“The retrospective engineering operations are fundamental to the building/site functioning as a dairy farm enterprise. For example, the concrete yard area is used a ‘loafing area’, which is essential for cow welfare standards. … 6. Conclusion and Planning Balance The proposal seeks retrospective planning permission for the retention of engineering operations carried out without formal planning permission. These works are required for this building/site to accommodate a dairy herd.”
“At present, the Environmental Protection Team does not consider sufficient measures have been demonstrated to address the concerns raised above. The Environmental Protection Team considers that robust control measures need to be implemented to prevent or minimise any potential detriment to amenity. The Environmental Protection Team requires the applicant to produce an environmental management plan, to be devised by an appropriately qualified professional body (eg. ADAS), that provides comprehensive details on measures that include noise and odour control, manure and slurry storage, pest control and fly management that will be introduced to prevent or minimise disturbance to neighbouring residential properties. The Environmental Protection Team will provide further comments upon receipt and following review of the environmental management plan.”
“The starting point for this application is to consider the existing baseline (i.e., what is going on on site and what can the applicant do without the need for planning permission). In this case none of the buildings have restrictions relating to the use of livestock, and the applicants are currently housing livestock in the buildings as a result. 3rd party representation notes that the buildings have not been used for livestock for a long time, but it appears to be accepted that they have been used for livestock in the past, and it is debatable about when this was. In addition, 3rd party representation claims that existing amendments to the buildings have enabled the buildings to be used for livestock (addition of doors on the southern elevation and some walling on the west). In the opinion of the Planning Officer, no material change of use has occurred on site, and the applicants can and could have used the buildings for livestock without consent. It is accepted that the walling on the western side of the building requires planning consent. In addition, it could be argued that the proposed walling on the western elevation increases the potential livestock numbers available to the applicants. On the other hand, it would not be development to put up internal walling within the building, such as cubicles (or walling on the outside of the building providing it was compliant with part 2 of the GDPO) to house the current stock, nor would a temporary/seasonal gale breaker be likely to be considered development. This would be similar to the existing current scenario, where a concrete plinth has been added to keep livestock in the buildings, and hay bales have been used as a windshield. Thus, the existing buildings can be used to house cattle, and a nuisance could arise as a result (indeed the neighbouring dwelling considers nuisance is already occurring). Even if this application were to be refused, the livestock use could remain, along with the internal developments such as the milking robots etc. The concrete yard area is not considered to increase stock numbers as it is an external area (despite 3rd party representations to the contrary). The cattle could have stood in proximity to the buildings previously, and the yard will simply assist in keeping the site tidy. It would not be common practice within the assessment of a planning application to suggest a yard area would increase stocking numbers. In support of this application, a Sound Impact Assessment and Environmental Management Plan (EMP) have been provided by the applicants. Objections to both documents have been received from the neighbouring dwelling. In addition, a SCAIL assessment has been carried out by Isopleth, which again the neighbours object to. An Odour Report has been submitted by the neighbouring dwelling, which identifies that the use of the building for cattle could have the potential for unacceptable odour pollution. This is responded to by Isopleth (on behalf of the applicants) who consider the submitted Odour Report inaccurate, and the author of the original report then proceeds to critique the Isopleth Response. All of the above reports relate to the applicants wider aims of developing the site, which includes extensions to the buildings and the erection of a slurry store. This application (1/1131/2021/FUL) is slightly different to the others, because the development would not result in any significant difference in how the existing site is run or managed (or could be run or managed without any 'development' taking place).”
“The key points (so far as material for present purposes) are:- a. The applicant has a lawful ability to undertake the fall-back development; b. The applicant can show that there is at least a “real prospect” that it will undertake the “fall back” development if planning permission is refused. In Mansell at §27, Lindblom LJ explained that : “the basic principle is that “for a prospect to be a real prospect, it does not have to be probable or likely: a possibility will suffice”. c. Where a planning authority is satisfied that a fall-back development should be treated as a material consideration, the authority will then have to consider what weight it should be afforded. This will involve: i. An assessment of the degree of probability of the fall-back occurring. As Dove J observes in Gambone at para 27, the weight which might be attached to the fall-back will vary materially from case to case and will be particularly fact sensitive; and ii. A comparison between the planning implications of the fall-back and the planning implications of the Proposed Development: Gambone paras 26-28. d. The Courts have cautioned against imposing prescriptive requirements as to how and with what degree of precision the fall-back is to be assessed by the decision maker. This is in recognition of the fact that what is required in any given case is fact sensitive. As Lindblom LJ observed in para 27(3) of Mansell, there is no general legal requirement that the landowner or developer set out “precisely how he would make use of any permitted development rights”
“As previously discussed, (in section 3), this application (1/1131/2021/FUL) is unlikely to materially impact on the stocking levels which are possible in the existing buildings, nor would it impact on the slurry arrangements on the holding. Therefore, the proposal cannot be said to have a significant impact on the SSSI's mentioned above. In addition, the nature of the development is minor in nature (walling to existing buildings and a concrete yard), and the proposals are significantly distanced from the SSSI’s (approximately 3.9 KM and 3.7KM respectively), again limiting any potential impacts. In combination with existing and proposed developments locally, this application will have a neutral impact due to the nature of the scheme (as previously discussed). In light of the above, this proposal is not considered to adversely affect the integrity of the above sites. This application has been screened against the Town and Country Planning (Environmental Impact Regulations), and due to the limited increases in any stocking, it is not considered that an Environmental Statement is required. Overall, the proposal is considered compliant with Policies DM08 and ST14 of the NDTLP and the NPPF.”
“3.3 Odour/Ammonia Emission Management Odour from slurry is principally caused by ammonia, which is emitted in its gaseous form from slurry and can have a pungent, obnoxious odour, particularly in high concentrations. The prevailing wind at Bidbeare is between west to south-west. The residential property immediately to the west of the farmstead at Bidbeare will, most times, be upwind from the farmstead and not be affected should any odour emanate from the farmstead. Best farming practice will be followed. Regular scraping of slurry from the surfaces of yards and passageways into the covered slurry channel, flushing of the channel by parlour washings and storage in the covered tank will minimise, as far as is practicable, ammonia emissions and odour throughout the year by limiting exposure of slurry to the air. Yards and passageways frequented by livestock will have excreta scraped to the slurry channel for storage, as necessary for livestock welfare and according to best farming practice, when occupied during the winter housing period. When livestock are at pasture and transiting from the field to the milking machines, the yard area to which livestock have access will be minimised and cleaned by regular scraping of slurry into the covered slurry channel, in order to minimise ammonia emissions and odour. Dry conditions can make a surface slippery for cows and scraping will be suspended if there is a danger to animal welfare. The steel tank will be emptied of slurry, in accordance with requirements of the NVZ Regulations, by pump to fill vacuum tankers or by using an umbilical hose which will apply the slurry to the land using low-emission techniques, to minimise ammonia emissions – a requirement of the Clean Air Strategy by 2025 - and odour.”
“Although as described above the results or conclusions of the MBAL report cannot be relied upon, I would agree that the EMP should be updated / added to in relation to measures to prevent odour release, monitoring and actions in the event of complaints, for example.”
“In general, there is a complete lack of detail on how odour emissions from the site will be controlled and reduced. Consideration to sensitive receptor positioning, specific prevailing meteorological conditions, activities that have the potential for greater emissions, monitoring of impacts and potential further mitigation measures for implementation during periods of abnormal emissions has not been provided. A risk assessment or similar to inform the process and the required level of control has also not been undertaken. Without this element it is unclear how potential impacts can be fully understood and the level of control required to reduce residual effects to the level required by the National Planning Policy Framework (NPPF).”
“29.04.2022 Further to the previous consultation response dated 13 April, the Environmental Protection Team has reviewed the final Environmental Management Plan which it considers addresses the representations raised with regards authenticity. Subsequently, the Environmental Protection Team wishes to update the previous response and recommends the imposition of the following condition: The proposed development will be operated at all times in accordance with the ADAS Environmental Management Plan dated26 April 2022 . 09.09.2022 The Environmental Protection Team has reviewed both the Michael Bull and Associates Ltd report (July 2022) submitted by Mr and Mrs Ward and the Isopleth Ltd report (August 2022) submitted by the applicants. The Environmental Protection Team had initial concerns with the assumptions and modelling contained within the Michael Bull and Associates Ltd report and these have been highlighted within the Isopleth Ltd report. It is the opinion of the Environmental Protection Team that the concerns raised within the Michael Bull and Associates Ltd report have been satisfactorily addressed within the Isopleth Ltd report. As there is mention of odour complaints within the reports, it is worth reiterating that this Authority has undertaken an investigation pertaining to a complaint of odour nuisance in accordance with theEnvironmental Protection Act 1990 and a statutory nuisance was not established. However, it should also be noted that the investigation, comprising of site visits, was based on the current operations and practices as opposed to the proposed operations. Both of the aforementioned reports suggest the inclusion of a complaints process. Whilst the Environmental Protection Team considers this to be a worthy addition to the Environmental Management Plan, a complaints process as per the Environment Agency's H4 Odour Management guidance would seem onerous given the scale of the operation and especially in light of the recent High Court decision in Cathie v Cheshire West andChester Borough Council (Case Number: CO/4229/2021). In summary, the Environmental Protection Team is satisfied, notwithstanding the addition of a complaints process to the Environmental Management Plan, that sufficient measures have been proposed by the applicants that will provide betterment to the farm operation as well as ensure the impact on neighbouring amenity is minimised. 27.09.2022 In relation to the above applications, the Environmental Protection Team has reviewed all information provided by both the applicant and the objector at the neighbouring dwelling. Clearly there is disagreement between the two parties in relation to the amenity impact from the agricultural operations subject of the applications which has made the process of review somewhat complex and convoluted. Whilst the concerns of the objector are acknowledged, it is the opinion of the Environmental Protection Team that the measures proposed by the applicant will provide betterment in terms of the agricultural operations whilst ensuring the protection of neighbouring residential amenity. Subsequently, the Environmental Protection Team has no objections to the applications and refers to its previous consultation responses with regards the imposition of conditions pertaining to the environmental management plan and noise. It should be noted that the environmental management plan, as with any management plan, is an active document and should be regularly reviewed and updated where necessary. Therefore, it is recommended that the environmental management plan is appended with a section that ensures an annual review and more regular review where significant operational changes may be planned or introduced.”
“Appendix 4 of the IAQM 'Guidance on the Assessment of Odour for Planning'6 provides a comparison of Odour Management Plan (OMP) requirements in various documents produced by the EA, Scottish Environmental Protection Agency (SEPA) and SNIFFER. The IAQM's own requirements are outlined in Table 8 of the document. Of these factors, the Environmental Management Plan does not provide: •Essential site details such as inventory of potential odour sources, a map of sensitive receptors and a wind rose of prevailing meteorological conditions; •Assignment of responsibility to individuals to undertake the described actions; •Identification of reasonably foreseeable abnormal conditions that may increase odour emissions and additional controls; •Triggers for additional controls; •Monitoring; and, •The management structure which will ensure the outlined control measures are implemented appropriately and effective.”