Introduction
Areas covered by the SPS Agreement
Principles of the AgreementThe agreement is based on 6 principles:
The WTO calls for SPS measures to be based on International Standards or to conduct a risk assessment (see below) where there is no agreed international standard or the importing country believes that this is insufficient to meet its policy objective. The WTO recognises certain sets of standards as the basis for SPS measures. Those with most relevance for NTFPs are: a) Food safety: guidelines and recommendations established by the Codex Alimentarius Commission, b) Plant protection: Secretariat of the International Plant Protection Convention (IIPC) c) Animal health: the recommendations of the International
Office of Epizootics are recognised by the WTO.
SPS measure should be established on the basis of scientific risk assessment (a process of hazard analysis, exposure assessment, toxicity assessment and risks communication). However, if sufficient scientific evidence does not exist, governments may temporarily establish regulations based on the precautionary principle, i.e. ‘when an activity raises threats of harm to human health or the environment, precautionary measures should be taken even if some cause and effect relationships are not fully established scientifically. It includes taking action in the face of uncertainty; shifting burdens of proof to those who create risks; analysis of alternatives to potentially harmful activities; and participatory decision-making methods’ (Raffensperger and Tickner, 1999). In its defence against the US challenge on the ban on hormone-treated beef, the EU used the argument that there was no evidence available, or rather any satisfactory evidence, on the risks of certain hormones in meat production. The WTO ruled against the EU and permitted the use of the precautionary principle only as a temporary measure with the proviso that risk assessments be carried out (see Zarrilli, 1999: 8, Roberts, 1998: 30). Whilst some WTO members have been concerned about the potential for the precautionary principle to be used for protectionist purposes, others defend it on scientific, administrative and environmental grounds. The supremacy of risk assessment procedures has been challenged by environmentalists, lawyers and consumer rights campaigners. Environmental NGOs argue for amendment or interpretation of Technical Barriers to Trade (TBT) and Sanitary and Phyto-sanitary Agreements to respect fully the precautionary principle (e.g. WWF, 1999). There has been considerable debate on the relative merits of the Precautionary
Principle and Risk Assessment.
Adaptation to regional conditions and pest-free areas Recognising that the situation regarding animal and plant disease may within a given country, the SPS Agreement specifies that regulations must adapt to regional conditions and pest-free areas. The importing country must consider whether there are zones within the exporting country that present less danger. Zarilli argues that many developing countries have not been able to fully benefit from this principle as the procedures to prove that specific areas are pest free can be ‘long and burdensome and often involve the need to provide complex scientific evidence’ (1999: 21). Expert assistance would facilitate market access here. Article 4 of the SPS agreement expresses the principle of equivalence of measures, i.e. countries shall recognise as equivalent those SPS measures that are not identical but have the same the same effect. However, many countries are expecting “sameness” rather than equivalent measures (Youssef, 1999:34), for example the EU’s emphasis on i.e. the use of ‘process-based controls enforced by a “competent authority” in exporting countries rather than border inspection’ (Henson and Loader, 1999: 12). Similarly, organic regulations for products imported in the EU have
become increasingly onerous for developing country producers in terms of
paper work, time limits for exemptions, which institutions bear responsibility
for ensuring eligibility of certification systems and transition periods
before a product can be designated organic for the European market (Nycander,
1999).
Provisions for transparency aim to ensure that Members are notified of a measure before it is implemented. Similarly members are encouraged to consult widely in the process of developing standards and indeed this is enshrined in the structures and procedures of the three bodies charged with developing international standards for food safety, plant health and animal health (link to box). However, there has been considerable criticism vis a vis the lack of southern participation in such bodies, particularly Codex. Many developing countries argue that their interests are not represented and the Codex standards are too high (Henson and Loader, 2000: 20; Kwa, 1999). The SPS Agreement provides a mechanism for dispute settlement. Member countries may challenge as unjustified each other’s SPS measures on grounds, for example, that a risk assessment has not been undertaken or the measures are not based on relevant international standards. See Nematodes and Conifers: An example of a plant health dispute However, in order to challenge Northern measures, a complainant needs information, technology and facilities. Analysis of WTO dispute panels or requests for consultations on account of SPS/ TBT measures by Wilson (1999) indicates that debates are predominantly between developed countries. Indeed there is a distinct lack of active participation in SPS Agreement
by developing countries, with some exceptions e.g. India, Egypt, Philippines
and Indonesia (Henson and Loader, 2000: 22). The SPS Agreement therefore
tends therefore to be driven by northern interests and its procedures are
largely not transparent.
Nematodes and Conifers: An example of a plant health dispute In 1998, the European Union instigated a new regulation on coniferous
sawn timber requiring it to be treated before importation for fear of nematode
infestation. Through the WTO, Canada asked for a consultation with
the EU focusing on the nature of the risk and the costs involved in treatment
and the treatment methods specified.
Source: Bourke and Leitch (1998) and Roberts (1998), Bridges July 1999.
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