sum Fal l
TP
0. 000. 050. 100. 150. 200. 25
Wi n Spr Sum Fal l
C mg
/L
MB1
MB2
MB3
MB4
MB5
TN
0. 02. 04. 06. 08. 0
Wi n Spr Sum Fal l
C mg
/L
MB1MB2MB3MB4MB5
The ratio of nitrogen over phosphorus
TN:TP Win Spr Sum Fall
MB1 78.5 79.4 29.8 41.5
MB2 98.7 81.7 24.0 35.4
MB3 92.3 81.2 25.1 30.2
MB4 74.9 85.0 27.4 20.8
MB5 53.4 76.0 27.9 15.9
Annual variation characters summary
• In winter and spring seasons the mole ratio of TN:TP are more higher than Readfield ratio (16) ; but in summer and fall seasons the mole ratio of TN:TP are almost equal to Readfield ratio.
• So there is dominant P limitation in Winter and Spring seasons (Colder season, water temperature < 20 oC ) and there is dominant N limitation in some areas in Summer and Fall seasons (Warmer season, water temperature > 20 oC ) except the P limitation in shore area of Lake Taihu.
• In open and central areas(B4 and B5) the mole ratio of TN:TP reduced serious than in river discharge area(B1) in whole year; so the open and central areas is the hot point for nitrogen limitation or nitrogen and phosphorus co-limitation mainly occur areas.
Dominant algae species in different areas (Oct. 27, 2003)
Area Name %
B1
Microcystis 29.19
Merismopedia 12.20
Scenesdesmus 36.22
Cyclotella 22.39
B2
Microcystis 67.51
Chlamydomonas 12.36
Euglena 8.08
Cyclotella 5.24
Cryptomonas 6.82
B3
Microcystis 93.27
Merismopedia 1.81
Chlamydomonas 2.80
Scenesdesmus 2.12
B4 Merismopedia 100.00
B5Merismopedia 81.53
Scenesdesmus 18.47
Conclusion• There is a phenomenon that phosphorus limitation ch
ange to nitrogen limitation from Liangxi river discharge area to the main body (open area) of Lake Taihu;
• Summer and Fall seasons is the nitrogen Limitation occur season; especially in the area that far away from pollution river discharge area such as in central area of Lake Taihu
• The phenomenon that limitation factor changes may occur in all large shallow eutrophication lakes and estuaries in east part of China and other north temperate zones
谢谢莅临指导 !
Thank you!
Welcome to Taihu Field Station !
Thank you for presentation