Preferred Options consultation document

Original response received 30.10 2019
Revised response received 18.12.2019

3. Implications for the Borough from sand and gravel and silica sand policies / areas
3.1 Tottenhill (Site 206 - West of Lynn Road) This is an extension of existing works. The Tottenhill sites would be worked sequentially to mitigate any cumulative impacts. Potentially acceptable subject to the requirements in the policy.

3.2 A site at East Winch (Site MIN06 Mill Drove, Middleton) is allocated for carstone extraction. Potentially acceptable subject to the requirements in the policy.

3.3 Silica sand - AoS's (E, F, J and I) and SIL01. The County Council concludes that Site SIL01 is suitable to allocate for silica sand extraction. Development will be subject to compliance with the relevant Minerals and Waste Local Plan Policies and Specific Site Allocation Policy SIL01. There are reasonable safeguards for the locality.

3.4 The AoS are the same as previously expressed in the Initial Consultation document. Silica sand is a nationally important industrial mineral, and as such, the County Council must make adequate provision for its extraction. However they are not able to find suitable sites for the quantity of sand required, especially having dropped a site at Shouldham / Marham. The AoS are large and the expectation is that a suitable location could be found within one of the areas. Without detailed further information or operator preferences, it is not possible to pinpoint a site and therefore assess the localised impacts. Whilst this may be unsatisfactory for local communities who fear the consequences of extraction, it does give a positive indication that the County Council is safeguarding land and narrowing down suitable sites. It would be unrealistic to seek to have no areas of search at all, and the Plan could be found 'unsound', which would not be of benefit to the area.

Policy MP13 Silica Sand Area of Search (AoS E - Shouldham Warren area) and Policy MP2 - Spatial Strategy for mineral extraction (including reference to Silica Sand Areas of Search, and buffer zones (clause e))
3.5 Policy MP13 provides a criterion based approach to potential development in Areas of Search, including Area E. The expectation is that various assessments about related impacts will be provided in support of any applications, covering matters such as archaeology, landscape etc. Heavy reliance is placed on the safeguards from supporting studies to achieve acceptable development.
The recent decision by Norfolk County Council (in respect of it's Environmental Policy - County Council 25 November) to support the planting of some 1 million trees over the next 5 years to mitigate for the effects of climate change suggests a significant policy shift in the important role that trees play in County Council operations. It is clear that much more attention needs to be given the retention of existing tree cover in any mineral extraction situation. Shouldham Warren is an extensive area of tree cover, with additional recreation opportunities. An elevated status needs to be given to this in the planning balance as to whether an Area of Search should be designated at Shouldham, the Borough Council view is that the County Council should remove the AoS for this reason.
Additionally, Policy MP2 provides a degree of protection for areas with defined characteristics. Clause a. refers to 'ancient' woodland. In view of the County Council decision referred to above, it would be appropriate to delete the word 'ancient', leaving an enhanced level of protection to woodland generally.
Conclusion on AoS E (Shouldham) - Taking into account the two proposed amendments to policies affecting the potential for extraction at Shouldham, and the significant additional constraints now evident, the AoS should be removed.
MP2 Clause e) - Whilst the hydrological catchment around Roydon Common and Dersingham Bog, is specifically mentioned in Policy MP2e for exclusion, the complex hydrology and geology of these extremely sensitive sites is not fully understood. These two habitats have been recognised through the Ramsar, SAC and SSSI designations as having protected status. The introduction of wider 1.5km buffer zones would better mitigate any risk.

3.6 Policy MP7 (relating to restoration and aftercare) suggests that preference will be given to enhancing biodiversity, green infrastructure, and high quality local landscapes. This approach is supported. Whilst not necessarily appropriate in all circumstances, tree planting on restored sites would be a useful additional boost to mitigate for climate change. It is proposed that an additional clause is added to this effect as a fifth bullet point in paragraph four to the policy.

4. Implications for the Borough from the NCC approach to proposed waste and other policies on 'energy minerals'.

4.1 NCC have reviewed the policies in the current plans and as with Minerals moved them on to an end date of 2036. One particular item is relevant to West Norfolk. This is the overall locational strategy for waste management facilities.
4.2 Main points:
* From Policy WP2 in the Preferred Options it would seem possible to locate waste management facilities away from the broad location that generated the waste. Thus necessitating potentially significant transport movements, and possibly generating resentment from recipient communities.
* Whilst not necessarily inappropriate for all types of waste where specialist facilities are needed, extremely careful thought should be given to general waste or significant quantities requiring movement.
* A better approach would seem to be one where the policy encouraged waste to be dealt with as near to the generating source as possible.
* It is suggested our original comments are still appropriate to make.
4.3 Incineration - For the avoidance of doubt, it would be helpful if the County Council could add text to explain the position whereby the County Council will not seek to procure incinerators within Norfolk.
The position of the Borough Council on incineration is clear from previous involvement in planning inquiries. A clear statement on the matter from the County Council in the Minerals and Waste Local Plan would avoid any uncertainty for residents.

4.4 Fracking - Reference could be made to latest Government announcements about the potential restrictions / banning on this subject.

Original response received 30.10 2019
Revised response received 18.12.2019

3. Implications for the Borough from sand and gravel and silica sand policies / areas
3.1 Tottenhill (Site 206 - West of Lynn Road) This is an extension of existing works. The Tottenhill sites would be worked sequentially to mitigate any cumulative impacts. Potentially acceptable subject to the requirements in the policy.

3.2 A site at East Winch (Site MIN06 Mill Drove, Middleton) is allocated for carstone extraction. Potentially acceptable subject to the requirements in the policy.

3.3 Silica sand - AoS's (E, F, J and I) and SIL01. The County Council concludes that Site SIL01 is suitable to allocate for silica sand extraction. Development will be subject to compliance with the relevant Minerals and Waste Local Plan Policies and Specific Site Allocation Policy SIL01. There are reasonable safeguards for the locality.

3.4 The AoS are the same as previously expressed in the Initial Consultation document. Silica sand is a nationally important industrial mineral, and as such, the County Council must make adequate provision for its extraction. However they are not able to find suitable sites for the quantity of sand required, especially having dropped a site at Shouldham / Marham. The AoS are large and the expectation is that a suitable location could be found within one of the areas. Without detailed further information or operator preferences, it is not possible to pinpoint a site and therefore assess the localised impacts. Whilst this may be unsatisfactory for local communities who fear the consequences of extraction, it does give a positive indication that the County Council is safeguarding land and narrowing down suitable sites. It would be unrealistic to seek to have no areas of search at all, and the Plan could be found 'unsound', which would not be of benefit to the area.

Policy MP13 Silica Sand Area of Search (AoS E - Shouldham Warren area) and Policy MP2 - Spatial Strategy for mineral extraction (including reference to Silica Sand Areas of Search, and buffer zones (clause e))
3.5 Policy MP13 provides a criterion based approach to potential development in Areas of Search, including Area E. The expectation is that various assessments about related impacts will be provided in support of any applications, covering matters such as archaeology, landscape etc. Heavy reliance is placed on the safeguards from supporting studies to achieve acceptable development.
The recent decision by Norfolk County Council (in respect of it's Environmental Policy - County Council 25 November) to support the planting of some 1 million trees over the next 5 years to mitigate for the effects of climate change suggests a significant policy shift in the important role that trees play in County Council operations. It is clear that much more attention needs to be given the retention of existing tree cover in any mineral extraction situation. Shouldham Warren is an extensive area of tree cover, with additional recreation opportunities. An elevated status needs to be given to this in the planning balance as to whether an Area of Search should be designated at Shouldham, the Borough Council view is that the County Council should remove the AoS for this reason.
Additionally, Policy MP2 provides a degree of protection for areas with defined characteristics. Clause a. refers to 'ancient' woodland. In view of the County Council decision referred to above, it would be appropriate to delete the word 'ancient', leaving an enhanced level of protection to woodland generally.
Conclusion on AoS E (Shouldham) - Taking into account the two proposed amendments to policies affecting the potential for extraction at Shouldham, and the significant additional constraints now evident, the AoS should be removed.
MP2 Clause e) - Whilst the hydrological catchment around Roydon Common and Dersingham Bog, is specifically mentioned in Policy MP2e for exclusion, the complex hydrology and geology of these extremely sensitive sites is not fully understood. These two habitats have been recognised through the Ramsar, SAC and SSSI designations as having protected status. The introduction of wider 1.5km buffer zones would better mitigate any risk.

3.6 Policy MP7 (relating to restoration and aftercare) suggests that preference will be given to enhancing biodiversity, green infrastructure, and high quality local landscapes. This approach is supported. Whilst not necessarily appropriate in all circumstances, tree planting on restored sites would be a useful additional boost to mitigate for climate change. It is proposed that an additional clause is added to this effect as a fifth bullet point in paragraph four to the policy.

4. Implications for the Borough from the NCC approach to proposed waste and other policies on 'energy minerals'.

4.1 NCC have reviewed the policies in the current plans and as with Minerals moved them on to an end date of 2036. One particular item is relevant to West Norfolk. This is the overall locational strategy for waste management facilities.
4.2 Main points:
* From Policy WP2 in the Preferred Options it would seem possible to locate waste management facilities away from the broad location that generated the waste. Thus necessitating potentially significant transport movements, and possibly generating resentment from recipient communities.
* Whilst not necessarily inappropriate for all types of waste where specialist facilities are needed, extremely careful thought should be given to general waste or significant quantities requiring movement.
* A better approach would seem to be one where the policy encouraged waste to be dealt with as near to the generating source as possible.
* It is suggested our original comments are still appropriate to make.
4.3 Incineration - For the avoidance of doubt, it would be helpful if the County Council could add text to explain the position whereby the County Council will not seek to procure incinerators within Norfolk.
The position of the Borough Council on incineration is clear from previous involvement in planning inquiries. A clear statement on the matter from the County Council in the Minerals and Waste Local Plan would avoid any uncertainty for residents.

4.4 Fracking - Reference could be made to latest Government announcements about the potential restrictions / banning on this subject.

Original response received 30.10 2019
Revised response received 18.12.2019

3. Implications for the Borough from sand and gravel and silica sand policies / areas
3.1 Tottenhill (Site 206 - West of Lynn Road) This is an extension of existing works. The Tottenhill sites would be worked sequentially to mitigate any cumulative impacts. Potentially acceptable subject to the requirements in the policy.

3.2 A site at East Winch (Site MIN06 Mill Drove, Middleton) is allocated for carstone extraction. Potentially acceptable subject to the requirements in the policy.

3.3 Silica sand - AoS's (E, F, J and I) and SIL01. The County Council concludes that Site SIL01 is suitable to allocate for silica sand extraction. Development will be subject to compliance with the relevant Minerals and Waste Local Plan Policies and Specific Site Allocation Policy SIL01. There are reasonable safeguards for the locality.

3.4 The AoS are the same as previously expressed in the Initial Consultation document. Silica sand is a nationally important industrial mineral, and as such, the County Council must make adequate provision for its extraction. However they are not able to find suitable sites for the quantity of sand required, especially having dropped a site at Shouldham / Marham. The AoS are large and the expectation is that a suitable location could be found within one of the areas. Without detailed further information or operator preferences, it is not possible to pinpoint a site and therefore assess the localised impacts. Whilst this may be unsatisfactory for local communities who fear the consequences of extraction, it does give a positive indication that the County Council is safeguarding land and narrowing down suitable sites. It would be unrealistic to seek to have no areas of search at all, and the Plan could be found 'unsound', which would not be of benefit to the area.

Policy MP13 Silica Sand Area of Search (AoS E - Shouldham Warren area) and Policy MP2 - Spatial Strategy for mineral extraction (including reference to Silica Sand Areas of Search, and buffer zones (clause e))
3.5 Policy MP13 provides a criterion based approach to potential development in Areas of Search, including Area E. The expectation is that various assessments about related impacts will be provided in support of any applications, covering matters such as archaeology, landscape etc. Heavy reliance is placed on the safeguards from supporting studies to achieve acceptable development.
The recent decision by Norfolk County Council (in respect of it's Environmental Policy - County Council 25 November) to support the planting of some 1 million trees over the next 5 years to mitigate for the effects of climate change suggests a significant policy shift in the important role that trees play in County Council operations. It is clear that much more attention needs to be given the retention of existing tree cover in any mineral extraction situation. Shouldham Warren is an extensive area of tree cover, with additional recreation opportunities. An elevated status needs to be given to this in the planning balance as to whether an Area of Search should be designated at Shouldham, the Borough Council view is that the County Council should remove the AoS for this reason.
Additionally, Policy MP2 provides a degree of protection for areas with defined characteristics. Clause a. refers to 'ancient' woodland. In view of the County Council decision referred to above, it would be appropriate to delete the word 'ancient', leaving an enhanced level of protection to woodland generally.
Conclusion on AoS E (Shouldham) - Taking into account the two proposed amendments to policies affecting the potential for extraction at Shouldham, and the significant additional constraints now evident, the AoS should be removed.
MP2 Clause e) - Whilst the hydrological catchment around Roydon Common and Dersingham Bog, is specifically mentioned in Policy MP2e for exclusion, the complex hydrology and geology of these extremely sensitive sites is not fully understood. These two habitats have been recognised through the Ramsar, SAC and SSSI designations as having protected status. The introduction of wider 1.5km buffer zones would better mitigate any risk.

3.6 Policy MP7 (relating to restoration and aftercare) suggests that preference will be given to enhancing biodiversity, green infrastructure, and high quality local landscapes. This approach is supported. Whilst not necessarily appropriate in all circumstances, tree planting on restored sites would be a useful additional boost to mitigate for climate change. It is proposed that an additional clause is added to this effect as a fifth bullet point in paragraph four to the policy.

4. Implications for the Borough from the NCC approach to proposed waste and other policies on 'energy minerals'.

4.1 NCC have reviewed the policies in the current plans and as with Minerals moved them on to an end date of 2036. One particular item is relevant to West Norfolk. This is the overall locational strategy for waste management facilities.
4.2 Main points:
* From Policy WP2 in the Preferred Options it would seem possible to locate waste management facilities away from the broad location that generated the waste. Thus necessitating potentially significant transport movements, and possibly generating resentment from recipient communities.
* Whilst not necessarily inappropriate for all types of waste where specialist facilities are needed, extremely careful thought should be given to general waste or significant quantities requiring movement.
* A better approach would seem to be one where the policy encouraged waste to be dealt with as near to the generating source as possible.
* It is suggested our original comments are still appropriate to make.
4.3 Incineration - For the avoidance of doubt, it would be helpful if the County Council could add text to explain the position whereby the County Council will not seek to procure incinerators within Norfolk.
The position of the Borough Council on incineration is clear from previous involvement in planning inquiries. A clear statement on the matter from the County Council in the Minerals and Waste Local Plan would avoid any uncertainty for residents.

4.4 Fracking - Reference could be made to latest Government announcements about the potential restrictions / banning on this subject.

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]

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]

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]

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]

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]

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]

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]