“(i) The High Court has jurisdiction to grant an injunction maintaining registration pending appeal to the FTT, which has been revoked by HMRC, when a parallel challenge to that decision is made in judicial review proceedings; (ii) The jurisdiction should not be exercised simply on the basis that the person concerned has a pending appeal with a realistic chance of success; (iii) If the decision is challenged only on the basis that HMRC could not reasonably have come to it, the case falls withinsection 15 of the Finance Act 1994 and the court should not intervene; (iv) If the challenge to the decision is on some other ground outside the statutory regime the court may entertain judicial review or grant interim relief; (v) A definition of the additional element needed is elusive but would include ‘abuse of power’, ‘impropriety’ and ‘unfairness’ as envisaged in the Harley Development Inc v Commissioner of Inland Revenue[1996] 1 WLR 727 .”
“81. In my opinion, a statutory appeal against a refusal of approval which is unable to provide a remedy before an appellant has been forced out of business, rendering the appeal entirely academic (or theoretical or illusory in the language of the Strasbourg Court) is capable of giving rise to a violation of article 6 which the High Court would be entitled to prevent by the grant of appropriate injunctive relief under section 37 of the 1981 Act. To that extent, the exceptions enumerated by Underhill LJ in CC&C Ltd[2015] 1 WLR 4043 can be expanded to include cases in which a claimant can demonstrate, to a high degree of probability, that the absence of interim relief would violate its ECHR rights. … … 83. It was no part of Mr Coppel’s case that interim relief should issue automatically even if a claimant could demonstrate that it would not be able to survive the wait for the appeal to be heard. He recognised that factors such as the strength of the appeal and the nature of the concern that led to the refusal to approve would be factors to weigh when considering whether to grant an injunction, itself a reflection of the fact that the Scheme exists to protect the public purse and legitimate traders. … 85. A claimant seeking an injunction would need compelling evidence that the appeal would be ineffective. It would call for more than a narrative statement from a director of the business speaking of the dire consequences of delay. The statements should be supported by documentary financial evidence and a statement from an independent professional doing more than reformulating his client’s stated opinion. Otherwise, a judge may be cautious about taking prognostications of disaster at face value. It should not be forgotten that a trader who sees ultimate failure in the appeal would have every incentive to talk up the prospects of imminent demise of the business, in an attempt to keep going pending appeal. Equally, material would have to be deployed which provided a proper insight into the prospects of success in an appeal. … Finally, there would have to be detailed evidence of the attempts made to secure expedition in the F-tT and the reasons why those attempts failed. Whilst the jurisdiction exists to grant interim relief in this way, its use is likely to be sparing because steps (i) and (ii) identified above should provide practical relief in cases which justify it and the circumstances in which it would be appropriate for injunctive relief to issue will be rare.”
“(1) In an application for an interim injunction in a public law case, the basic principles which are familiar from American Cyanamid v Ethicon Ltd[1975] AC 936 are applied with some modification [51]. (2) Accordingly, ‘… whether to grant an injunction in a public law case involves the exercise of a discretion which takes all relevant matters into account, including the strength of the case advanced by the party seeking relief, but without applying a rigid test to that aspect, such as requiring a “strong prima facie case”
“(6) Sir Ross Cranston ruled that there was a power to grant the injunction sought but (1) the public interest would carry significant weight in the balance of convenience, (2) an applicant would need to establish to a high degree of probability that the absence of interim relief would render its appeal rights illusory and (3) that, following CC & C, an applicant had to show not just a realistic chance of success but something akin to an abuse of power, impropriety or unfairness.”
“(7) Although there were differences between the relevant statutory schemes, these did not mean that there should be different approaches to the grant of injunctive relief [92]. (8) If insolvency were to become a real prospect, the claimant's primary remedy should be to seek further expedition of its FTT appeal [126].”
“The operator shall manage and operate the activities: (a) in accordance with a written management system that identifies and minimises the risks of pollution, including those arising from operations, maintenance, accidents, incidents, non-conformances, closure and those drawn to the attention of the operator as a result of complaints; and (b) using sufficient competent persons and resources.”
“The operator is only authorised to carry out the activities specified in schedule 1, table S1.1.”
“The activities shall, subject to the conditions of this permit, be operated using the techniques and in the manner described in the documentation specified in Schedule 1, table S1.2, unless otherwise agreed in writing by the Environment Agency.”
“i. The landfill will be constructed and operated on the principle of containment. Details of the design of the site are presented in Section 2 of the Working Plan. Following the completion of landfilling and prior to the issue of a Certificate of Completion or equivalent under IPPC the best available techniques for pollution prevention and control will be used tominimise the risk of pollution from the site. The main subjects for pollution prevention and control are leachate and landfill gas management details of which are presented in paragraphs 2.17 to 2.31 and 2.32 to 2.52 of the Working Plan. The techniques for the management of leachate and landfill gas are consistent with the guidance presented in Waste Management Papers 26B and 27. ii. As described in Section 5 of the Working Plan monitoring in the post closure period will be carried out. Consistent with the guidance presented in Waste Management Paper 4 the monitoring will include leachate and groundwater levels and quality, surface water quality and landfill gas. The monitoring will be carried out to confirm the continued effectiveness of the containment system and the measures for leachate and landfill gas management at the site.”
“Emissions from the activities shall be free from odour at levels likely to cause pollution outside the site, as perceived by an authorised officer of the Environment Agency, unless the operator has used appropriate measures, including, but not limited to, those specified in any approved odour management plan, to prevent or where that is not practicable to minimise the odour.”
“(2) If the regulator revokes an environmental permit in part, it may vary the permit conditions to the extent that it considers necessary to take account of the revocation. (3) Where the regulator decides to revoke an environmental permit, it must serve a notice on the operator specifying— (a) the reasons for the revocation, (b) in the case of a partial revocation— (i) the extent to which the environmental permit is being revoked, and (ii) any variation to the conditions of the environmental permit, and (c) the date on which the revocation will take place, which must not be less than 20 working days after the date on which the notice is served. (4) Unless the regulator withdraws a revocation notice, an environmental permit ceases to have effect on the date specified in the notice— (a) in the case of a revocation in whole, entirely, (b) in the case of a partial revocation, to the extent of the part revoked.” (a) the reasons for the revocation, (b) in the case of a partial revocation— (i) the extent to which the environmental permit is being revoked, and (ii) any variation to the conditions of the environmental permit, and (c) the date on which the revocation will take place, which must not be less than 20 working days after the date on which the notice is served. (a) in the case of a revocation in whole, entirely, (b) in the case of a partial revocation, to the extent of the part revoked.”
“Closure and after-care procedures Member States shall take measures in order that, in accordance, where appropriate, with the permit: (a) a landfill or part of it shall start the closure procedure: (i) when the relevant conditions stated in the permit are met; or (ii) under the authorisation of the competent authority, at the request of the operator; or (iii) by reasoned decision of the competent authority; (b) a landfill or part of it may only be considered as definitely closed after the competent authority has carried out a final on-site inspection, has assessed all the reports submitted by the operator and has communicated to the operator its approval for the closure. This shall not in any way reduce the responsibility of the operator under the conditions of the permit. (c) after a landfill has been definitely closed, the operator shall be responsible for its maintenance, monitoring and control in the after-care phase for as long as may be required by the competent authority, taking into account the time during which the landfill could present hazards. The operator shall notify the competent authority of any significant adverse environmental effects revealed by the control procedures and shall follow the decision of the competent authority on the nature and timing of the corrective measures to be taken; (d) for as long as the competent authority considers that a landfill is likely to cause a hazard to the environment and without prejudice to any Community or national legislation as regards liability of the waste holder, the operator of the site shall be responsible for monitoring and analysing landfill gas and leachate from the site and the groundwater regime in the vicinity of the site in accordance with Annex III.”
“Application for a permit Member States shall take measures in order that the application for a landfill permit must contain at least particulars of the following: … (g) the proposed plan for the closure and after-care procedures.”
“Conditions of the permit Member States shall take measures in order that: (a) … (iv) adequate provisions, by way of a financial security or any other equivalent, on the basis of modalities to be decided by Member States, has been or will be made by the applicant prior to the commencement of disposal operations to ensure that the obligations (including after-care provisions) arising under the permit issued under the provisions of this Directive are discharged and that the closure procedures required by Article 13 are followed. This security or its equivalent shall be kept as long as required by maintenance and after-care operation of the site in accordance with Article 13(d). Member States may declare, at their own option, that this point does not apply to landfills for inert waste.” (a) … (iv) adequate provisions, by way of a financial security or any other equivalent, on the basis of modalities to be decided by Member States, has been or will be made by the applicant prior to the commencement of disposal operations to ensure that the obligations (including after-care provisions) arising under the permit issued under the provisions of this Directive are discharged and that the closure procedures required by Article 13 are followed. This security or its equivalent shall be kept as long as required by maintenance and after-care operation of the site in accordance with Article 13(d). Member States may declare, at their own option, that this point does not apply to landfills for inert waste.”
“Content of the permit Specifying and supplementing the provisions set out in Article 9 of Directive 75/442/EEC and Article 9 of Directive 96/61/EC, the landfill permit shall state at least the following: … (c) requirements for the landfill preparations, landfilling operations and monitoring and control procedures, including contingency plans (Annex III, point 4.B), as well as provisional requirements for the closure and after-care operations.”
“Progressing operational landfills through definite closure to after-care” (“the Landfill Closure Guidance”). The guidance on closures initiated by the Environment Agency includes the following: “We can start the closure process. This will normally be when the management of an operational site is poor and further operation of the site may result in significant, long-term pollution… Starting the closure process following a failure of the management of an operational landfill is similar toa revocation notice. You must only use it as a last resort once you have exhausted all other enforcement options (e.g., a suspension notice)… When you issue a landfill closure notice, the operator must still comply with their permit conditions. This ensures the operator remains responsible for maintaining active pollution control measures. A revocation notice may provide a similar level of control while it is in place, but its aim is to remove the permit. That is undesirable for a landfill that may present a pollution risk for decades.”
“persistent non-compliance with permit conditions that suggest that the operator is not competent to manage the activity.”
“The results for hydrogen sulphide in December 2024 were above the World Health Organization (WHO) odour annoyance guideline value for a significant percentage of the time at all three monitoring sites (MMF Maries Way, MMF Silverdale Pumping Station and MMF Galingale View). Since August 2024, the monthly percentage odour annoyance values have increased overall at all three monitoring sites. Exceedances of the odour annoyance guideline value may result in headache, nausea, dizziness, watery eyes, stuffy nose, irritated throat, cough or wheeze, sleep problems and stress. The more time spent above the guideline, the greater the likelihood of symptoms being experienced and consequently impacting people’s health and wellbeing. All three monitoring sites … show a monthly average concentration in December 2024 above the long-term (lifetime) health-based guidance value. Since August 2024, the monthly average hydrogen sulphide concentrations have increased overall at all three monitoring sites. The cumulative average concentrations for MMF Maries Way and MMF Galingale View are above the long-term (lifetime) health-based guidance value. At MMF Silverdale Pumping Station, the cumulative average concentration is below the long-term (lifetime) health-based guidance value. The risk to long-term (lifetime) health cannot be excluded, where the cumulative average concentrations are above the long-term health-based guidance value. Currently this risk is likely to be small, but the longer the exposure is above the long-term (lifetime) health-based guidance value, the greater any potential risk will become.”
“UKHSA is aware that residents living near Walleys Quarry Landfill site have experienced increased odour pollution from the site throughout December, continuing into January. The air quality data supplied by the Environment Agency (EA), for our December risk assessment, shows that hydrogen sulphide levels over the Christmas period were substantially above the World Health Organization (WHO) odour annoyance guideline level, with continual periodic high spikes of emissions throughout this time. This is consistent with the increase in local complaints sent to the EA and local authority. … The interim concentrations of hydrogen sulphide for the period 6 to12 January 2025 were above the WHO odour annoyance guideline value for a significant percentage of the time at MMF Maries Way, MMF Silverdale Pumping Station, and MMF Galingale View. The more time spent above the guideline, the greater the likelihood of symptoms being experienced and consequently impacting on people’s health and wellbeing. Assessment of daily exposure UKHSA has also used the WHO 24-hour air quality guideline value of 150 μg/m 3 to assess daily average exposure to hydrogen sulphide. This value is protective of eye irritation. The weekly raw (indicative) hydrogen sulphide monitoring data for the period 6 to12 January 2025 has been converted to 24-hour averages for each of the monitoring days. At MMF Maries Way, 24-hour average values were below the WHO 24-hour guideline value of 150 μg/m3. However, at MMF Pumping Station and MMF Galingale, the 24-hour average guideline value was exceeded on three days during the monitoring period: 10 January at MMF Pumping Station, and both 10 and11 January 2025 at MMF Galingale, with 24-hour average concentrations of 205 μg/m3 and 213 μg/m3 (10 January) and 258 μg/m3 (11 January). Exposure to concentrations of hydrogen sulphide above the WHO 24-hour guideline value may cause irritation of the eyes nose and throat. … Overall conclusions The assessment is that while the risk to long-term health is still likely to be small, short-term transient health effects may be experienced such as irritation to the eyes, nose and throat, in addition to effects resulting from odour such as headache, nausea, dizziness, watery eyes, stuffy nose, irritated throat, cough or wheeze, sleep problems and stress. Individuals with pre-existing respiratory conditions such as asthma and chronic obstructive pulmonary disease (COPD), may be more susceptible to these effects. ... UKHSA strongly recommends that all measures be taken to reduce the off-site odour pollution from the landfill site, to reduce the health impacts experienced in the local community.”
“1. The Environment Agency considers the management of Walleys Quarry Landfill Site to be poor, and that further operation of the site may result in significant long-term pollution from fugitive emissions of landfill gas. 2. The site operator has not installed capping systems or gas collection infrastructure promptly to minimise fugitive gas emissions. In addition, the site operator is not controlling leachate formation adequately or managing surface water to alleviate hydrogen sulphide generation. The site operator has been unwilling or unable to prevent acceptance of waste that has continued to produce hydrogen sulphide. The site operator has failed to manage the phasing and deposit of waste at the site to minimise emissions of landfill gas and facilitate the installation of capping and gas collection infrastructure in a timely manner. The site operator has had ample opportunity to address these shortcomings but has failed to do so. 3. The failure of the site operator to take the measures necessary to reduce fugitive gas emissions, with unacceptable levels of hydrogen sulphide, has resulted in odour pollution over an extended period and a risk to human health experienced by the community, as described by the UK Health Security Agency in its Health Risk Assessments. 4. The Environment Agency has therefore concluded that the site needs to close as the risk of significant odour pollution will continue as long as the site operator continues to accept waste.”
“With effect from 00:01 on29 November 2024 cease accepting waste and do not recommence the acceptance of waste for disposal or recovery at the landfill.”
“Except to the extent otherwise stated in our report, our work has been carried out on the basis that any information supplied (whether or not in writing and by Management or otherwise) to A&M and on which our work is based is complete, accurate and not misleading. Documents relied upon are referenced in the body of the report and at Appendix 3 as appropriate. All documents provided are assumed to be original or otherwise true and accurate copies. We have not tested, nor been asked to test, the accuracy and integrity of the documents and information provided to us. We take no responsibility for the integrity of documents, data, or other information provided as part of this engagement. A&M has not performed anything in the nature of an audit nor, except where otherwise stated, have we subjected the financial or other information contained in this report to checking or verification procedures. Because A&M’s services are limited in nature and scope, A&M cannot be relied upon to discover all documents and other information or provide all analyses that may be of importance in this matter. There is no assurance that all matters of significance will be disclosed by A&M’s work. A&M assumes no responsibility for the realisation of any projections.”