Pollution and Local Amenity Impacts

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Comment

Preferred Options consultation document

Representation ID: 98736

Received: 30/10/2019

Respondent: Environment Agency

Representation Summary:

We agree with the inclusion of paragraph 8.12 that lighting levels should be assessed with consideration given to the impact lighting will have on European Protected species. Mitigation could include limiting the operational hours of the site and using down lighting.

Full text:

Preferred Options Plan
Thank you for the opportunity to comment on the Preferred Options stage of the Norfolk Minerals and Waste Local Plan. We have commented on the policies and allocated sites in the same format as the Local Plan itself below.

The Process so far
We are pleased to see water resources are mentioned in this section. However, this section could be strengthened by making reference to whether working beneath the water table is required and whether dewatering is required. This could potentially pose a challenge to sites moving forward so it should have a stronger mention in this section.

Policy MW2: Development Management Criteria
We are pleased to see that point k in this policy makes reference to the natural and geological environment. This point could be enhanced by also making reference to the hydrogeological environment including maintaining groundwater dependent wetlands, surface water flows, groundwater quantity and flow regime.

The policy makes no reference to local air quality regarding waste developments, be it from gas utilisation units or fugitive emissions from landfilled areas and their perimeter. This is especially key where development is close to sensitive receptors or such receptors are developed close to the sites.

We welcome the inclusion of point D in the policy. This could be enhanced to state
"flood risk TO THOSE WORKING on site or an increase in flood risk elsewhere" (addition in CAPITALS ). The policy could also be improved by requiring a Flood Response Plan to manage the safety of the people on site.

Pollution and Local Amenity Impacts
We agree with the inclusion of paragraph 8.12 that lighting levels should be assessed with consideration given to the impact lighting will have on European Protected species. Mitigation could include limiting the operational hours of the site and using down lighting.

We fully support the protection of Local Wildlife sites (county wildlife sites, local nature reserves and local wildlife sites) highlighted in paragraph 8.20 as well as priority habitats and species. We agree that any proposal should only be permitted where it can be demonstrated that the activities will not significantly harm the site, and will require submission of appropriate ecological surveys, carried out by an appropriately qualified ecologist, at the correct time of year as described in paragraph 8.21. We recommend the rewording of the final sentence of paragraph 8.20 to state "Development that may affect Water Framework Directive waterbodies e.g. rivers, streams, lakes will require a WFD compliance assessment".

Water Framework Directive
The plan should make reference to the fact that any development that could impact the status of a water body, whether WFD or not, should be subject to a WFD assessment.

Flooding, Water resources and water quality
We agree with the reference this section makes to flood risk betterment after restoration, reducing flood risk elsewhere and acknowledgement that climate change needs to be considered. However this section does not refer to ensuring there is no increase in flood risk elsewhere through the duration of the works. In addition there is no mention of the flood risk to people on site and the need for management to ensure their safety with a Flood Response Plan. The plan should therefore be updated to this effect.


It is encouraging to see that paragraph 8.40 makes it clear that dewatering for mineral abstraction purposes requires a water abstraction licence from the Environment Agency. However, it should be noted that an abstraction licence for dewatering may not be granted and it is likely that any de-watering water will need to be returned to the aquifer close to where it is abstracted and in a timely manner after the abstraction takes place. Our current Catchment Area Management Strategy (CAMS) policy for issuing abstraction licences intervening use of this water for activities such as mineral washing and dust suppression which have a consumptive element will not be permitted, this be a challenge for sites going forward if alternative sources of water for associated activities such as mineral washing and dust suppression cannot be found.

Paragraph 8.40 refers to the Water Framework directive. A WFD assessment is a good addition and we welcome the suggestion to protect the designated drinking water source protection zones. We also support the use of pollution prevention measures, to prevent pollution of surface and groundwater. This paragraph should also state that the assessment should determine if there could be a deterioration in WFD status. Activities should not allow any deterioration in any of the WFD elements. Minerals and waste management developments should not cause deterioration or prevent a water body from achieving Good Ecological Status/Potential, and whenever possible, help to implement environmental improvement measures to improve waterbodies.

Policy MW4: Climate Change mitigation and adaptation
Paragraph 10.2 states the need to minimise demands on potable water resources. The sentence should continue by saying 'and water resources in general'. As stated above, we are not issuing new consumptive abstraction licences.

A possible linkage could be made between point's b and c - on site renewable energy (both electricity and hot water) could well be provided from captured landfill gas emissions. Any excess energy could then be fed into the local networks.
It would be beneficial to update the wording of point 3 to state "...including rising sea levels, LARGER RIVER FLOWS, and coastal erosion..." (addition in CAPITALS).

Waste Management Specific Policies
In terms of paragraph W0.3, you should ensure that you plan for sites that will 'Prepare for Re-use' as it has been stated that greater weight is being put to the management methodology at the top of the waste hierarchy.

W1.12
The plan states "The latest Defra estimate of C&I waste growth for England is 0.6% per annum, therefore an alternative option would be to forecast C&I waste growth over the Plan period at 0.6% per annum instead of 1.5% per annum. However, it is considered that it is more appropriate to use the Norfolk specific figure of 12.5% per annum". We are unsure where and how this figure of 12.5% has been calculated and why it is so different to DEFRA's estimate. Sustainable economic growth will need enough commercial and industrial waste processing capacity to deal with this increase in waste generation.

Policy WP2: Spatial Strategy for Waste Management Facilities
We support the policy WP2 regarding the location of Water Recycling Centres. It should be noted that the decision, ultimately, remains with Anglian Water Services.

Policy WP3: Land potentially suitable for waste management facilities
This policy should state that waste management facilities (aggregate recycling) also need to consider consumptive water use and where this water will come from.

Policy WP6: Transfer, Storage, Processing and treatment of hazardous waste
It is highly likely that any proposals for the discharge of hazardous waste to surface water or groundwater will require a discharge permit, if allowed. The policy could be improved by saying that under no circumstances, should there be a discharge of treated hazardous waste/materiel to surface waters or groundwater without prior consultation with the EA.

Policy WP9: Anaerobic Digestion
The policy could be improved by making reference to Emergency Planning. Proposals for Anaerobic Digestion (AD) facilities should include a detailed emergency plan should there be an incident, such as a major leak or fire for example. AD leachate is extremely rich in nutrients, which if entering a watercourse, could cause significant environmental harm. We suggest the emergency pan includes nearby watercourses, overlying geology, depth to water table, detailed site drainage plan for example. If possible, an emergency plan should be provided for the Environment Agency to review.

W12: Non-hazardous and hazardous waste landfill
Along with section 5.35, we question whether allowing planning permission for Blackborough End to become an inert landfill and reducing the county's non-hazardous landfill waste capacity to just 1.53 million cubic metres is sufficient for residual waste disposal over the plan period. It is unclear from the Local Plan what the options for residual waste disposal will actually be, except reliance on Refuse Derived Fuel (RDF) and its export. Bearing in mind NCC are keen for sustainable waste management, then the export of RDF by definition its potential energy, does not appear the best long term option. Although waste management options higher up the waste hierarchy are always preferable, there will always be waste streams that can only be disposed in landfill.

Policy WP13: Landfill Mining and Reclamation
Please note that such a proposal will require detailed input and agreement from the Environment Agency.

Policy WP15: Whitlingham Water Recycling Centre
We have previously provided comments stating that we welcomed that the WRC has a long term policy to ensure that further capacity is provided in line with growth. We continue to support long term plans being developed for Whittingham and other WRCs.
W15.2 mentions the sites location is close to the Broads and the associated 'landscape and flood risk concerns'. The location also means there are concerns for water quality due to the close proximity of sensitive protected sites of conservation importance. A statement to acknowledge that water quality needs to be protected should therefore be added to the plan here or in this policy.

Policy MP2: Spatial Strategy for mineral extraction
Point e makes reference to the hydrological catchment around Roydon Common SSSI and Dersingham Bog SSSI. It should be ensured that it is mentioned that it is the hydrological and hydrogeological catchment around Roydon Common and Dersingham bog which should be avoided.
We support the policy to provide a 250m buffer around ancient woodland and designated sites.

Policy MP5: Core River Valleys
This policy should also include "the impact of mineral development on groundwater and the potential to need to work beneath the water table".
Any proposal for quarrying activity within a core river valley should not be approved unless the applicant can demonstrate no adverse effect on the WFD status of the river water body, or its tributaries. A Full WFD assessment (as outlined above) will be required for any proposal for this activity to be carried out within a floodplain.

Policy MP7: Progressive working, restoration and after-use
We are fully supportive of supporting paragraph 7.3 which states there may be suitable ark sites to protect wild-clawed crayfish. Such sites need to be identified well in advance of de-commissioning to that the site can remain bio-secure.
The first bullet point in policy MP7 refers to BAP habitat. Please note that this has been superseded by Priority Habitat (S41 NERC Act, 2006).

Policy MP12: Conventional and unconventional oil and gas development
Unconventional oil and gas production requires a lot of water to be used so it is likely an abstraction licence will be required. In addition, much of this water ends up as wastewater so the appropriate storage, treatment and disposal methods will be required. Discharge to any surface waters or groundwater will likely require a discharge permit and an application will need to be submitted. Having said this, the local plan indicates it is highly unlikely there will be hydrocarbon exploration in Norfolk in the foreseeable future so these comments may not be necessary at this point in time.

Policy MP13: Areas of search for silica sand extraction
As stated in our previous response, policy MP13 needs to address the need for an FRA. An FRA is vital if any of the allocations are located in Flood Zones.
Site Allocations

MIN38: Land at Waveney Forest, Fritton
Following our previous comments, we are welcome the conclusions drawn in this document which state the allocation is unsuitable for allocation.

MIN200: Land West of Cuckoo Land, Carbrooke
The site allocation text mentions that the site will be worked dry above the water table several times. If this is the case then this would alleviate our concerns on impacts on Scoulton Mere SSSI. This however is not included within the policy on page 124 and must be included.

MIN40: Land East of Grandcourt Farm, East Winch
We have concerns regarding this site. In the existing site, permeant dewatering of Carstone is proposed in restoration which goes against our previously raised comments. We would recommend not allocating this site.
Any depth of extraction should be severely limited to minimise de-watering. This could impact of the amount of mineral which can be recovered. As this is a principal aquifer, any de-watering water would need to be returned to the aquifer from which it is taken. An appropriate hydrogeological impact assessment will be required and it may well be that de-watering is not considered suitable at this site, which could limit the amount of mineral that could be recovered.

MIN35: Land at Heath Road, Quidenham
Our comments that we gave to the 2018 consultation remain valid.We have no concerns as it is proposed to work above the water table. This may need to be a planning condition on any application submitted.

MIN102: Land at North Farm, Snetterton
This site is adjacent to Swangey Fen SSSI. We previously stated that we do not consider the site suitable for mineral extraction. We are therefore supportive of the conclusions drawn in this consultation document stating that it is considered unsuitable for allocation

MIN201: Land at North Farm, Snetterton
This site is adjacent to Swangey Fen SSSI. We previously stated that we do not consider the site suitable for mineral extraction. We are therefore supportive of the conclusions drawn in this consultation document stating that it is considered unsuitable for allocation.

MIN6: Land off East Winch Road, Middleton
We are pleased to see that the specific site allocation policy for MIN 6 states the need to work above the water table. However, a hydrogeological impact assessment (not impact assessment) would be required to establish the depth of working.

Min204: Land off Lodge Road, Feltwell
Our previous comments raised within the issues and options stage of the consultation remain valid.

MIN74: Land at Turf Field, Watlington Road, Tottenhill
We agree with the conclusion that this site is unsuitable to be carried forward. If the site were to be taken forward, we would want to see a suitable hydrogeological impact assessment.

MIN76: Land at West Field, Watlington Road, Tottebhill
We are already aware of the planning application that has been submitted in terms of this application and have no further comments to make.

MIN77: Land at Runns Wood, South of Whin Common, Tottenhill
We agree with the conclusion that this site is unsuitable to be carried forward. If the site were to be taken forward, we would want to see a suitable hydrogeological impact assessment.

MIN206: Land at Oak Field, west of Lynn Road, Tottenhill
We consider this site suitable for sands and gravel extraction. The need for a hydrogeological impact assessment must be included within a bullet point in the specific site allocation policy. It's likely that de-watering will be required here.

MIN32: Land west of Lime Kiln Road, West Dereham
We agree with the conclusion that the site is unsuitable to be carried forward. We would want to see a suitable hydrogeological impact assessment if the site was carried forward and, as it is sands and gravels overlying chalk bedrock, it is possible that de-watering would not be considered a suitable option.

Area of search for AOE E
Given previous issues we have had with silica sand extraction in the vicinity of this site, we would expect all extraction to be above the watertable. This is likely to limit the amount of resource that can be recovered. It should be noted that the silica sand is part of a principal aquifer.


SIL01, AOS F, AOS I and AOSJ
The starting position should be not to allow de-watering as outlined in our comments to site allocation MIN40.

Silica Sand search locations
If de-watering is not to occur at the silica sand search locations as mentioned in our response above, this can heavily impact on the amount of resource available.

We trust this advice is useful.

Comment

Preferred Options consultation document

Representation ID: 98877

Received: 30/10/2019

Respondent: West Winch parish council

Representation Summary:

Para 8.9 there should be no impact on human health - densely populated area King's Lynn and proposed massive development at South East King's Lynn (SEKL).

Full text:

Fracking
Unnatural disturbance of the Earth's geological structure and plates is caused by fracking. Unknown effects could be disastrous and harmful for communities. It is irresponsible and dangerous for the current and future population. Fracking will contribute to climate change so goes against all policies to lessen effects of unnatural 'actions', eruptions and earth tremors.
Fracking already taking place in the Country has caused several tremors, causing fear, alarm and distress to residents. This is a material effect on human health and well-being.

Incineration
West Norfolk is responsible for more than a quarter of the County's emissions
(Lynn News page 12 - 9 August 2019.)

To allow, or even think of putting incineration into policies, is blatantly going against democracy of the last King's Lynn & West Norfolk Borough Poll where 65,000 people voted against incineration and NCC wasted millions of pounds on an abandoned project. Efforts should be put into alternative methods of waste reduction and disposal, or re-use schemes.

Questions asked by Norfolk County Councillor, Alexandra Kemp to NCC Cabinet.
Following £34 million lost from Council's budget, with the cancellation of the infamous South Lynn incinerator contract for Planning Failure in 2014, Council agreed a No-Incineration-in-Norfolk Policy, ("Appendix M").

West Norfolk is alarmed by the criteria-based Draft Waste Plan, which fails to state our No-Incineration Policy, instead permissively lists forms of incineration ( page 56), endangers West Winch Growth Area by permitting prospecting for fracking ( page 90), erroneously ignoring prospecting always causes earthquakes.

Can Cabinet amend the Plan to state " in West Norfolk, where 65,000 people voted against incineration in the Borough Poll, applications for incinerators will not be permitted"; and exclude fracking and prospecting for fracking?

West Winch Parish Council agrees with the County Councillor, Alexandra Kemp.

We do not need these policies which can cause more problems with emissions and climate change.

Policy WS07 Huge risks to human health and well-being and Air Quality page 17, para 5.18.

Page 26 Presumption in favour of sustainable development is likely to breach 7.1 (b) Communities health....
'Presumption in favour ...' should be removed.

Policy MW2 Development Management Criteria
'Unacceptable impact on (a) to (m).

Page 28 Pollution and Local Amenity Impacts
Para 8.9 there should be no impact on human health - densely populated area King's Lynn and proposed massive development at South East King's Lynn (SEKL).
Para 8.20 mentions Ancient Woodland - This must also apply to historical Grazing Commons, especially in West Winch and North Runcton.

Historical Environment
Para 8.28 - King's Lynn has ancient historical buildings. Harmful emissions and fracking would affect these valued buildings which attract visitors and tourists, contributing major finance to the area's economy.

West Winch and North Runcton have protected sites of local value -
Reference - page 20, West Winch and North Runcton Neighbourhood Plan (Planning material consideration)
Plus, 2 sites of Special Scientific Interest, and
3 County Wildlife Sites, including West Winch Common.

Page 32 - Land and Soil Resources
Para 8.31 Agricultural Land, which should include Grazing Common Land, must all be protected from contamination to protect our food chain for the future of the whole Country.

Page 34 Cumulative Impacts
It is imperative that cumulative impacts are taken into account as too often measurements are only taken close to the proposed development. Cumulative measurements impact on human health.

Page 46 '.... Not considered necessary to allocate any waste management sites in the Plan' - which means these sites can be developed anywhere on industrial sites etc and they could be near to densely populated areas.
This should be scrutinised more closely and incineration must be deleted.

Page 46 Policy WP1 Hazardous -----
Norfolk County Council needs to keep tight control over hazardous waste received from other Waste Planning Authorities.

Page 48 Policy WP2 Distance
Distance of waste facilities needs to be considerably increased to safe levels for human health away from populated areas.

Comment

Preferred Options consultation document

Representation ID: 98953

Received: 15/10/2019

Respondent: Broads Authority

Representation Summary:

* 8.12 - request there is some text, perhaps as a footnote, that refers to the identified dark skies of the Broads and refers to our maps and policy.
* 8.16 says 'Directing lighting downwards and away from properties' but taking this literally, this contradicts - implying angling the light away from properties which could cause light pollution. I think you are saying design any lighting so it points downwards and ensure that there is no light trespass for example into neighbouring properties. You might want to consider that wording and you might want to look at our policy on light pollution. The key point is - do you really need lighting, if so why? Keep it to a minimum, use it when needed and point it down and have it fully shielded - I suggest you get those points across strongly in the policy.

Full text:

* 1.5 - one specific site[s] for carstone extraction
* 1.14 - tpa - presume that is tonnes per annum - not used consistently in this para
* Page 12 - SA section - bullet point list does not mention landscape impact or biodiversity
* 5.16 The area known as the [Breaks] Brecks
* Where is MW1? The first policy is MW2.
* MW2 - The first part is written in quite a different way to other policies I have read; rather than saying that impacts of development will be minimised on the criteria, or schemes will address the criteria, you ask for information only. I am not sure how strong this approach is. b) what about the quantity of surface water (as in what to do with it in relation to flooding) and the quality of water bodies? E) what agriculture land class do you consider this to be - Grade 1 and 2 perhaps - might need to say that. What about if the soil that is to be excavated or disturbed is peat soils? Peat soils have many special qualities, such as are a carbon sink but a carbon source if allowed to dry out. We recommend that you consider protecting Peat Soils - you can look at our Peat Soils policy for ideas. i) what are 'outdoor recreation facilities' and do you need to include Local Green Space as well as Open Space?
* 8.12 - request there is some text, perhaps as a footnote, that refers to the identified dark skies of the Broads and refers to our maps and policy.
* 8.16 says 'Directing lighting downwards and away from properties' but taking this literally, this contradicts - implying angling the light away from properties which could cause light pollution. I think you are saying design any lighting so it points downwards and ensure that there is no light trespass for example into neighbouring properties. You might want to consider that wording and you might want to look at our policy on light pollution. The key point is - do you really need lighting, if so why? Keep it to a minimum, use it when needed and point it down and have it fully shielded - I suggest you get those points across strongly in the policy.
* 8.24 first bullet point - weave in wording that refers to the setting of the landscapes.
* 8.31 and section 12 - I see you refer to soil grades 1, 2 and 3a. As a bit of advice from our experience, do you know where 3a is? There is limited mapping relating to 3a. You might want to consider removing this or just saying '3'. Happy to chat this through. Should the soil grade be mentioned in the policy? Note what is said on page 73, I - that 3a and 3b are not mapped.
* 8.32, 12.2 - temporary yes, but for a number of years. Suggest that text is clarified. See above regarding if the soil is peat soils and its care.
* 8.35 - is it worth asking applicants to state how they have considered water and rail and road and thoroughly justify their chosen mode, rather than just encourage it?
* MW3, last bullet point - is that a travel plan? MW4 refers to travel plans.
* MW4 - is it better to just say 'greenhouse gas emissions'? Does using the term 'endeavour' reduce the strength of criterion c? d) just demonstrate or implement too?
* 12.4 says 'Given their nature, most waste management facilities will tend to be suitably located on previously developed land and industrial locations and it is not expected that there will be a great need to locate such uses on agricultural land' - not sure what this is saying - they tend to be located there or are suitable to be located there?
* Map 3 - see above comments - where are areas of 3a?
* Section 12 - no mention of peat soils and their qualities - see above.
* Page 41 onwards and then 64 onwards - formatting - should this have a section number - perhaps section 13? The bullet points are numbered differently to elsewhere in the Plan - WO rather than, say, 13.2 etc.
* WP4 - a) when compared to another option that takes longer?
* W7.1 - do you mean 2018?
* WP13 - so a, b, c are 'or' and d, e, f are 'and'. It might be easier to separate them out and say something like 'in all cases d, e, f will apply'.
* WP15 - first para seems reasoned justification rather than policy text. Suggest the Broad Authority be involved in the organisations listed in para 3 - the organisations in para 4 seem to be the ones that need to be involved in the Masterplan.
* WP17 and MP11 - on adoption, presume we will be sent these GIS layers to upload to our system?
* Page 71, and MP2 - that NPPF paragraph applies to the Broads too. We have a Major Development policy. Why is the AONB excluded and the Broads not? Or is it?
* Page 73, g - why not the undesignated heritage assets?
* MP2.14 - 'Developers wanting to [extraction] extract mineral from specific sites or land within an area of search allocated in the Minerals and Waste Local Plan Review will still need to apply for and be granted planning permission before mineral extraction can take place'.
* MP2 - why the 3mile/5 mile rule for minerals?
* MP4.1 and MP4 - how about if the reservoir is not associated with mineral abstraction?
* Page 76 - what is shown on this map? There is no key. If it is core river valleys, why are the rivers over in the Broads not blue?
* MP6 might make sense but the first part says acceptable, unacceptable and acceptable. A check might be needed.
* MP8.3 'The need for annual reports after the initial five-year period [for] will be assessed on a case by case basis'.
* M65.5 - starts off saying 'The site is not located within...'. Being within is one issue, but affecting the setting of is another. So such assessments should state whether the site is near to those designations. This should therefore correctly read that the site is near to the Broads.
* Page 181 onwards - Min 38 - Waveney Forest, Fritton - support not allocating this site.
* Min 65, Stanninghall Quarry - extension to existing minerals site. No landscape visual or character concerns with regards to the Broads itself.
* Min 25, we would definitely want to be consulted on any forthcoming planning applications on this site, particularly concerning landscape scheme and restoration as the landscape character areas in this locality are well defined and susceptible to change.
* Min 211, Restoration as wet grassland for biodiversity needs to be balanced with long-term effects on local landscape character. The local character and experience of the landscape varies between the north and south of the site and restoration should reflect this.
* Generally, an LVIA assesses the effects of a development (the impact) on the landscape as a resource and the effects on visual receptors. The assessment will cover both the site itself and a wider study area determined by desk study and ground-truthing. LVIA's should be carried out to a set standard (Guidelines for landscape and visual impact assessment, 3d edition - which I believe is part of the NCC validation checklist) so by definition will be required to include the site and any surrounding area that could be affected by the development; Existing: "Submission of a Landscape and Visual Impact Assessment which will identify any potential impacts to the wider landscape and suggest appropriate mitigation measures ..." Proposed: "Submission of a Landscape and Visual Impact Assessment which will identify any potential effects and suggest appropriate mitigation measures ..." This text is used across a number of the policies.

SA Part A Scoping
Page 31 needs a very big update.
* Core Strategy, DM and Sites not in place any more.
* Local Plan adopted May 2019.
* Flood Risk SPD - most recent is 2017
* Broads Plan is 2017
Seems relevant to refer to our dark skies data and policy

SA - Part B
4.5 - did you consider a zone from the Broads?


Please note: The Broads Authority has adopted a new Local Plan which can be found here. The policies in the Core Strategy, Development Management and Site Specific documents are all superseded and not in place anymore.

Comment

Preferred Options consultation document

Representation ID: 99024

Received: 30/10/2019

Respondent: Borough Council of King's Lynn and West Norfolk

Representation Summary:

Environmental Quality and Community Safety and Neighbourhood Nuisance Comments on Mineral Site Specific Allocations

Summary:
If sites have to be progressed to the planning application stage, we would hope that sites furthest from residential dwellings are looked at primarily, as this could ensure that the impact on residential health and amenity is negligible. Clearly these sites would be preferred by us, if needed at all.
Submitted noise assessments and air quality/dust assessments should consider and include mitigation measures to deal appropriately with any potential health impacts, such as operational practices, separation/standoff areas and screening and/or bunding in line with Development Management Policies DM12 and DM13.
These allocated sites have been reviewed in line with Development Management Policies DM12, DM13, and DM15 as detailed within Norfolk Minerals and Waste Development Framework.

Lighting:
Lighting is not included in the document as this is generally something which can be considered at any proposed planning application stage; however we would hope that any proposed lighting for site security and worker safety would be carefully considered prior to the planning stage so details can be submitted with any planning application. We would assume lighting would be pole mounted in elevated positions, and therefore the throw and spread of this should be assessed to ensure that there is no impact on residents. Light should be contained within the confines of sites and positioned appropriately. If necessary lighting is located near dwellings, this should be angled away and hooded/cowled to prevent any adverse impact on residents.

Vibrations:
The potential impact from vibrations should also be considered at any future planning stage, if sites are chosen close to residential receptors - including vibrations from site operations and associated transportation of extracted materials.

Soil Stripping:
Soil stripping operations must be effectively controlled through mitigation methods (e.g. buffer zones and bunding) to reduce fugitive emissions, which pose short term health impacts on nearby residents. These mitigation measures must be included in any future planning application.

Haul Roads:
Fugitive emissions from haul roads need to be addressed in any future planning application, with mitigation planned where necessary such as wheel washing.

Full text:


Environmental Quality and Community Safety and Neighbourhood Nuisance Comments on Mineral Site Specific Allocations October 2019

Summary:
If sites have to be progressed to the planning application stage, we would hope that sites furthest from residential dwellings are looked at primarily, as this could ensure that the impact on residential health and amenity is negligible. Clearly these sites would be preferred by us, if needed at all.
Submitted noise assessments and air quality/dust assessments should consider and include mitigation measures to deal appropriately with any potential health impacts, such as operational practices, separation/standoff areas and screening and/or bunding in line with Development Management Policies DM12 and DM13.
These allocated sites have been reviewed in line with Development Management Policies DM12, DM13, and DM15 as detailed within Norfolk Minerals and Waste Development Framework.

Lighting:
Lighting is not included in the document as this is generally something which can be considered at any proposed planning application stage; however we would hope that any proposed lighting for site security and worker safety would be carefully considered prior to the planning stage so details can be submitted with any planning application. We would assume lighting would be pole mounted in elevated positions, and therefore the throw and spread of this should be assessed to ensure that there is no impact on residents. Light should be contained within the confines of sites and positioned appropriately. If necessary lighting is located near dwellings, this should be angled away and hooded/cowled to prevent any adverse impact on residents.

Vibrations:
The potential impact from vibrations should also be considered at any future planning stage, if sites are chosen close to residential receptors - including vibrations from site operations and associated transportation of extracted materials.

Soil Stripping:
Soil stripping operations must be effectively controlled through mitigation methods (e.g. buffer zones and bunding) to reduce fugitive emissions, which pose short term health impacts on nearby residents. These mitigation measures must be included in any future planning application.

Haul Roads:
Fugitive emissions from haul roads need to be addressed in any future planning application, with mitigation planned where necessary such as wheel washing.

[see attached table for comments on individual sites]

Environmental Quality and Community Safety and Neighbourhood Nuisance Comments on Waste Site Specific Allocations October 2019

Summary:
If sites have to be progressed to the planning application stage, we would hope that sites furthest from residential dwellings are looked at primarily, as this could ensure that the impact on residential health and amenity is negligible. Clearly these sites would be preferred by us, if needed at all.
Any future applications for waste sites should be accompanied by noise, odour, dust, and air quality management schemes, which should identify potential sources and mitigation/control measures to prevent nuisance issues and health impacts (e.g. emissions from as gas flaring).
Where sites are likely to be illuminated for safety/security, lighting plans and details should also be submitted which should include where lights will be located, their heights and angle/orientation, the type of lighting and the throw and spill of light across the site, and measures to ensure light spill is contained within site boundaries.
These allocated sites have been reviewed in line with Development Management Policies DM12, DM13, and DM15 as detailed within Norfolk Minerals and Waste Development Framework

Existing Waste Site Specific Allocation Policies:
We note that WAS 05, WAS 25, WAS 36, WAS 40, WAS 37, WAS 45 and WAS 65 are no longer required and would therefore be deleted. There is therefore no risk to residential amenity from these sites.

Odour:
An odour impact assessment should be included within any future planning applications for allocated waste sites, along with suitable mitigation measures where appropriate.

Climate Change:
Climate change mitigation should be considered with regards to methane emissions (a greenhouse gas) released from allocated landfill sites.

[see attached table for comments on individual sites]

Comment

Preferred Options consultation document

Representation ID: 99025

Received: 30/10/2019

Respondent: Borough Council of King's Lynn and West Norfolk

Representation Summary:

Environmental Quality and Community Safety and Neighbourhood
Nuisance Comments on Waste Site Specific Allocations

Summary:
If sites have to be progressed to the planning application stage, we would hope that sites furthest from residential dwellings are looked at primarily, as this could ensure that the impact on residential health and amenity is negligible. Clearly these sites would be preferred by us, if needed at all.
Any future applications for waste sites should be accompanied by noise, odour, dust, and air quality management schemes, which should identify potential sources and mitigation/control measures to prevent nuisance issues and health impacts (e.g. emissions from as gas flaring).
Where sites are likely to be illuminated for safety/security, lighting plans and details should also be submitted which should include where lights will be located, their heights and angle/orientation, the type of lighting and the throw and spill of light across the site, and measures to ensure light spill is contained within site boundaries.
These allocated sites have been reviewed in line with Development Management Policies DM12, DM13, and DM15 as detailed within Norfolk Minerals and Waste Development Framework

Odour:
An odour impact assessment should be included within any future planning applications for allocated waste sites, along with suitable mitigation measures where appropriate.

Climate Change:
Climate change mitigation should be considered with regards to methane emissions (a greenhouse gas) released from allocated landfill sites.

Full text:


Environmental Quality and Community Safety and Neighbourhood Nuisance Comments on Mineral Site Specific Allocations October 2019

Summary:
If sites have to be progressed to the planning application stage, we would hope that sites furthest from residential dwellings are looked at primarily, as this could ensure that the impact on residential health and amenity is negligible. Clearly these sites would be preferred by us, if needed at all.
Submitted noise assessments and air quality/dust assessments should consider and include mitigation measures to deal appropriately with any potential health impacts, such as operational practices, separation/standoff areas and screening and/or bunding in line with Development Management Policies DM12 and DM13.
These allocated sites have been reviewed in line with Development Management Policies DM12, DM13, and DM15 as detailed within Norfolk Minerals and Waste Development Framework.

Lighting:
Lighting is not included in the document as this is generally something which can be considered at any proposed planning application stage; however we would hope that any proposed lighting for site security and worker safety would be carefully considered prior to the planning stage so details can be submitted with any planning application. We would assume lighting would be pole mounted in elevated positions, and therefore the throw and spread of this should be assessed to ensure that there is no impact on residents. Light should be contained within the confines of sites and positioned appropriately. If necessary lighting is located near dwellings, this should be angled away and hooded/cowled to prevent any adverse impact on residents.

Vibrations:
The potential impact from vibrations should also be considered at any future planning stage, if sites are chosen close to residential receptors - including vibrations from site operations and associated transportation of extracted materials.

Soil Stripping:
Soil stripping operations must be effectively controlled through mitigation methods (e.g. buffer zones and bunding) to reduce fugitive emissions, which pose short term health impacts on nearby residents. These mitigation measures must be included in any future planning application.

Haul Roads:
Fugitive emissions from haul roads need to be addressed in any future planning application, with mitigation planned where necessary such as wheel washing.

[see attached table for comments on individual sites]

Environmental Quality and Community Safety and Neighbourhood Nuisance Comments on Waste Site Specific Allocations October 2019

Summary:
If sites have to be progressed to the planning application stage, we would hope that sites furthest from residential dwellings are looked at primarily, as this could ensure that the impact on residential health and amenity is negligible. Clearly these sites would be preferred by us, if needed at all.
Any future applications for waste sites should be accompanied by noise, odour, dust, and air quality management schemes, which should identify potential sources and mitigation/control measures to prevent nuisance issues and health impacts (e.g. emissions from as gas flaring).
Where sites are likely to be illuminated for safety/security, lighting plans and details should also be submitted which should include where lights will be located, their heights and angle/orientation, the type of lighting and the throw and spill of light across the site, and measures to ensure light spill is contained within site boundaries.
These allocated sites have been reviewed in line with Development Management Policies DM12, DM13, and DM15 as detailed within Norfolk Minerals and Waste Development Framework

Existing Waste Site Specific Allocation Policies:
We note that WAS 05, WAS 25, WAS 36, WAS 40, WAS 37, WAS 45 and WAS 65 are no longer required and would therefore be deleted. There is therefore no risk to residential amenity from these sites.

Odour:
An odour impact assessment should be included within any future planning applications for allocated waste sites, along with suitable mitigation measures where appropriate.

Climate Change:
Climate change mitigation should be considered with regards to methane emissions (a greenhouse gas) released from allocated landfill sites.

[see attached table for comments on individual sites]