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Marine Ecosystem and Environment in the Tokyo Bay

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<strong>Mar<strong>in</strong>e</strong> <strong>Ecosystem</strong> <strong>and</strong> <strong>Environment</strong><br />

<strong>in</strong> <strong>the</strong> <strong>Tokyo</strong> <strong>Bay</strong><br />

–Past <strong>and</strong> Current-<br />

Naho HORIMOTO<br />

Department of Ocean Sciences<br />

Faculty of Marie Science<br />

<strong>Tokyo</strong> University of <strong>Mar<strong>in</strong>e</strong> Science <strong>and</strong> Technology


Moor<strong>in</strong>g operation <strong>and</strong> recovery<br />

Real time measurement of Primary Productivity <strong>in</strong> Sagami <strong>Bay</strong><br />

(SORST - JST)<br />

Depth, Temperature, Sal<strong>in</strong>ity, In situ PAR,<br />

Chlorophyll fluorescence,<br />

Primary Productivity by Fast Reputation Rate of Fluorescence<br />

Underwater w<strong>in</strong>ch is designed<br />

that Buoy moves up <strong>and</strong><br />

down with Kevlar rope <strong>in</strong><br />

accordance with a time-table<br />

user programmed.<br />

Profil<strong>in</strong>g Data is send to <strong>the</strong><br />

Lab by email


CTD SYSTEM<br />

(Conductivity=sal<strong>in</strong>ity, Temperature <strong>and</strong> Depth)<br />

CTD Cast W<strong>in</strong>ch Control<br />

Steel Wire Armored Cable<br />

Water Sampl<strong>in</strong>g<br />

Slip r<strong>in</strong>g<br />

Deck Unit<br />

PC Operation


CTD Sensors<br />

Pressure<br />

(Depth)<br />

Conductivity<br />

(Sal<strong>in</strong>ity)<br />

Cradle for<br />

Nisk<strong>in</strong> Bottle<br />

Sampler<br />

Chlorophyll Fluorometer<br />

Temperature<br />

Dissolved Oxygen<br />

light quantum<br />

(Irradiance)<br />

Ma<strong>in</strong> Body<br />

Light Attenuation Coefficient<br />

(Turbidimeter)


Pressure (Depth, m)<br />

CTD Vertical Profile <strong>in</strong> 20th December 2005 at Sagami <strong>Bay</strong><br />

Temperature(oC)<br />

Sal<strong>in</strong>ity<br />

Temperature<br />

Dissolved Oxygen<br />

Sal<strong>in</strong>ity (Practical Sal<strong>in</strong>ity Unit)<br />

Dissolved Oxygen (ml/l)<br />

Turbidimeter (%)<br />

In vivo Chlorophyll (ug/l)<br />

light quantum<br />

Chlorophyll<br />

light quantum (uE/m3/s)<br />

Turbidimeter


DIN (µM)<br />

Si(OH) 4 -Si (µM) PO 4 -P (µM)<br />

75<br />

70<br />

65<br />

60<br />

55<br />

50<br />

45<br />

40<br />

35<br />

30<br />

25<br />

1.6<br />

1.4<br />

1.2<br />

1.0<br />

0.8<br />

0.6<br />

0.4<br />

50<br />

40<br />

30<br />

20<br />

10<br />

1989<br />

Result from Mastumura et al. (2001)<br />

F3<br />

F6<br />

1990 1991 1992 1993 1994 1995 1996 1997 1998<br />

Cocks-Start Test<br />

Trends of decrease<br />

(a=0.05)<br />

Changes <strong>in</strong> surface nutrient concentrations at Sta.F3 <strong>and</strong> F6


After Kawabe <strong>and</strong> Kawabe (1997)<br />

(Chemical Oxygen Dem<strong>and</strong>)<br />

Variation of surface COD <strong>and</strong> DIN, <strong>and</strong> solar radiation


Chl a (µg/l)<br />

Solar radiation (MJ/m 2 )<br />

DIN (µM)<br />

40<br />

30<br />

20<br />

10<br />

14<br />

13<br />

13<br />

12<br />

12<br />

11<br />

11<br />

75<br />

70<br />

65<br />

60<br />

55<br />

50<br />

45<br />

40<br />

35<br />

30<br />

25<br />

Result from Mastumura et al. (2001)<br />

F3<br />

F6<br />

1989 1990 1991 1992 1993 1994 1995 1996 1997 1998<br />

Variation of Chl a, solar radiation, <strong>and</strong> DIN at Sta. F3 <strong>and</strong> F6<br />

F3<br />

F6


Before 1950s<br />

Ceratium<br />

Occurrence Times<br />

Gonyaulax<br />

Red Tide (a decade AV)<br />

Red Tide<br />

Skeletonema<br />

Prorocentrum<br />

Chaetoceros<br />

Heterosigma<br />

1950-1970s 1980-1990s<br />

Blue Tide<br />

(a decade AV)<br />

Occurrences of red tide <strong>and</strong> blue tide<br />

Blue Tide


greatly <strong>in</strong>creased amounts of phosphorus or nitrogen<br />

enter<strong>in</strong>g an aquatic ecosystem from ei<strong>the</strong>r sewage<br />

systems or agricultural fertilizers<br />

Sulfur was educed due to<br />

oxidation of hydrogen<br />

sulfide, that color is light<br />

blue <strong>and</strong> t<strong>in</strong>t smells of<br />

sulfur<br />

P N<br />

Bottom anoxia <strong>and</strong> ext<strong>in</strong>ction of benthos<br />

Red Tide <strong>and</strong> Blue Tide<br />

Red tide <strong>and</strong><br />

End of bloom, phytoplankton accumulate on <strong>the</strong> sea<br />

bottom <strong>and</strong> microbes consume large amount of<br />

oxygen to decompose <strong>the</strong>m.<br />

Phytoplankton are microscopic, s<strong>in</strong>gle-celled plants.<br />

Phytoplankton is a primary producer <strong>in</strong> <strong>the</strong> ocean.<br />

Sou<strong>the</strong>rn w<strong>in</strong>d cause upwell<strong>in</strong>g


size<br />

0.2µm<br />

PICO<br />

2µm<br />

NANO<br />

20µm<br />

MICRO<br />

200µm<br />

Dissolved<br />

organic carbon<br />

Microbial loop<br />

Trophic transfer of carbon<br />

Diagram of a mar<strong>in</strong>e food cha<strong>in</strong><br />

Classic food cha<strong>in</strong><br />

MACRO


30<br />

Annual mean nitrate at <strong>the</strong> surface<br />

(source World Ocean Atlas @ NODC)<br />

L<br />

Open Ocean<br />

Small<br />

(µM)<br />

nutrient<br />

s<br />

Chl a<br />

0.1<br />

0.5 1 10<br />

Composite image of chlorophyll<br />

concentration <strong>in</strong> <strong>the</strong> ocean<br />

(source SEAWIFS project)<br />

Coastal +<br />

Upwell<strong>in</strong>g area<br />

Large<br />

How does phytoplankton biomass <strong>and</strong> species composition vary ?<br />

What size dom<strong>in</strong>ates with<strong>in</strong> each area?<br />

H<br />

Chl a<br />

(µg L -1 )

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