“While I recognise the force of the matters raised in the Acknowledgement of Service, the elaborate and lengthy arguments do not persuade me that the claim is unarguable. The categorisation of the waste and the effects of the dust are highly material and it seems to me to be arguable that the officer’s report did not adequately inform the committee of all that was needed.”
“The Environment Agency recognises that most incinerator bottom ash (IBA) is likely to be classified as non-hazardous waste. However, IBA is classified on the List of Wastes as a ‘mirror entry’ which means it could potentially be categorised as a hazardous waste if it is found to possess a hazardous property.”
“The site will process Incinerator Bottom Ash (IBA) produced at the Trident Park Energy Recovery Facility in Cardiff. The ERF plant will burn 350,000 tonnes of waste a year. This will result in the production of 75,000 of IBA which equates to just over 20% of the burnt waste. This rate of production is expected to continue for the foreseeable future, although it could fluctuate. The IBA is non-hazardous and suitable for processing to produce recycled aggregates. The Barry facility would produce approximately 67,500 tonnes of recycled aggregate and therefore be a major source of recycled material in South Wales, contributing towards meeting the planned requirements as an alternative to Land 1 materials.”
“8.1.3 Dust will be managed according to best practice under a dust management plan. No adverse impact is therefore predicted either on site or on adjacent sites… 8.2.1 The closest non-statutory site, the Cadoxton Wetlands SNCI is within 50 metres at the closest point. It is concluded that there will be a negligible impact on the site… 10.1.3 The development will not affect the only area of semi-natural vegetation and the impact on the site is considered to be negligible. There is not considered to be any greater effect on adjacent land including Cadoxton Wetlands SNCI on the grounds of direct impact, dust, disturbance and hydrology.”
“IBA is produced from the incineration of municipal waste and as such is highly variable in composition and typically consists of a mixture of glass, ceramics, brick and cement, as well as ash and clinker (e.g. nodules of coke and slag). Raw IBA has a high pH and a relatively high moisture content. The IBA conditioning process is exothermic and steam can rise from the windrows, especially in cold weather. A salty odour can derive from the IBA during conditioning. There is a range of methods for producing IBAA from IBA; most involve ‘dry’ treatment which involves mechanical processing of the IBA such as size reduction, screening and ferrous/non-ferrous metals separation. Prior to screening, IBA is naturally aged (i.e. weathered) in stock piles outdoors for several weeks. This stabilises the material by utilising the pozzolanic (cement-like) properties of the incinerator ash and allowing a range of chemical processes to take place, including oxidation, carbonation, hydration and hydrolysis. The IBA aging process reduces the pH of the resultant IBAA to below 10, with a typical pH of 9.5-9.8. Stock is rotated so that the IBA is aged sufficiently before processing and weekly tests are undertaken to determine the pH with the IBAA. The chemical composition of the IBA varies widely according to source material but can comprise common elements such as silicon, iron and calcium. Less abundant elements include lead (Pb) and Cadmium (Cd). The proportions of the elements found in IBA are likely to vary between incinerators and within the same incinerator over time due to the changeable composition of waste disposed.”
“Dust propagation at source depends on particle size, wind energy and other mechanical disturbance activity. Large dust particles generally travel shorter distances than small particles. It is often considered that particles greater than 30UM will largely deposit within 100 metres of sources; those between 10-30UM to travel up to 250-500 metres and particles less than 10UM to travel up to 1km from sources.”
“Secondly, in relation to wind-blown dust, table 2 shows that less than 10% of the winds blow in an arc from north-east to south-west at speeds above 6m/s. Therefore, from figure 4, there is a low likelihood of propagation of wind-blown dust towards residential receptors along Dock View Road and Hillary Road. As previously, figure 5 indicates that the magnitude of any dust impact at Dock View Road and Hillary Road would be negligible. Consequently, from figure 6, there is also a near-zero risk of dust impact from wind-blown dust at residential receptors from the proposed operation. Again, because table 2 shows that the frequency of dry winds is similar to that for all winds, there is both a near zero risk of dust propagation in dry weather conditions as well as in all weather conditions at the residential receptors along Dock View Road and Hillary Road from the proposed operation. With regard to ecological impact on environmental receptors (such as the Dow Corning Nature Centre) recent guidance for demolition and construction sites can be adapted to consider the sensitivity of such receptors to dust. The key table from this guidance is reproduced at table 4… Given that the Down Corning Nature Centre is more than 50 metres from the proposed operations at the IBAA facility, this guidance suggests that it could be considered to have Low sensitivity to dust.”
“Likewise, for visible dust, from the assessment undertaken and the nature of the operations proposed, there is very little potential for site operations to cause adverse annoyance impact at off-site receptors.”
“The IBA is the result of the burning of processed waste in a furnace at over 800°c. At this temperature some fusion occurs and any combustible materials are burnt off. The ERF Permit required that unburnt shall not exceed 2%. The residual IBA, which has reduced by 80% by weight from input, is then quenched in a pit at the ERF before being placed in stockpiles at Trident Park prior to dispatch to the recycling site by lorry. At this stage the material is classified as non-hazardous waste (As agreed through the Energy Services Agency (‘ESA’) Protocol).”
“The second step in the assessment scheme is to use the standards defined in the protocol to judge whether or not the plant’s IBA waste stream, as represented by the samples, should be deemed hazardous or non-hazardous. The classification procedure in the Protocol, as approved by the Environment Agency, is based upon a 90th percentile standard. This means that for the IBA to be non-hazardous, the threshold concentration should be exceeded for no more than 10% of the time. The Protocol requires the plant operator to judge compliance with the 90th percentile by counting the number of samples that exceed the WM2 thresholds… Although 10% equates to 2.4 exceedances in every 24 samples, in practice even a compliant IBA process may experience as many as 6 exceedances over a single year due to random sampling variations. For that reason up to 6 exceedances are allowed which thereby ensures that the risk of complaint IBA being mistakenly classified as hazardous waste is limited to 5%.”
“The document promises routine testing under the ESA protocol to check the IBAA ‘remains non-hazardous’; yet that protocol checks only twice-monthly samples and disregards many that come over the ‘hazardous waste’ threshold, up to 5 exceedances in 24 samples, 2 in a row, or exceedance 4 times over the threshold (s2.1of the ESA protocol). It tests the full 15 hazard characteristics including H14 ecotoxicity once a year. It does not isolate samples which exceed the standard but investigates causes for repeated breaches or a 4 times exceedance. Nor does it propose to isolate IBA that should be called as ‘hazardous waste’ under EU rules, pending tests that take weeks, preparatory to returning it to Viridor.”
“The protocol was derived looking at performance over a long period of time and showed IBA to be non-hazardous, consistent with that similarly produced in the rest of Europe and elsewhere in the world…Most of the hazardous properties are not relevant for IBA and so full assessments are carried out less frequently (annually). Those properties that are pertinent to IBA are assessed twice monthly from a restricted suite of analysis.”
“To this end, the proposal is complying with the general principles of waste strategy set out in the national documents by recycling 100% of the bottom ash material that would be produced by the ERF plant in Cardiff. In essence, this would recycle a non-hazardous waste material that would otherwise be sent to landfill, but also produces a usable secondary aggregate product that could reduce the need for quarried stock material for both aggregate and cement production.”
“In any case, where an expert tribunal is the fact finding body the threshold of Wednesbury unreasonableness is a difficult obstacle for an applicant to surmount. That difficulty is greatly increased in most planning cases because the Inspector is not simply deciding questions of fact, he or she is reaching a series of planning judgments…Moreover, the Inspector's conclusions will invariably be based not merely upon the evidence heard at an inquiry or an informal hearing, or contained in written representations but, and this will often be of crucial importance, upon the impressions received on the site inspection. Against this background an applicant alleging an Inspector has reached a Wednesbury unreasonable conclusion on matters of planning judgment, faces a particularly daunting task.”
“Whilst planning officers' reports should not be equated with inspectors' decision letters, it is well established that, in construing the latter, it has to be remembered that they are addressed to the parties who will be well aware of the issues that have been raised in the appeal. They are thus addressed to a knowledgeable readership and the adequacy of their reasoning must be considered against that background. That approach applies with particular force to a planning officer's report to a committee. Its purpose is not to decide the issue, but to inform the members of the relevant considerations relating to the application. It is not addressed to the world at large but to council members who, by virtue of that membership, may be expected to have substantial local and background knowledge. There would be no point in a planning officer's report setting out in great detail background material, for example, in respect of local topography, development planning policies or matters of planning history if the members were only too familiar with that material. Part of a planning officer's expert function in reporting to the committee must be to make an assessment of how much information needs to be included in his or her report in order to avoid burdening a busy committee with excessive and unnecessary detail.”
“Democratically elected bodies go about their decision-making in a different way from courts. They have professional advisers who investigate and report to them. Those reports obviously have to be clear and full enough to enable them to understand the issues and make up their minds within the limits that the law allows them. But the courts should not impose too demanding a standard upon such reports, for otherwise their whole purpose will be defeated: the councillors either will not read them or will not have a clear enough grasp of the issues to make a decision for themselves. It is their job, and not the court's, to weigh the competing public and private interests involved.”
“a) A report is not addressed to the world at large but to council members, who, by virtue of that membership, may be expected to have substantial local and background knowledge including local development plan polices. b) It is not necessary for the report to set out development plan policies as it is reasonable to anticipate that the members will be familiar with that material. c) The report should not contain excessive and unnecessary detail. d) Reports do not (and should not) seek to be exhaustive. e) The report by a planning officer to his committee is not and is not intended to provide a learned disquisition of relevant legal principles or to repeat each and every detail of the relevant facts to members of the committee who are responsible for the decision and who are entitled to use their local knowledge to reach it. f) The report is not susceptible to textual analysis appropriate to the construction of a statute or the directions provided by a judge when summing a case up to the jury. g) The courts should not impose too demanding a standard upon such reports, for otherwise their whole purpose will be defeated. h) An application for judicial review based on criticisms of the planning officer's report will not normally begin to merit consideration unless the overall effect of the report significantly misleads the committee about material matters which thereafter are left uncorrected at the meeting of the Planning Committee before the relevant decision is taken. i) It is the job of the Council, and not the court's, to weigh the competing public and private interests involved.”
“IBA is generally classified as non-hazardous, but may sometimes be classified as hazardous. However this application and the relevant permit are both limited to non-hazardous IBA”
“In Wales, health boards have the statutory responsibility for the health and wellbeing of the population they serve. To support health boards fulfil their environmental health protection responsibility, services are delivered through a collaborative working model between Public Health Wales and Public Health England’s Centre for Radiation, Chemical and Environmental Hazards (CRCE) Wales. Public Health Wales is the lead agency in Wales and provides partner agencies and the public with independent, specialist advice and support to minimise exposures to, and health impact from, environmental hazards.”
“It sought to address objectors' concerns on a significant issue, namely flood risk, by giving ‘a description of the measures envisaged in order to avoid, reduce, and if possible remedy significant adverse effects’. (Schedule 4, part II, paragraph 2). It was therefore "any other information" within the reg. 2(1) definition and caught by the publicity provisions of reg. 19(3)(d) to (g). The fact that it satisfied the EA is immaterial on this point.”
“71. In my judgment, information is "any other information" within the meaning of Regulations 2(1) and 19 of the EIA Regulations if it is substantive information provided by the applicant to ensure that the Council is provided with the information required for inclusion in an environmental statement as required by Schedule 4 to the EIA Regulations. Thus, if the original document comprising the environmental statement was considered not to include all the information required by Schedule 4, then additional information provided at the direction of the Council to make it an environmental statement would be "further information". If such information were provided voluntarily by the applicant, it would be "any other information". Conversely, the phrase "any other information" in Regulations 2 and 19 does not include comments or responses made by the applicant in response to the concerns of, or points raised by, third parties or Council officers. Still less does it include documents submitted by third parties or generated by the Council. I reach that conclusion for the following reasons. … 75. Fourthly, the Claimant's interpretation could lead to such odd or absurd consequences that it is unlikely that those drafting the relevant regulations intended them to be interpreted as the Claimant submits should be done. On the Claimant's analysis, the provision of substantive information in response to a concern raised by a third party must be the subject of a notice in a local newspaper. Each time that occurs, the Council must suspend determination of an application for 21 days to allow time for further comment on the information provided. There are likely to be many occasions when additional information is provided in response to points raised. On the Claimant's case, there must be a publication in a local newspaper of the fact that that information has been provided and a suspension of the determination of the application each time. Furthermore, if a person were opposed to a planning application, there would be ample opportunity to raise a point, receive a response from the application for planning permission and then claim that that was substantive information provided by the applicant which required publication and a suspension of determination. In my judgment, the regulations were not intended to produce such results. That is neither required by, nor in my judgment, consistent with effective public participation, in environmental decision making.” (Emphasis supplied)
“Allowing for the differences in the issues raised by the national law in that case (including the issue of burden of proof), I find nothing in this passage inconsistent with the approach of this court in Walton. It leaves it open to the court to take the view, by relying "on the evidence provided by the developer or the competent authorities and, more generally, on the case-file documents submitted to that court" that the contested decision "would not have been different without the procedural defect invoked by that applicant". In making that assessment it should take account of "the seriousness of the defect invoked" and the extent to which it has deprived the public concerned of the guarantees designed to allow access to information and participation in decision-making in accordance with the objectives of the EIA Directive.”