Part III. Compilation of comments on the issue made during
the third session of the Open-ended Working Group
A. Extract from the report of the third session of the Open-ended Working Group regarding analysis of issues related to Annex VII
“57. The Working Group took up the item at its 6th meeting, on the afternoon of 28 April. In its consideration of the item, it had before it an analysis prepared by the Secretariat for the Group’s second session on issues related to Annex VII (UNEP/CHW/OEWG/2/7), a consolidation of comments received on the study during the period between the Group’s second and third sessions (UNEP/CHW/OEWG/3/INF/6) and a note by the Secretariat prepared for the current session on analysis of issues related to Annex VII (UNEP/CHW/OEWG/3/10).
58. The representative of the Secretariat introduced the documentation under the item and reviewed the work done to date. Noting that five Parties and one environmental non-governmental organization had provided comments on document UNEP/CHW/OEWG/2/7 during the inter sessional period, she asked for further comments and guidance from the Parties so that the analysis could be finalized in time for the seventh meeting of the Conference of the Parties, as contemplated in decision VI/34 of the Conference of the Parties and decision OEWG II/6.
59. There was considerable debate under the item. A number of representatives, one speaking on behalf of a regional grouping, said that the analysis contained in document UNEP/CHW/OEWG/2/7 should be finalized during the Working Group’s current session, in accordance with decision VI/34 of the Conference of the Parties. Those representatives repeatedly stressed that the point of the analysis, as stated in the preamble to decision VI/34, was to assist Parties to ratify the Ban Amendment contained in decision III/1, which they characterized as vital to the environmentally sound management of hazardous wastes in developing countries. The importance of the Basel Convention regional centres in regard to facilitating ratification and implementation of the Ban Amendment was highlighted.
60. A number of representatives drew attention to the enormous problems posed for developing countries by the massive new wave of exports of end-of-life equipment and pointed out the consequent importance of the Ban Amendment.
61. The representatives of two environmental non-governmental organizations criticized the draft analysis for presenting what they called an unrealistic picture of the costs and benefits to a country of ratifying the Ban Amendment. That, they said, would discourage developing countries from ratifying the amendment, which was arguably the most significant environmental achievement since the 1992 United Nations Conference on Environment and Development, and reflected an apparent effort on the part of some Parties to undermine the amendment. They argued that the analysis was unbalanced and did not serve its intended purpose.
62. Many representatives outlined proposed changes to the analysis and the draft decision contained in the note by the Secretariat, in the light of which the Working Group agreed to establish a contact group, chaired by Mr. Pavel Suian (Romania), with the task of reviewing how to deal with the comments submitted and preparing a draft decision on the item for the Working Group and elements for a decision by the Conference of the Parties. A number of representatives, noting the history of difficult negotiations under the item, argued that it was essential for the contact group to limit itself to those tasks and to avoid revisiting issues on which agreement had previously been reached or raising new issues.
63. The Working Group took up the item again at its 9th meeting, on the morning of Friday, 30 April, at which time it adopted a decision on the item on the basis of the draft contained in the relevant conference room paper. The decision as adopted is set out as decision OEWG-III/5 in annex I to the present report.
64. At the same meeting, the Working Group approved the text of a draft decision on the item for possible adoption by the Conference of the Parties at its seventh meeting on the basis of the draft decision contained in the relevant conference room paper. The draft decision as approved by the Working Group is contained in annex II to the present report.”
B. Comments on the analysis of issues related to Annex VII (Phase II) Submitted by the Basel Action Network (BAN)10
(April 2004)
General Comments
After many years of work and many hundreds of thousands of dollars spent in meeting costs on the Annex VII study, the result is a paper that does not assist the Parties to ratify the Ban Amendment as is its mandate. Indeed the document seems to be intent on doing the opposite.
As it stands now, the study suffers from bias and imbalance, with far more statements that appear to be critical of the ban than statements illustrating its obvious merits.
The mandate of the terms of reference for phase II of the Annex VII analysis states that “the purpose of this analysis is to explore, in a transparent, objective and comprehensive manner, health, environmental, social, economic and other issues related to Annex VII that are considered important to the Conference of Parties and to assist Parties to ratify the ban amendment.”
The requirements are clear that the exploration of the issues must be transparent, objective and comprehensive, and be included with a view to assist Parties in ratifying the Basel Ban Amendment. The present document fails the test of meeting fair standards of objectivity and comprehensiveness, and moreover is, on balance, not aimed to assist Parties to ratify the ban amendment.
One striking example is found at the very beginning of the document, where the list of issues regarding implementation of the Ban Amendment all contain negatives and no positives. This imbalanced portrayal belies the fact that in 2003 8 ratifications occurred for the Ban Amendment and one has already occurred in January of 2004. The amendment has been on a steady pace of achieving more than 5 ratifications per year and recently this average is seeing an increase. Compared with a similar instrument like the London Protocol (receiving 2.66 ratifications per year, thus far) that bans the dumping of industrial wastes at sea, the Basel Ban Amendment has received excellent support. Presently there are now 44 total ratifications in total. Surely, these 44 nations see something positive or have experienced something positive in ratifying and/or implementing the Ban Amendment. Most significantly the Annex VII countries that have implemented the Ban (including the entire European Union) have not had their very positive experience translated or communicated into the analysis. Wouldn’t the experiences of those that have ratified the ban be vital with respect to the consideration of assisting parties to ratify the ban? So far the paper is lacking this vital information, and as such reveals a certain imbalance and lack of objectivity in contradiction to its mandate.
Another crucial point that continues to be bypassed is the economic costs on the environment and human health - the price tag for pollution. While there has been repeated mention of economic benefits from toxic waste, no recognition is made of the far greater costs that are hidden in medical costs, loss of arable land, fisheries, contamination of air, water, remediation costs, enforcement costs etc. Without this kind of economic assessment of these externalized costs the study lacks all credibility.
The comments that follow are consistent with the mandate to not consider new issues or attempt to raise new issues not already dealt with in the current analysis. The comments below are given to help steer the present analysis closer to what the terms of reference have originally called for in terms of balance, objectivity and with a view to assisting the parties to ratify the Ban Amendment.
III. A.
There is a need to mention the positive experiences of Parties who have ratified the Ban Amendment in this survey or summary of issues raised by Parties. Recently, the Ban has seen an increase in ratifications with 9 being deposited in the last 13 months. The Parties who have ratified the Ban Amendment have something valuable to contribute in the analysis, as to why they ratified, and the noted benefits of doing so. Thus, it is imperative to include such positive issues in order to arrive at a balanced and well-rounded analysis of the Annex VII issue. As this new text must be provided by those countries that have ratified and/or implemented the ban, we would request that those parties be asked to submit some observations about this experience before the text is finalized.
IV. B. 1.
Para. 13. This paragraph is incorrect in that some of the noted “principles” are in fact obligations of the Convention. The “proximity principle”, on the other hand, does not in fact exist in the Convention and is therefore not of significant standing in this paper. Further, despite the fact that the self-sufficiency principle and least transboundary movement principles are actually obligations of the Convention, it is incorrect to state these obligations so vaguely as: “recognizing that the application of those principles will vary from country to country.” Further, the statement, “…in some cases, however environmentally sound and efficient management of certain hazardous wastes may be achieved at specialized facilities located in another country”, flies in the face of the obligations of the Convention, and likely the Ban Amendment. Further, there is no recognition of Annex VII itself here which the analysis is supposed to be about. Annex VII was created to respect the special needs of developing countries as well as the special responsibilities of developed countries. Therefore, we strongly suggest that the text be dramatically altered to read as follows:
The Convention calls on all Parties to minimize the transboundary movement of hazardous wastes and to strive for national self-sufficiency in hazardous waste management. Thus there must be an effort to build capacity for such environmentally sound management in each country in order to reduce transboundary movements. Developed countries have a special role in this regard, vis-à-vis, developing countries.
Para. 14. The first sentence of paragraph 14 makes an assertion of fact, which we believe to be true, yet it is not supported by any citation of evidence or sources proving the factual claim. The study mentioned in the second sentence only examines zinc and lead, and would thus, fail to qualify as supportive of the previous assertion in the paragraph.
The statement in sub-paragraph (a) is fine. However, it discusses a percentage of the total zinc wastes traded that are in fact non-hazardous under the Convention and this bears no relation to sub-paragraph (b) which begins a discussion about competitiveness. In fact, sub-paragraph (b) doesn’t assert anything other than the fact that something “could” occur. The fact that something “could” occur in the future without evidence of its propensity to do so, is hardly relevant here, as the list of things that “could” occur, should they be cited in full would be a long list indeed.
For the foregoing reasons, we suggest that paragraph 14 be deleted as being unhelpful in fulfilling the mandate of the study.
IV. B. 2.
Para. 16. There is a significant logical flaw in the conclusion arrived at by the study as stated in the first sentence in this paragraph, as it misinterprets the requirements under the Basel Convention and Decision III/1. BAN had commented on this fact earlier in our comments on the consultant’s incorrect conclusion.
While the Convention imposes obligations on all Parties, Decision III/1, on the other hand, only calls for implementation on the part of Annex VII countries, namely those countries that are members of the Organization for Economic Cooperation and Development (OECD), the European Union and Liechtenstein. Thus, it is incorrect to assert that the countries that must implement the Ban Amendment have inadequate capacity or resources to do so. Rather, the Ban Amendment was designed precisely to place responsibility on countries that were certain to have all of the infrastructure and economic development to implement the ban. The thrust of the entire paragraph -- that countries lack the infrastructure, resources or legislative capacity to implement the ban, when only the OECD states must implement it, is an utter falsehood. The analysis with this faulty conclusion fails in fulfilling the terms of reference requirement of assisting parties in ratifying the Ban Amendment, as it regrettably discourages any ratification from occurring. For these reasons the paragraph should be deleted.
IV. B. 3.
Para. 17. Again this section is a discussion of the implementation of decision III/1 which only must be implemented by Annex VII countries. Therefore, we cannot understand the relevance of statements about the lack of capacity of non-Annex VII countries. As there is little revealed in this paragraph regarding OECD countries, we suggest deleting this paragraph. At the very least, all references to non-OECD countries should be deleted as the paragraph is meant to deal with implementing Decision III/1.
Para. 18. The discussion in the final three sentences refers to a matrix and a baseline. As this analysis is not meant to be a summary of other papers but a stand-alone document, we would suggest deleting the last three sentences of this paragraph.
Para. 19. Oddly there is no discussion here about the increase or decrease of hazardous waste flows from Annex VII countries to non-Annex VII countries as plotted over time. This is the most relevant data, as the ban is not designed to minimize other waste flows, only those from Annex VII to non-Annex VII. This data can also help Parties revisit the significance of the ban, which can ultimately assist them in ratifying the Ban Amendment. All other data are irrelevant to the issues concerning the ban and Annex VII.
Para. 21. The cautionary statement in para. 20 requires that the two cases cited in this paragraph be sufficiently described to highlight the particular nature of the cases to the country in which they were derived from. Having had the opportunity to look at the actual paper cited for the first case, BAN noted some objective details missing from the case summary. We suggest the following adjustments in order to more accurately reflect the paper in question:
One non-Annex VII country developed a lead recovery industry in the late 1980s due to the huge capital outlay needed to mine its lead deposits. In spite of an admitted lack of a national effort to collect domestic used batteries, the country made a determination that the national supply of lead through secondary sources was insufficient to ensure a viable and efficient use of the lead smelters. As a consequence, the country imported lead-acid batteries principally from a single source in an Annex VII country until 1994. As the lead recycling industry developed in this non-Annex VII country, lead poisoning in workers and the community around the recycling plants became commonplace. In fact, the rise in lead poisoning incidents and the hazards of such recycling plants prompted some regions in the same non-Annex VII country to shut down all used battery processing factories.
In the process of amending the environmental law, the legislative assembly of that country requested the banning of hazardous waste imports, with exception of used batteries, up to the year 2002. The exemption was based on the commonly used argument by the battery recycling industry that because the supply from domestic sources was insufficient to reach an economic production level, used batteries were needed to be imported until the local supply could satisfy the economic needs. Yet this argument was made in the absence of an adequate domestic collection system for locally generated waste batteries.
Meanwhile, the Annex VII country (principal source of used batteries) stopped its export of used lead-acid batteries, in line with decision III/1. Since 1998, the used batteries are imported principally from non-Annex VII countries. In the meantime, progress in encouraging and improving the collection of used batteries at the local level remain slow. In addition, small-scale recyclers which do meet the country’s environmental and health requirements are still operating illegally.
BAN has not been able to find the source of the second case noted here. But given the experience in reading the actual cited case above, and comparing it to the analysis summary, we believe it would be prudent to allow the Parties to actually review this case. In order to arrive at a more transparent and objective summary of the case, BAN suggests that subparagraph (b) be placed in square brackets and remain open for modifications until the source for the case has been given to Parties for review, and for the Parties to weigh-in with comments on whether the case has been adequately summarized and whether its argumentation is sound.
IV. B. 5.
Para. 27. This paragraph largely claims that there is a lack of data regarding the health impacts from hazardous waste management operations. This is certainly not the case. There are numerous studies in existence. In fact several studies even exist which document health effects from the importation and subsequent handling and management of toxic waste. Some that come to mind are studies conducted in Cambodia following the importation of mercury-laden waste from Taiwan which included several deaths as a result. Likewise, imported mercury wastes caused the death of 2 workers at the Thor Chemical plant in South Africa. Studies of shipbreaking workers that have also been done evaluate health impacts and the prospective deaths from cancer from asbestos alone. It is vital that the Secretariat cite this existing and published information. Further, no relevance here with respect to illegal traffic and thus this sentence should be removed, particularly as it seems to imply that there are no health impacts from the legal traffic of hazardous wastes. Finally, the reference to an Annex III list of “wastes” is incorrect, as Annex III is a list of hazardous characteristics and not wastes.
IV B. 6.
Para. 29. Here it must be noted that ratification and implementation are two different things. In other words it is clear that while all Parties are urged to ratify the Ban Amendment, only the Annex VII countries are to implement it. The group of countries that were among the first to implement the Basel Ban was the European Union member states. Therefore, we propose that the EU experience and steps for implementation be reflected here. The EU experience can be well-documented, thus belying the assertion here that the information does not exist.
IV. B. 7.
Para. 32. Here the term “sham” recycling needs to be augmented. Sham recycling refers to recycling that is nor really recycling at all. What is more often the case is “dirty” recycling – highly polluting operations. Thus we would recommend the formulation: “sham and dirty recycling”. Further, the final sentence in this paragraph is extremely misleading. The implication here is that only those that freely trade in waste might get access to newer and cleaner technologies. This is patently false. Everyone in the world has access to clean technologies if they are made available. There are no trade restrictions of any kind on clean technologies! This latter sentence needs to be scrapped.
Para. 33. This paragraph is extremely imbalanced and not objective. Suddenly the text is calling wastes “secondary raw materials”. These are “wastes” and in fact are hazardous or other wastes in the Basel context which are known to cause environmental harm when disposed or recycled. Nothing in this paragraph suggest why scrap and wastes migrate from Annex VII to non-Annex VII countries. This is quite amazing as it is a well-known phenomenon which spawned the Basel Convention itself. Hazardous waste migrates to take advantage of cheaper recycling labor, lack of environmental and occupational protections etc. found in developing countries or weaker economies. It is small wonder that the flows of wastes from Annex VII to non-Annex VII countries and not the other way around. The Basel Convention calls for self-sufficiency in waste management. This paragraph seems to have forgotten this obligation completely. Further, this paragraph implies that all that is necessary to allow the export of hazardous wastes from Annex VII countries to non-Annex VII countries is enhanced technology in the non-Annex VII country. However, regardless of technology levels, pollution is still transferred. What remains unanswered by technological “solutions” are the incentives to prevent waste in the first place, the fact that technology alone cannot guarantee levels of environmental and human health protection, and finally, the justice issue of allowing weaker economies to receive a disproportionate burden of the world’s waste simply because they are relatively poor. This paragraph is of such bias; it must be deleted.
New Para. 34 The contents in item 7 do not properly bear or coincide with the terms of reference it was intended to fulfill. The heading in Item 7 refers to an evaluation of the cost benefit and effectiveness of hazardous waste recycling versus health risks and environmental damage, yet no mention is made of existing efforts in the international community to determine the environmental costs of the emissions of toxic substances. One such study was commissioned by the Nordic Research Council on the economic valuation of emissions of several toxic substances. In this regard, we suggest that the following paragraphs be inserted as a new paragraph 34, under item 7:
There have been efforts in placing economic values to the adverse environmental effects of toxic substances. One such effort was commissioned by one Annex VII country. It was designed as an aid to policy-makers in arriving at a rational decision on how to prioritize measures in curbing pollution from particular hazardous substances.
In determining the economic value for a particular substance, the study compiled recent weighting/ranking methodologies on the adverse impact of several substances, particularly their physical effects. The monetary values were based on surveys conducted by several Annex VII countries. From there the study developed a best, low, and high estimate of the environmental cost of a particular substance. An anchor substance was chosen in order to come up with an evaluation of the other substances. In this case, the study chose lead as the anchor substance due to its known effects, and for the numerous studies that have been carried out to assess the damage caused by its emissions.
Some of the resulting values of the study are:
Substance
|
Best estimate*
|
Low estimate*
|
High estimate*
|
Dioxin
|
2.2E+06
|
8.4E+05
|
6.0E+06
|
TBT
|
261
|
98
|
697
|
Chromium 6+
|
163
|
61
|
434
|
Mercury
|
111
|
41
|
296
|
PCB
|
96
|
36
|
256
|
Cadmium
|
32
|
12
|
87
|
Lead
|
6.1
|
2.3
|
16
|
* Prices are in Norwegian Kroner per gram.
Thus, if a 25,000 metric ton capacity/year lead-acid battery recycling plant operating in a non-Annex VII country, importing lead acid batteries has a 98% lead recovery rate, with 2% fugitive emissions, that means 500 tons of lead per year is being emitted in the vicinity of the plant. Applying the study values, based on the low estimate of NOK 2.3 per gram of lead emission, the low estimate would equate to an environmental cost of the 500 tons of lead emission as NOK 1,150,000,000 (US$166,064,982) per year to the country where this particular plant is located. Under the best estimate the environmental cost would be pegged at NOK 3,050,000,000 (US$440,433,213) per year.
The values presented under this study and others like it can greatly aid Parties in their analysis of the economic benefits and cost of hazardous substances. Too often these costs resulting from emissions and residues in even state of the art recycling operations are not calculated, and result in cost externalities and dramatic economic inefficiencies.
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