Identifi cation and testing The United States currently imports about 16 million MAF per year. Shipments can range from 20 to 25 or more boxes for small tropical fi sh, while larger shipments can include 50 or more boxes. Each box may contain several hundred fi sh, with each fi sh packaged in an individual bag or with mixed species in larger bags. Opening <strong>the</strong> bags to examine a fi sh introduces oxygen out <strong>of</strong> <strong>the</strong> bag and fur<strong>the</strong>r threatens survival. This poses a huge challenge for identifying all species and possibilities for cyanide testing. The optimal strategy for testing would include a rapid, simple diagnostic test for use at <strong>the</strong> port, such as a “dipstick” method, that would simply identify <strong>the</strong> presence <strong>of</strong> cyanide (“yes or no” system). The test cannot take more than a few minutes, based on shear size <strong>of</strong> import shipments, lack <strong>of</strong> manpower, and split attention for ESA and CITES identifi ed priority species. If <strong>the</strong> fi eld test confi rmed <strong>the</strong> presence <strong>of</strong> cyanide, a shipment could be seized and sent on to a diagnostic laboratory where a more detailed test could be performed to quantify levels <strong>of</strong> exposure. Table 1: Shipments <strong>of</strong> marine ornamental fi sh in each United States port city between July 2004 and June 2005. No. <strong>of</strong> Shipments % <strong>of</strong> Total Shipments Quantity % <strong>of</strong> Total Quantity Agana, GU 7 0 1,865 0 Atlanta, GA 230 2 435,498 3 Baltimore, MD 1 0 45 0 Blaine, WA 2 0 16 0 Buffalo-Niagara Falls, NY 51 0 293 0 Chicago, IL 257 2 519,547 3 Detroit, MI 74 1 90,430 1 Dallas-Ft.Worth, TX 272 2 295,832 2 Honolulu, HI 1,492 13 584,755 4 Los Angeles, CA 5,548 47 8,994,755 56 Miami, FL 1,898 16 2,442,173 15 Newark, NJ 54 0 70,730 0 New York, NY 946 8 1,570,988 10 Portland, OR 78 1 51,950 0 Seattle, WA 73 1 54,689 0 San Franciso, CA 662 6 954,049 6 Sumas, WA 1 0 2 0 San Diego-San Ysidro 10 0 3,545 0 Tampa, FL 75 1 7,925 0 unknown 20 0 6,896 0 Totals 11,751 100 16,085,983 100 34
No. <strong>of</strong> Shipments 6,000 5,000 4,000 3,000 2,000 1,000 0 10 9 8 7 6 5 4 3 2 1 0 Agana, GU Atlanta, GA Baltimore, MD Blaine, WA Buffalo-Niagara Falls, NY Chicago, IL Detroit, MI Dallas-Ft.Worth, TX Agana, GU Atlanta, GA Baltimore, MD Blaine, WA Buffalo-Niagara Falls, NY Chicago, IL Detroit, MI Dallas-Ft.Worth, TX Honolulu, HI Los Angeles, CA Miami, FL Newark, NJ New York, NY Portland, OR Seattle, WA San Franciso, CA Sumas, WA San Diego-San Ysidro Tampa, FL unknown Ports Figure 1: Number <strong>of</strong> Shipments by Port from July 2004 to June 2005. Quantity (in millions) Honolulu, HI Los Angeles, CA Miami, FL Newark, NJ New York, NY Ports Figure 2: Quantity <strong>of</strong> Marine Ornamental Fish by Port from July 2004 to June 2005. 35 Portland, OR Seattle, WA San Franciso, CA Sumas, WA San Diego-San Ysidro Tampa, FL unknown
- Page 1 and 2: Proceedings of the International Cy
- Page 3 and 4: Proceedings of the Cyanide Detectio
- Page 5 and 6: ACKNOWLEDGEMENTS The Proceedings of
- Page 7: PREFACE The International Cyanide D
- Page 11 and 12: EXECUTIVE SUMMARY The International
- Page 13 and 14: ATCA) in homogenized fi sh tissue m
- Page 15 and 16: Validation of the ISE method applie
- Page 17 and 18: Importing countries should also req
- Page 19 and 20: INTRODUCTION Cyanide fi shing is a
- Page 21 and 22: through the implementation of a net
- Page 23 and 24: Working Group 2 The Export Working
- Page 25 and 26: o o o o Can the U.S. require verifi
- Page 27 and 28: Polymeric membrane based ion select
- Page 29 and 30: Goal 2: Provide recommendations on
- Page 31 and 32: hands-on training that develops a d
- Page 33 and 34: Goal 3: Identify research needs to
- Page 35 and 36: Working Group 1 Participants Bob KO
- Page 37 and 38: estimated at roughly 3 to 5 days. H
- Page 39 and 40: Goal 2 : Identify steps, agreements
- Page 41 and 42: 3) certifi cate, but tests positive
- Page 43: Report from Working Group 3 The Par
- Page 47 and 48: Goal 3: Provide a recommendation wi
- Page 49: Working Group 3 Participants Eric P
- Page 53 and 54: Introduction Since the early 1960
- Page 55 and 56: ainbow trout exposed to 40 mg SCN -
- Page 57 and 58: Blennies, which were net-caught and
- Page 59 and 60: electrical potential (similar to an
- Page 61 and 62: in the Philippines under contract w
- Page 63 and 64: endorsing the IMA’s use of the IS
- Page 65 and 66: The intended products from the rese
- Page 67 and 68: WPCF 1992, 1998). Both of these stu
- Page 69 and 70: ASTM (1997) Standard test methods f
- Page 71 and 72: Kuegsen, M., Kloock, J.P., Knobbe,
- Page 73 and 74: Philippines. In Proceedings from th
- Page 75 and 76: 3) 4) 5) 6) the metabolism of cyani
- Page 77 and 78: or new matrices. 5.2.3 Modifi catio
- Page 79 and 80: Level Two: The method should be val
- Page 81 and 82: of cyanide exposure and to identify
- Page 83 and 84: Special considerations for the anal
- Page 85 and 86: tissue samples indispensable. Altho
- Page 87 and 88: y reduction and subsequent separati
- Page 89 and 90: can also be used for analysis of cy
- Page 91 and 92: thiocyanate in saliva and serum bas
- Page 93 and 94: are many discrepancies in the liter
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Table 3. Analytical Methods to dete
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Poisoning, In Textbook of military
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(70) Odoul, M., Fouillet, B., Nouri
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V. (1975) Stable reagents for the c
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(159) Felscher, D. and Wulfmeyer, M
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Purpose of this Document The purpos
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day. One cyanide tablet (2 g) is mi
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10-90% following exposure to cyanid
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existing cyanide detection methods
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- Plasma lactate — elevated plasm
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Method Advantages Disadvantages Hig
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Paper Method Matrix Detection Limit
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Table 4 lists experts identifi ed t
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X Jerry Thomas CDC Em Steve Borron
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References Barber, C. and Pratt, V.
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Rates of Recovery. Environmental Ma
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COUNTRY REPORTS
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The first three of these destructiv
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enforcement is minimal. There is an
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1. Management/guidance to the Minis
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in Vietnam now and requires more ef
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Figure 2: Administrative structure
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References Baquero, J. (1999) Marin
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Acronyms • CDT • Cyanide Detect
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Law/Ordinance/Decree /Decision 52/2
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of samples required for analysis. U
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Field test kit. BFAR recognizes the
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Political Will Having planted the s
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gravely by fi shing communities. Th
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ecome the partner and counterpart o
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Ion-Selective Electrodes for Cyanid
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References Alban, J., Manipula, B.E
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levels with mV readings recorded as
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Trends Determined by Cyanide Testin
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Implementing agencies: • Quaranti
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APPENDIX
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1:30 Overview of and Potential Cyan
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Kristine Johnson Director Kingfi sh
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Assessment of U.S. Role in Trade: U