"The background levels were already around and in excess of the air quality guidelines. The incinerator was a significant further contributor to pollution, which was going to make matters even worse. Even if the incinerator was not "leading to" breach of the standards, because of existing levels, that did not mean there would be no breach. Nor did it mean that the breach would not be made worse because of the incinerator. And it certainly did not follow that there was no risk to health. The air quality standards, designed to reflect public safety, were exceeded (ie breached)."
"I have focused on one issue, namely nitrogen dioxide and the air quality standard. There are other points which could be made about other aspects, and would call for scrutiny were there some forum for public scrutiny of the evidence. However, I have stuck to an outline of what I consider to be the strongest point, appreciating that if this does not assist the Court others will not do so."
"Southampton and South West Hampshire Health Authority comments that the Environmental Report appears to give a carefully considered and sound assessment of the direct effects of the energy recovery facility on the environment. The conclusion that there will be negligible health effects seems well founded, based on existing knowledge and the safety criteria quoted in the report."
"9.29 Concern has been raised about pollution and health issues associated with incineration. In particular, it is alleged that minute quantities of certain pollutants represent a threat to health in the long term, particularly to the more vulnerable. 9.30 Regulation of the operation of the plant and its emissions to air, water and land has to be in accordance with the necessary European and UK standards. This is the responsibility of the Environment Agent through the IPC procedure. HWS has received an IPC authorisation for the operation of the proposed incinerator and the Agency does not object to the planning application. 9.31 However, the County Council has to take a view on this issue, particularly because it is raised as an objection to the planning application, and cannot rely solely on the views of the Environment Agency. 9.32 Therefore, the Southampton and South West Hants Health Authority and New Forest District Council's and Southampton City Council's Environmental Health Officers were consulted. The conclusion of these consultees is that there is no evidence that the past operation of an incinerator at Marchwood has led to an increase in health problems for the local population with respect to cancer, asthma or other respiratory diseases. Also, the background monitoring, dispersion modelling and emission standards included in the planning application and ES are appropriate and would not lead to a breach of air quality guidelines and standards, and so any risk to health would be negligible."
"As set out in this report, the County Council does not accept that there are any general health effects resulting from this development. There may be an effect on certain very vulnerable individuals with existing health problems. There may also be an effect on individuals who are particularly anxious concerning the health risks associated with incineration. While it is believed these fears are unjustified and the number of people concerned likely to be small, this does need to be taken into account. However, it is considered that the public benefits of the development outweigh these potential effects on individuals."
"The Government considers that emissions from such plants are strictly regulated and that environment protection standards are sufficient to protect the environment and public health. It is considered that the emissions and operation of the proposed plant are capable of meeting existing, and more stringent proposed, European and UK standards. Consequently, there would not be an objection on the grounds of a significant health risk."
"... total concentrations, including background levels, would not exceed the air quality standards set by the UK Government or the World Health Organisation."
"8.1 Emissions to the air are a consequence of the combustion process for the ERF; the type and quantity of substances being emitted varies depending on the materials being burnt. The quantities at which pollutants may be emitted from the ERF is regulated by the Integrated Pollution Control authorisation...and must comply with the limits set by UK and European standards. This plant will be designed to meet not only the existing standards but also future standards which the Europe council is currently drafting. This is achieved through the adoption of controlled incineration and through the provision of the high performance technology for the clean-up of the exhaust gasses prior to emission. 8.2 An extensive programme of air quality monitoring (covering a 15 month period) was undertaken by HWS around the site of the ERF and at other sites in Hampshire. The purpose of this was to determine how air quality in general compared to existing air quality standards to assess whether the site would be suitable for the levels of emission associated with the ERF. The findings showed that the air quality at the site would not preclude the construction of waste management facilities of this type."
"The data collected as part of the HWS background air quality programme, in conjunction with routine measurements made by DETR sponsored networks in Hampshire, indicate that existing air quality at and around the proposed Integra South West ERF site is such that air quality standards are not generally exceeded or approached. Data measured in the centre of the Southampton indicates that air quality targets for the year 2005 are not currently being met, but this is not an unusual situation for city centres in the UK. Importantly, in the context of an assessment of an ERF, concentrations of dioxins and metals in air, and also in the soil and grass, are comparable with what is known in similar locations in the UK. The available evidence suggests that the ERF is not proposed for an area with air quality problems of a scale which preclude waste management facilities of this type."
"The principal sources of emissions to atmosphere from the normal operation of the proposed ERF will be from the main 65 metre stacks and will include carbon dioxide, carbon monoxide, water vapour, oxides of nitrogen, sulphur dioxide, particulate matter, trace metals and organic compounds. In addition, there will be some vehicle movements associated with the operation of the proposed ERF. 7.6.3 Emissions from the Main Sacks. The most critical pollutant with respect to the NAQS air quality objectives and EU Directives is nitrogen dioxide. The NAQS (published in March 1997 and revised in January 2000) includes two objectives for NO2, a 1-hour mean (which allows 18 exceedances per year and is therefore equivalent to the 99.8th percentile) and an annual mean. Nitrogen dioxide is considered separately as the key pollutant, for short term (the maximum of 99.8th percentile 1-hour mean) and long term effects (with reference to the annual mean)."
"NO2 annual mean background concentrations ranged from 24-36 ug m-3 at the background diffusion tube monitoring sites in Southampton (1995-96). At the HWS monitoring sites, the estimated annual mean concentrations from the monitoring ranged from 23-50 ug m-3. Given the year-to-year variability of the data and the small relative impact of the ERF on the annual mean concentrations it is unlikely that the emissions from the ERF would produce any measurable effect on annual mean ground level concentrations or lead to guidelines or limits to be exceeded."
"As with any combustion process of this kind, there will be emissions to atmosphere of a range of pollutants. It is the responsibility of the developer to demonstrate that the emissions control technology and facility design including stack height are sufficient to render these pollutants harmless at ground level. To assess this effect quantitatively, it is necessary to understand the quality of the air into which the releases are to be made and how the releases disperse and dilute in the atmosphere. Ambient air quality in the region of the proposed site has been examined. The data collected as part of the HWS background air monitoring programme, in conjunction with routine measurements made by DETR sponsored networks in Southampton, indicate that existing air quality at and around the site is such that air quality standards are not generally exceeded or approached. The semi-urban location of this site means that it is subject to influences from traffic emissions. Consequently, concentrations of pollutants are relatively high when compared to rural background concentrations, particularly for those pollutants associated with vehicles, (eg NO2). Importantly, in the context of an assessment of an ERF, concentrations of dioxins and metals in air, and also in the soil and grass, are comparable with what is known of similar locations in the UK. The available evidence suggests that the proposed ERF is not proposed for an area with air quality problems of a scale which preclude waste management facilities of this type."
"In conclusion, the emissions from the proposed ERF will have a small impact on the local air quality. Ground level concentrations resulting from emissions from the proposed facility are unlikely to lead to breaches of ambient air quality standards and guidelines or cause a risk to health. A stack height of 65m for the main stacks is sufficient to ensure adequate dispersion of all pollutants."
"The annual mean concentrations of nitrogen dioxide have been exceeded in some years at the the AUN site and all local authority sites, except the background sites in Southampton (on Pennine Road and Landseer Road). The National Air Quality Strategy contains predictions that the annual mean NO2 concentrations will decrease to 19-29 ug m-3 at the Southampton AUN site by 2005. These predicted reductions suggests that long-term NO2 NAQS guidelines are likely to be achieved by the deadline of31/12/2005 ."
"Comparison has also been made of the four week means to the annual average guideline, this gives a useful indication of magnitude but may not necessarily indicate exceedance or compliance. The four week concentration exceed the NAQS annual average objective at the SCCC site. Monitoring at the SCCC site was undertaken during the winter months (January and February) when concentrations of nitrogen dioxide are expected to be higher (due to lower atmospheric mixing heights in the winter). Therefore, the measurements made at SCCC during the four week period would not be representative of measurements made throughout the year."
"There is widespread exceedance of the 40 [annual mean] in the Redbridge/Millbrook area, the Avenue, City Centre, Bitterne Road and in the vicinity of the M27." "
"It is only in wholly exceptional circumstances that the risk of a future violation may nevertheless confer the status of "victim" on an individual applicant, and only then if he or she produces reasonable and convincing evidence of the probability of the occurrence of a violation concerning him or her personally: mere suspicions or conjectures are not enough in that respect. In the instant case, the Court considers that the mere mention of the pollution risks inherent in the production of steel from scrap iron is not enough to justify the applicants' assertion that they are the victims of a violation of the Convention. They must be able to assert, arguably and in a detailed manner, that for lack of adequate precautions taken by the authorities the degree of probability of the occurrence of damage is such that it can be considered to constitute a violation, on condition that the consequences of the act complained of are not too remote...."
"Under the Court's case law, for Article 6(1) in its "civil" limb to be applicable, there must be a "dispute" over a "right" which can be said, at least on arguable grounds, to be recognised under domestic law. The "dispute" must be genuine and serious; it may relate not only to the actual existence of a right but also to its scope and the manner of its exercise. The outcome of the proceedings must be directly decisive for the right in question. As the Court has consistently held, mere tenuous connections or remote consequences are not sufficient to bring Article 6(1) into play."
"The Court reiterates that, according to the principles enunciated in its case law, it has first to ascertain whether there was a dispute ( contestation ) over a "right" which can be said, at least on arguable grounds, to be recognised under domestic law. The dispute must be genuine and serious; it may relate not only to the actual existence of a right but also to its scope and the manner of its exercise; and, finally, the result of the proceedings must be directly decisive for the right in question."