ä»åã¯ã天ä¸ã®ã調æ»æ鯨ãå£ããä»å¹´åã® JARPNIIï¼ç¬¬äºæå西太平æ´é¯¨é¡æç²èª¿æ»ï¼ãçµãããã¨ãå
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In terms of meeting logistics, the Panel was seated at a round table in one part of the room while the Proponents, when present, were seated in another part of the room.
During the morning session of each of the first three days, the Proponents gave a brief overview of their results on a particular main topic and answered questions of clarification from the Panel.
The rest of the day was a closed session for Panel discussion and report writing.
The report itself was constructed as follows.
Under each agenda item there was a statement of the objectives and summary of the results written by the Proponents themselves.
This was followed by a section on the Panelâs discussion of the papers presented and its conclusions and
recommendations.
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"the Panel" ã£ã¦ã®ã¯ãããã®è°è«ã«ãããå 容æ¤è¨¼æ å½ã£ã¦æãï¼
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The Committee commended the Panel on having undertaken its review in a critical but constructive manner.
However, it also expressed concern that the Panel was not provided with the information and guidance necessary to review programme progress, to draw conclusions regarding the appropriateness of programme sample sizes, and to assess the effects on two of the stocks (common North Pacific minke whales and sei whales).
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以ä¸ã2009å¹´ IWC ç·ä¼ç§å¦å§å¡ä¼å ±åæ¸ P.86 ãããããã³ã¦ã¯ã¸ã©ã®èª¿æ»ã«é¢ããè°è«é¨åãå¼ç¨ãã¦ããã
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Some members reiterated the Panelâs questioning of the value of the data derived from sperm whales against all of the objectives of the programme.
When asked how the Proponents[e.g. Japanese participantsï¼] would respond to these criticisms, the Proponents clarified that the initial fieldãwork had focussed on small sperm whales for logistical reasons, and that preliminary Ecopath modelling confirmed the potential for a species effect.
They therefore plan to increase their capability to take larger animals.
However, because the ecosystem model is still in the early stages of development they will continue to take a small number of samples, including larger animals, and will include areas where sampling was previously limited.
Some members expressed strong concern that notwithstanding broader criticisms they have about the overall JARPN II programme, a decision by the Proponents to continue with the take of sperm whales brings into question the credibility and purpose of the review process itself.
In the view of these members, a refusal to alter any aspect of the lethal sampling, even when confronted with such strong criticism from a review, brought into question the value of the time and money invested in this process.
The Proponents expressed their strong disagreement with this and expanded their explanation above.
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ãç§å¦çããªèª¿æ»ã§æ¬å½ã¯å¿ è¦ãããããªãããã³ã¦ã¯ã¸ã©ãæç²ããªãã§ãã³ã¯ã¯ã¸ã©ãã¤ã¯ã·ã¯ã¸ã©ã°ããç²ã£ã¦ã以ä¸ãJARPN II ãçã£å½ãªèª¿æ»æ鯨ãªã®ãã©ããæ¹å¤ãåºãããªã
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ãã£ã¨ãããã®ç§å¦å§å¡ä¼ã® JARPN II ã«é¢ãã話ã§ä½æ°ã«éè¦ã ã£ãã®ã¯ãæç²èª¿æ»ã¨éæç²èª¿æ»ã® Cost-effectiveness analysisï¼CEAï¼è²»ç¨å¯¾å¹ç仮説ï¼ï¼ãã©ãã ããªã®ãã«ã¤ãã¦æ¤è¨¼ãæ±ãããã¨ã
å ãã¿ã¯âã®è«æï¼R.S.Waples, and M.L. Plummer èï¼ã ãã»ã»ã»
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The primary effects would be the scientific information developed from the samples and the consequences of sampling on the populations.
The simplest application of CEA in this case would probably be to standardise costs, which could be done by taking actual effort expended under the JARPN II or a similar programme of scientific whaling and considering the most effective non-lethal sampling programme that could be conducted for the same level of effort.
This exercise would almost certainly highlight inherent tradeoffs between different types of effects (e.g., increasing information content might entail more negative consequences for the population).
In that case, the choice between the two programmes would rest on assigning weights to the various effects, which inherently involves applying a set of values to this problem.
The costeffectiveness framework can therefore illuminate the tradeoffs that are present in choosing between the two programmes, but it cannot indicate (or is unlikely to indicate) which is preferable from a social perspective.
Nevertheless, CEA could be useful in helping to objectively evaluate aspects of the problem that are amenable to quantitative analysis and in helping to focus discussions on a narrower set of normative issues.
In discussion, the author clarified that this would not be a simple analysis, and further thought would be required to weigh specific costs and benefits in the context of special permits.
The Committee welcomes the scientific framework discussed in SC/61/O1 and encourages that it be developed and further discussed next year.
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P.82ï½P.88ã«æ²è¼ããã¦ã JARPN II ãªã©ã«é¢ããè©ä¾¡ã§ã¯ã主ã«ä»å¹´1æã«è¡ããã JARPN II è©ä¾¡ä¼è°ã®çµæè©ä¾¡ãè¡ããã¦ããã
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ã¨ããã®åã«ãããã§ã®è°è«ã®æ¹æ³ã«ã¤ãã¦è¿°ã¹ã¦ãé¨åã P.82 ã«ãã£ãã®ã§ãç§å¦å§å¡ä¼ã®å ±åæ¸ããå¼ç¨ãã¦ããã
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In terms of meeting logistics, the Panel was seated at a round table in one part of the room while the Proponents, when present, were seated in another part of the room.
During the morning session of each of the first three days, the Proponents gave a brief overview of their results on a particular main topic and answered questions of clarification from the Panel.
The rest of the day was a closed session for Panel discussion and report writing.
The report itself was constructed as follows.
Under each agenda item there was a statement of the objectives and summary of the results written by the Proponents themselves.
This was followed by a section on the Panelâs discussion of the papers presented and its conclusions and
recommendations.
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---- å¼ç¨ä»¥ä¸ ----
"the Panel" ã£ã¦ã®ã¯ãããã®è°è«ã«ãããå 容æ¤è¨¼æ å½ã£ã¦æãï¼
ã§ã"the Proponents" ã£ã¦ã®ã¯ãå¤åä»å¹´1æã«è¡ãããè©ä¾¡ä¼è°ã§åãé£ãã¦ã人éï¼çºè¡¨è ï¼ãã¨ã
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以ä¸ã2009å¹´ IWCç·ä¼ç§å¦å§å¡ä¼ã®å ±åæ¸ãã P.85 ã®ä¸é¨ãï¼ç¥
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The Committee commended the Panel on having undertaken its review in a critical but constructive manner.
However, it also expressed concern that the Panel was not provided with the information and guidance necessary to review programme progress, to draw conclusions regarding the appropriateness of programme sample sizes, and to assess the effects on two of the stocks (common North Pacific minke whales and sei whales).
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以ä¸ã2009å¹´ IWC ç·ä¼ç§å¦å§å¡ä¼å ±åæ¸ P.86 ãããããã³ã¦ã¯ã¸ã©ã®èª¿æ»ã«é¢ããè°è«é¨åãå¼ç¨ãã¦ããã
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Some members reiterated the Panelâs questioning of the value of the data derived from sperm whales against all of the objectives of the programme.
When asked how the Proponents[e.g. Japanese participantsï¼] would respond to these criticisms, the Proponents clarified that the initial fieldãwork had focussed on small sperm whales for logistical reasons, and that preliminary Ecopath modelling confirmed the potential for a species effect.
They therefore plan to increase their capability to take larger animals.
However, because the ecosystem model is still in the early stages of development they will continue to take a small number of samples, including larger animals, and will include areas where sampling was previously limited.
Some members expressed strong concern that notwithstanding broader criticisms they have about the overall JARPN II programme, a decision by the Proponents to continue with the take of sperm whales brings into question the credibility and purpose of the review process itself.
In the view of these members, a refusal to alter any aspect of the lethal sampling, even when confronted with such strong criticism from a review, brought into question the value of the time and money invested in this process.
The Proponents expressed their strong disagreement with this and expanded their explanation above.
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---- å¼ç¨ä»¥ä¸ ----
ãç§å¦çããªèª¿æ»ã§æ¬å½ã¯å¿ è¦ãããããªãããã³ã¦ã¯ã¸ã©ãæç²ããªãã§ãã³ã¯ã¯ã¸ã©ãã¤ã¯ã·ã¯ã¸ã©ã°ããç²ã£ã¦ã以ä¸ãJARPN II ãçã£å½ãªèª¿æ»æ鯨ãªã®ãã©ããæ¹å¤ãåºãããªã
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å ãã¿ã¯âã®è«æï¼R.S.Waples, and M.L. Plummer èï¼ã ãã»ã»ã»
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件ã®å§å¡ä¼ã§ã¯ãã調æ»æ鯨ãã«é¢ããè°è«ãããã«é²ãã§ãªãçç±ã«ãæç²èª¿æ»ã¨éæç²èª¿æ»ã®ã¡ãªããã»ãã¡ãªããã«ã¤ãã¦æ¯è¼ãè¡ããã¦ãªããã¨ãæãã¦ããã
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The primary effects would be the scientific information developed from the samples and the consequences of sampling on the populations.
The simplest application of CEA in this case would probably be to standardise costs, which could be done by taking actual effort expended under the JARPN II or a similar programme of scientific whaling and considering the most effective non-lethal sampling programme that could be conducted for the same level of effort.
This exercise would almost certainly highlight inherent tradeoffs between different types of effects (e.g., increasing information content might entail more negative consequences for the population).
In that case, the choice between the two programmes would rest on assigning weights to the various effects, which inherently involves applying a set of values to this problem.
The costeffectiveness framework can therefore illuminate the tradeoffs that are present in choosing between the two programmes, but it cannot indicate (or is unlikely to indicate) which is preferable from a social perspective.
Nevertheless, CEA could be useful in helping to objectively evaluate aspects of the problem that are amenable to quantitative analysis and in helping to focus discussions on a narrower set of normative issues.
In discussion, the author clarified that this would not be a simple analysis, and further thought would be required to weigh specific costs and benefits in the context of special permits.
The Committee welcomes the scientific framework discussed in SC/61/O1 and encourages that it be developed and further discussed next year.
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