Preferred Options consultation document

Norfolk Minerals and Waste Local Plan: Preferred Options Consultation (MIN 35 - land at Heath Road, Eccles, Quidenham)

Further to the publication of the above I would like to make the following comments on behalf of Frimstone Ltd and wish to register an Objection to the Consultation Draft and support the allocation for MIN 35 for the reasons outlined below.

Landscape
Following the initial findings of the Preferred Options Consolation a Landscape and Visual Statement was commissioned and completed by Collington Winters in October 2019. The report demonstrates and concludes that the site would have acceptable local landscape impacts and that the screening would not be intrusive in its own right. The report also recommends that it will be possible to mitigate adverse landscape impacts through advance planting and bunding.

It is highlighted in the enclosed Landscape and Visual Statement that the proposed site is not located within the AONB, a Core River Valley or any other designated landscape features. It must be noted that unlike MIN 69 - land north of Holt Road, Aylmerton, MIN 211 - land west of Bath Hills Road, Earsham (Extension area 3) which is adjacent to the boundary of the Broads Authority Executive Area and MIN 25 - land at Manor Farm (between Loddon Road and Thorpe Road), Haddiscoe which is adjacent to a Core River Valley and also is adjacent to the boundary of the Broads Authority Executive Area).

The enclosed report also demonstrates that the existing landscape detractors mean that the proposed site cannot be considered a tranquil, unspoilt area of the countryside.
The proposal sets the limit of extraction approximately 150 metres from the southern boundary of the site, so as to allow the site to be screened in a way which would not be significantly detrimental to the views from the immediate south. Existing bunding associated with the historic landfill is present which already screens out long-range views for properties to the south of the proposed site.
The proposed new bunding associated with the MIN 35 development will be set back from the southern boundary so as to not have an adverse effect on views over the field and the woodland to the west from those properties to the south of the site. The proposed limit of extraction means that there would be less difference between the views of the existing bunding associated with the historic landfill and those of new bunding associated with this proposed development from the south and southeast of the site.

Screen bunding and advance hedge planting is proposed along the site boundary on Heath Road to ensure that users of Heath Road are not able to gain medium-to-long-range views across the site, including the existing partially screened timber yard opposite the area of the site not proposed to be worked.

Any future application for mineral extractions at this site will be accompanied with a
further carefully designed landscape scheme that addresses the visual impacts that may, unless controlled, potentially affect local residents. Substantial buffer zones are proposed comprising advanced planting of woodland copses and planting belts, that are to be retained within the site restoration, and screen bunds in place surrounding the immediate area proposed for mineral extraction.

The temporary bunds are proposed to be of adequate height to screen the upper story views from housing and it will be ensured that the grading, profiles appearance and management of vegetation on the temporary bunds will benefit from careful treatment. These mitigation requirements shall be followed to ensure that the screening features are not visually intrusive as it is recognised that residents may have views of these across the existing agricultural fields to the east and southwest of the site, and also from the adjacent road.

I therefore wish to object to the conclusions reached in terms of considering MIN 35 unsuitable for allocation in landscape terms, as following a review of baseline information, together with consideration of likely landscape and visual effects, it is considered that the application site and wider landscape is able to accommodate the proposal for mineral extraction, in landscape and visual terms, without having an unacceptable effect or loss of landscape character or visual amenity. Any loss of landscape character would be temporary and upon restoration, character would be reinforced and enhanced.

Provision for minerals extraction (Policy MP1)
The NPPG suggests that the 10-year rolling average, 3 year rolling average and the sub-national guidelines should all be considered in order to establish a broad understanding of current and future mineral demand, especially during reviews of planned provision. The sub-national guidelines are for Norfolk to produce 2.57 million tonnes of sand and gravel a year.
It has been considered by the MPA that planning to provide the 20-year average annual production figure would enable a sufficient quantity of sand and gravel resources to be available over the 18- year plan period and would take into account potential fluctuations in the economy.
Over the 18-year plan period to 2036, using the considered suitable 20-year average of 1.868 million tpa, 33.624 million tonnes of sand and gravel resources would be needed in total. Taking into account the existing permitted reserve, the remaining need for allocated sites is 20.313 million tonnes of sand and gravel.
However, using the sub-national guidelines for sand and gravel, as specified in the NPPG this would mean that sites for 32,949,300 tonnes of sand and gravel extraction would need to be allocated over the plan period. The sub-national guideline figures cover the period 2005-2020 and therefore remains current at this stage of the Consultation process, and must remain so until these figures are updated. Therefore, a stronger case has to be made by the MPA as to why they consider the current subnational guidelines not to be relevant in producing this plan and more specifically the landbank figure required in the Plan period to the end of 2036. Furthermore, may I raise the question to the MPA as to what the justification is for using a 20-year average annual production figure, rather than a 25-year
average or likewise 18-year to cover the remainder of the plan period, for example?

I therefore wish to object to the methodology used in establishing the required tonnages of sand and gravel resource to be allocated within the Plan period to the end 2036 as referred to in Policy MP1: Provisions of minerals extraction. The 20-year average methodology has not been accepted as a valid methodology for establishing this figure and therefore should not be considered as sound. This is demonstrated by the NPPG which considers that only the 10-year rolling average, 3 year rolling average and the sub-national guidelines should all be considered in order to establish a broad understanding of current and future mineral demand, especially during reviews of planned provision.

I would consequently like to object to this figure in relation to MIN 35, which at the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review was considered as suitable for allocation based on the proposed 20-year average annual production figure in August 2018.

However, the current proposed allocation figure less than 18 months later is greatly reduced and is considered the only reason for the site to now be considered as unsuitable, due to the fact that the proposals have not changed in terms of the site development since that date.

Suitability of alternatives considered as suitable for allocation
There are a number of sites that have been considered suitable for allocation in the Norfolk Minerals and Waste Local Plan Review that are very similar to MIN 35 in terms of their potential impact on the local landscape from viewpoints from surrounding sensitive receptors. The table below and subsequent consultation extracts identifies and breaks down each site in terms of the number of sensitive receptors within 250m and 100m of the proposed extraction area compared with MIN 35, respectively. Therefore, on a logical comparative basis MIN 35 sits within the top three of the proposed sites with the least number of sensitive receptors.

INSERT TABLE

MIN 210 "the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting. The views of the mineral working from Park Farm Cottages will predominantly be screened by bunding"

MIN 211 "the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting. The views of the mineral working from nearby properties will predominantly be screened by bunding"

MIN 65 "glimpses of the land can be seen from Frettenham Road to the west through gaps in boundary hedges. Views could also be seen from two properties which lie close to the site perimeter to the west and east respectively"

MIN 213 "views into the site may be possible from Shorthorn Road, through the proposed entrance"

MIN 25 "there are mature screen planting forming hedgerows on all sides of the site, except a section of the eastern boundary closest to Manor Farm"

MIN 12 "views of the site would be seen from Field Lane, a road used as a public path which bounds the site to the north. In addition, the southern part of the site is slightly elevated and may be visible in a long view from public paths crossing land to the north of the Whitewater valley"

MIN 209 "a number of properties back onto the road overlook the site, the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting"

The above findings were concluded by the MPA as being acceptable subject to the erection of screen bunds and advanced planting. Likewise, it is stated that any potential views of MIN 35 would require mitigation through screen bunding and advance hedge planting. Therefore, given the supporting information above, as part of the independent Landscape and Visual Statement, it is considered that the MIN 35 site should be considered suitable for allocation due to the similarities it shares in landscape terms with the above sites that themselves have been considered suitable for allocation.

Furthermore, three sites have been considered suitable for allocation that are either within or adjacent to the AONB, a Core River Valley or any other designated landscape features, namely MIN 69, MIN 211 and MIN 25. Since MIN 35 is not located within or even close to any of these designated landscape features, preference must be given to this site in planning terms as required by the
requirements of NPPF Paragraph 205.

Since the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review and additional site has come forward and is now considered as suitable for allocation in the 'Preferred Options Consultation'. This is MIN 213 land at Mansom Plantation, Stratton Strawless for a total estimated sand and gravel resource of 1 million tonnes. The site has been selected in preference to MIN 35, due to the fact that the MIN 35 site was formerly considered as suitable for allocation at the 'Initial Consultation' stage. However, it is considered that this new site (MIN 213) not only presents a similar landscape impact to MIN 35 as described above, but also represents a site that will result in the permanent loss of a well-established coniferous plantation for after use as a holiday lodge development. MIN 213 is also located adjacent to an ancient replanted woodland to which deterioration is likely to occur as a result of the mineral operation. As such, any application that concludes this unless there are wholly exceptional reasons should be refused as in accordance with NPPF Paragraph 175c. Therefore, the site cannot be considered as being suitable for allocation given this likely impact.

I therefore would like to object to the inclusion of the above sites as being considered suitable for allocation, whereas MIN 35 is considered unsuitable solely on landscape grounds. It has been demonstrated above that preference should not be given to any of these sites over and above MIN 35 and that MIN 35 should be reconsidered in light of the additional supporting landscape and visual statement and be concluded as once again suitable for allocation as at the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review.

Conclusion
On behalf of Frimstone Limited, I would contend that the information submitted as part of this consultation adequately addresses the reasons why this site has not been considered suitable for allocation and that the site should now be allocated. This would add only a further 0.5 million tonnes to the overall landbank figure for the plan period and be worked and restored considerably before the end of 2036. Therefore, I see no reason why these revisions should not be carried forward to adoption in the review of the Local Plan.

Enc.
Landscape and Visual Statement (Ref. CW0121-RPT-001), dated 30 October 2019
Ecological Scoping Report (Ref. E17864), dated 2 August 2017

Norfolk Minerals and Waste Local Plan: Preferred Options Consultation (MIN 35 - land at Heath Road, Eccles, Quidenham)

Further to the publication of the above I would like to make the following comments on behalf of Frimstone Ltd and wish to register an Objection to the Consultation Draft and support the allocation for MIN 35 for the reasons outlined below.

Landscape
Following the initial findings of the Preferred Options Consolation a Landscape and Visual Statement was commissioned and completed by Collington Winters in October 2019. The report demonstrates and concludes that the site would have acceptable local landscape impacts and that the screening would not be intrusive in its own right. The report also recommends that it will be possible to mitigate adverse landscape impacts through advance planting and bunding.

It is highlighted in the enclosed Landscape and Visual Statement that the proposed site is not located within the AONB, a Core River Valley or any other designated landscape features. It must be noted that unlike MIN 69 - land north of Holt Road, Aylmerton, MIN 211 - land west of Bath Hills Road, Earsham (Extension area 3) which is adjacent to the boundary of the Broads Authority Executive Area and MIN 25 - land at Manor Farm (between Loddon Road and Thorpe Road), Haddiscoe which is adjacent to a Core River Valley and also is adjacent to the boundary of the Broads Authority Executive Area).

The enclosed report also demonstrates that the existing landscape detractors mean that the proposed site cannot be considered a tranquil, unspoilt area of the countryside.
The proposal sets the limit of extraction approximately 150 metres from the southern boundary of the site, so as to allow the site to be screened in a way which would not be significantly detrimental to the views from the immediate south. Existing bunding associated with the historic landfill is present which already screens out long-range views for properties to the south of the proposed site.
The proposed new bunding associated with the MIN 35 development will be set back from the southern boundary so as to not have an adverse effect on views over the field and the woodland to the west from those properties to the south of the site. The proposed limit of extraction means that there would be less difference between the views of the existing bunding associated with the historic landfill and those of new bunding associated with this proposed development from the south and southeast of the site.

Screen bunding and advance hedge planting is proposed along the site boundary on Heath Road to ensure that users of Heath Road are not able to gain medium-to-long-range views across the site, including the existing partially screened timber yard opposite the area of the site not proposed to be worked.

Any future application for mineral extractions at this site will be accompanied with a
further carefully designed landscape scheme that addresses the visual impacts that may, unless controlled, potentially affect local residents. Substantial buffer zones are proposed comprising advanced planting of woodland copses and planting belts, that are to be retained within the site restoration, and screen bunds in place surrounding the immediate area proposed for mineral extraction.

The temporary bunds are proposed to be of adequate height to screen the upper story views from housing and it will be ensured that the grading, profiles appearance and management of vegetation on the temporary bunds will benefit from careful treatment. These mitigation requirements shall be followed to ensure that the screening features are not visually intrusive as it is recognised that residents may have views of these across the existing agricultural fields to the east and southwest of the site, and also from the adjacent road.

I therefore wish to object to the conclusions reached in terms of considering MIN 35 unsuitable for allocation in landscape terms, as following a review of baseline information, together with consideration of likely landscape and visual effects, it is considered that the application site and wider landscape is able to accommodate the proposal for mineral extraction, in landscape and visual terms, without having an unacceptable effect or loss of landscape character or visual amenity. Any loss of landscape character would be temporary and upon restoration, character would be reinforced and enhanced.

Provision for minerals extraction (Policy MP1)
The NPPG suggests that the 10-year rolling average, 3 year rolling average and the sub-national guidelines should all be considered in order to establish a broad understanding of current and future mineral demand, especially during reviews of planned provision. The sub-national guidelines are for Norfolk to produce 2.57 million tonnes of sand and gravel a year.
It has been considered by the MPA that planning to provide the 20-year average annual production figure would enable a sufficient quantity of sand and gravel resources to be available over the 18- year plan period and would take into account potential fluctuations in the economy.
Over the 18-year plan period to 2036, using the considered suitable 20-year average of 1.868 million tpa, 33.624 million tonnes of sand and gravel resources would be needed in total. Taking into account the existing permitted reserve, the remaining need for allocated sites is 20.313 million tonnes of sand and gravel.
However, using the sub-national guidelines for sand and gravel, as specified in the NPPG this would mean that sites for 32,949,300 tonnes of sand and gravel extraction would need to be allocated over the plan period. The sub-national guideline figures cover the period 2005-2020 and therefore remains current at this stage of the Consultation process, and must remain so until these figures are updated. Therefore, a stronger case has to be made by the MPA as to why they consider the current subnational guidelines not to be relevant in producing this plan and more specifically the landbank figure required in the Plan period to the end of 2036. Furthermore, may I raise the question to the MPA as to what the justification is for using a 20-year average annual production figure, rather than a 25-year
average or likewise 18-year to cover the remainder of the plan period, for example?

I therefore wish to object to the methodology used in establishing the required tonnages of sand and gravel resource to be allocated within the Plan period to the end 2036 as referred to in Policy MP1: Provisions of minerals extraction. The 20-year average methodology has not been accepted as a valid methodology for establishing this figure and therefore should not be considered as sound. This is demonstrated by the NPPG which considers that only the 10-year rolling average, 3 year rolling average and the sub-national guidelines should all be considered in order to establish a broad understanding of current and future mineral demand, especially during reviews of planned provision.

I would consequently like to object to this figure in relation to MIN 35, which at the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review was considered as suitable for allocation based on the proposed 20-year average annual production figure in August 2018.

However, the current proposed allocation figure less than 18 months later is greatly reduced and is considered the only reason for the site to now be considered as unsuitable, due to the fact that the proposals have not changed in terms of the site development since that date.

Suitability of alternatives considered as suitable for allocation
There are a number of sites that have been considered suitable for allocation in the Norfolk Minerals and Waste Local Plan Review that are very similar to MIN 35 in terms of their potential impact on the local landscape from viewpoints from surrounding sensitive receptors. The table below and subsequent consultation extracts identifies and breaks down each site in terms of the number of sensitive receptors within 250m and 100m of the proposed extraction area compared with MIN 35, respectively. Therefore, on a logical comparative basis MIN 35 sits within the top three of the proposed sites with the least number of sensitive receptors.

INSERT TABLE

MIN 210 "the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting. The views of the mineral working from Park Farm Cottages will predominantly be screened by bunding"

MIN 211 "the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting. The views of the mineral working from nearby properties will predominantly be screened by bunding"

MIN 65 "glimpses of the land can be seen from Frettenham Road to the west through gaps in boundary hedges. Views could also be seen from two properties which lie close to the site perimeter to the west and east respectively"

MIN 213 "views into the site may be possible from Shorthorn Road, through the proposed entrance"

MIN 25 "there are mature screen planting forming hedgerows on all sides of the site, except a section of the eastern boundary closest to Manor Farm"

MIN 12 "views of the site would be seen from Field Lane, a road used as a public path which bounds the site to the north. In addition, the southern part of the site is slightly elevated and may be visible in a long view from public paths crossing land to the north of the Whitewater valley"

MIN 209 "a number of properties back onto the road overlook the site, the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting"

The above findings were concluded by the MPA as being acceptable subject to the erection of screen bunds and advanced planting. Likewise, it is stated that any potential views of MIN 35 would require mitigation through screen bunding and advance hedge planting. Therefore, given the supporting information above, as part of the independent Landscape and Visual Statement, it is considered that the MIN 35 site should be considered suitable for allocation due to the similarities it shares in landscape terms with the above sites that themselves have been considered suitable for allocation.

Furthermore, three sites have been considered suitable for allocation that are either within or adjacent to the AONB, a Core River Valley or any other designated landscape features, namely MIN 69, MIN 211 and MIN 25. Since MIN 35 is not located within or even close to any of these designated landscape features, preference must be given to this site in planning terms as required by the
requirements of NPPF Paragraph 205.

Since the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review and additional site has come forward and is now considered as suitable for allocation in the 'Preferred Options Consultation'. This is MIN 213 land at Mansom Plantation, Stratton Strawless for a total estimated sand and gravel resource of 1 million tonnes. The site has been selected in preference to MIN 35, due to the fact that the MIN 35 site was formerly considered as suitable for allocation at the 'Initial Consultation' stage. However, it is considered that this new site (MIN 213) not only presents a similar landscape impact to MIN 35 as described above, but also represents a site that will result in the permanent loss of a well-established coniferous plantation for after use as a holiday lodge development. MIN 213 is also located adjacent to an ancient replanted woodland to which deterioration is likely to occur as a result of the mineral operation. As such, any application that concludes this unless there are wholly exceptional reasons should be refused as in accordance with NPPF Paragraph 175c. Therefore, the site cannot be considered as being suitable for allocation given this likely impact.

I therefore would like to object to the inclusion of the above sites as being considered suitable for allocation, whereas MIN 35 is considered unsuitable solely on landscape grounds. It has been demonstrated above that preference should not be given to any of these sites over and above MIN 35 and that MIN 35 should be reconsidered in light of the additional supporting landscape and visual statement and be concluded as once again suitable for allocation as at the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review.

Conclusion
On behalf of Frimstone Limited, I would contend that the information submitted as part of this consultation adequately addresses the reasons why this site has not been considered suitable for allocation and that the site should now be allocated. This would add only a further 0.5 million tonnes to the overall landbank figure for the plan period and be worked and restored considerably before the end of 2036. Therefore, I see no reason why these revisions should not be carried forward to adoption in the review of the Local Plan.

Enc.
Landscape and Visual Statement (Ref. CW0121-RPT-001), dated 30 October 2019
Ecological Scoping Report (Ref. E17864), dated 2 August 2017

Norfolk Minerals and Waste Local Plan: Preferred Options Consultation (MIN 35 - land at Heath Road, Eccles, Quidenham)

Further to the publication of the above I would like to make the following comments on behalf of Frimstone Ltd and wish to register an Objection to the Consultation Draft and support the allocation for MIN 35 for the reasons outlined below.

Landscape
Following the initial findings of the Preferred Options Consolation a Landscape and Visual Statement was commissioned and completed by Collington Winters in October 2019. The report demonstrates and concludes that the site would have acceptable local landscape impacts and that the screening would not be intrusive in its own right. The report also recommends that it will be possible to mitigate adverse landscape impacts through advance planting and bunding.

It is highlighted in the enclosed Landscape and Visual Statement that the proposed site is not located within the AONB, a Core River Valley or any other designated landscape features. It must be noted that unlike MIN 69 - land north of Holt Road, Aylmerton, MIN 211 - land west of Bath Hills Road, Earsham (Extension area 3) which is adjacent to the boundary of the Broads Authority Executive Area and MIN 25 - land at Manor Farm (between Loddon Road and Thorpe Road), Haddiscoe which is adjacent to a Core River Valley and also is adjacent to the boundary of the Broads Authority Executive Area).

The enclosed report also demonstrates that the existing landscape detractors mean that the proposed site cannot be considered a tranquil, unspoilt area of the countryside.
The proposal sets the limit of extraction approximately 150 metres from the southern boundary of the site, so as to allow the site to be screened in a way which would not be significantly detrimental to the views from the immediate south. Existing bunding associated with the historic landfill is present which already screens out long-range views for properties to the south of the proposed site.
The proposed new bunding associated with the MIN 35 development will be set back from the southern boundary so as to not have an adverse effect on views over the field and the woodland to the west from those properties to the south of the site. The proposed limit of extraction means that there would be less difference between the views of the existing bunding associated with the historic landfill and those of new bunding associated with this proposed development from the south and southeast of the site.

Screen bunding and advance hedge planting is proposed along the site boundary on Heath Road to ensure that users of Heath Road are not able to gain medium-to-long-range views across the site, including the existing partially screened timber yard opposite the area of the site not proposed to be worked.

Any future application for mineral extractions at this site will be accompanied with a
further carefully designed landscape scheme that addresses the visual impacts that may, unless controlled, potentially affect local residents. Substantial buffer zones are proposed comprising advanced planting of woodland copses and planting belts, that are to be retained within the site restoration, and screen bunds in place surrounding the immediate area proposed for mineral extraction.

The temporary bunds are proposed to be of adequate height to screen the upper story views from housing and it will be ensured that the grading, profiles appearance and management of vegetation on the temporary bunds will benefit from careful treatment. These mitigation requirements shall be followed to ensure that the screening features are not visually intrusive as it is recognised that residents may have views of these across the existing agricultural fields to the east and southwest of the site, and also from the adjacent road.

I therefore wish to object to the conclusions reached in terms of considering MIN 35 unsuitable for allocation in landscape terms, as following a review of baseline information, together with consideration of likely landscape and visual effects, it is considered that the application site and wider landscape is able to accommodate the proposal for mineral extraction, in landscape and visual terms, without having an unacceptable effect or loss of landscape character or visual amenity. Any loss of landscape character would be temporary and upon restoration, character would be reinforced and enhanced.

Provision for minerals extraction (Policy MP1)
The NPPG suggests that the 10-year rolling average, 3 year rolling average and the sub-national guidelines should all be considered in order to establish a broad understanding of current and future mineral demand, especially during reviews of planned provision. The sub-national guidelines are for Norfolk to produce 2.57 million tonnes of sand and gravel a year.
It has been considered by the MPA that planning to provide the 20-year average annual production figure would enable a sufficient quantity of sand and gravel resources to be available over the 18- year plan period and would take into account potential fluctuations in the economy.
Over the 18-year plan period to 2036, using the considered suitable 20-year average of 1.868 million tpa, 33.624 million tonnes of sand and gravel resources would be needed in total. Taking into account the existing permitted reserve, the remaining need for allocated sites is 20.313 million tonnes of sand and gravel.
However, using the sub-national guidelines for sand and gravel, as specified in the NPPG this would mean that sites for 32,949,300 tonnes of sand and gravel extraction would need to be allocated over the plan period. The sub-national guideline figures cover the period 2005-2020 and therefore remains current at this stage of the Consultation process, and must remain so until these figures are updated. Therefore, a stronger case has to be made by the MPA as to why they consider the current subnational guidelines not to be relevant in producing this plan and more specifically the landbank figure required in the Plan period to the end of 2036. Furthermore, may I raise the question to the MPA as to what the justification is for using a 20-year average annual production figure, rather than a 25-year
average or likewise 18-year to cover the remainder of the plan period, for example?

I therefore wish to object to the methodology used in establishing the required tonnages of sand and gravel resource to be allocated within the Plan period to the end 2036 as referred to in Policy MP1: Provisions of minerals extraction. The 20-year average methodology has not been accepted as a valid methodology for establishing this figure and therefore should not be considered as sound. This is demonstrated by the NPPG which considers that only the 10-year rolling average, 3 year rolling average and the sub-national guidelines should all be considered in order to establish a broad understanding of current and future mineral demand, especially during reviews of planned provision.

I would consequently like to object to this figure in relation to MIN 35, which at the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review was considered as suitable for allocation based on the proposed 20-year average annual production figure in August 2018.

However, the current proposed allocation figure less than 18 months later is greatly reduced and is considered the only reason for the site to now be considered as unsuitable, due to the fact that the proposals have not changed in terms of the site development since that date.

Suitability of alternatives considered as suitable for allocation
There are a number of sites that have been considered suitable for allocation in the Norfolk Minerals and Waste Local Plan Review that are very similar to MIN 35 in terms of their potential impact on the local landscape from viewpoints from surrounding sensitive receptors. The table below and subsequent consultation extracts identifies and breaks down each site in terms of the number of sensitive receptors within 250m and 100m of the proposed extraction area compared with MIN 35, respectively. Therefore, on a logical comparative basis MIN 35 sits within the top three of the proposed sites with the least number of sensitive receptors.

INSERT TABLE

MIN 210 "the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting. The views of the mineral working from Park Farm Cottages will predominantly be screened by bunding"

MIN 211 "the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting. The views of the mineral working from nearby properties will predominantly be screened by bunding"

MIN 65 "glimpses of the land can be seen from Frettenham Road to the west through gaps in boundary hedges. Views could also be seen from two properties which lie close to the site perimeter to the west and east respectively"

MIN 213 "views into the site may be possible from Shorthorn Road, through the proposed entrance"

MIN 25 "there are mature screen planting forming hedgerows on all sides of the site, except a section of the eastern boundary closest to Manor Farm"

MIN 12 "views of the site would be seen from Field Lane, a road used as a public path which bounds the site to the north. In addition, the southern part of the site is slightly elevated and may be visible in a long view from public paths crossing land to the north of the Whitewater valley"

MIN 209 "a number of properties back onto the road overlook the site, the impact of the proposed mineral working on the wider landscape would predominantly be the decreased long-distance views and increased roadside vegetation due to the proposed bunding and advanced planting"

The above findings were concluded by the MPA as being acceptable subject to the erection of screen bunds and advanced planting. Likewise, it is stated that any potential views of MIN 35 would require mitigation through screen bunding and advance hedge planting. Therefore, given the supporting information above, as part of the independent Landscape and Visual Statement, it is considered that the MIN 35 site should be considered suitable for allocation due to the similarities it shares in landscape terms with the above sites that themselves have been considered suitable for allocation.

Furthermore, three sites have been considered suitable for allocation that are either within or adjacent to the AONB, a Core River Valley or any other designated landscape features, namely MIN 69, MIN 211 and MIN 25. Since MIN 35 is not located within or even close to any of these designated landscape features, preference must be given to this site in planning terms as required by the
requirements of NPPF Paragraph 205.

Since the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review and additional site has come forward and is now considered as suitable for allocation in the 'Preferred Options Consultation'. This is MIN 213 land at Mansom Plantation, Stratton Strawless for a total estimated sand and gravel resource of 1 million tonnes. The site has been selected in preference to MIN 35, due to the fact that the MIN 35 site was formerly considered as suitable for allocation at the 'Initial Consultation' stage. However, it is considered that this new site (MIN 213) not only presents a similar landscape impact to MIN 35 as described above, but also represents a site that will result in the permanent loss of a well-established coniferous plantation for after use as a holiday lodge development. MIN 213 is also located adjacent to an ancient replanted woodland to which deterioration is likely to occur as a result of the mineral operation. As such, any application that concludes this unless there are wholly exceptional reasons should be refused as in accordance with NPPF Paragraph 175c. Therefore, the site cannot be considered as being suitable for allocation given this likely impact.

I therefore would like to object to the inclusion of the above sites as being considered suitable for allocation, whereas MIN 35 is considered unsuitable solely on landscape grounds. It has been demonstrated above that preference should not be given to any of these sites over and above MIN 35 and that MIN 35 should be reconsidered in light of the additional supporting landscape and visual statement and be concluded as once again suitable for allocation as at the 'Initial Consultation' stage of the Norfolk Minerals and Waste Local Plan Review.

Conclusion
On behalf of Frimstone Limited, I would contend that the information submitted as part of this consultation adequately addresses the reasons why this site has not been considered suitable for allocation and that the site should now be allocated. This would add only a further 0.5 million tonnes to the overall landbank figure for the plan period and be worked and restored considerably before the end of 2036. Therefore, I see no reason why these revisions should not be carried forward to adoption in the review of the Local Plan.

Enc.
Landscape and Visual Statement (Ref. CW0121-RPT-001), dated 30 October 2019
Ecological Scoping Report (Ref. E17864), dated 2 August 2017