Advancing Global Understanding on the Origin and Impacts of Ciguatera …file.iocwestpac.org/TMO/5-9...

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1 Advancing Global Understanding on the Origin and Impacts of Ciguatera Fish Poisoning in Tropical Oceans Dr. Leo Chan State Key Laboratory in Marine Pollution Shenzhen Key Laboratory for the Sustainable Use of Marine Biodiversity Department of Biomedical Sciences City University of Hong Kong

Transcript of Advancing Global Understanding on the Origin and Impacts of Ciguatera …file.iocwestpac.org/TMO/5-9...

  • 1

    Advancing Global Understanding

    on the Origin and Impacts of Ciguatera

    Fish Poisoning in Tropical Oceans

    Dr. Leo Chan

    State Key Laboratory in Marine Pollution

    Shenzhen Key Laboratory for the Sustainable Use of Marine Biodiversity

    Department of Biomedical Sciences

    City University of Hong Kong

  • 2

    Regional Meeting on Future Focus and Cooperation in HAB Research

    2nd

    ASIAN GEOHAB MEETING

    28 January – 1 February 2008

  • 3

    • Hong Kong people consumes 30,000 to

    35,000 tonnes of reef fish per annum (with a

    total wholesale value about US$ 500 millions).

    Live Reef Food Fish Trading (LRFFT)

    • Annual regional trade in live reef food fish in the Asia-Pacific region

    is estimated around US$ 810 million;

  • Variola louti (yellow-edged lyretail)

    Epinephelus fuscoguttatus (Brown-marbled grouper)

    Plectropomus leopardus (leopard coral grouper)

    Gymnothorax spp. (moray eel)

    Plectropomus areolatus (areolated coral grouper)

    Cromileptes altivelis (humpback grouper)

    Epinephelus polyphekadion (camouflage grouper)

    Epinephelus lanceolatus (giant grouper)

    Common live coral reef food fish species in Hong Kong

    香港常見進口珊瑚礁可食用魚類品種

    Cheilinus undulaus (humphead wrasse)

    Lutjanus bohar (two-spot red snapper)

    Lutjanus argentimaculatus (mangrove red snapper)

    Docosahexaenoic acid

    (DHA)

    • Because of their superior

    taste and texture, fish

    captured on coral reefs have

    become the most valued

    fishes in seafood markets of

    Hong Kong and Mainland

    China;

    • Consumption of fish provides

    energy, protein and a range

    of other important nutrients;

    • Groupers are regarded as a

    delicacy and a luxury food

    item.

  • Variola louti (yellow-edged lyretail)

    Epinephelus fuscoguttatus (Brown-marbled grouper)

    Plectropomus leopardus (leopard coral grouper)

    Gymnothorax spp. (moray eel)

    Plectropomus areolatus (areolated coral grouper)

    Cromileptes altivelis (humpback grouper)

    Epinephelus polyphekadion (camouflage grouper)

    Epinephelus lanceolatus (giant grouper)

    Common live coral reef food fish species in Hong Kong

    香港常見進口珊瑚礁可食用魚類品種

    Cheilinus undulaus (humphead wrasse)

    Lutjanus bohar (two-spot red snapper)

    Lutjanus argentimaculatus (mangrove red snapper)

    Docosahexaenoic acid

    (DHA)

    • Because of their superior

    taste and texture, fish

    captured on coral reefs have

    become the most valued

    fishes in seafood markets of

    Hong Kong and Mainland

    China;

    • Consumption of fish provides

    energy, protein and a range

    of other important nutrients;

    • Groupers are regarded as a

    delicacy and a luxury food

    item.

  • P-CTX-1

    Neuron

    Gastrointestinal disorder:

    Abdominal pain | vomiting |

    nausea | diarrhea

    Neurological disorder:

    Paraesthesia | reversal of hot

    and cold sensation | numbness

    | tingling

    Cardiovascular disorder:

    Irregular pulse | decreased blood

    pressure | bradycardia | dizziness

    Ciguatoxin (CTX)

    雪卡毒素

    Human Illness Associated with CFP

    6

    Sodium Channel

  • 7

    Diagnosis of CFP

    Diagnosis of CFP is based on intoxication

    symptoms;

    Test in the remaining fish meal by Mouse

    Bioassay (MBA) (Caillaud et al, 2010);

    Clinical differential diagnosis remains

    problematic because no reliable biomarkers;

    Misdiagnosed as illness such as influenza

    (Lewis, 2006).

  • P-CTX-1

    Neuron

    Gastrointestinal disorder:

    Abdominal pain | vomiting |

    nausea | diarrhea

    Neurological disorder:

    Paraesthesia | reversal of hot

    and cold sensation | numbness

    | tingling

    Cardiovascular disorder:

    Irregular pulse | decreased blood

    pressure | bradycardia | dizziness

    Ciguatoxin (CTX)

    雪卡毒素

    Human Illness Associated with CFP

    8

    Sodium Channel

    • Over 100 symptoms worldwide and not one

    specific symptom can be used to diagnose the

    illness

    • No way to predict whether a case will

    become chronic

    • There is no antidote

  • P-CTX-1

    Neuron

    Gastrointestinal disorder:

    Abdominal pain | vomiting |

    nausea | diarrhea

    Neurological disorder:

    Paraesthesia | reversal of hot

    and cold sensation | numbness

    | tingling

    Cardiovascular disorder:

    Irregular pulse | decreased blood

    pressure | bradycardia | dizziness

    Ciguatoxin (CTX)

    雪卡毒素

    Human Illness Associated with CFP

    9

    Sodium Channel

    • Worldwide public health institutions have

    ranked CFP as one of the most common food-

    borne illnesses;

    • About 50,000 – 500,000 reported cases of CFP

    annually, but could be under-reported and under-

    estimated due to a lack of diagnosis of CFP;

    • A Health Hazard to global seafood consumers.

  • 10

    An issue of local and global

    importance

  • 11

    Problems with CTX detection

    Patchy CTX occurrence;

    Many types of CTX;

    Available methods:

    Animal feeding test (e.g. mouse bioassay);

    Cell bioassay (e.g. neuroblastoma assay);

    Instrumental method (e.g. HPLC/MS/MS).

  • • > 400 species of bony fish at all trophic levels have been identified as

    ciguatoxic.

  • Variola louti (yellow-edged lyretail)

    Epinephelus fuscoguttatus (Brown-marbled grouper)

    Plectropomus leopardus (leopard coral grouper)

    Gymnothorax spp. (moray eel)

    Plectropomus areolatus (areolated coral grouper)

    Cromileptes altivelis (humpback grouper)

    Epinephelus polyphekadion (camouflage grouper)

    Epinephelus lanceolatus (giant grouper)

    Common live coral reef food fish species in Hong Kong

    香港常見進口珊瑚礁可食用魚類品種

    Cheilinus undulaus (humphead wrasse)

    Lutjanus bohar (two-spot red snapper)

    Lutjanus argentimaculatus (mangrove red snapper)

    Prevention of CFP is only based on

    avoidance of:

    • high risk fish species;

    • large fishes or;

  • Variola louti (yellow-edged lyretail)

    Epinephelus fuscoguttatus (Brown-marbled grouper)

    Plectropomus leopardus (leopard coral grouper)

    Gymnothorax spp. (moray eel)

    Plectropomus areolatus (areolated coral grouper)

    Cromileptes altivelis (humpback grouper)

    Epinephelus polyphekadion (camouflage grouper)

    Epinephelus lanceolatus (giant grouper)

    Common live coral reef food fish species in Hong Kong

    香港常見進口珊瑚礁可食用魚類品種

    Cheilinus undulaus (humphead wrasse)

    Lutjanus bohar (two-spot red snapper)

    Lutjanus argentimaculatus (mangrove red snapper)

    High Risk

    High Risk

    High Risk

    High Risk

    High Risk

    High Risk

    High Risk

    High Risk

    High Risk

  • Common live coral reef food fish species in Hong Kong

    香港常見進口珊瑚礁可食用魚類品種

    6.36ppb P-CTX equivalent

    E. caeruleopunctatus

    (油杉斑)

    4.82ppb P-CTX equivalent

    Epinephelus tauvina

    (花杉頭)

    Cephalopholis argus

    (藍星斑)

    12.88ppb P-CTX equivalent

    The toxicity thresholds for adverse effects in seafood consumers is

    0.1ppb P-CTX equivalent

    Herbivores (草食性魚)

    Ctenochaetus striatus

    (刺尾魚)Ctenochaetus lineatus

    (刺尾魚)

    4.71ppbP-CTX equivalent 6.26ppb P-CTX equivalent

    Carnivores (肉食性魚)

    75 cm 60 cm 40 cm

    18 cm - 24 cm 18 cm - 24 cm

  • Common live coral reef food fish species in Hong Kong

    香港常見進口珊瑚礁可食用魚類品種

    6.36ppb P-CTX equivalent

    E. caeruleopunctatus

    (油杉斑)

    4.82ppb P-CTX equivalent

    Epinephelus tauvina

    (花杉頭)

    Cephalopholis argus

    (藍星斑)

    12.88ppb P-CTX equivalent

    The toxicity thresholds for adverse effects in seafood consumers is

    0.1ppb P-CTX equivalent

    Herbivores (草食性魚)

    Ctenochaetus striatus

    (刺尾魚)Ctenochaetus lineatus

    (刺尾魚)

    4.71ppbP-CTX equivalent 6.26ppb P-CTX equivalent

    Carnivores (肉食性魚)

    75 cm 60 cm 40 cm

    18 cm - 24 cm 18 cm - 24 cm

    •For these reasons, recommendations

    regarding the consumption of smaller

    fishes or certain species to avoid the

    problem of ciguatera are only partly

    useful, and at times can be misleading.

  • Variola louti (yellow-edged lyretail)

    Epinephelus fuscoguttatus (Brown-marbled grouper)

    Plectropomus leopardus (leopard coral grouper)

    Gymnothorax spp. (moray eel)

    Plectropomus areolatus (areolated coral grouper)

    Cromileptes altivelis (humpback grouper)

    Epinephelus polyphekadion (camouflage grouper)

    Epinephelus lanceolatus (giant grouper)

    Common live coral reef food fish species in Hong Kong

    香港常見進口珊瑚礁可食用魚類品種

    Cheilinus undulaus (humphead wrasse)

    Lutjanus bohar (two-spot red snapper)

    Lutjanus argentimaculatus (mangrove red snapper)

    Prevention of CFP is only based on

    avoidance of:

    • high risk fish species;

    • large fishes or;

    • fishes imported from the CFP

    endemic regions.

  • Large number of live coral reef fish are

    imported into Hong Kong each year

    1970s

    1980s

    1990s

    Source: Sadovy, YJ (2003) The Live Reef

    Food Fish Trade While Stocks Last,

  • As a result of :

    1. The lack of an effective screening tool

    for CFP;

    2. There is no regulation on record of

    origin;

    3. Avoidance based on experiences and

    historical knowledges of local

    fishermen and consumers.

  • Apple Daily, 26th

    October, 2004Southcn.com, 2

    ndApril, 2004

    This was how our story began………

    Two prominent outbreaks in 1998 and

    2004

    more than 100 cases, affecting more

    than 400 people (Wong et al., 2005)

    29 tones of unscreened coral

    reef fishes were disposed of

    in one operation (Ta-Kung

    Pao, March 12, 1999)

  • Apple Daily, 26th

    October, 2004Southcn.com, 2

    ndApril, 2004

    This was how our story began………

    Two prominent outbreaks in 1998 and

    2004

    more than 100 cases, affecting more

    than 400 people (Wong et al., 2005)

    29 tones of unscreened coral

    reef fishes were disposed of

    in one operation (Ta-Kung

    Pao, March 12, 1999)

    CFP is confirmed to be an important

    cause of toxin food poisoning illness

    and a significant public health hazard

    in Hong Kong.

  • Coral

    Bioeroison

    Grazers*

    Food Sources

    Grazers*

    (Vectors)

    * Grazers are fishes that graze on

    hard surfaces for food and can be

    herbivorous, omnivorous and

    carnivorous fishes

    Loss of biodiversity

    Overgrazing

    Population

    explosions

    Diverse community

    with many species

    Community dominant

    by few species

    “Dead” community with

    no species present

    Human Health

    Predators

    Ec

    om

    onic

    Loss

    Ciguatera Fish Poisoning (CFP) / OverharvestingE

    nviro

    nm

    en

    ta

    l D

    estru

    ctio

    n

    Although ciguatera fishing poisoning is a

    significant human health hazard, an

    important microbial component of coral

    reefs, and a potential threat to tropical

    fisheries and coral reef ecosystems, the

    general state of knowledge on ciguatera

    fishing poisoning remains poor.

  • • Amount of CTX authentic standards is limited

    • several milligrams in the globe;

    • not commercially available;

    • Extremely expensive;

    • CTXs are at trace levels in coral reef fishes and remnants of consumed fish are often unavailable for testing

    • threshold level for acute CFP induction

    = 0.1 ng/g P-CTX-1 equivalent in fish muscle;

    • proposed safety level

    = 0.01 ng/g P-CTX-1 equivalent in fish muscle;

    • Analytical method for rapid, robust and reliable CTX detection is limited

    • regular screening of imported fishes for protection of human health.

    Challenges and key technological issues in

    CFP research

    (US$ 3,000 per microgram of

    P-CTX-1/P-CTX-2/P-CTX-3)

    US$40 per gram of Gold

    US$ 3 billion per gram of

    P-CTX-1/P-CTX-2/P-CTX-3

  • • Amount of CTX authentic standards is limited

    • several milligrams in the globe;

    • not commercially available;

    • Extremely expensive;

    • CTXs are at trace levels in coral reef fishes and remnants of consumed fish are often unavailable for testing

    • threshold level for acute CFP induction

    = 0.1 ng/g P-CTX-1 equivalent in fish muscle;

    • proposed safety level

    = 0.01 ng/g P-CTX-1 equivalent in fish muscle;

    • Analytical method for rapid, robust and reliable CTX detection is limited

    • regular screening of imported fishes for protection of human health.

    Challenges and key technological issues in

    CFP research

    (US$ 3,000 per microgram of

    P-CTX-1/P-CTX-2/P-CTX-3)

    US$40 per gram of Gold

    US$ 3 billion per gram of

    P-CTX-1/P-CTX-2/P-CTX-3

  • • Amount of CTX authentic standards is limited

    • several milligrams in the globe;

    • not commercially available;

    • Extremely expensive;

    • CTXs are at trace levels in coral reef fishes and remnants of consumed fish are often unavailable for testing

    • threshold level for acute CFP induction

    = 0.1 ng/g P-CTX-1 equivalent in fish muscle;

    • proposed safety level

    = 0.01 ng/g P-CTX-1 equivalent in fish muscle;

    • Analytical method for rapid, robust and reliable CTX detection is limited

    • regular screening of imported fishes for protection of human health.

    Challenges and key technological issues in

    CFP research

    (US$ 3,000 per microgram of

    P-CTX-1/P-CTX-2/P-CTX-3)

    US$40 per gram of Gold

    US$ 3 billion per gram of

    P-CTX-1/P-CTX-2/P-CTX-3

  • Republic of Kiribati 基里巴斯共和國A global hotspot of CFP occurrence and a fishing ground of

    imported wild-caught coral reef fishes of Hong Kong

    147k

    m

    China

    Australia

    Marakei Island

    马拉凯岛

    Tarawa Island

    塔拉瓦岛South Pacific Ocean

    Kiribati

    147km

    Apple Daily, 5th

    September 2004

  • Republic of Kiribati 基里巴斯共和國A global hotspot of CFP occurrence and a fishing ground of

    imported wild-caught coral reef fishes of Hong Kong

    147k

    m

    China

    Australia

    Marakei Island

    马拉凯岛

    Tarawa Island

    塔拉瓦岛South Pacific Ocean

    Kiribati

    147km

    Apple Daily, 5th

    September 2004

  • Republic of Kiribati 基里巴斯共和國A global hotspot of CFP occurrence and a fishing ground of

    imported wild-caught coral reef fishes of Hong Kong

    147k

    m

    China

    Australia

    Marakei Island

    馬拉凱島

    Tarawa Island

    塔拉瓦島South Pacific Ocean

    Kiribati

    147km

  • Our voyage of discovery to the South Pacific Ocean (2005-2013)

    Marakei Island: The Poison Island

  • 30

    Algal Toxins: Development of Analytical and Bioassay Detection

    Methods & Assessment of Environmental Transfer in Marine Food

    Webs (CityU3/CRF/08); Collaborative Research Fund, 2009 – 2012,

    HK$3.2M;

    Dr. CHAN Leo Lai (2010-2012)

    Prof. Paul K.S. Lam

    Dr. MURPHY Margaret B.

    Dr. CHAN Leo Lai (2009-2010)

    Prof. SADOVY Yvonne

    Dr. GU Ji-Dong

    Dr. ANDERSON Donald M.

    Dr. LU Chung-Kuang

    Co-investigators:

  • 31

    Sampling of Ciguatoxic Reef Fishes from

    Ciguatera Outbreak Area

  • 32

    Sampling of Ciguatoxic Reef Fishes from

    Ciguatera Outbreak Area

  • 33

    Purification and Isolation of Toxins

    Preparation of Authentic Toxin Standards

    Towards Certified Reference Materials

    Gymnothorax javanicus

    (Giant moray eel)

    Toxicity: 95 μg/Kg tissue

    Length: 165 cm

    Weight: 14Kg

    HPLC-UV chromatograph

    74 µg P-CTX-1

  • • Amount of CTX authentic standards is limited

    • several milligrams in the globe;

    • not commercially available;

    • Extremely expensive;

    • CTXs are at trace levels in coral reef fishes and remnants of consumed fish are often unavailable for testing

    • threshold level for acute CFP induction

    = 0.1 ng/g P-CTX-1 equivalent in fish muscle;

    • proposed safety level

    = 0.01 ng/g P-CTX-1 equivalent in fish muscle;

    • Analytical method for rapid, robust and reliable CTX detection is limited

    • regular screening of imported fishes for protection of human health.

    Challenges and key technological issues in

    CFP research

    (US$ 3,000 per microgram of

    P-CTX-1/P-CTX-2/P-CTX-3)74 µg P-CTX-1

    US$222,000

    HK$1.73M

  • Development of clean-up method for quantification of CTXs in marine fishes

    Extraction Clean-upInstrumental

    analysisSample

    collection

    UPLC-MS/MS, UPLC-QTOF or UPLC-HR/AM MS

    (A) Abiota (including seawater and sediment)

    (B) Dinoflagellates

    (C) Fish tissue (including brain, skin, muscle, gill, liver)

    Solid phase extraction

    Accelerated solvent extraction (ASE)

    Ultrasonication

    C18 & PSA

    Target phycotoxins

  • 36

    Two rapid, robust and reliable analytical methods

    were optimized and validated for simultaneous

    quantification of three Pacific CTXs in fish muscle

    and blood

  • 37

    Two rapid, robust and reliable analytical methods

    were optimized and validated for simultaneous

    quantification of three Pacific CTXs in fish muscle

    and blood

  • 38

    LOQ P-CTX-1 P-CTX-2 P-CTX-3

    Fish blood

    (n = 4)

    0.0003 –

    0.0023

    ng/mL

    0.0025 –

    0.0233

    ng/mL

    0.0025 –

    0.0233

    ng/mL

    Fish

    muscle

    (n = 3)

    0.0005 ng/g 0.0050 ng/g 0.0050 ng/g

    The Limit of Quantification (LOQ)

    was 20-time lower than the toxicity

    thresholds for adverse effects in

    seafood consumers

    (0.01 ng/g P-CTX-1 equivalent in fish

    muscle) of acute CFP incidence.

    Two rapid, robust and reliable analytical methods

    were optimized and validated for simultaneous

    quantification of three Pacific CTXs in fish muscle

    and blood

  • Development of instrumental method for identification of

    BETA-related phycotoxins in marine life

    Q ExactiveTM

    hybrid

    quadrupole-Orbitrap

    mass spectrometer

    (UPLC-HR/AM MS)

    combines high-

    performance

    quadrupole precursor

    selection with high-

    resolution, accurate-

    mass (HR/AM)

    Orbitrap™ detection,

    enable the detection of

    phycotoxins with high

    molecular mass.

    Figure The chromatographs of standards of 20 phycotoxins identified using UPLC-HR/AM MS

  • Instrumental Detection Limits (IDLs)

    N um ber T oxin E S I m ode C hem ical form ula M olecular w eight M olecular ion R T (m in) m /z calculated R 2LO Q (ppb) of

    LC -H R /A M -M S

    1 D inophysistoxin 1 negative C 45H 70O 13 818.48109 [M -H ]- 9.80 817.47437 0.9983 0.1

    2 D inophysistoxin 2 negative C 44H 68O 13 804.46654 [M -H ]- 9.15 803.45872 0.9960 0.05

    3 Y essotoxin negative C 55H 82O 21S 2 1142.47955 [M -H ]- 8.21 1141.47172 0.9929 0.5

    4 P ectenotoxin-2 positive C 47H 70O 14 858.47710 [M +N H 4]+ 9.38 876.51038 0.9923 0.05

    5 P alytoxin positive C 129H 223N 3O 54 2679.48240 [M +2H -2H 2O ]2+ 6.34 1322.73819 0.9979 10

    6 M aitotoxin negative C 164H 256O 68S 2N a2 3424.58444 [M -2H ]2- 8.04 1689.30300 0.9996 5

    7 O kadai cacid positive C 44H 68O 13 804.46544 [M -H ]- 8.91 803.45872 0.9961 0.5

    8 B revetoxin2 positive C 50H 70O 14 894.47710 [M +H ]+ 10.19 895.48383 0.9981 20

    9 B revetoxin3 positive C 50H 72O 14 896.49166 [M +H ]+ 9.49 897.49948 0.9979 20

    10 B revetoxin9 positive C 50H 74O 14 898.50841 [M +H ]+ 9.65 899.51513 0.9926 5

    11 C iguatoxin1 positive C 60H 86O 19 1110.57578 [M +N H 4]+ 8.52 1128.61016 / 6.25

    12 C iguatoxin2 positive C 60H 86O 18 1094.58087 [M +N H 4]+ 9.90 1112.61524 / 0.25

    13 C iguatoxin3 positive C 60H 86O 18 1094.58087 [M +N H 4]+ 10.26 1112.61524 / 0.25

    14 A zaspiracid-1 positive C 47H 71N O 12 841.49708 [M +H ]+ 9.88 842.50490 0.9979 0.006

    15 A zaspiracid-2 positive C 48H 73N O 12 855.51273 [M +H ]+ 10.16 856.52055 0.9937 0.004

    16 A zaspiracid-3 positive C 46H 69N O 12 827.48143 [M +H ]+ 9.47 828.48925 0.9946 0.0009

    17 G ym nodim ine positive C 32H 45N O 4 507.33431 [M +H ]+ 6.33 508.34214 0.9956 0.002

    18 13-D esm ethyl-spirolide C positive C 42H 61N O 7 691.44425 [M +H ]+ 6.98 692.45208 0.9921 0.004

    Table Summary of MS parameters, retention time, linearity and IDLs of phycotoxins detected by UPLC-HR/AM MS

  • 41

    Recovery: 62 – 94%

    CV: 4.46 – 14.9%

    Recovery: 82 – 98%

    CV: 2.57 – 20.8%

    The recoveries of five P-CTXs in (a) dinoflagellates, and (b) various fish tissues

    including brain, gill, skin, muscle and liver.

    (a) (b)

    Optimization of clean-up method for quantification

    of BETA-related phycotoxins in marine life

    Recovery in dinoflagellates and fish tissue

  • • Amount of CTX authentic standards is limited

    • several milligrams in the globe;

    • not commercially available;

    • Extremely expensive;

    • CTXs are at trace levels in coral reef fishes and remnants of consumed fish are often unavailable for testing

    • threshold level for acute CFP induction

    = 0.1 ng/g P-CTX-1 equivalent in fish muscle;

    • proposed safety level

    = 0.01 ng/g P-CTX-1 equivalent in fish muscle;

    • Analytical method for rapid, robust and reliable CTX detection is limited

    • regular screening of imported fishes for protection of human health.

    Challenges and key technological issues in

    CFP research

    (US$ 3,000 per microgram of

    P-CTX-1/P-CTX-2/P-CTX-3)74 µg P-CTX-1

    US$222,000

    HK$1.73M

  • • Amount of CTX authentic standards is limited

    • several milligrams in the globe;

    • not commercially available;

    • Extremely expensive;

    • CTXs are at trace levels in coral reef fishes and remnants of consumed fish are often unavailable for testing

    • threshold level for acute CFP induction

    = 0.1 ng/g P-CTX-1 equivalent in fish muscle;

    • proposed safety level

    = 0.01 ng/g P-CTX-1 equivalent in fish muscle;

    • Analytical method for rapid, robust and reliable CTX detection is limited

    • regular screening of imported fishes for protection of human health.

    Challenges and key technological issues in

    CFP research

    (US$ 3,000 per microgram of

    P-CTX-1/P-CTX-2/P-CTX-3)

    US$40 per gram of Gold

    US$ 3 billion per gram of

    P-CTX-1/P-CTX-2/P-CTX-3

  • 1. Sources

    Gambierdiscus

    live on seaweed

    3. Biotransformation,

    bioaccumulation and transfer

    Carnivorous fish

    2. Biotransformation,

    bioaccumulation and transfer

    Herbivorous fish, Invertebrates

    Randall 1958

    P-CTX-1

    Gambiertoxins

    CTX-4A/4B

    4. Consumption of fishes

    resulted in CFP

    P-CTX-2/3

    Assessment of Environmental Transfer in

    Marine Food Webs

    (precursor compounds)

    MW = 1061

    LC50

    = 4 µg/kg

    MW = 1095

    LC50

    = 2.3 µg/kg

    MW = 1111

    LC50

    = 0.08 - 0.25 µg/kg

  • 45

    With the success in

    identification CFP endemic region ……

  • Toxicity of Gambierdiscus spp. Distribution of ciguatoxic fish

    Marakei Island of

    the Republic of

    Kiribati

    The spatial distribution of toxigenic Gambierdiscus spp.

    in Marakei, the Republic of Kiribati

    In western

    region,

    Gambierdiscus

    spp. and coral

    reef fish were

    found to be

    toxic.

    In eastern region,

    Gambierdiscus

    spp. were less

    toxic and coral

    reef fish were

    considered to be

    free of CTXs.

    Target-oriented

    and nature-

    inspired sampling

  • HO

    91 1

    5 E

    F202865

    DS

    -1HO

    91 4

    EF

    202871

    44D

    7-2

    NO

    AA

    9 1

    1 E

    F20287

    GTT91

    4 1

    0 EF20

    2879

    HIT

    D5

    1 EF2

    0288

    8

    GTT

    91 4

    1 E

    F202

    878

    21M5

    -1

    1112

    M1M0

    3

    21D8-1

    1114M4D07

    51D3-1

    24D1-1

    21M8-1

    24D2-1

    K070922 2 C7 AB764258

    KW070922 1 C5 AB764248

    K070922 2 C5 AB764257

    NOAA2 3 EF202877

    NO

    AA5 E

    F202870

    NO

    AA

    18 2

    2 E

    F202868

    NO

    AA

    12 4

    EF

    202908

    NO

    AA

    1 1

    2 E

    F202911

    NO

    AA

    12 8

    EF

    202910

    M08

    08

    28

    2 C

    7 A

    B76

    42

    84

    WI9

    2G

    C2 A

    B76

    42

    79

    GT

    03004

    NO

    AA

    ext1

    3 E

    F202926

    NO

    AA

    7 2

    9 E

    F202915

    NO

    AA

    4 5 23 E

    F20

    2924

    GT25001

    M08

    0906

    5 A

    B764

    302

    M08

    0828

    4 A

    B764

    301

    S080

    911 1

    AB76

    4303

    NOAA

    6 3 4 E

    F20290

    1

    NOAA6 7

    1 EF2028

    99NOAA6 7 6 EF2

    028981D00-1

    TB2 5 EF202903

    TB2 2 2 EF202902

    TB2 2 9 EF202907

    IR4G AB764310

    IR4G AB764311

    IR4G

    AB764309

    Alexandrium

    tamarense A

    J415510

    Gym

    nodinium breve A

    F172714

    Pro

    roce

    ntru

    m lim

    a Y

    16235

    Pro

    rocentru

    m lim

    a A

    B189779

    0.02Gambierdiscus toxicus

    Gambierdiscus cf. yasumotoi

    Gambierdiscus polynesiensis

    Gambierdiscus carolinianus

    Gambierdiscus australes

    Gambierdiscus pacificus

    Gambierdiscus sp. type 1

    Gambierdiscus belizeanus

    Gambierdiscus carpenteri

    Gambierdiscus sp. type 2

    Gambierdiscus caribaeus

    Analysis ------------------------ Phylogeny Reconstruction

    Statistical Method -------------- Maximum Likelihood

    Substitutions Type -------------- Nucleotide

    Model/Method -------------------- Tamura-Nei model

    Rates among Sites --------------- Uniform rates

    Gaps/Missing Data Treatment ----- Complete deletion

    ML Heuristic Method ------------- Nearest-Neighbor-Interchange (NNI)

    Initial Tree for ML ------------- Make initial tree automatically (Default - NJ/BioNJ)

    Branch Swap Filter -------------- Very Strong

    Codons Included ----------------- 1st+2nd+3rd+Non-Coding

    No. of Seqs : 57

    No. of Sites : 1523

    May be a novel Gambierdiscus sp.

    The relative phylogeny position of 1D01 strain in

    Gambierdiscus species

    20 µm

    C.K. LU, National Research Institute of Chinese Medicine, Taiwan

  • Purification scheme of P-CTX-2 & 3

    Hydrophilic

    LC-MS/MS analysis for tracking CTXs toxins

    & toxins purification by HPLC P-CTX-2 & 3

    RP-HPLC

    C.K. LU, National

    Research Institute of

    Chinese Medicine,

    Taiwan

  • XIC of +MRM (17 pairs): 1112.700/1077.800 Da ID: P-CTX-2/3a from Sample 6 (P-CTX3mix) of 20131003_Lu.wiff (Turbo Spray) Max. 2.7e4 cps.

    0.0 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 10.0 11.0 12.0 13.0 14.0Time, min

    0.0

    2000.0

    4000.0

    6000.0

    8000.0

    1.0e4

    1.2e4

    1.4e4

    1.6e4

    1.8e4

    2.0e4

    2.2e4

    2.4e4

    2.6e4

    2.7e4

    Inte

    nsity

    , cps

    6.07

    5.36

    P-C

    TX-3

    P-C

    TX-2

    System: Agient UPLC 1290 couple with

    AB 5500 Qtrap MS/MS

    Column: Thermo FALC 2.2um,

    2.1x100mm

    Mobile phase:

    (A) 0.1% formic acid + 2mM

    ammonium formate in Milli Q

    water

    (B) 0.1% formic acid + 2mM

    ammonium formate in 95%

    ACN(aq)

    Gradient: 50% (B) to 100% (B) in 2 min,

    then hold for 20 min

    Flow rate: 0.2 mL/min

    Transition:

    1112.7 [M+NH4]+> 1077.8 [M-H

    2O+H]

    +

    XIC of +MRM (25 pairs): 1112.700/1077.800 Da ID: P-CTX-2/3a from Sample 13 (2-39-7) of 20131003_Lu.wiff (Turbo Spray) Max. 2.9e5 cps.

    0.0 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 9.0 10.0 11.0 12.0 13.0 14.0 15.0 16.0 17.0 18.0 19.0 20.0Time, min

    0.0

    2.0e4

    4.0e4

    6.0e4

    8.0e4

    1.0e5

    1.2e5

    1.4e5

    1.6e5

    1.8e5

    2.0e5

    2.2e5

    2.4e5

    2.6e5

    2.8e5

    Inte

    nsity

    , cps

    5.29

    P-C

    TX-3

    P-C

    TX-2

    Fr. MII-7

    Gambierdiscus sp. 1D00-01,

    cultural medium

    P-CTX-2 & 3 were found in Fr. MII-7, 1D00-01 by LC-MS/MS analyses

    Toxins standard

    C.K. LU, National Research Institute of Chinese Medicine, Taiwan

  • CTX-like activity

    analyzed by NBA

    in MII-7

    subfractions

    Fr. MII-7-4

    CTX-2 & -3

    isolated

    C.K. LU, National

    Research Institute of

    Chinese Medicine,

    Taiwan

    Assay Guide isolation of CTXs lead to new structure elucidation

  • Elucidation of food web transfer of Pacific CTXs

    in a ciguatoxic coral reef ecosystem

    51

    • Pacific CTX-1

    possessed a trophic

    magnification factor

    (TMF) > 1, indicating its

    bioaccumulative

    potential.

    • Identification CTX vectors in coral

    reef ecosystem

    • Identification of CTX composition

    profiles in food web components of

    different trophic levels

  • 52

    In addition to the conventional clinical

    symptoms of CFP, CTXs can cause……

    Change in activities of anterior cingulate cortex

    (ACC) in rats by acute CTX exposure

    Change in sensory functional recovery and

    reduction in motor function of mice by repeated

    CTX exposure

    Chronic sub-clinical exposure of P-CTX-1

    induced:

    (a) maladaptive decision making

    (b) impairment of spatial memory of rats

  • 53

    In addition to the conventional clinical

    symptoms of CFP, CTXs can cause……

    Change in activities of anterior cingulate cortex

    (ACC) in rats by acute CTX exposure

    Change in sensory functional recovery and

    reduction in motor function of mice by repeated

    CTX exposure

    Chronic sub-clinical exposure of P-CTX-1

    induced:

    (a) maladaptive decision making

    (b) impairment of spatial memory of rats

    Question:Do CTXs have effects on other organisms?

  • CTX exposure can also adversely affect

    physiological, behavioural and survival of fish

    54

  • CTX exposure can also adversely affect

    physiological, behavioural and survival of fish

    55

  • Our findings

  • Biotransformation,

    bioaccumulation and transfer

    Biotransformation,

    bioaccumulation and transfer

    A. Ciguatoxins adversely affect

    physiological, behavioural and

    survival of fishes and eliminate

    CTX-sensitive coral reef fishes

    B. Increased abundance of grazers due

    to lack of predators

    C. Increased coral

    bioerosion due to

    overgrazingtoxigenic

    Gambierdiscus spp.

    Grazers

    Predators

    CTX-2/3

    CTX-4A/4BCTX-1

    CTXs may not only affect human health, but also cause a shift in fish

    community structure and subsequently affect ecological function of

    CFP-endemic coral reef ecosystem

  • Biotransformation,

    bioaccumulation and transfer

    A. Ciguatoxins adversely affect

    physiological, behavioural and

    survival of fishes and eliminate

    CTX-sensitive coral reef fishes

    B. Increased abundance of grazers due

    to lack of predators

    C. Increased coral

    bioerosion due to

    overgrazingtoxigenic

    Gambierdiscus spp.

    Grazers

    Predators

    CTX-2/3

    CTX-4A/4BCTX-1

    CTXs may not only affect human health, but also cause a shift in fish

    community structure and subsequently affect ecological function of

    CFP-endemic coral reef ecosystem

    D. Increased cell density of

    toxigenic Gambierdiscus spp.

    as increased supply of hard

    surface such as coral rubbles

    Biotransformation,

    bioaccumulation and transfer

  • Coral

    Bioeroison

    Grazers*

    Food Sources

    Grazers*

    (Vectors)

    * Grazers are fishes that graze on

    hard surfaces for food and can be

    herbivorous, omnivorous and

    carnivorous fishes

    Loss of biodiversity

    Overgrazing

    Population

    explosions

    Diverse community

    with many species

    Community dominant

    by few species

    “Dead” community with

    no species present

    Human Health

    Predators

    Ec

    om

    onic

    Loss

    LRFFT Overharvesting + CFP E

    nviron

    me

    nta

    l D

    estru

    ctio

    n

    (Active sources of GTXs/CTXs)

  • 60

    Taiwan

    1. National Cheng Kung University (Dr Yi-Min Chen)

    2. National Research Institute of Chinese Medicine,

    Ministry of Health and Welfare (Dr Chung-Kuang

    Lu)

    French Polynesia

    1. Institut Louis Malardé

    concourt (Dr Mireille Chinain)

    Japan

    1. Japan Food Research

    Laboratories (Prof Takeshi

    Yasumoto)

    International Collaboration with

    International Academia

    China

    1. Second Institute of Oceanography

    SOA (Prof Douding Lu)

    2. Tsinghua Shenzhen Graduate School

    (Dr. Jin Zhou)

    The U.S.

    1. University of Connecticut (Prof Senjie Lin)

    2. Woods Hole Oceanographic Institute (Dr Don

    Anderson)

    3. University of Maryland (Prof Feng Chen)

    Malaysia

    1. University of Malaya

    (Drs Po Teen Lim &

    Chui Pin Leaw)

  • Knowledge Transfer and Screening Service

    Xiamen Entry-Exit Inspection and Quarantine Bureau

    - Training on the analytical methods to quantify Pacific

    CTX-1

    - Provision of Pacific CTX-1 authentic standards

    Shenzhen Entry-Exit Inspection and Quarantine Bureau

    - Support on development of analytical methods for

    Pacific CTX quantification

    Tuvalu Ministry of Fisheries

    - Screening of coral reef fish after an

    outbreak of CFP

    To ensure corresponding authorities to equip essential techniques

    and obtain scientific data/knowledge for making policy decisions

    to better protect human health and manage fishery resource

    and meet their socio-economic needs

    http://www.tuvalufisheries.tv/http://www.szciq.gov.cn/index.aspx?siteid=27565

  • Training and Exchange with Academia and

    Government

    Training Workshop on the Culturing and Identification of

    Benthic Harmful Marine Dinoflagellates (2016)

    – Involved local Government Authority such as Agriculture, Fisheries and Conservation Department (AFCD)

  • Partnerships for International Research

    and Education (PIRE): Advancing Global

    Strategies and Understanding on the

    Origin of Ciguatera Fish Poisoning in

    Tropical Oceans”. LEAD INVESTIGATOR:

    Alison Robertson, Ph.D.

    LEAD INSTITUTION:

    The University of South

    Alabama & the Marine

    Environmental Sciences

    Consortium at the Dauphin

    Island Sea Lab

    24 Co-Is

    13 institutions

    7 countries

    Opportunities

    for

    collaborative

    research

    coupled with

    teaching and

    outreach

    opportunities

  • 醫療衞生研究基金

    National Natural Science

    Foundation of China

    國家自然科學基金委員會

    Shenzhen Science and

    technology Innovation

    Committee

    深圳市科技創新委員會

    Acknowledgements

    SKLMP Advanced Scientific Diving Team

    We might not have it

    altogether, but

    together we have it all.