
Submissions

Attn Minerals and Waste Planning Policy
Elizabeth 11 Court West,
The Castle,
Winchester
SO23 8UD
5th March 2024
email only
Dear Minerals & Waste Planning Policy,
Hampshire Minerals & Waste Plan: Partial Update (2023) Regulation 19 Consultation
Attached to the accompanying email message is the response from Friends of Ringwood Forest (FoRF) to the Regulation 19 Consultation, together with 4 related documents. Please note that our website at www.liveforest.org is also part of our evidence base and is referred to in our response.
FoRF wishes to participate in hearing sessions to represent the interests of community members most directly affected by the outcome of this consultation with regard to the proposed Purple Haze site.
FoRF also wishes to be kept informed when the Plan is submitted for independent examination, when the examination recommendations are published, when the Plan has been adopted and also of future minerals and waste policy work.
Please contact me should any questions arise or if further clarification is required.
Britt Poyntz
Secretary - Friends of Ringwood Forest (FoRF)
Cc. Lisa Kirby-Hawkes, Head of Development & Flood & Water Management
Enc 1: GWP Consultants LLP Report & covering letter (2 documents)
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Enc 2: FoRF Responses to Purple Haze Planning Application 21/10459 (2 documents)

Submission March 2024: Hampshire Minerals & Waste Plan: Partial Update (2023) Reg 19 Consultation
1. Background
Friends of Ringwood Forest (FoRF) is a local community action group based in Verwood, Dorset leading the No2PurpleHaze campaign and representing 4.7K+ supporters drawn from local communities and from visitors to both Ringwood Forest and Moors Valley Country Park (MVCP).
FoRF was established in 2011 to challenge the allocation of Purple Haze, located in Ringwood Forest and adjacent to Moors Valley Country Park, by Hampshire County Council (HCC) in its then proposed Minerals & Waste Plan (M&WP) 2013 as a soft sand & gravel site and subsequent waste landfill site.
FoRF has continued to strongly object to the development of the Purple Haze site with particular regard to Community Impact concerns in response to all related public consultations including the yet to be determined Planning Application, HCC ref: NFD03 21/10459, submitted by the site developer, Grundon Sand & Gravel, to develop Purple Haze as a quarry only.
FoRF’s position for the current Regulation 19 Consultation, and with regard to the Purple Haze site in particular, remains unchanged. We therefore submit below a further Objection in response to our review of the HCC Minerals and Waste Plan: Partial Update – Proposed Submission Plan (2023) which we consider to be Unsound.
2. About Our Submission
While our submission primarily addresses Community Impact concerns, FoRF also recognises and strongly supports the expert opinions of other organisations such as EDEP and the Statutory Consultees which will set out the significant hydrological, ecological and environmental harm which, should Purple Haze ever be developed as a minerals and/or waste site, is certain to damage - deeply and irreparably - a tranquil and highly valued landscape as well as nearby sensitive & protected locations, particularly Ebblake Bog SSSI [part of the Dorset Heaths SAC, Dorset Heathlands SPA and Ramsar].
Our aim is the removal from HCC’s Proposed M&WP (2023) of the allocation of Purple Haze as a quarry site together with any implication it could also be utilised, at some future point, to manage inert and/or non-hazardous waste.
In support of our Regulation 19 Submission, we also include this additional documentation: -
(i) the GWP Consultants Report & covering letter October 2011 (see para 3.1. below) – click for original documents:
The content of the No2PurpleHaze campaign website www.liveforest.org is also included as part of our evidence base supporting our Objection to the inclusion of Purple Haze in the Hampshire Minerals & Waste Plan (2023). It expands on the primary concerns included in our submission below and demonstrates that HCC’s Proposed M&WP (2023) is Unsound.
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3. Regulation 19 Consultation Response – Purple Haze
3.1 About the Minerals
3.1.1 Site Allocation (Policy 20)
Much of the material extracted from Blue Haze, sharing similar geological strata as Purple Haze on the opposite side of the B3081, is understood to have been of such poor quality and low marketable value that it was mostly used as inert landfill – for example, as landfill for Nea Farm as well as being suggested for use to make good the haul road.
Very little detailed bore hole drilling information has been made available. Failure to provide the detailed hard evidence required to confirm the quality and quantity of the soft sand resource throughout Purple Haze, the primary reason for its continuing allocation in the proposed Hampshire M&WP 2023 (Policy 20), casts doubt on the projected amount of soft sand to be extracted for sale as well as the burden of clay/silt also requiring removal during pre-sale processing.
That doubt is confirmed in a report here and covering letter here commissioned from GWP Consultants LLP by FoRF during examination of the proposed Hampshire M&WP (2013).
Until the required hard evidence has been provided, and about soft sand particularly, there will be continuing doubt about the volume and quality of the minerals available for extraction. The allocation of Purple Haze as a required soft sand quarry to meet Hampshire’s needs is therefore considered unsafe. The proposed Hampshire M&WP (2023) continuing allocation for Purple Haze (Policy 20) is considered Unsound.
3.1.2. Volume of Minerals
Following the allocation of Purple Haze in the Hampshire M&WP (2013), planning application 21/10459, currently undetermined, was submitted in 2021 by the operator - Grundon Sand & Gravel.
Following submission of their application, the operator excluded areas at the northern and southern ends of the site from their extraction plans. The very limited drilling information available indicates a variance in the quality of the mineral resource across the site such that soft sand will require washing to remove clay & silt deposits.
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It is noted, however, that –
(i) both the Hampshire M&WP (2013) and the Hampshire M&WP: Partial Update – Proposed Submission Plan 223 (Page 179) and updated Policy 20 state the total resource as 7.25m tonnes of soft sand and 0.75m tonnes of sharp sand and gravel, and
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(ii) the anticipated soft sand resource following removal of 2 extraction areas has not been stated in the planning application.
In addition, water levels across the site will be far higher than when the test boreholes were drilled in April 2019 (highlighted in the table below). Even then, much of the resource was wet.
The impact of this and of increased rainfall due to climate change on the availability of the resource and on the hydrology of the site have not been addressed.
Rainfall data
Table 1 Rainfall data (mm)
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* from Applicants’ report ** from Hurn data
Changes are therefore required to both Hampshire M&WP Policy 20 and the Hampshire M&WP Proposed Plan (2023) either to reflect any anticipated reduction in the soft sand available or to confirm that the claimed resource is unaffected by both the reduction in the site’s overall extraction area and the impact of increased rainfall and storm events due to climate change. To fail to do so would cause the proposed Hampshire M&WP (2023) to be considered Unsound.
3.1.3 Use of landfill
Based on their very poor experience of the close proximity of the Blue Haze landfill site to Verwood, local residents were extremely concerned in 2011 that Purple Haze had been allocated in the Hampshire M&WP 2013 to operate eventually as a waste landfill site.
When considering the proposed Hampshire M&WP Submission Plan (2023) it was noted that Purple Haze has not been allocated as a waste management site. However:-
(i) Hampshire Minerals & Waste Plan: Partial Update Sustainability Appraisal (Incorporating Strategic Environmental Assessment) Environmental Report - Page 181 states: -
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'3. in the event that further capacity is required, or if any other shortfall arises for additional capacity for the disposal of non-hazardous waste, the need may be met at the following reserve area, provided any proposal addresses the relevant development considerations outlined in Appendix A – Site allocations: i. Purple Haze, near Ringwood (Inset Map 12)'
(ii) Hampshire Minerals & and Waste Plan: Partial Update – Proposed Submission Plan (2023) Page 179 states under the Restoration heading: - 'If the site is not used for non-hazardous landfill, inert fill will be used to agreed levels'.
(ii) Under Development Considerations it is stated: - “Importation of material as part of the restoration would need appropriate supporting investigations and risk assessment” which would, it is construed, include both non-hazardous & inert waste as well as other more suitable materials.
In other words, Purple Haze has been effectively safeguarded, but not formally allocated, as a waste management site. This is contrary to the carefully crafted statements made at successive public events held in Verwood with regard to the planning application submitted by the operator that Purple Haze would NOT be a waste management site.
Additionally, ecology and environmental experts are understood to agree that if the desired “better than before” mixed landscape is going to be achieved, non-hazardous/inert waste should NOT be imported to fill the deep voids left after mineral extraction in order to support the restored desired landscape.
There is no local record of successful restoration of desired landscapes in and around Ringwood Forest using waste materials as landfill. See Blue Haze, across the road from the proposed Purple Haze site, as just one example of failed restoration over waste landfill. For these reasons, the proposed Hampshire M&WP (2023) must be considered Unsound.
Changes required include:
(i) The removal of the reference, from both locations mentioned above in the proposed Hampshire M&WP (2023), to the use of non-hazardous/inert waste as landfill to support restoration at Purple Haze.
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(ii) Amend the Planning Consideration addressing the need for a Transport Assessment to include the volume of traffic likely to be generated to remove surplus waste clay and silt and the importation of material to support restoration. It is understood this need has not been addressed in the Transport Assessment completed to support the yet to be determined planning application for Purple Haze.
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3.1.4 Financing restoration
Restoration to the desired mixed landscape will also have, we believe, a considerable financial cost, probably for perpetuity. There is no evidence of how those considerable costs will be guaranteed to be met over the entire projected restoration period if, for example, the operator withdraws from the site for any reason. The proposed Hampshire M&WP (2023) is therefore considered to be Unsound.
4. About the ecology
As well as damaging sensitive and protected sites such as the Ebblake Bog SSSI [part of the Dorset Heaths SAC, Dorset Heathlands SPA and Ramsar] the development of Purple Haze will deeply damage, if not destroy, the habitats of a number of rare and endangered species such as smooth snakes and sand lizards which are the UK’s rarest and most secretive reptiles.
The Purple Haze site also contains populations of rare threatened or near threatened birds and the rare and endangered Coral Necklace plant. The proposed plans for extraction and restoration pose a significant risk to the biodiversity of the area.
Ecology & environmental experts all agree that plans to protect rare and endangered species currently in and located near to Purple Haze, both flora & fauna, are not good enough. The mitigation offered to move, for example, rare reptiles to new locations in what are known as offset areas are also considered by the experts to be inadequate and very likely to fail.
Unless improved provision is made to protect and restore the habitats of rare and endangered species, restoration after mineral extraction will fail. For this reason, the proposed Hampshire M&WP (2023) is considered Unsound.
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5. Planning considerations – Purple Haze
Planning considerations requiring amendment: -
• Dust, noise and lighting management plan and monitoring baseline data are required to be in place before Mineral extraction commences. The monitoring processes must include regular liaison with Verwood Town Council.
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• Protection and enhancement of the amenity with no net loss and for users of the Moors Valley Country Park and other local residents. Restoration of amenity should be phased to avoid reliance on the completion of extraction.
Additional planning consideration(s) Required: -
• Protection of Verwood’s mains water supply.
• Provision within the restored landscape for open public spaces to be used for recreational amenity.
Change requested: It would be helpful if related Planning Considerations were grouped together by subject area.
END 2024 SUBMISSION
Submission April 2023: Purple Haze. Response to application no: 21/10459 Site ref: PLAN/NF272
Proposal: Extraction and processing of building sand together with incidental sand and gravel, ecological mitigation works, new access off the B3081 Verwood Road, processing plant, conveyor system, weighbridge, site office and welfare facilities, staff parking with progressive restoration to a mosaic of lowland heath, gorse scrub, woodland and pond areas
1. Introduction
Friends of Ringwood Forest (FoRF) is a local community action group leading the No 2 Purple Haze campaign. Our supporters are drawn from the Dorset town of Verwood (pop. 15K+), its surrounding communities as well as from regular visitors to Moors Valley Country Park which is adjacent to the proposed site.
About the FoRF Objection . . .
Our strong Objection to permitting the planning application for the development of Purple Haze as a mineral extraction site is reiterated following public invitations to review and comment on the content of this response.
The reiteration of our Objection is necessary after examining the applicant’s Regulation 25 Response and the related new and revised documentation where we have focussed on interest areas which have significant Community Impact. Other organisations and consultees have addressed the major environmental & ecological issues arising from the updated proposals for the Purple Haze site and we fully support their conclusions.
Preparation of our response to the Regulation 25 Request Consultation was not assisted by the applicant’s failure to ensure -
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Information about a subject referred to in several locations within the updated application documentation is consistent,
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all data referred to as analysed, and from which conclusions had been drawn, was available for examination,
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referenced externally authored documents had been published in order to prevent future changes impacting any Plan’s construction or forecast outcomes,
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documents/plans are not presented as revised where only the version/date has changed,
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and, importantly, contributors to document preparation recognised that while Hampshire County Council is the MPA for the Purple Haze site, the vast majority of residents affected most directly by their proposals live and work in Dorset.
The issues outlined above drove an increasing lack of confidence in the documentation presented for this consultation. Given the importance placed on the outcome of the Purple Haze planning application by so many people and organisations, generating the level of concern driven by the applicant’s Regulation 25 Response documentation appears disrespectful and is simply not acceptable.
The following documents were examined: -
2. Outline Landscape and Ecology Management and Monitoring Plan (LEMMP)
2.1.2 LEMMP Much more detail is needed on the off-setting areas as outlined in this Plan; for example - How will the developer create the right off-set environment to support the off-setting objectives? Who has agreed to this? What public access would be permitted and when? What parking would be available to cope with any increased usage? It is not made clear within this Plan whether the off-set areas are intended purely for wild-life or whether they are intended to also provide the public with additional walking facilities. It appears they are to attempt to provide incompatible functions.
There are, however, enough bits of information amongst other application documentation to construe that the smaller offset is intended mainly for biodiversity (despite the car park and bridleway bisecting it) with the larger, known as Jack’s Garden, intended for biodiversity + displaced visitor access. It is anticipated that other consultation responders will have questioned the appropriateness of Jack’s Garden for the latter purpose. We would support those responders and will welcome any resultant clarification.
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2.5.1 This section is too vague. When does the 60-year period of responsibility start? Where can the definition of appropriately qualified contractors and ecologists be found?
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2.5.2 This section doesn’t go far enough. A Planning Condition is therefore required setting out: -
(i) the precise responsibilities of the appointed ecologist and who they will be accountable to,
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ii) how they will report back to the public, to both the Hampshire and Dorset Mineral Planning
Authorities plus other interested parties, and
iii) whether they will have the power to stop operations if they determine there are new or currently unforeseen ecological risks or problems.
2.6.1 & 2.6.2 Further clarification is required. It’s very unclear how the restoration proposals dovetail with the emerging Forest Plan if this latter plan is yet to be published. We understand that a significantly revised Plan is awaiting further consultation: until it is published and finally signed off, there will always remain a possibility it will change.
2.6.4 We challenge the statements made here. We cannot determine the basis of the assumption that the proposed works will not result in the displacement of visitors to other sensitive sites. Local knowledge suggests that recreational users are unlikely to drive distances to access other locations, such as in the New Forest, or will stick to pathways that are on the immediate boundary of the quarry works. People are more likely to instead access pathways close to nearby Ebblake Bog, along the edge of the Moors Valley golf course and onto Rushmoor (part of the Holt and West Moors SSSI) which lies adjacent to the road from Verwood towards Three Legged Cross.
2.6.9 The reptile mitigation strategy seems to be based on the retention of an area of habitat that is far too small and cannot provide all the requirements for all 6 species and the translocation of reptiles to both this and the newly created habitat between the fire break and B3081. Yet the strategy is “Outline” only: given the national and regional importance of sand lizard and smooth snake far more precise detail is needed at this stage.
2.6.10 Detail is needed on how Nightjars will be provided with a suitable alternative habitat. How will the extraction plan deal with nesting Nightjars in terms of ensuring that their nests are identified and they are not disturbed during the nesting/breeding season? Clarification is required.
4.4.3 This section appears to be an attempt to impose more controls in the area, i.e., dogs on leads, walkers on guided paths only. This appears to be being done in the name of conservation. It is, however, a significant change to the way that people use the whole area today and how they would normally conduct themselves elsewhere within the adjacent Moors Valley Country Park. It’s unclear how this could possibly be policed/controlled – for example, any number of people visit this area out of normal hours solely because of the seclusion and tranquillity it offers at those times.
Further clarification is also required here as it is unclear whether there will be permanent public exclusion from areas other than those determined by the proposed Final Footpath Plan.
4.7.2 We are concerned by the implied threat that if people consistently stray away from the prescribed paths, then fences/barriers are likely to be erected to stop them. We would suggest that, instead, the applicant invests in appropriate solid track making such as those successfully established in nearby locations such as Stephens Castle and Dewlands Common or, indeed, elsewhere in the adjacent Moors Valley Country Park.
5.1.1 This section is hypothetical and not based on scientific analysis. The implications that the extraction plan will not have any impact on the SSSI are not based on objective analysis. When considering the information provided elsewhere in this application’s latest set of documentation, it is simply not possible for the applicant to guarantee that run off will not happen from the extraction sites. Relying on the depth of a void to prevent overflow seems a risky strategy. A deep void with even a small amount of water sitting in it for any amount of time would instead create a potential and considerable public safety issue.
5.2.1 This section acknowledges there is a risk of run-off pollution but does not specify how this will be monitored in real time and dealt with if pollution does occur. A Planning Condition is required to establish an effective 24hr real-time monitoring system with an agreed action plan in the event of a pollution incident.
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7.4.1 The proposal to enhance the two off-set areas to compensate for the loss of SINC quality habitats lacks detail. A full survey is required not just for vegetation and should include information on current visitor use. A minimum net gain of 10% must be demonstrated.
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9.1.17 It is recognised that public access to the Purple Haze location is permitted by the Somerley Estate. The applicant has failed to set out, as referred to elsewhere in this response, how the replacement of existing access managed through facilities operated/managed by the adjacent Moors Valley Country Park such as 2 cycle routes and the Bridleway, is going to be managed and the ongoing maintenance funded.
It follows that the existing car parks at Bakers Hanging and the Coach Road, used for recreational purposes by visitors to enjoy Moors Valley Country Park locations as well as to access the current Purple Haze tracks, will close. To help maintain visitor numbers to Moors Valley Country park, and so offset risk from potential future financial impact, it’s clear that facilities at both the Ebblake and Watchmoor Wood permitted car parks must therefore be substantially extended. This will also impact on biodiversity. This is not covered in the Plan.
9.1.18 The tragic accident near to Bakers Hanging in the last two years shows the dangers that can arise if trees are felled and the remaining trees are exposed to strong winds and risk of wind throw, especially where soils are wet. Inspection of the health of the trees every 3 years or after an extreme weather event will simply not remove the danger to the public using the B3081. Because of the nature of the soil here and exposure to wind, the Plan should be updated to require the trees referred to in this section to be inspected every year and after all extreme weather events.
9.1.20 This section doesn’t go far enough. The final sentence should be amended to change “should” to “will”.
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13.1.3 This section should be extended to cover the likely impact on public access during tree felling. We have set out during previous consultations the adverse impact on tracks which can be caused by the vehicles involved, often making some impassable or waterlogged. Where tracks so affected are not within the boundary of the proposed site, the action which will be taken by the applicant to resolve any such issues should be set out in this Plan and covered by a Planning Condition.
13.2.4 This section confirms that the public will only be allowed on the permitted paths. Further clarification is required as it’s unclear whether this solely applies to the quarry area or also to the whole broader area covered by the marked paths.
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14.2.3 Seems completely unrealistic. How will quarry workers be trained and incentivised to identify reliably individual bird species and then stop work to allow an ecologist to assess the situation? The applicant should provide examples of where this practice has been successful during the operation of other mineral extraction sites they manage.
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15.1.2 It would be hoped that other interested parties could be allowed to participate in the inspection of aftercare operations, or as a bare minimum, the resultant reports made available to the public and that this requirement is supported by a Planning Condition.
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16.1.1 As the site is on their doorstep, we’d like to see this section expanded to include the involvement of local residents in the process, perhaps through liaison via Verwood Town Council. Residents who visit this area could then become effective eyes & ears, especially outside of the site’s normal operating times.
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3. Proposed Diversion Plan (Drawing 2785-4-3-2 DR0002-S4-P1)
The Plan is incomplete. No mention is made of the intended fates of either the Watchmoor or the Somerley cycle routes. Nor has Bridleway BR E60/50 been included. The bridleway is of importance as part of a recognised Safe Route used to navigate the B3081. Please note that submitted comments to date have addressed only the Hampshire Rights of Way. An alternative route must be found which is established prior to site start-up, supported by a Planning Condition.
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4. Transport (Revised Environmental Statement III: Figures and Appendices 1-12, dated January 2023, Appendix 10)
The applicant has stated that a Regulation 25 Response update of this document was not required as
Hampshire Highways raised no objections to previous Highway design proposals for site access (B3081). It is, however, a consequence of the changed content of updated documentation presented in response to the Regulation 25 Request, that these issues now need to be addressed –
1. Dorset Council felt that a three week survey of the overall traffic figures should be carried out. The Junction Assessment of 2022, however, only appears to relate to site/staff/public vehicles entering or leaving the site. The purpose of the survey is unclear. It’s also unclear whether it complies with transport related impact requirements.
2. Proposed mitigation for likely unacceptable congestion around the B3081 and Bakers Hanging junction is not mentioned.
3. There is no assessment of the impact of the construction of the proposed road layout - How long would this take? Will traffic be rerouted whilst the work is carried out? Have the numbers in potential queues been assessed and, if so, where’s the data?
4. There is no assessment of the dual danger of traffic entering/leaving the Somerley Recycling Site and the entrance to Purple Haze at the same time during construction of the new road layout and site operation access and possibly after their completion. A recent road traffic accident involving several vehicles in this area highlights situations which are a frequent risk when queues form nearby. For example, an assessment for this current period of vehicles entering Somerley Recycling Site suggest that if all slots are booked this could result in 187 vehicles per day.
5. The opening of the Hamer Warren Solar Farm site on the road from Bakers Hanging junction to
Alderholt would also result in an increase in traffic. The junction has been described by Dorset Council as a site of long standing concern. The cumulative effect of traffic involved in other sites in the area – e.g., Blue Haze Landfill Site - other quarries and those servicing the continued housebuilding in Verwood do not appear to have been considered.
6. There is likely to be additional risk around the site entrance during the hours of darkness which may need mitigation. Streetlighting is not advocated as a solution and would be resisted as provision will have a damaging ecological impact.
7. No assessment is evident of the impact which the combination of hard landscaping near the site together with the proposed clear felling of some of the trees along the B3081 will have on surface flooding of the road, increased run-off and therefore possible ground pollution which must be considered and mitigated.
8. Additionally, no indication can be found of how the proposed clear felling of the roadside border beside the site and the B3081 will be managed – particularly how avoidance of verge damage will be achieved when using of heavy machinery and vehicles. How long will clear felling in this area take to complete? Will road drainage gullies be kept clear during the felling? More detail is required.
9. Where and how would walkers, of which organised groups as well as individuals can be seen using the B3081 verges between Verwood and Bakers Hanging, be diverted to? Ideally, the long needed, and often requested, multi-user pathway/track with a compact surface alongside the Verwood to Bakers Hanging stretch of the B3031 - often referred to locally as a cycle path - would be installed prior to the site commencing operations. It would be a major community benefit to local people and visitors alike. It would also take some pressure off tracks on the Moors Valley Country Park side of the site from walkers, cyclists and others who currently use them solely to safely avoid the main road.
10. Finally, it’s unclear how the clear-felled area, with perhaps some trees remaining, between the B3081 and the site boundary would be maintained long-term and whether this area extends beyond the immediate site entrance. Assuming a longer area might be clear-felled, it’s worth noting that the B3081 verges are frequently strewn with litter. Litter-picking by both Hampshire & Dorset Councils can be sporadic and often relies on public reporting to get it cleared. Verge cutting usually takes places seasonally and often without litter picking immediately beforehand. Given the more open aspect resulting from clear felling, what measures will be taken specifically to prevent micro-plastics and larger items of litter entering the site both during and after both operations and restoration? It’s also not clear who will take maintenance responsibility for the clear-felled areas between the B3081 and the site boundary. Clarification is required.
5. Visitor Survey (Environmental Statement Appendix 2: Ecological Chapter - Appendix 12)
Opinion Summary
The Visitor Survey Appendix is considered to be totally inadequate, biased and with some conclusions drawn which are more opinion than data analysis based. It is also considered to be fundamentally flawed for these key reasons: -
• The Visitor Survey Report has been constructed in such a way as to draw positive conclusions, regardless of the data.
• The survey sample size (368 surveys completed) is too small to draw any meaningful conclusions and the decision to conduct it outside a main holiday period paints a false picture of the true number of visitors to the impacted area.
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• The survey exercise was shambolic and is discredited by the admission that the CCTV detection systems were placed in such a way that they were likely to miss people passing them, again minimising the numbers. The admission that they were unable to man all of their chosen survey locations again reduces the effectiveness of the survey.
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• The survey was conducted in the middle of the Covid pandemic and whilst there were no restrictions on accessing Ringwood Forest, it is clear that many people were still reluctant to leave home and to risk any social contact. This paints a low and false picture of the normal use of the surveyed area.
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Conclusion: Now there is greater social mobility following the Covid pandemic, a further Visitor Survey is required which embraces at least a representative part of a holiday period, offers correct choices for other sites to visit and includes all data analysed to support the conclusions subsequently drawn.
Detailed evidence supporting the above Conclusion follows -
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About the Key Findings . . .
The Key Findings section in the report is considered to be superficial and biased as set out in our following comments -
368 visitor survey forms were completed, with 36.7% of users not choosing to conduct a questionnaire when invited to do so. 4,164 site users were observed during the seven days of monitoring at six locations with CCTV cameras.
Comment: Average of 99 users per location per day.
There were a wide variety of reasons for visiting the site, with proximity to home being the key Reason.
Comment: This is not a reason for visiting the site, it is a simple data point which refers to where people travel to the site from.
Activities conducted whilst on site included walking/jogging, dog walking, cycling, socialising, looking at wildlife, horse riding, golf, and Segway. Cyclists tended to use the ‘Through the Forest’ cycle route rather than other tracks. 75% of site users make use of other sites within the local area to conduct their chosen activities.
Comment: This is a meaningless statement in terms of trying to understand why people visit the impacted area. It implies that 75% of people can simply go elsewhere if they don’t like the impact of the quarry, which is an unsafe conclusion to draw.
23-33% of activity (depending on the survey method) is outside the typical operation hours of the proposed quarry, with weekends typically being busier than weekdays.
Comment: This implies that there will be no impact to visitor experience outside of the hours of operation, which is plainly false.
The majority (average of 60.5%) of site users who have a dog or dogs do not keep them on the lead for the duration of their activity.
Comment: A pointless statement. That said, it is recognised that if these dog walkers were to go to nearby designated heaths that would have huge impact, especially to nesting birds.
Respondents indicated that there are a wide range of reasons which might reduce the likelihood of them visiting the area, many of which will not be influenced by the proposals.
Comment: Here they are simply glossing over the real reasons why people would be less likely to visit the area and so have not provided any hard evidence or data to support their conclusion.
Mitigation measures will be included to reduce the likelihood of noise or dust reducing the attractiveness of the site to users. A detailed assessment on the potential for displacement has concluded that whilst localised displacement may occur, the off-site habitats north-west of the site within the SAC, SPA and RAMSAR are currently subject to a low level of use.
Comment: Why has this detailed assessment not been published? It is impossible to judge the accuracy of the conclusion without the data. This Finding is therefore simply an opinion.
The potential for displacement of site users to this area is considered less likely than displacement to other forest tracks within Moors Valley Country Park or Ringwood Forest SINC due to their condition, choice of routes and ease of access being more attractive to users.
Comment: This Finding is once again not supported by data. It is therefore a subjective opinion.
With regards to alternative sites, 27% of respondents indicated that they currently make use of Nature Reserves or SSSIs, 20% of which make use of the New Forest (i.e., 73 of 368 respondents).
Comment: The intention here appears to be to suggest that there are plenty of alternative sites for people to go to. However, they chose not to point out the personal financial cost and impact on the environment of people travelling further to access similar amenities such as in the New Forest. It is understood that the applicant was guided towards also using the Dorset designated heathlands for the impact assessment but chose instead to look solely at the impact on suggested more distant New Forest sites plus other unfamiliar sites included in Appendix 3 which seems a strange choice.
During operation of the proposed quarry, users will have open access to the majority of current tracks within the site, enabling continued choice which is considered of value to users. The restoration scheme will reinstate and/or increase the provision of tracks for mixed use and cycling, with improved measures to ensure the long-term protection of habitats and wildlife interests of the site.
Comment: This trivialises the impact by basically implying that everything will be OK again when the quarrying has ended, and the area restored. They failed to say how long a time period this will stretch over – it could be 60 years in some cases.
About the Survey Form . . .
3.2.1 The primary aim of the survey was to understand how local people use the local area recreationally, therefore the survey was timed to avoid the summer holidays when visitor numbers are at their highest.
Comment: Why would it be considered that only local people are impacted when we have first-hand knowledge that visitors to the adjacent Moors Valley Country Park (numbering hundreds of thousands per annum) also access the site location for cycling, exercise etc.? The implication that this is an area that is only ever used by a relatively small number of local people misrepresents the situation.
3.4.3 A local Facebook group ‘No 2 Purple Haze’ was encouraging local people to visit the site as much as possible throughout the duration of the CCTV surveys which may have influenced the frequency of visits to the area above the typical baseline.
Comment: This is a mischievous suggestion as any impact the Facebook group may have had is dwarfed by the impact of the Covid pandemic which is not referenced at all in the survey.
3.4.4 & 3.4.5 Comment: These sections, when taken together, are an admission that the CCTV exercise was mis-managed and is most likely to have led to incorrect numbers and time periods being captured.
4.2.4 Comment: Acknowledges that 70% of the people surveyed accessed the area via a vehicle, but there is no mention made about the problems that might arise for this group when car parking capacity along the Verwood to Ringwood road (B3081) is reduced.
5.1.2 & 5.1.3 Comment: These sections, when taken together, try to create the impression that the continued usage of the north-eastern and south-eastern car parks (which are not directly impacted by the development) will alleviate any parking issues. We have suggested under our analysis of the LEMMP that both of the alternative car parks mentioned must therefore be enlarged to compensate.
Comment: The section on behaviour of visitors appears to be irrelevant.
5.2.2 From Year 3, the proposals will require the temporary redirection of the ‘Through the Forest’ cycle route along Track F on the western boundary of the site. This will reduce the length of the 7.15km route by 430m (6%). This is not considered likely to reduce the attractiveness of the route to users. The route will be reinstated within the site with a more varied topography and an equal or greater length than currently present on site.
Comment: The survey does not set out for how long (from year 3) the cycle route will be impacted and when it will be restored. Clarification is required together with inclusion in any future survey.
5.2.4 The proposals will not change the accessibility of the site but will have a minor impact on the choice of routes available. Tracks A, B, E & F and the unnamed track on the north-western boundary of the site will remain open for access by site users throughout operation of the quarry. Tracks C and D which bisect the site will be closed during extraction of some areas and reinstated as part of the restoration process.
Comment: This, again, is very subjective and an expression of opinion rather than fact supported by data.
5.2.6 The woodland habitat will be reduced in extent, however, in the long-term, woodland will be reinstated along many of the tracks, keeping the feel of a wooded landscape, with woodland edge habitat increasing from 8.9km to 11.46km.
Comment: No time period is given, and this could therefore be misleading. What is ‘long term’ in years? The type of woodland will also change to species that are unsuitable for this location.
5.3.3 This demonstrates that around a quarter of activity at the time of the survey (when sunrise was at c. 06:45 and sunset was at 19:20) took place outside of the proposed operational hours of the quarry. Timing of activity is likely to vary seasonally.
Comment: This is misleading. It should state that 75% of activity takes place during the proposed hours of operation of the quarry. Making a positive point out of minority data is mischievous.
5.4.2 These behaviours are considered likely to be causing potential disturbance impacts to wildlife such as basking reptiles and ground nesting birds within the SINC and off-site SAC, SPA and RAMSAR. The proposals to include measures to limit public access to habitat enhancement areas and areas of the restored quarry is likely to be of benefit to wildlife within the site.
Comment: This is complete conjecture and again focuses on a small issue to try to justify incorrectly the claim that the development of a quarry will enhance the environment for wildlife. It’s simply wrong to state things this way.
5.5.1 25% of respondents to Q8 of the QS indicated that they did not visit other sites, reflecting the importance of the site to local people. However, around 160 alternative sites (some of which may be alternative names for the same site) are used by the remainder of respondents, with
choice of site influenced by a range of factors, such as alternative sites including woodland or forest (45%), heathland (29%), and beach or coastal sites (10%).
​
Comment: This is highly misleading. Most of the alternate sites are a long distance from Ringwood Forest. No mention is made of the negative impact on the environment if people have to travel further (by vehicle) to alternate sites. We have commented above on the misleading and wrongly selected choice of alternative sites offered by the survey.
Section 5.5.2 Comment: is written in such a way as to completely dismiss the concerns about the factors that would make visiting the area less attractive. It is considered biased in the extreme.
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6. Socio Economic & Health (Revised Environmental Statement Section)
Socio Economic
6.2 of the revised Environmental Statement states: The main socio-economic impacts that would be associated with the development proposals would be in respect of:
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Tax contribution;
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Employment (direct and indirect); and
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Supply of Sand and Gravel to the construction industry
Comment: As previously noted the tax receipts (estimated in section 6.4 of the revised Environmental statement to be in the region of 600K pa) will accrue to Hampshire not Dorset; however, the communities most impacted by this development lie within Dorset Council’s boundary.
As the financial benefits from the location of Purple Haze do not accrue to Dorset Council area residents, the applicant, together with Hampshire CC, should consider how best to deliver tangible community benefits for the nearby Dorset communities. Local residents have endured too many years of living near to Hampshire’s various mineral extraction and waste management operations. In doing so they have experienced all the cumulative effects of the inconvenience and daily problems arising which in any year can include any/all of the following -
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highly unpleasant odours lingering for days when the wind blows, or doesn’t, in the wrong direction,
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vermin in nearby gardens,
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the worry caused by landfill fires, especially when the weather is dry,
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seeing the abundant rubbish strewn along the B3081, some of which has been observed to fall from waste lorries,
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car damage to windscreens & bodywork caused by hard objects falling from quarry lorries, especially near to the Bakers Hanging turning,
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a poor quality road surface (B3081) causing pothole reporting to be considered almost a local sport with the winner being the resident who can first report the latest one,
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etc, etc, etc . . .
6.5. states: At a local level, mineral extraction provides benefits to the local economy through employment (both direct and indirect), generation and support of economic activity and provision of building products.
Comment: The materials extracted from this quarry are most likely to be used by HCC & BCP and all the planned & proposed building construction in the nearby Ringwood/Fordingbridge area, with little
direct benefit to Dorset. It is stated there will be just 7 full time roles at the site. This is not anticipated to generate much additional economic activity for local Verwood based businesses.
6.6. states: The proposed development will provide new employment with the creation of 7 full time jobs at the site. The revenue generated at the quarry will be returned directly into the local economy in staff wages and expenditure on the goods and services it requires. In addition, a substantial element of financial return to the community will arise through the payment of business rates to the local council.
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Comment: As above, 7 jobs will provide little stimulus to the local economy. We would expect the applicant to already have contracts in place for the support services it needs, so it is highly doubtful that much supplementary business will be generated for local (Verwood/Dorset based) businesses. As above, the business rates will be paid to Hampshire and not to Dorset – a fact the applicant should be aware of already.
6.7 states: Indirect employment will be provided through the use of local suppliers where possible for goods and services such as plant and vehicle maintenance and spares, fencing and ecologists at the proposed development. It is anticipated that this will create up to 12 jobs.
Comment: As above, we would expect the applicant to have some suppliers already on contract for vehicle maintenance etc. The speculative impact of a total of 19 jobs is unlikely to have much impact on the local community based in Verwood, especially when compared to the inconvenience, disruption, and long term damage to the local property market they could face.
Section 6.8 states: The proposed development will provide a local supply of high quality sand and gravel which is required to sustain the planned local economic development. The nearest local supply of sand and gravel has very limited remaining reserves. By not planning for the replenishment of these reserves there will be an increase in cost to local developers/builders, as the needed construction materials will have to be imported from farther afield.
Comment: Such vehicle movements are considered to be unsustainable and have the potential to increase road congestion and CO2 and NOx emissions. It is expected the majority of the material extracted is to be for use by HCC, BCP & NFDC and all the planned building in the Ringwood/Fordingbridge area, and for HCC planned local economic development. This will offer little, if anything, to Dorset.
Section 6.11 states: No significant adverse effects on local businesses are anticipated. A number of positive socio-economic effects would occur as a result of the proposed development. These positive effects will include the associated expenditure in wages and in payments to local suppliers, as well as the long term benefits associated with the improvements for tourism/recreation associated with restoration.
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Comment: The disruption to traffic flows whilst road improvements are made and after the site opens for trade may well impact Verwood based businesses negatively. As already stated, the amount of money related to wages (due to the limited number of jobs created) has not been quantified but is likely to be insignificant. Similarly, the spend with local suppliers is speculative but is not expected to be meaningful. As to long term benefits, these will take many years to be delivered and are unlikely to deliver benefit for many current Verwood based businesses.
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Health
Health Assessment Screening Document appended to the ES at Appendix 11
This states: As regards the impact on the health from Air quality, noise, light and water management
A range of technical assessments have been prepared and submitted as part of an Environmental
Statement. It is demonstrated that through the use of appropriate mitigation, the proposed development will not result in any significant adverse impacts in relation to air quality, noise, light and water management.
​
Comment: This remains to be seen, and why robust monitoring will be essential, as it is possible that irreparable harm will be done which is not immediately obvious. Any issues arising in the early stages of this development may persist or develop over a considerable period of time as the proposed site is anticipated to operate for 20 + years.
This document contradicts Section 6.6 of the Environmental statement which states that the project will deliver 7 full time roles. Inconsistencies in documentation are unacceptable and lead the reader to consider whether other errors have been made. This assessment has not been updated and is dated 2020. Despite being included within revised documents, it has not been revised.
Section 8.8 states: that in order to complete a Health Impact Assessment a baseline needs to be established.
​
Comment: It goes on to say that the HIA has consulted the latest available version of the Hampshire Health and Wellbeing Board – Joint Strategic Needs Assessment (JSNA). The JSNA looks at the current and future health and wellbeing needs and inequalities within the Hampshire population. This is a significant oversight requiring correction. Whilst the development may be within the borders of Hampshire the effect of the quarry will be felt, in the main, by residents in Dorset. We therefore strongly contest the use of Hampshire data as the baseline. All statistics provided as a baseline are therefore inappropriate.
Section 8.8 states: Should planning permission be granted, it is anticipated that both Mineral Planning Authorities would wish to impose Planning Conditions which will require the monitoring, mitigation, and environmental commitments to be implemented as proposed.
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Comment: We have assumed the applicant is referring to both Hampshire County Council & Dorset Council.
Site Management Measures
(I) Daily visual assessment of emissions to include the quarry processing plant; water sprays; conveyor; stockpiles; loading areas; haul road; wheel wash and entrance road/exit.
ii) General site inspection checklist to include inspections of conveyor; edge protection; site security and vehicle sheeting requirements.
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Comment: The outcome and results of these inspections will be provided to HCC. Clarification is required to demonstrate how the general public and Dorset Council will be advised whether the requirements are being met.
iii) Complaints Register: any complaints will be logged, investigated, actioned as appropriate and the complainant notified of the outcome, with a full written record retained
​
Comment: There are no details of the processes by which complaints will be handled, the time limits required for responses, escalation, etc. For the public to have confidence it should be entirely clear how complaints will be handled from start to finish, including what appeal process is available. Additionally, it’s unclear how out of hours concerns will be addressed – if via the widely recognised Environment Agency reporting route or another route, the applicant should say so.
Table 8.2 Noise
Section 8.2 (iii) states: Operations will occur as far away from potential receptors as practicable.
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Comment: Clarity is needed on what the receptors are – people, homes, roads, ecology? In reality, the work will take place in the phase being developed at the time, some of these are nearer to potential receptors, some further away. Moving the work as far away as possible will not be possible if a phase being worked on is closer to potential receptors.
Additionally, much of the language used around the mitigation of site issues is loose – “should”, “where practicable” etc. This does not give any level of assurance that all necessary measures will be taken to stop noise and dust issues. One interpretation, therefore, is that the applicant’s mitigation strategies will be implemented only where they deem it possible and when convenient to them. Clarification is required.
Section 8.19 states: 8.19 The table above outlines a wide range of attenuation measures and controls that will reduce emissions that might otherwise impact upon the health and well-being of nearby sensitive receptors. Subject to the grant of planning permission, it is anticipated that many of these measures will be controlled through the use of planning conditions, of which there will be routine compliance monitoring undertaken by each Mineral Planning Authority.
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Comment: As the MPAs have not been named above, we have assumed they are intended to be Hampshire County Council and Dorset Council.
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7. Noise & Dust
For all issues we had raised previously concerning site Noise and Dust management, there are numerous references within the applicant’s Regulation 25 Response to proposed operational practice, control measures and planning conditions which are offered as mitigation of the majority of those concerns.
Some of the mitigation measures proposed are, however, based on technical assessments which we are not, as an organisation, qualified with the necessary skills to challenge at a detailed level. For Noise, however, please see our detailed concerns set out in Section 6 above. For Dust, we remain of the opinion that automated monitoring is a necessity despite the suggested mitigation.
In both cases, however, it is essential that any resultant agreed processes for reporting Noise & Dust issues, whether covered by Planning Conditions or not, are clearly sign-posted to the general public from before commencement of ground works for creation of the Site Office through to confirmation that quarrying works have ended and the related site office has closed for day-to-day activities. It is also essential that the outcomes of the required monitoring of both Dust & Noise Management are also made readily accessible to the public.
END

Submission May 2021: Purple Haze: response to planning application NF272 site ref PLAN/NF272
Proposal: Extraction and processing of building sand together with incidental sand and gravel, ecological mitigation works, new access off the B3081 Verwood Road, processing plant, conveyor system, weighbridge, site office and welfare facilities, staff parking with progressive restoration to a mosaic of lowland heath, gorse scrub, woodland and pond areas
1. Introduction
Friends of Ringwood Forest (FoRF) is a local community action group managing the No 2 Purple Haze campaign. Our supporters are drawn from the Dorset town of Verwood (pop. 14,700+), its surrounding communities and regular visitors to Moors Valley Country Park which is adjacent to where the proposed site known as Purple Haze is located.
About the FoRF Objection
Our strong Objection to granting permission for planning application Ref: NF272 is submitted after our supporters were able to review and comment on the content.
We will demonstrate: -
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that the applicant has failed to meet Planning Policy requirements and Development Considerations* for the site known as Purple Haze as set out in Hampshire County Council’s Minerals & Waste Plan adopted in 2013
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that the applicant has failed to meet all Scoping Request requirements
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that the applicant has failed to provide either adequate or accurate data across all documentation submitted with the application
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that the applicant has failed to demonstrate adequate consideration of issues and suggestions following the two Community Involvement Events referred to within the application
*Note: For ease of reference, FoRF has numbered the Development Considerations for the Purple Haze site in the range PH01 > PH14 as shown in Appendix A to this document.
Our objection is based on examining the applicant’s submission regarding the following –
2. Transport - Traffic/Highways
2.1 Introduction
Referring to paragraph 4.81 of the applicant’s Planning Statement, we strongly disagree with the HMWP Inspector’s Report that: “the additional traffic generated was unlikely to have significant impact on the B3081 or the wider transport network”.
We note the Highways Authority’s response to the application but suggest it does not consider the experiences of those who live locally and who are only too aware of the problems which occur on this road.
We discuss below how local concerns, such as those regarding the proposed site access junction and other highway safety issues, have not been considered adequately by the applicant.
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2.2 Background
Verwood with a population of 14,700+ is the largest town in the North Dorset Parliamentary constituency and slightly less in population size than the nearby Hampshire town of Ringwood.
Verwood is a dormitory town with poor public transport links and few of the services, restaurants, shops, and amenities etc. available to Ringwood residents. Verwood trades and businesses trade in Ringwood. The reverse is true for Ringwood businesses. To access Ringwood’s amenities and business/trade links, Verwood residents and trades have to travel along the B3081, past where access to the Purple Haze site would be located.
Verwood residents who commute to work daily use the B3081 as the most direct and straightforward means of accessing the A31 and nearby larger towns. The B3081 is the road taken by residents attending hospital appointments, accessing railway stations and nearby airports, and going to college/university and to school.
For Verwood residents and businesses alike, the B3081 is a critical arterial road link with the wider area, often via the A31 heading east and west and via the A338 heading north and south.
Ringwood businesses and trades use the same arterial road to reach their Verwood clients. Ringwood residents, together with residents from other Hampshire locations, travel to Verwood using the B3081 to access Morrisons supermarket. It is certain that traffic to and through Verwood will increase once the Lidl supermarket, currently under construction, opens for business.
The section of the B3081 between the A31 and Verwood is considered by local residents to be poorly maintained. It is not considered a safe route for use by cyclists and pedestrians.
Alternative vehicular routes to access the A31 are available via the smaller B3072 road and travelling through the village of Three Legged Cross; however, due to hazards along this road, it is speed limited to 40mph throughout other than for a further reduction to 30mph through the village.
Being narrow and winding the B3072 route does not have the same capacity as the B3081. If there are accidents or incidents on the B3081, causing traffic to reroute through Three Legged Cross, this alternative route quickly becomes congested, causing gridlock and leaving Verwood essentially cut off for all except those prepared to take a long diversion, for example towards the Blandford – Salisbury road or a route via Wimborne. These longer diversions involve uncategorised roads, which are more dangerous.
Any forecast of increased volume of traffic on the B3081 will therefore cause significant concern to Verwood residents. Delivery of road “improvements” which would necessarily mean significant disruption are viewed with considerable misgivings.
In addition, HGV drivers use the B3081 route on diversion through Verwood in either direction when there are delays or incidents causing congestion on the A31/M27.
Conclusion. The applicant has failed to consider the proposed road improvements to widen the A31 at its junction with the A338 and related diversions, which will compound the issues unless the A31 works are completed in totality prior to development of the site.
Conclusion. The applicant has failed to also consider the seasonal variations of traffic along the A31 during summer months which exacerbate traffic issues on surrounding road networks leading to, amongst congestion problems, increases in pollution from idling HGVs.
Conclusion: The applicant has therefore failed to meet the requirements of Planning Policy 12 by not adequately considering the impact of:
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an increase in HGV traffic volume on the B3081, and
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the inevitable disruption from congestion and/or incidents, nearby major roadworks schemes, and
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the need to improve the nearby Baker’s Hanging junction
on the lives of Verwood residents, and other local communities such as Ringwood, where residents and businesses are entirely dependent on the road link that is provided by the B3081.
Recommendation: The applicant should be required to provide, as a minimum –
(i) an outline of the programme of work required for the development roadworks so that potential traffic upheaval may be better gauged than can be achieved with the limited data provided in the Transport Assessment Report, and
(ii) their proposals demonstrating how such disruption will be mitigated.
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2.3 Road Safety
2.3.1 About Baker’s Hanging
This section discusses the Traffic Assessment addendum to the Planning Statement which fails to consider the impact of serious incidents which occur at the accident black spot of the junction taking traffic to/from Alderholt from the B3081 known as Baker’s Hanging.
The applicant’s original request for police data scoped only the stretch of the B3081 on which the quarry access is proposed to be sited. The applicant was advised additional accidents had occurred just outside of this area. The applicant then fails to mention them, despite having requested the data related to the additional accidents which took place between the proposed site entrance and the A31. The applicant therefore states, inaccurately, that there were 6 accidents in the 5-year period examined when police records show there were 18.
The proximity of the Baker’s Hanging junction, to which the applicant makes no reference, to the proposed site entrance adds a serious road safety hazard to the site access proposals. It is extremely difficult for vehicles to exit the junction, particularly when attempting to turn right onto the B3081. The difficulty increases regularly when additional traffic has been diverted to/from the A338 and via Alderholt back to either the A31 or A338 near to Ringwood.
With the proposed increase in traffic, and particularly with additional slow-moving HGV traffic with cars bunched up behind, this part of the B3081 will become more difficult to travel through for all road users. It is considered that an increased number of accidents and fatalities will result.
Conclusion. The applicant has failed to meet the requirements of Plan Policy 12a by failing to mitigate the effects on highway safety by disregarding the accidents at the Baker’s Hanging junction.
2.3.2 About the “Ghost Islands”
Site access proposals include two staggered right turn “ghost islands” permitting traffic to enter the quarry site from the north and the Somerley HWRC from the south to avoid queuing traffic behind.
We consider this to be the worst junction choice from the options presented during the public engagement event held at The Hub, Verwood. The combination of two staggered right turn ghost islands will create a complicated and dangerous area with potentially four lanes of vehicles either proceeding or waiting to turn right. The section of the B3081 approaching and leaving the area around the entrances to the Purple Haze site and the HWRC would therefore become more perilous for all road users and for cyclists particularly.
It is also not clear how easy it will be for traffic, particularly slow-moving HGVs, exiting from the quarry to turn right to return to the south, nor for traffic exiting the household recycling centre to turn right to return north. In fact, despite the Road Safety Audit, it is the considered opinion of those who use this road regularly that the provision of these mid road junctions will make the road more dangerous and not less so.
2.3.2.1 Drainage
Paragraph 7.1.5 of the Traffic Assessment references a requirement for improved drainage works for the new road junction.
Conclusion. The applicant has failed to indicate where the contaminated water run-off will drain to and how it will be prevented from ultimately entering as diffuse pollution the mire system including Ebblake Bog SSSi (SAC, SPA, Ramsar).
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2.4 Cyclists
There are local cyclists who like, or who need to as their only means of transport, to cycle regularly along the B3081 towards Ringwood. They have no suitable alternative route except one that is longer via Moors Valley and the Castleman Trailway and which is considered suitable for mainly daylight use. Local cyclists report that using the B3081 is very unpleasant and that it feels dangerous being overtaken by HGVs at their current levels.
Given current road conditions, some residents have made the decision that the B3081 is currently too dangerous to cycle. They have stopped doing so and now drive a vehicle instead. This outcome is at variance with Government efforts in response to the Climate Emergency to reduce the volume of motorised vehicles using UK road networks.
Other residents have raised concerns that it would be too dangerous for cycling sporting events frequently held at Somerley Estate if these plans were to go ahead. We consider that increasing the number of HGVs on the B3081 will make it even more hazardous.
When there are roadworks to create the quarry site access, or there is an incident or seasonal congestion on the B3081, more road users, including cyclists, will be tempted to use the surrounding minor roads which are dangerous.
Conclusion. The applicant has failed to contribute to the vision offered by the HCC Cycling Strategy, see Page 6 at https://documents.hants.gov.uk/transport-strategy-documents/HampshireCyclingStrategy.pdf, as their plans will result in cyclists being driven away from using the B3081.
Conclusion. The applicant has failed to evidence adequate mitigation of the effects on road safety as required by Policy 12.
Conclusion. The applicant has failed to meet the requirements of Development Consideration PH13 which states there should be “safe and satisfactory access including alternatives to access off the B3081 to ensure provision for vulnerable highway users”.
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2.5 Traffic Management
The applicant has included in the Planning Statement an underestimation of 90 HGV movements per weekday. Our concern with the applicant’s estimate is based on a recent planning application extending operations of the Blue Haze landfill site to handle a further 770,000 tonnes of waste with a predicted increase from 34,000 two-way movements to 35,000 two-way movements per annum and equating to 126 HGV movements per day.
Verwood residents who have lived close to quarries elsewhere advise that despite the applicant stating they expect HGV visits to be flat profile, HGVs queue or park up in readiness for site access, often in the mornings and at other times during the day causing congestion and disruption.
Conclusion. The applicant has failed to provide adequate data supporting their estimate of 90 HGV movements per weekday and should therefore be required to: -
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provide detailed evidence to substantiate their estimate, and
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identify the variables, and
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identify proposed mitigation for the variables, individually and in combination.
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2.6 Traffic Through Verwood
The applicant has not provided sufficient evidence to:
(i) support the claim that 90% of the expected traffic will arrive from the A31 and 10% through Verwood, and
(ii) to evidence their consideration of other local factors affecting traffic travelling through Verwood as follows below.
The B3081 within Verwood is called Ringwood Road: it is residential and extremely busy for pedestrians to cross. The figure of 9 HGV movements per day is a significant additional amount of HGV traffic through Verwood.
Conclusion. The applicant has failed to state and consider the tolerance level in terms of capacity, road, and pedestrian safety, and has failed to consider the overall impact if the estimate of 9 HGV movements per day proves to be inaccurate.
We consider, however, that the estimate of 9 HGV movements per day may be inaccurate because there is a housebuilding plan and expansion of local amenities currently underway in Verwood, leading to more residents using the B3081 and a current increase in HGVs, and other trade vehicles, travelling into Verwood to serve the building sites etc.
Conclusion. The applicant has failed to evidence consideration of all the factors set out above.
Conclusion. The applicant has also failed to consider the cumulative effects of HGV traffic already using the B3081 to access the Veolia landfill site, especially in the future when Blue Haze closes in 2031 until which time waste laden HGV movements are likely to increase, and then moves into a significant restoration phase with, potentially, an as yet unknown volume of associated HGV movements or to also access the Somerley HWRC.
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2.7 Damage to Vehicles/Highway
Conclusion. The applicant has failed to show how the risk of any spillages on the highway, occurring after loaded vehicles have exited the site, will be mitigated.
Recommendation. The applicant should be required to provide a legally binding undertaking regarding the measures which will be taken, by themselves or others, to contribute to reducing the vehicle damage currently caused by the poor maintenance of the B3081 road surface between the A31 and Verwood and/or how the applicant will operate to mitigate the frequent damage caused to windscreens and vehicle bodywork by stones flying off quarry/gravel lorries already using the B3081 and/or the Baker’s Hanging junction.
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2.8 Traffic Conclusion Summary
(i) The applicant has failed to meet the requirements of Policy 12 to ensure that the development mitigates adverse effects on highway and pedestrian safety, highway capacity and the environment.
(ii) The applicant has failed to meet the requirements of Policy 10 that the development should not cause an unacceptable cumulative impact arising from other mineral and waste sites.
(iii) The applicant has failed to meet the requirements of Development Consideration PH14 which mandates the consideration of traffic issues including cumulative impact with other mineral workings and the protection of Verwood from mineral traffic.
3. Noise
3.1 Equipment Operating at Site
The Noise report states, “in summary, for normal daytime site operations the noise limit at residential properties should be no greater than 10 dB above the existing background level with an upper limit of 55 dB LAeq,1h. For Temporary operations, the noise limit at residential properties should be no greater than 70dB LAeq,1h.”
The Noise report states that noise sources within the extraction areas will include an excavator, dump truck and conveyor.
The noise sources within the plant area include processing plant for the excavated material, a loading shovel and HGVs. There are two processing plants running in parallel at the site: one for dry screened sand and the other for washed sand. The loading shovel will move the material and load the HGVs at the plant site. There are to be up to 90 HGV movements per day (around 8 vehicles per hour).
However, the Dust report mentions additional equipment as follows: "sand screeners, a hydrocyclone and dewatering screen*, plus fixed and mobile dust extraction and suppression equipment.”
* which may be the two processing plants mentioned in the previous paragraph.
Conclusion. The applicant has failed to demonstrate that noise sources likely to operate within the site, and their related noise level estimates, have been identified in totality for the purposes of the Noise report.
Recommendation. The Noise report as presented for examination should be withdrawn.
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3.2 Total Noise Levels
The report states that temporary operations, which can take place for a period of 8 weeks a year are permitted to generate higher noise levels (70 dB). Temporary operations include works to restore earlier worked phases.
Whilst it is not clear from the Noise report whether these temporary operations and normal operations will occur at the same time, it is clear from the Planning Statement, Section 3.18 that restoration works, and normal excavation operations will occur at the same time. It states "While sand is extracted from phase 2, phase 1 will undergo levelling to the restoration profile and restoring using soils and overburden stripped from phase 3. Following restoration, the area will be planted and seeded as required to meet the restoration after use”.
This clearly indicates that as works move from phase to phase, restoration and excavation will occur concurrently.
Further reading seems to indicate that this concurrence of activity has not been considered as the Noise report states "These noise levels have been calculated for extraction activity at the nearest phase to each noise sensitive receptor and at the maximum working height. The calculated noise levels also include simultaneous processing of material at the plant site. As such, these calculated levels are considered to be a reasonable worst case. The activity assumptions for normal daytime operations are presented in Appendix F."
This seems to suggest that the noise generated by extraction and processing occurring concurrently has been considered but the noise generated by temporary operations (levelling and restoring) occurring simultaneously has not been considered when calculating the maximum noise levels. This level of ambiguity is unacceptable.
Conclusion. The applicant has failed to demonstrate that the overall level of noise to be generated during periods when normal activity and temporary operations are occurring concurrently has been accurately assessed.
Recommendation. The Noise report as presented for examination should be withdrawn.
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3.3 Impact on users of Moors Valley
The noise impact on users of Moors Valley is dismissed as being negligible because the paths and routes within the country park are transient areas and people do not stay in the area for extended periods of time.
If people have come to the park for a quiet walk and find their tranquillity disturbed by the works, this might prevent repeat visits and ultimately damage the business of the country park; alternatively, they may choose to visit the nearby sensitive Heathlands instead.
Conclusion. The applicant fails to mention the impact on horse riders who use this area as a safe route to travel between Verwood and Ringwood. It appears that the British Horse Society has not been consulted and so we have provided them with information about the planning application.
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3.4 Plant Site
The plant site will be built 3 metres below ground and will be the first area to be built, there will be no bunds to dampen sound whilst this building is going on.
Conclusion. The applicant has failed to include mitigation for noise levels from this initial phase of development, nor for the noise created by the road alterations, although they could be significant.
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3.5 Afforestation
Mention is made that the forest will provide a degree of screening. The forest is managed.
The proposed restoration of the site will lead to replanting of young trees and some different species, it is not clear what impact this will have on noise levels. Most of those proposed are deciduous so will only offer any degree of screening when mature and when in full leaf, i.e., for about 6 months a year.
Conclusion. The applicant has failed to identify what additional sound mitigation will be provided if trees which had been providing screening are removed and noise levels rise to unacceptable levels.
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3.6 Mitigation, Monitoring and Management
The Noise report contains an extract from the Planning Practice Guidance Minerals (PPMG) which states that those making mineral development proposals should, amongst other things:
identify proposals to minimise, mitigate or remove noise emissions at source;
monitor the resulting noise to check compliance with any proposed or imposed conditions.
The only mitigation apparent in the report is embedded mitigation, which consists of the soil bunds as follows:
Embedded Mitigation
The proposed phasing plans show that bunding is to be incorporated in the scheme formed from topsoil and overburden excavated from the site. The bunds are between 1.5m and 3m in height.
Topsoil and overburden from the plant site area, phase 1 and phase 2 will be used for a 2m high bund along the NE and SE sides of the plant site area and a 3m high bund along the SE side of the plant area.
As phases are worked, the topsoil and overburden from each will be used for form 1.5m tall bunds around the outside edges of the active phases.
The acoustic screening attenuation provided by the bunds is included in the site noise calculations and assessment. No additional mitigation is offered in the Noise report and nothing additional appears in the conclusions. There is no apparent commitment in the Noise report to ongoing monitoring of noise levels.
The Environmental Statement section 8 Table 8.2 makes a series of recommended best practices regarding noise but does not commit to regular monitoring or advise any additional mitigation.
We note the response from Environmental Protection at New Forest District Council but suggest the lack of any apparent commitment to ongoing noise monitoring will make it impossible for the applicant to demonstrate compliance with the target levels as described in government guidance.
As there is no operational plan we do not know if the applicant will provide ongoing noise monitoring at the receptors used to create the calculations set out in this report. If there is no ongoing monitoring, how will we know that the limits are not being exceeded?
Conclusion. The applicant has failed to demonstrate proposals to monitor noise to ensure that the noise limits set out in this report are not breached.
Conclusion. The applicant has failed to demonstrate proposals to monitor noise to provide evidence that it is compliant with any planning conditions imposed by the local authority.
Recommendation. The applicant should be required by a planning condition to provide adequate and regular noise monitoring.
4. Dust
4.1 Silica
Sand quarries generate silica dust (Respirable Crystalline Silica - RCS) yet silica is not mentioned specifically in the Dust report nor in the Environmental Statement. This is concerning because silica is identified by the UK government as a hazardous material. Its particles are so small it is invisible but if inhaled can lodge in the lungs and cause serious lung disease.
The report concludes that monitoring of dust using passive or real-time units is not recommended at this stage but goes on to say that dust emissions should be routinely monitored by visual means. Silica is invisible, the lack of passive monitoring means that dangerous dust may well be missed.
Conclusion. The applicant has not provided data regarding what percentage of the possible dust emissions will be silica. It is therefore not possible to determine whether adequate processes and procedures, including dust monitoring by other than visual means, should be in place to protect nearby community members, including recreational users of the area, from this material.
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4.2 Dust Management Plan
The Dust report contains a dust management plan which identifies potential strategies to minimise hazards from dust. However, as there is no Operational plan there is no guarantee that any of these mitigations will be implemented.
The environmental statement includes attenuation measures, however whilst it is implied these will be implemented and will be controlled through planning conditions, there is no guarantee that these measures will indeed be implemented. This leaves a considerable degree of uncertainty that protection measures will be adequate.
Conclusion. On examination of the relevant application report content alone, because HCC has yet to state what planning condition(s) will be applied to Dust Management, it is not possible to determine whether adequate measures will be in place to protect nearby community members.
4.3 Water Use
Much of the mitigation proposed in the dust management plan is linked to use of water, to dampen down etc. It is not clear how much water will be used, how the proposed water well will be operated and what impact this may have on local supplies, drought orders, etc.
Conclusion. The applicant should be required to provide the missing information concerning water use on site.
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4.4 Weather
The report states that “As an overriding requirement, during dry windy weather, i.e. ‘red’ conditions as defined in Table 4.1, if any operations are identified as causing or likely to cause visible emissions across the site boundaries and towards sensitive receptors, or if abnormal emissions are observed within the site, the Site Manager should immediately modify, reduce or suspend those operations until either effective remedial actions can be taken or the weather conditions giving rise to the emissions have moderated.”
The above is a recommendation only and relies on visible emissions. It not clear, because there is no operational plan, that this type of action will be taken when the site is operating. It is also not clear what warnings will be given to local residents and users of Moors Valley Country Park in the event that emergency actions are required and how these will be transmitted.
Conclusion. The applicant should be required to state how red condition warnings will be notified and to whom.
5. Socio-Economic & Health
This report, by referring to Hampshire Socio-Economic & Health data alone, is considered irrelevant to the application, demonstrating a lack of care concerning identification of impact on the local community in Dorset near to Purple Haze and which the applicant has failed to recognise for the purposes of this report and elsewhere in their application.
The landowner and operator are not Dorset based, therefore no financial or tangible benefit, and long-term profit investment, is likely to accrue within Dorset where the greater and expanding population of people will reside who are affected directly by developing the Purple Haze site - except for access, if proposed restoration plans are accepted, to water bodies surrounded by gorse thicket proposed to the south of the site plus information boards to be located around the site. This is an omission which should be rectified.
Conclusion. The applicant should be required, via a planning condition, that when considering their employment and local supplier needs, they commit to giving priority to nearby Dorset residents and businesses.
Conclusion. The applicant has failed to indicate to Dorset communities and businesses a willingness to provide adequate Community Benefits or improvements to Community Amenity in compensation for the upheaval and disruption likely to be experienced over the 25+ years the site will operate and an unknown period beyond during ongoing restoration.
Recommendation. This report should be withdrawn as it does not reflect that while the site is physically located in Hampshire, the consequent impact of its development will affect, primarily, nearby Dorset community members.
6. Hydrology
It will be recalled that we submitted considerable detailed evidence about Hydrology concerns in relation to the Purple Haze site during previous proceedings to adopt the HCC Minerals & Waste Plan in 2013 and the related Examinations in Public including, in particular, our comprehensive response to the Main Modifications & DCLG Guidance Consultation. We were opposed to HCC adopting the site due to the significant and unresolved concerns as touched on in the Planning Inspector’s final report and which were discussed with HCC Officers at the time.
After a detailed examination of the planning application for Purple Haze together with the supporting reports which reference Hydrology, no reasons to proceed have emerged which negate our previous significant concerns and so our position is unchanged. We remain convinced the site should not be developed.
In order to avoid repetition of the content of other responses to the current consultation, we wish instead to attach our strong affirmation to the arguments for refusing planning permission when considering the site’s hydrology/hydrogeology as presented by other respondents and those of the Environment Agency and EDEP in particular.
Conclusion. In summary, we object to planning permission being granted on the grounds that the applicant has not provided sufficient detail of the location and movement of water into, within, under and away from the site as it is now and how that would change, nor have they demonstrated that development of Purple Haze would avoid harm to the nearby areas of important biodiversity interest and particularly Ebblake Bog SSSI (SAC, SPA, Ramsar) and its catchment.
7. Archaeology
The Cultural Heritage Assessment Report recommends that it should be a requirement of the planning consent that a thorough mitigation strategy should be instigated to ensure the preservation by record of the probable barrow and other archaeological sites within the development area. This mitigation strategy covers the full excavation of the probable barrow and establishes a plan to ensure that there is an ongoing programme of observation and investigation throughout the life of the project. This entails a review of each area before soil stripping commences, throughout the life of the project. This mitigation is endorsed by Hampshire County Councils Senior Archaeologist.
The Planning Statement acknowledges the requirement for mitigation prior to the excavation of the probable barrow and states that a detailed Written Scheme of Investigation would be submitted to Hampshire County Council before development commenced and would be subject to a planning condition requiring its implementation. It only makes a passing reference to the need for ongoing monitoring, stating that a "watching brief" will be held over the remainder of the site. Both the Planning Statement and the Environmental Statement contain a comment as follows: It is concluded that this balanced approach should be a consideration in the decision-making process.
Recommendation. The wording in both the Planning Statement and the Environmental Statement seems weak compared to the detail set out in the Cultural Heritage Assessment and as endorsed by the Senior Archaeologist. We would like to see a firm commitment from the applicant that they will follow the mitigation as set out in the Cultural Heritage Assessment, throughout the life of the project and would like confirmation from Hampshire County Council that this will be enforced through planning conditions.
8. Community Benefit & Amenity
8.1 Post Restoration Access
The applicant has proposed a three stage “clear, extract, restore” approach to extract minerals on a strip-by-strip basis. Should the restoration plan for any worked strip be accepted to include the provision of replacement habitat, public access is likely to be denied to that strip for at least 30 years to prevent replacement habitat disturbance.
It is therefore considered unlikely that public access to the majority of the Purple Haze site will be regained for many years and plans to, for example, divert cycle tracks and marked trails could fail where restoration plans involve habitats for sensitive species such as the sand lizard population present on site.
Recommendation. The applicant should be required to demonstrate how and when public access will be restored for each strip as extraction progresses, to show how any replacement habitats for sensitive species will be protected from disturbance and to demonstrate how this will affect the diversion of current amenities such as cycle tracks and marked trails.
8.2 Information Boards
It is proposed that information boards will be provided at suitable locations around the site. While their provision would be welcomed, the applicant should be aware there is a history of local anti-social behaviour involving the defacement and unauthorised removal of such boards.
Recommendation. The applicant should be required to work with Moors Valley Country Park to design, install and maintain the information boards accordingly.
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8.3 Permitted Parking on B3081 to access Moors Valley Country Park
Parking and access tracks from the B3081 are provided by Forestry England to facilitate local informal recreation. These parking areas, along with those on other roads bordering Moors Valley Country Park and the park’s main car park, are often full during weekends, over Bank and school holidays. If the parking capacity along the B3081 is reduced for any reason, the recreational users affected may migrate to nearby Heathlands.
Conclusion. The applicant has failed to state the mitigation measures which will replace permitted parking when tracks from the B3081 into Moors Valley are closed to the general public for any length of time due to site operations.
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8.4 Tracks, Informal Paths & HGVs: Making Good
When planned harvesting of trees takes place within Ringwood Forest, HGVs use existing gravel tracks and also cross informal pathways which become unsuitable for recreational access until they have been made good.
It is considered that when preparations for site operations get under way beyond the site’s boundary, recreational users are likely to experience similar unsuitable track and pathway conditions so preventing permitted access.
Conclusion. The applicant has failed to state how long each of the tracks and pathways used by HGVs during site set up would be inaccessible, when the impact of such HGV disturbance on each will be made good and to what standard to meet the requirements of both users and biodiversity.
9. Community Involvement & Engagement
Timing of the Application Consultation
We appreciate that the timing of any planning application consultation is dictated by rules and regulations rather than by simple custom and practice. This consultation is no different, except that it is taking place during the Covid-19 pandemic. It is a time of national social unsettlement when local community members have other priority concerns.
Recommendation. When the time comes for a decision to be made on whether planning permission will be granted or refused, we would ask that it be noted that any lack of direct public response to the consultation is considered to be due more to current social circumstances than to any decline in public concern about the effect of the site’s development on an environment that is highly valued, locally cherished and considered worth protecting from harm.
10. Accessibility of Application Content
10.1 Empowering Inclusion
We accept that while the applicant is responsible for submitting the plans, text and data required to support their application, authorship of individual report content has often been the responsibility of more than one organisation as evidenced by both style and content.
The perception of accessibility by the general public to the wealth of information provided to support this application has therefore varied between “way too technical for me to read” (creating exclusion) to “that was easy to understand” (empowering inclusion). Specific examples of the variance in accessibility can be provided if requested.
Recommendation. We doubt that the overall approach to the authoring of individual application reports is going to change. However, it would be helpful if the applicant were reminded to consider, before signing off their content for submission, that the intended audience includes lay people who may or may not have the same degree of technical understanding enjoyed by those consultees routinely working or volunteering in roles related directly to the application.
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10.2 Cross Sections & 3D Modelling
The application includes a number of 2D graphics using contour lines to demonstrate how the site landscape changes over time. Feedback to FoRF indicates that these have caused frustration for a number of people who have had difficulty in visualising how contour lines “work”.
During both public engagement events, we advised the applicant that 3D modelling would be a helpful aid to understanding the proposed landscape changes given that Purple Haze cannot be described as either a regularly or flatly contoured site.
We also note that, in response to the Scoping Opinion consultation, Dorset Council advised that cross-sections should be provided and, in their application response, EDEP has reiterated the need for before and after cross-sections of worked strips demonstrating the landscape changes.
Conclusion. The applicant has failed to meet Scoping requirements with regard to providing cross sections and should be required to provide them before the application can be further considered.
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Appendix A Purple Haze: Development Considerations
PH01 Protection of the Dorset Heathland Special Area of Conservation (SAC), Special Protection Area (SPA) and Ramsar site, the Avon Valley SPA and Ramsar site and the River Avon SAC*.
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PH02 The impact on the offsite foraging and breeding areas of the qualifying bird species of nearby SPA/Ramsar*.
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PH03 The impact on Ringwood Forest and Home Wood Site of Importance for Nature Conservation.
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PH04 Protection and enhancement of the amenity and users of the Moors Valley Country Park and other local residents.
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PH05 Maintenance and management of levels of permissive access and recreational use of the Moors Valley Country Park via the B3081*.
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PH06 Protection of the nearby cycle paths and footpaths.
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PH07 Management arrangements to secure short and long term objectives for amenity and biodiversity.
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PH08 Phasing programme and working to protect the amenity of local residents and permissive access to the site.
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PH09 The impact on the Bronze Age burial mound and its preservation.
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PH10 Protection of the amenity of Verwood residents, other residents in the vicinity and local businesses.
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PH11 Exclusion from extraction and buffer of the northern end of the site to protect the amenity of local residents*.
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PH12 Protection of the water quality and recharge of the underlying aquifer, groundwater and surface water and safeguard the hydrological regime of Ebblake Bog Site of Special Scientific Interest*.
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PH13 Safe and satisfactory access including alternatives to access off the B3801 to ensure provision for vulnerable highway users and the impact on peak flows is managed.
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PH14 Traffic issues including cumulative impact with other mineral workings and the protection of Verwood from minerals traffic.
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END 2021 Submission