The Ciguatera Problem

Feeding biology of the introduced fish Roi (Cephalopholis argus), and its impact on Hawaiian coral reef-fishes and fisheries The Ciguatera Problem Ja...
Author: Dominic King
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Feeding biology of the introduced fish Roi (Cephalopholis argus), and its impact on Hawaiian coral reef-fishes and fisheries

The Ciguatera Problem Jan Dierking (UH Hawaii at Manoa) Charles Birkeland (UH Hawaii at Manoa) William Walsh (DAR Kona)

Picture: Max Wilkie

Background (Recapitulation)

Introduced in 1956 & 1961

Situation in 2004: • Widespread and abundant • Concerns about impacts

Background (Recapitulation)

The Ciguatera problem Common Name

Feeding Habit

No.

Grouper

Carnivorous

21

Jack

Carnivorous

20

Surgeonfish (var.)

Herbivorous

18

Surgeonfish (Kole)

Herbivorous

16

Goatfish

Omnivorous

10

Snapper

Carnivorous

9

Barracuda

Carnivorous

4

Moray Eel

Carnivorous

4

Mullet

Omnivorous

4

Other

20

Total

126

DOH Communicable Disease Report, Sept./Oct 2001

Figure: Oceanit

Ciguatera accumulation

Fishes associated with Ciguatera in Hawai’i (1996-2000)

Questions 1. Is the problem really as bad as perceived by the public? What is the Ciguatoxin level in Roi in Hawaii?

2. What are factors influencing Ciguatoxin levels in Roi? • Geographic location (site, island) • Size • Age • Prey type

Key management question: Feasibility of Roi fishery in Hawaii

Methods 1. Roi sample

N = 110 15 sites

N = 194 13 sites

2. Ciguatera analysis Objective: Æ determine ciguatoxicity level for each fish of the sample

• Ciguatera test

Monoclonal Immunobead Assay (MIA) Membrane stick

colored immunobead (antibody) ciguatoxin (antigen)

2. Ciguatera analysis (continued) • MIA test procedure

• MIA test output:

2. Ciguatera analysis (continued) • MIA test Ciguatera scores: Teststicks No coloration: Faint blue coloration: Blue coloration: Strong blue coloration:

Score 0 0.5 1 2

Total score for each fish sum of three tissue samples (head, body, tail): Actual range of possible fish-scores: 0 to 6 (min.: 3 x 0 = 0; max.: 3 x 2 = 6)

• Practical meaning: Score classes: 0 – 0.5 1–2 2.5 – 4 4.5 – 6

Æ negative Æ marginal Æ positive Æ strong positive

Conventional interpretation: Safe to eat Usually safe, but incident possible Incident possible Incident likely

Results • The overall sample • Ciguatoxin levels by Site and Island • Ciguatoxin level and Roi size Switch between SCORES and the SCORECLASSES with more practical implications

The overall sample

+

90 80

Frequency

70 60 50 40 30 20 10 0 0

1

2

3

4

Ciguatera score

5

6

The overall sample Ciguatera levels, frequency & percent 40; 14% 13; 4% 104; 36%

0-0.5 1-2 2.5-4 4.5-6

n = 292 135; 46%

The overall sample - conclusions • Majority of Roi safe to eat, but close to 1/5th of fish in positive category, and 4% strongly positive (likely to cause Ciguatera) • Question: how does this compare to other reef fish species?

Site d sewer pipe

S Kiholo

Red Hill N

Puako

Mahukona

ne Tree Arch

na resort 3/4

na resort 1/2

ona Paradise

ko Arches 2

aneohe 6/7/8

Kaneohe 4/5

Kaneohe 2/3

Kaiwi Point

Honaunau S

lden Arches

Alahaka

Score (Jan)

Ciguatoxin level by Site Boxplots of Score (J by Site (means are indicated by solid circles)

6

5

4

3

2

1

0

Ciguatoxin level by Site

100%

Strong pos. 60%

Positive 40%

Marginal

20%

Negative

M

K-

ah u

ko

n Ki a ho K- lo L K - on e Go l K - de n Ko lo K- ko Ka K - iw i K - Pu Ho a k na o un K- au Ko n K- a K - Re d Al ah ak a OK2 OK4 O- O-K Ko 6 ol in a 2 Al l

0%

K-

F re q u e n c y

80%

Site One-way ANOVA: Score versus Site Analysis of Variance for Score

Source Site Error Total

DF 16 275 291

SS 69.55 499.20 568.75

MS 4.35 1.82

F P 2.39 0.002

M ah u K-

ko

n Ki a ho K- lo Lo K- ne Go l K - de n Ko lo K- ko Ka K - iw i K - Pu Ho a k na o un K- au Ko n K- a K - Re d Al ah ak a OK2 OK4 O- O-K Ko 6 ol in a 2 Al l

K-

F re q u e n c y 100%

80%

Strong pos.

60%

Positive

40%

Marginal

20%

Negative

0%

Site

Ciguatoxin level by Island 70

60

Oahu

Kona

Two-Sample T-Test Ciguatera toxicity and Island

Percent

50

Origin Kona Oahu

40

N Mean 185 1.55 107 0.73

StDev 1.48 1.07

Difference = mu(Kona)- mu(Oahu)

30

20

T-Test of difference = 0 (vs not =):

10

0 negative (0-0.5) marginal (1-2) positive (2.5-4)

Ciguatera class

strongly positive (4.5-6)

T-Value = 5.47 P-Value = 0.000 DF = 275

Ciguatoxin level by geographic location - conclusions • Significant association of location & Ciguatoxin level • Sites differ significantly in Ciguatoxin levels • Mean Roi Ciguatoxin scores low at some sites, however, strongly positive outliers can occur at these sites • Roi from Oahu and Hawaii Island differ significantly in Ciguatoxin levels, mean level on Oahu less than half as high as on the Big Island

Ciguatoxin level and Roi size

6

Ciguatera score

5 4 3 2 1 0 15

25

35

Standard length

45

Ciguatoxin level and Roi size 6

Ciguatera score

5 4 3 2 1 0 15

25

35

45

Standard length

Regression Analysis: Ciguatera score versus Standard length The regression equation is: Score = 0.146 + 0.0411 Standard length Predictor Constant Standard

Coef SE Coef 0.1459 0.3942 0.04106 0.01430

S = 1.381

T P 0.37 0.712 2.87 0.004

R-Sq = 2.8%

R-Sq(adj) = 2.4%

Analysis of Variance: Source Regression

DF 1

SS 15.713

MS 15.713

F 8.24

P 0.004

Ciguatera level and Roi size - conclusions • Fish length and Ciguatera toxicity are positively associated, however, only a very small degree (2.8%) of variation in toxicity is explained by fish length

General conclusions 1. Is the problem really as bad as perceived by the public? • While the majority of Roi in Hawaii appears safe for consumption, a significant amount of fish is ciguatoxic – the current public caution is therefore justified

2. What are the factors influencing Ciguatera in Roi? • Geographic location and Ciguatera are associated • Significant differences between Ciguatera levels at different sites suggest that Roi from certain sites are predictably safer than from other sites. However, ciguatoxic fish can occur at the ”relatively safe” sites

• Roi from Oahu are significantly safer for consumption than Roi from the Big Island. However, high variation in Ciguatera levels means that ciguatoxic and strongly ciguatoxic fish nonetheless occur.

• Ciguatera and Roi size (standard length) are positively associated. Size only explains a very small amount of variation in Ciguatera, and is therefore not a useful indicator of Roi toxicity levels.

General conclusions Key management question: Feasibility of Roi fishery in Hawaii Æ At this time, data do not indicate potential for risk-free fishery

Next steps Ciguatera: • Enhance statistical analysis • Look at remaining factors that may influence Ciguatera levels as information becomes available • Age and Ciguatera • Prey type and Ciguatera

Other: Feeding biology component of study

Next HCRI presentation: Stomach content analysis results

Prey items found in preliminary run through Roi stomachs of our sample

Acknowledgments • HCRI • UH specialization in Ecology, Evolution and Conservation Biology

Questions?

Picture: Max Wilkie