monitoring of harmful algal blooms - science for management to...
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Monitoring of Harmful algal blooms
- Science for management
to prevent occurrence of harm
Yasuwo Fukuyo Emeritus Professor
The University of Tokyo [email protected]
2014.8.12
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Monitoring purpose of HAB 1. Science development in order to know nature of harmful algae; ecophysiology, toxin chemistry, biology etc. 2. Management system in order to prevent occurrence of harm; through preventing fish mass mortality, human poisoning, and economic loss.
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Monitoring purpose of HAB 1. Science development in order to know nature of harmful algae; ecophysiology, toxin chemistry, biology etc. 2. Management system in order to prevent occurrence of harm; through preventing fish mass mortality, human poisoning, and economic loss.
![Page 4: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/4.jpg)
Monitoring purpose of HAB 1. Science development in order to know nature of harmful algae; ecophysiology, toxinchemistry, biology etc. 2. Management system in order to prevent occurrence of harm; through preventing fish mass mortality, human poisoning, and economic loss.
Experience in Japan, and the Philippines
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Two types of Harmful Algae and consequences
of their Blooms (HABs)
1. Toxin-producer (toxic plankton): People killer
toxin contamination in shellfish and fish,
poisoning (PSP, DSP, ASP, NSP, Ciguatera)
2. Red tide maker: Fish killer
mass mortality of marine life due to anoxia
and biochemical and mechanical damages,
unusual scenery
rem: 90% of Red tides (Algal Blooms) are
harmless or useful (increase of fish catch, etc.) .
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Two types of Harmful Algae and consequences
of their Blooms (HABs)
1. Toxin-producer (toxic plankton): People killer
toxin contamination in shellfish and fish,
poisoning (PSP, DSP, ASP, NSP, Ciguatera)
2. Red tide maker: Fish killer
mass mortality of marine life due to anoxia
and biochemical and mechanical damages,
unusual scenery
rem: 90% of Red tides (Algal Blooms) are
harmless or useful (increase of fish catch, etc.) .
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14
42
7
60
9
34
20
00
0
17
17
44
44
1
18
2
0 5 0 0 1 0 0 0 1 5 0 0 2 0 0 0 2 5 0 0
Philippines Philippines
Thailand Thailand
Malaysia Malaysia
Indonesia Indonesia
Brunei Brunei
PSP cases PSP cases Death Death
14
427
609
34
2267
17
44 44
1
134
0 5 0 0 1 0 0 0 1 5 0 0 2 0 0 0 2 5 0 0
Philippines Philippines
Thailand Thailand
Malaysia Malaysia
Indonesia Indonesia
Brunei Brunei
fatal case patients
(1976-2006)
Number of poisoning cases with fatal ones occurred after eating shellfish contaminated by paralytic toxins produced by microalgae
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Character of toxic algal bloom and algae
Toxic microalgae possess toxins. Toxin composition vary by microalgal species. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
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Five types poisoning
Different symptom by different toxins which are produced by different types of organisms
PSP
ciguatera
ASP
DSP
NSP
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Character of toxic algal bloom and algae
Toxic microalgae possess toxins. Toxin composition vary by microalgal species. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
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planozygotes
fussion of gametes
Hypnozygotes (resting cysts)
Vegetative cells
Life cycle of Dinoflagellates
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Character of toxic algal bloom and algae
Toxic microalgae possess toxins. Toxin composition vary by microalgal species. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.) Environmental condition temperature, salinity, nutrients, grazing pressure Therefore toxin amount in one cell vary time by time. It means that prediction of toxin amount in shellfish
(plankton feeders) cannot be calculated or predicted by number of toxic plankton cells.
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Toxin
Filter feeders such as bivalves and tunicates feed on microalgae and decompose them. Toxins are absorbed inside body of the bivalve and some are excreted to outside. Difference between intake and outgoing are accumulated inside the bivalve. Speed of accumulation and excretion vary by species of filter feeders. Toxin mostly stay at mid-gut gland in case of bivalves.
decomposition
If people eat bivalves accidentally keeping toxins more than a certain level, people become sick.
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Comparison between toxic algal cell number and toxicity of mussel.
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Character of toxic algal bloom and algae Toxic microalgae possess toxins. Toxin composition vary by microalgal species. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.) Environmental condition temperature, salinity, nutrients, grazing pressure Therefore toxin amount in one cell vary time by time. Prediction of toxin amount in shellfish (plankton feeders)
cannot be calculated or predicted by number of toxic plankton cells.
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Noble ScallopChlamys nobilis
Short-necked clamTapes philippinaris
Blue MusselMytilus edulis
Yesso SallopPactinopectein yessoensis
Japanese oyster(Giant pacific oyster)Crassostrea gigas
Common bivalve species and ascidian species for monitoring on the PSP and DSP in Japan.
Sea squirt Halocynthia roretzi
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Character of toxic algal bloom and algae
Toxic microalgae possess toxins. Toxin composition vary by microalgal species. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
![Page 19: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/19.jpg)
Character of toxic algal bloom and algae
Toxic microalgae possess toxins. Toxin composition vary by microalgal species. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
![Page 20: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/20.jpg)
planozygotes
fussion of gametes
Hypnozygotes
(resting cysts) Vegetative cells
Life cycle of Dinoflagellates
![Page 21: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/21.jpg)
Character of toxic algal bloom and algae
Toxic microalgae possess toxins. Toxin composition vary by microalgal species. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
therefore we need to monitor toxicity of fish and shellfish
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Management to prevent harmful consequences of toxic blooms
1. Prevention of bloom: IMPOSSIBLE Sometimes decrease of nutrients works favorable to the bloom
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Management to prevent harmful consequences of toxic blooms
1. Prevention of bloom: IMPOSSIBLE Sometimes decrease of nutrients works favorable to the bloom
2. Prevention of toxin contamination: IMPOSSIBLE
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Management to prevent harmful consequences of toxic blooms
1. Prevention of bloom: IMPOSSIBLE Sometimes decrease of nutrients works favorable to the bloom
2. Prevention of toxin contamination: IMPOSSIBLE
3. Prevention of poisoning: POSSIBLE 3-1. monitoring of toxins at appropriate system centralize vs. localize monitoring representativeness of sample (location, depth, frequency) authorized laboratory for toxin/plankton analysis (QA/QC) by internationally recognized methods 3-2. public awareness (including enforcement)
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Management to prevent harmful consequences of toxic blooms
1. Prevention of bloom: IMPOSSIBLE Sometimes decrease of nutrients works favorable to the bloom
2. Prevention of toxin contamination: IMPOSSIBLE
3. Prevention of poisoning: POSSIBLE 3-1. monitoring of toxins at appropriate system centralize vs. localize monitoring representativeness of sample (location, depth, frequency) authorized laboratory for toxin/plankton analysis (QA/QC) by internationally recognized methods 3-2. public awareness (including enforcement)
4. Prevention of fatal case of poisoning: POSSIBLE 4-1. public awareness including medical doctors 4-2. preparation of artificial respirator at hospital
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Areas affected by
PSP in Japan
Alexandrium
Expansion of the affected area become obvious in 1990s.
Red color parts show prefectures having closure of harvesting of shellfish by PSP toxin contamination. (data:Japan Fisheries Agency)
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Sea areas affected by Paralytic Shellfish Poisoning with exceeding the quarantine limits of 4MU/g are shown by closed circles.
Coasts of Hokkaido, Iwate, Aomori, Miyagi Prefectures are officially divided into some areas for restriction. In other prefectures, the restricted areas have been decided according to the shellfish fishery grounds.
Decadal map of PSP outbrakes in Japan (1991-2000)
sampled, but no toxicity detected
one time (one year)
2-5 times
6-10 times
Lake Saroma
Yamada Bay
Lake Hamana
Ofunato Bay
Monitoring of shellfish toxicity and plankton occurrence is made. But only the toxicity data is used for regulation (closure of area).
Localized monitoring system
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Philippine case where expansion of area affected by PSP was so wide and quick
June 1994 Dec 1997 Oct 1991 Oct 1998
July 1983 Aug 1983 Sep 1983 Apr 1987
Aug 1988 Nov 1988 Feb 1990 Sep 1990
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…To prevent recurrence of poisoning, we can do something…
• Effective management requires:
1. Cost-effective monitoring system and techniques
2. Dedicated and responsible personnel to conduct monitoring
3. Strategies to educate/inform the people
Experience in the Philippines with BFAR request from one poor fisherman who lost his son by poisoning
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Country background information
archipelago w/ > 7,100 islands
land area = 298,170 sq km
total territorial waters = 2.2 M sq km
coastline length = 36,289 km
Population = 76 million 35% below poverty line Poverty line=monthly income <P15,000 or <400 USD
Administrative division: Province = 78 cities = 61
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Socio-economic profile of
shellfish workers/fishermen
- No fishermen cooperative/union - Farm workers are paid daily wage of P240 or 6USD - Shellfish are cheap source of protein for low income people
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Green mussel farms in Manila Bay
Green mussels
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Oyster farms in Manila Bay
Oysters
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Clipping of Newspaper in the Philippines
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Occurrence and Distribution of PSP in the Philippines
Pyrodinium bahamense
Most of shellfish aquaculture sites are far from Manila where PSP toxin can be measured.
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Public health impact of HABs in the
Philippines
0
50
100
150
200
250
300
350
Year
Num
ber
PSP cases
deaths
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Manila Bay weekly monitoring
In other local areas monthly monitoring: not enough
Toxin analysis is done in central laboratory in Manila
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Organizational Structure of the National Red Tide Task Force
IACEH
NRTTF
BFAR DOH EMB DILG PIA PCG DOST
Regional/Provincial RT Testing Centers
List of Acronyms: IACEH - Inter-Agency Committee BFAR – Bureau of Fisheries and on Environmental Health Aquatic Resources NRTTF - National Red Tide Task Force EMB- Environment and Management DOH - Department of Health Bureau DILG - Department of Interior and DOST- Department of Science and Local Government Technology PIA - Philippine Information Agency PCG – Philippine Coast Guard
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Limitations/constraints of management
1. Lack of technical capability
-trained manpower
-laboratory facilities and equipment
2. Lack of mechanism to disseminate accurate and timely information
3. Multi-sectoral agencies involved cause delays in implementation of regulatory action
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Vision of HAB Management in the Philippines
1. Shift from centralized to decentralized management regime
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Consultation/dialogue
How to decentralized Management???
Understanding/recognition of problems
Needs assessment
Capability building
Transfer and acceptance of responsibility/ authority
Empowerment of LGUs
1
2
3 4
5
6
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JICA’s assistance to enhance monitoring capability
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Vision of HAB Management in the Philippines
2. Cost effective and efficient system:
• Country-wide plan
• Empowerment of LGUs in management decisions (regulatory actions)
1. Shift from centralized to decentralized management regime
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Vision of HAB Management in the Philippines
2. Cost effective and efficient system:
• Country-wide plan
• Empowerment of LGUs in management decisions (regulatory actions)
1. Shift from centralized to decentralized management regime
3. Prevent and reduce impact of HAB on public health and economy
• Information campaign to educate fishermen and the public
• Dissemination of timely and accurate information
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People died in the Philippines
People are saved in Canada
Still problem remains
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People died in the Philippines
People are saved in Canada
Still problem remains
Still need raising more concern from public, especially fishery folks, medical doctors, and mass media.
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Two types of Harmful Algae and consequences
of their Blooms (HABs)
1. Toxin-producer (toxic plankton): People killer
toxin contamination in shellfish and fish,
poisoning (PSP, DSP, ASP, NSP, Ciguatera)
2. Red tide maker: Fish killer
mass mortality of marine life due to anoxia
and biochemical and mechanical damages,
unusual scenery
rem: 90% of Red tides (Algal Blooms) are
harmless or useful (increase of fish catch, etc.) .
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Two types of Harmful Algae and consequences
of their Blooms (HABs)
1. Toxin-producer (toxic plankton): People killer
toxin contamination in shellfish and fish,
poisoning (PSP, DSP, ASP, NSP, Ciguatera)
2. Red tide maker: Fish killer
mass mortality of marine life due to anoxia
and biochemical and mechanical damages,
unusual scenery
rem: 90% of Red tides (Algal Blooms) are
harmless or useful (increase of fish catch, etc.) .
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Two types of Harmful Algae and consequences
of their Blooms (HABs)
1. Toxin-producer (toxic plankton): People killer
toxin contamination in shellfish and fish,
poisoning (PSP, DSP, ASP, NSP, Ciguatera)
2. Red tide maker: Fish killer
mass mortality of marine life due to anoxia
and biochemical and mechanical damages,
unusual scenery
rem: 90% of Red tides (Algal Blooms) are harmful
or useful.
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Toxin amount (and composition?) vary depending on physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
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Red red tide at surface
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Subsurface red tide by Chattonella antiqua detected by change of color made by propeller of fishing boats running at red tide area
Subsurface grey red tide
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
![Page 55: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/55.jpg)
Pink and green red tides
Japan, Noctiluca
Thailand, Noctiluca
Australia, Noctiluca
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Brown and grey red tides
Germany, Nodularia
Japan, Karenia
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White red tide
Australia, Gephyrocapsa
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The color varies depending on growth stage algae.
Finland, cyanobacteria
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Noctiluca bloom at night (shinning white)
(from web-site)
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Green tide: bloom of macroalgae Ulva and Enteromorpha
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Toxin amount (and composition?) vary depending on
physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
![Page 62: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/62.jpg)
One drop of discolored water by Cochlodinium polykrikoides
in the Gulf of Thailand
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Cochlodinium polykrikoides
Normal condition Usually more than 50 different species can be found
Red Tide 1-2 species are
dominanat.
Pyrodinium bahamense
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Number of causative species of red tides
Among 140 cases of red tides in 1964-1970 Dominance (>95%) by one species: 97 cases (69%) Two species One species 95-75%, the other 25-1%: 25 cases Each species occupied 75-25%: 18 cases (Adachi 1972)
Among 1020 cases of red tides in 1992-2000 Dominance by one species: 803 cases (79%) Dominance by two species: 165 cases (16%) Dominance by three species: 52 cases (5%) (Seto Inland Sea Fisheries Coordination Office, 1993-2001)
One species forms red tides in most of cases, but plural species sometimes form them.
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Toxin amount (and composition?) vary depending on physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
![Page 66: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/66.jpg)
How many causative species can we count ?
Adachi 1972: 41 species Seto Inland Sea Coordination Office 1992-2000: 46 spec Fukuyo 1992: 48 species of dinoflagellates
Number of causative species must be more than 80.
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Frequent causative organisms (genus) and red tide case number in western Japan in 1992-2000
Genus names 1992 1993 1994 1995 1996 1997 1998 1999 2000 Total
Noctiluca 31 39 25 18 25 30 24 16 29 237
Gymnodinium 17 10 15 23 32 23 6 8 18 152
Heterosigma 22 22 19 14 12 17 16 15 14 151
Mesodinium 3 6 4 6 3 29 11 18 6 86
Skeletonema 5 10 6 10 8 8 13 9 10 79
Prorocentrum 8 8 5 7 4 13 4 16 9 74
Gonyaulax 0 7 4 3 0 1 15 2 1 33
Chaetoceros 1 3 4 2 4 4 4 2 6 30
Chattonella 3 3 1 3 0 5 2 7 3 27
Thalassiosira 2 0 6 1 2 0 1 6 4 22
Heterocapsa 1 1 0 1 1 4 4 5 1 18
Alexandrium 2 0 2 3 0 2 0 5 0 14
Leptocylindrus 1 0 2 2 1 1 3 0 4 14
Pseudo-Nitzschia 1 1 4 0 1 3 3 0 0 13
Ceratium 1 1 0 1 6 3 0 0 0 12
Cochlodinium 1 1 0 0 3 0 1 5 1 12
Rhizosolenia 0 2 2 0 0 1 2 1 2 10
Eutreptiella 1 2 2 0 1 0 0 0 1 7
Fibrocapsa 1 1 0 0 1 0 0 2 1 6
Eucampia 0 1 1 0 0 0 1 1 0 4
Gyrodinium 0 0 0 1 1 0 0 1 0 3
Peridinium 0 0 1 0 0 0 0 0 1 2
Coscinodiscus 1 0 0 0 0 0 0 0 0 1
Dictyocha 0 1 0 0 0 0 0 0 0 1
Lauderia 0 1 0 0 0 0 0 0 0 1
Navicula 0 0 0 0 0 0 0 0 1 1
Pseudo-nitzschia 0 0 0 0 0 0 0 0 1 1
dinoflagellates 562/1011
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) amount (and composition?) vary depending on physiological
condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
![Page 69: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/69.jpg)
120,000 Het.a
128,000 Het.a
130,000 Het.a
135,000 Het.a
147,150 Het.a
153,000 Het.a
158,500 Gon.ma
160,000 Kar.m
209,000 Pr.d
240,000 diatom
258,000 Het.a
298,000 Het.a
298,000 Het.a
300,000 Het.a
390,000 Het.a
476,700 Het.a
10 Noc.s 20 Noc.s 24 Noc.s 26
Coc. Cos.
50 C.a 50 Noc.s 50 Het.a 75 Noc.s 75 Noc.s 75 Noc.s 95 C.a
100 Noc.s 100 Noc.s 100 Noc.s 100 Noc.s 100 Noc.s 112 Ak.sa
Higher and smaller cell number (cells/ml) in a red tide water (among 762 cases)
Het.a: Heterosigma akashiwo Pr.d: Prorocentrum “dentatum” Kar.m: Karenia mikimotoi Gon.ma: Gonyaulax polygramma
Higher number Smaller number
Ak. sa: Akashiwo sanguinea Noc. s: Noctiluca scintillans C.a: Chattonella amtiqua Cos.: Coscinodiscus sp.
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Cell number in red tide water is 10-476,700 in 1 ml.nt (and
composition?) vary depending on physiological condition of cell (growth stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
![Page 71: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/71.jpg)
coverage of area (km2) of red tide (among 455 cases)
Ske. c: Skeletonema costatum Noc. s: Noctiluca scintillans Lep. d: Leptocylindrus danicus Gon.ma: Gonyaulax polygramma Kar. m: Karenia mikimotoi
Mes. r: Mesodinium rubeum Noc. s: Noctiluca scintillans C. m: Chattonella marina Per. q.: Peridinium quinquecorne 0.0005 Noc.s
0.0020 C.m
0.0020 Noc.s
0.0040 Kar.m
0.0050 Noc.s
0.0050 Pr.d
0.0100 Mes.r
0.0100 Noc.s
0.0100 Noc.s
0.0160 Noc.s
0.0190 Noc.s
0.0200 Per.q
0.0200 Noc.s
0.0200 Noc.s
0.0300 Noc.s
0.0300 Mes.r
Smaller RT
650 Het.a
660 Kar.m
672 Ske.c
675 Ske.c
720 Ske.c
750 Gon.ma
750 Lep.m
828 Lep.d
890 Ske.c
900 Noc.s
1,040 Ske.c
1,040 Ske.c
1,288 Ske.c
1,360 Ske.c
644 Ske.c
Larger RT
640 Ske.c
>1,000 km2: 4 cases > 800 : 3 > 600 : 14 > 400 : 18 > 200 : 53 > 100 : 43
> 50 : 33 > 10 : 64 > 5 : 36 > 1 :104 < 1 : 83
A half of RTs is <10 km2
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Cell number in red tide water is 10-476,700 in 1 ml of water. Size of red tides is 0.0005-1,360 km2. Average < 10 km2. ) vary depending on physiological condition of cell (growth
stage, speed, etc.)
Bloom of toxic microalgae, even in low conc. (20 cells/one L), associates harmful consequence.
Toxin accumulation rate in marine organisms vary by species.
Many PSP toxin producers possess cyst stage in life cycle. → simultaneous occurrence and disappearance, and
expansion of blooming area DSP and ciguatera causing algae may not have cyst stage.
People cannot eat toxic microalgae directly, as they are too small, but people eat shellfish and fish which feed the toxic ones.
![Page 73: Monitoring of Harmful algal blooms - Science for management to …iocwestpac.org/files/upload_manual/YF HAB management.pdf · 2014. 11. 12. · Monitoring of Harmful algal blooms](https://reader034.vdocuments.us/reader034/viewer/2022052101/603a9f30b0719b6a2135427b/html5/thumbnails/73.jpg)
Frequency of red tide duration (among 1020 cases)
25 15 15 14 16 13 16 12 23 11 14 10
23 9 49 8 40 7 34 6 51 5 56 4 74 3
111 2 276 1
Case RTnumber RT Days
9 30 7 29 3 28 7 27 1 26 6 25 3 24 3 23
20 22 7 21 8 20
14 19 12 18 13 17 13 16
2 45 1 44 2 43 1 42 0 41 4 40 0 39 2 38 3 37 5 36 1 35 1 34 2 33 5 32 3 31
1 60 0 59 2 58 1 57 0 56 1 55 1 54 1 53 2 52
0 51 4 50 1 49 1 48 1 47 1 46
1 106 1 99 1 97 1 94 1 87 1 85 1 81 1 80 1 76 3 72 1 71 1 69 2 65 1 64
517
642
728
823
A half of RTs is <4 days Total
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Cell number in red tide water is 10-476,700 in 1 ml of water. Size of red tides is 0.0005-1,360 km2. Average < 10 km2. Duration of red tides is 1-276 days. Usually shorter than 4 days.
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How many red tide number can we observe?
Areas with intensive monitoring for red tides
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In total about 200 red tide cases are observed annually in 1980-2000 in the four areas of the western Japan
No Data
No Data
No Data
No Data
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Cell number in red tide water is 10-476,700 in 1 ml of water. Size of red tides is 0.0005-1,360 km2. Average < 10 km2. Duration of red tides is 1-276 days. Usually shorter than 4 days. Red tide case number varies depending on area.
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east – west: 450 km, north – south: 15-55 km
area: 23,203 km2, average depth: 38.0 m shoreline: 6,868 km, 700 islands
Fish aquaculture industry became active since 1960s.
Experience of Japan on red tides
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瀬戸内海における赤潮発生件数と漁業被害件数の推移
0
50
100
150
200
250
300
350
1950 55 60 65 70 75 80 85 90 95 2000
年次
赤潮
発生
件数
0
5
10
15
20収
穫量
(10,0
00 t)
赤潮発生件数
ブリ類養殖収穫量(10,000 t)
Red t
ide c
ase
num
ber
Red tide case number
Yellow tail fish Production
Pro
ductio
n o
f yello
w ta
il fish b
y a
quacu
lture
(x 1
,000t)
No data on red tide case
Parallel increase of red tide occurrences and yellow tail fish aquaculture industry are obvious.
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Cell number in red tide water is 10-476,700 in 1 ml of water. Size of red tides is 0.0005-1,360 km2. Average < 10 km2. Duration of red tides is 1-276 days. Usually shorter than 4 days. Red tide case number varies depending on area. Also case number varies depending on environmental condition.
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‘70 ‘75 ‘80 ‘85 ‘90 ‘95 ‘00
In the early stage red tides with fisheries damages occupied nearly half of the cases.
After the early stage red tides with fisheries damages occupied almost 10% of the case number.
RT and HAB
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Cell number in red tide water is 10-476,700 in 1 ml of water. Size of red tides is 0.0005-1,360 km2. Average < 10 km2. Duration of red tides is 1-276 days. Usually shorter than 4 days. Red tide case number varies depending on area. Also case number varies depending on environmental condition. About 10 % red tide cause mass mortality of fish and shellfish.
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Heterocapsa circularisquama In 1988-1998 26 cases red tides. Among the 26 cases,
15 cases with mass mortality of bivalves (oyster, pearl oyster,
short necked clam, mussel )
Economic loss equivalent to
ca. 100M US$ (from Matsuyama 1999)
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Mass mortality of shellfish
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Mechanisms of fish mortality 1: daytime
free fatty acid production
normal gill
gill covered by mucus
difficulty in respiration
red tide plankton fish
faster swimming to get more O2
O2 production by photosynthesis
O2 in water
low high
recovery (live)
lactic acid in muscle
low blood pH
blood carry less O2 death
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Mechanisms of fish mortality 2: night time
free fatty acid production
normal gill
gill covered by mucus
difficulty in respiration
red tide plankton fish
faster swimming to get more O2
O2 consumption by respiration
O2 in water
low high
recovery (live)
lactic acid in muscle
low blood pH
blood carry less O2 death
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Mechanisms of fish mortality 3: night time and high temp.
free fatty acid production
normal gill
gill covered by mucus
difficulty in respiration
red tide plankton fish
faster swimming to get more O2
O2 consumption by respiration
O2 in water
low high
recovery (live)
lactic acid in muscle
low blood pH
blood carry less O2 death
high temperature
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Economic loss caused by red tides
Number of red tides
causing
fisheries damages
in the four areas
Lo
ss :
mil
lio
n U
SD
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Cell number in red tide water is 10-476,700 in 1 ml of water. Size of red tides is 0.0005-1,360 km2. Average < 10 km2. Duration of red tides is 1-276 days. Usually shorter than 4 days. Red tide case number varies depending on area. Also case number varies depending on environmental condition. About 10 % red tide cause mass mortality of fish and shellfish. Economic loss by harmful red tides is sometimes >50M USD
mostly by fish in aquaculture farms.
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Character of red tide and red tide algae
Red tide is a discoloration of surface or subsurface water by microalgae.
Color of red tide is various, depending on causative organism. Species number of red tides are 1 or 2. Number of red tide causative species is >80 in one area.
(composition vary depending on area. Why?) Cell number in red tide water is 10-476,700 in 1 ml of water. Size of red tides is 0.0005-1,360 km2. Average < 10 km2. Duration of red tides is 1-276 days. Usually shorter than 4 days. Red tide case number varies depending on area. Also case number varies depending on environmental condition. About 10 % red tide cause mass mortality of fish and shellfish. Economic loss by harmful red tides is sometimes >50M USD
mostly by fish in aquaculture farms.
Is it possible to prevent red tides by science and management ????
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Fisheries production is still growing in the western Pacific, although those from other regions might reach the maximum plateau.
Comparing to the increase of the catch, that of the aquaculture production is much bigger.
re: observe the difference of unit of vertical axis
Aquaculture becomes important more and more.
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Fish cage culture
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Fish cage culture in Batam, Indonesia
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Small scale hatchery (Backyard Hatchery) in Indonesia
Difficult in controlling quality of their wastewater
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Shrimp culture ponds in Cam Ranh, Khanh Hoa, Vietnam
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River mouth areas along Thailand coast
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Mega scale land based aquaculture
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Shrimp farms in Sumatra, Indonesia
Mega scale aquaculture farm
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(Revised from Japan Fisheries Resource Conservation Association)
Mechanism: factors related to red tide blooming
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Mass mortality of milkfish, associating with red tide of Prorocentrum minimum in the Philippines
late January to
early February 2002
● Bolinao Bay
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by Chattonella in Japan
by Cochlodinium in Korea
by Karenia in Hong Kong
Fish Mass Mortality associated with a Red Tide
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(Revised from Japan Fisheries Resource Conservation Association)
Mechanism: factors related to red tide blooming
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Countermeasures (management) for elimination of red tide occurrences and harmful consequences Indirect: 1. Water and sediment quality improvement through regulations 2. Water and sediment quality improvement by projects of rehabilitation 3. Improvement of aquaculture technology 4. Management and info. exc. net work Direct: 1. Spray of clay 2. Filtration 3. Chemicals etc.
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Countermeasures (management) for elimination of red tide occurrences and harmful consequences Indirect: 1. Water and sediment quality improvement through regulations 2. Water and sediment quality improvement by projects of rehabilitation 3. Improvement of aquaculture technology 4. Management and info. exc. net work Direct: 1. Spray of clay 2. Filtration 3. Chemicals etc.
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瀬戸内海における赤潮発生件数と漁業被害件数の推移
0
50
100
150
200
250
300
350
1950 55 60 65 70 75 80 85 90 95 2000
年次
赤潮
発生
件数
0
5
10
15
20収
穫量
(10,0
00 t)
赤潮発生件数
ブリ類養殖収穫量(10,000 t)
Red t
ide c
ase
num
ber
Red tide case number
Yellow tail fish Production
Pro
ductio
n o
f yello
w ta
il fish b
y a
quacu
lture
(x 1
,000t)
No data on red tide case
Parallel increase of red tide occurrences and yellow tail fish aquaculture industry are obvious.
Setting various regulation
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Change of load to Seto Inland Sea (from International EMECS Center 2008) Rem: duration of the upper and lower figures are different.
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瀬戸内海における赤潮発生件数と漁業被害件数の推移
0
50
100
150
200
250
300
350
1950 55 60 65 70 75 80 85 90 95 2000
年次
赤潮
発生
件数
0
5
10
15
20収
穫量
(10,0
00 t)
赤潮発生件数
ブリ類養殖収穫量(10,000 t)
Red t
ide c
ase
num
ber
Red tide case number
Yellow tail fish Production
Pro
ductio
n o
f yello
w ta
il fish b
y a
quacu
lture
(x 1
,000t)
No data on red tide case
Parallel increase of red tide occurrences and yellow tail fish aquaculture industry are obvious.
Setting various regulation
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Reduction of N and P may have relation to decrease of fishery production. If so, how to prevent eutrophication (degradation) without having reduction of fisheries production???
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Decolored Normal
Decoloration of culturing Nori (Porphyra sp.) seaweed
Culture raft of Nori
Winning diatom
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Countermeasures (management) for elimination of red tide occurrences Indirect: 1. Water and sediment quality improvement through regulations 2. Water and sediment quality improvement by projects of rehabilitation 3. Improvement of aquaculture technology 4. Management and info. exc. net work Direct: 1. Spray of clay 2. Filtration 3. Chemicals etc.
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Mitigation: Prevention of harmful red tides by Chattonella by prolongation of diatom red tide.
Chattonella cannot bloom during diatom red tide.
Diatom red tide itides useful, as they are foods for marine lives and keep environment clear.
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Countermeasures (management) for elimination of red tide occurrences and harmful consequences Indirect: 1. Water and sediment quality improvement through regulations 2. Water and sediment quality improvement by projects of rehabilitation 3. Improvement of aquaculture technology 4. Management and info. exc. net work Direct: 1. Spray of clay 2. Filtration 3. Chemicals etc.
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Mitigation using algicidal bacteria
Seaweeds have many bacteria on the surface which excrete substances killing microalgae.
Culture of seaweed at surface of fish cages.
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Countermeasures (management) for elimination of red tide occurrences Indirect: 1. Water and sediment quality improvement through regulations 2. Water and sediment quality improvement by projects of rehabilitation 3. Improvement of aquaculture technology 4. Management and info. exc. net work Direct: 1. Spray of clay 2. Filtration 3. Chemicals etc.
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Countermeasures (management) for elimination of red tide occurrences Indirect: 1. Water and sediment quality improvement through regulations 2. Water and sediment quality improvement by projects of rehabilitation 3. Improvement of aquaculture technology 4. Management and info. exc. net work Direct: 1. Spray of clay 2. Filtration 3. Chemicals etc.
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対策 粘土散布
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Occurrences of C. polykrikoides in Japan and Korea
Red tides of C. polykrikoides have continuously occurred along coastal waters,
does this imply that the Japanese and Korean population are identical?
Jun-Aug
2002
?
Miyahara et al. 2005
Matsuoka & Iwataki 2004
Sep. 2003
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Malaysia
Palawan
Cochlodinium
polykrikoides
Red tide occurred in Malaysian and
Philippine waters (from Azanza 2005)
How to confirm safety of fishes?
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Thank you for your patience
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expansion of utilization of costal area
HABs occurrence mechanism 1
toxin producing species
change of water quality
optimum for the growth of certain phytoplankton
red tide causing species
toxin accumulation in marine organisms
mass mortality of marine organisms
red tide
people poisoning closure of market
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expansion of utilization of costal area
HABs occurrence mechanism and countermeasure 1
toxin producing species
change of water quality
optimum for the growth of certain phytoplankton
red tide causing species
toxin accumulation in marine organisms
mass mortality of marine organisms
red tide
people poisoning closure of market
management for conservation of coastal environment
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expansion of utilization of costal area
HABs occurrence mechanism 2
increase of chance to eat marine
products having contaminated toxins
increase of population (resident, tourist)
increase of aquaculture and
its products (fish, shellfish)
mass mortality of marine organisms
people poisoning closure of market
increase of chance to meet red tide
increase of chance to accumulate toxins
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expansion of utilization of costal area
HABs occurrence mechanism and countermeasures 2
increase of chance to eat marine
products having contaminated toxins
increase of population (resident, tourist)
increase of aquaculture and
its products (fish, shellfish)
mass mortality of marine organisms people poisoning closure of market
increase of chance to meet red tide
increase of chance to accumulate toxins
management for monitoring toxins in marine products
improvement of aquaculture technology
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あってほしいと考える「海」は人によって異なる。そのため、期待する海を創造していく方法も異なる。今まで、我々は多くの試行錯誤を繰り返してきたので、それを「赤潮、富栄養化」を例に考えてみたい。 「きれいな海」と「豊かな海」 を両立させるためには、何をどのように考えていかなければならないか?
きれいな海と望ましい環境
どのような海と環境を望み、創り、守るのか?
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あってほしいと考える「海」は人によって異なる。そのため、期待する海を創造していく方法も異なる。今まで、我々は多くの試行錯誤を繰り返してきたので、それを「赤潮、富栄養化」を例に考えてみたい。 「きれいな海」と「望ましい環境」 を両立させるためには、何をどのように考えていかなければならないか?
きれいな海と望ましい環境
どのような海と環境を望み、創り、守るのか?
とても一筋縄ではいかない。でも将来のために
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JAICAF 2010
漁業の現状
世界の漁獲量はすでに頭打ちの状態。今後人口はより増える。だから賢い養殖が必要。
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FAO 2008
世界の養殖漁業
中国
中国以外のアジア
中国
中国以外のアジア
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養殖量の多いトップ15の内、11カ国はアジア、そのうち東南アジアと東アジアがそれぞれ5,4カ国となっている。 JAICAF 2010
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魚貝類が死ぬ原因はいくつかあり、単純ではない
酸素欠乏 鰓つまり(粘液分泌量増加、赤潮プランクトン付着) 鰓表皮細胞の機械的損壊 血液のpH低下
赤潮プランクトンの分泌する毒物質
酸欠水 赤潮プランクトンの腐敗
赤潮が起こっても魚が死なない養殖をする。
すべての赤潮が魚貝類被害を伴うわけではなく、瀬戸内海では発生した赤潮の10%程度が問題となっている。この割合は養殖技術の向上などにより以前より低くなっている。
例えば
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瀬戸内海における赤潮発生件数と漁業被害件数の推移
0
50
100
150
200
250
300
350
1950 55 60 65 70 75 80 85 90 95 2000
年次
赤潮
発生
件数
0
5
10
15
20収
穫量
(10,0
00 t)
赤潮発生件数
ブリ類養殖収穫量(10,000 t)
Red t
ide c
ase
num
ber
Red tide case number Yellow tail fish Production
Pro
ductio
n o
f yello
w ta
il fish b
y a
quacu
lture
(x 1
,000t)
No data
魚類斃死は発生した赤潮の10%程度でみられる
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魚類の斃死機構