Response from Walsham le Willows Parish Council

Re: WASTE CORE STRATEGY ISSUES AND OPTIONS (PART2) – STRATEGIC SITES

 

 

Summary

 

In response to the Suffolk County Council Waste Core Strategy (Final Consultation) July 2009 (WCS 07/09)

Walsham le Willows Parish Council (WLW-PC) hereby lodges its VERY STRONG OBJECTION to site 26 Shepherds Grove Industrial Estate being chosen as a potential Strategic Site within the Suffolk County Council Waste Core Strategy (WCS).

 

The WLW-PC rejects the suitability specifically of Site 26.

 

The WLW-PC has a major concern in that it is being asked to make comment upon a strategy document which gives little indication as to the potential final development in terms of:

What is it MBT OR EFW?

Size 100,000 tonnes - 350,000 tonnes?

 

With this stated we have kept our objections to the specific site and its characteristics as seen by the local Parish Councillors and the representations of our Parishioners.

 

The Parish Council specifically asks that both Suffolk County Council (SCC) Officers and our Elected Councillors have full sight of this document.

 

The WLW-PC specifically rejects the suitability of Site 26 on the following grounds

 

1.      The negative impact of additional traffic

1.1  Unsuitable major road access

1.2  Unsuitable minor road access via Local Villages

 

2.      The Site and its Strategic position.

2.1  The Site

2.2  Distances from major centres

2.3  The site and surrounding topography

                2.4 Current site uses and problems

 

3.      The negative impact on the environment

3.1  Visual Impact

3.2  Light and Noise pollution

3.3  Aquifer

 

4        Sustainable development

                4.1 Employment

                4.2 Sources and types of waste material

                4.3 Waste Reduction

                4.4 Impact on our way of life

 

5        Health concerns

 

 

Development of each of these points is included in the subsequent submission

 

1. The negative impact of additional traffic

 

1.1 Unsuitable major road access

 

WCS 07/09 6.2.28 states in conclusion that “the site is well related to the Strategic Lorry Network” (SLN). Inclusion or exclusion of a road from the SLN is an absolute statement. WLW-PC disputes the suitability of the A143 as part of the SLN and its ability to cope with further substantive lorry movements. The A143 is a single carriageway road and only part of the SLN as no other suitable East West link road exists. The status of the A143 within the SLN should not be classed as on a par with the A14, the two road capacities are totally different. A site near a dual carriageway SLN is more suited to this type of development than one adjacent to a single carriageway road; the WLW-PC do not agree with the statement in 6.2.28.

 

The A143 runs through several villages from the A14 North East to the site and from the A140 West to the site. These villages are already highly congested and the subject of requests for a bypass, e.g. Great Barton. As far as we know there are currently no road improvements planned for the A143 between Bury St Edmunds and Scole.

 

The A143 already has a high level of accidents and a poor safety record at the current traffic levels. Additionally, there are no suitable relief roads when congestion occurs due to road closure. The diversion of traffic through small rural communities along C class roads or single track ways causes damage to verges and hedges and endangers local road users and pedestrians thus impacting adversely on rural amenity.

 

The current traffic position on the A143 is already exacerbated by the seasonal impact of the Sugar beet Campaign and the congestion problems at the St.Saviours Interchange on the A14 in Bury St. Edmunds (British Sugar plc Plant roundabout).

 

To speculate on the numbers of additional lorries is difficult, however within the WCS 07/09 5.18 300,000 to 350,000 tonnes is stated as a likely requirement for Commercial and Industrial Waste. The lorry movements for this volume would be totally inappropriate for the A143 and the local road network. The figure of 300-350kt has been used as it has been stated by SCC Officers that the Gt. Blakenham site will handle the residential waste of 250,000 tonnes.

 

In the original Pick Everard Site Appraisal, site 26 was ranked 7th and 8th for single and multi site disposal options, in other words better options are available in terms of minimizing average km travelled per tonne.

 

WCS 07/09 6.2.2 refers to the planning permission previously granted for the IKEA Distribution Warehouse development. This should not be seen as a precedent in reference to potential traffic impact. The WLW-PC makes the following observations to support this view.

1.      The IKEA proposal occupied a significantly larger proportion of the area (32.78 hectares) when compared to the WCS proposal which is for only 5ha.

2.      A planning application was submitted in 2002 and planning consent for the IKEA development was agreed in 2006. Over recent years we have seen significant increases in traffic movements along the A143.

3.      If further development then occurs on the large area of land still available on the rest of the site it would have an increasingly detrimental impact upon the A143.

4.      The recent expansion of operations in particular on the County Mulch site has already resulted in a large increase in HGV traffic movements.

 

WLW-PC believes that the provision of a roundabout on the A143 to link the industrial site to the main road is an insufficient response to adequately upgrade this single carriageway road.

 

As only a small proportion of the total site (5ha) area available at Site 26 would be required for either an MBT or EFW facility, the likelihood of a disproportionate increase in traffic is inevitable, as development of the rest of the site occurs. The Suffolk Waste Local Plan 2006 (SWLP) states (3.13/3.14, page 13) “Major investment is planned to improve east-west rail services” and “A number of road improvements are planned, though in general promotion of sustainable transport modes are prioritized. The shift of road-borne freight to rail, water and pipeline is encouraged in the County Structure Plan.” As there is no existing railway line or navigable water course anywhere near the Stanton Industrial Estate, realistically access by an inadequate road is the only possible, albeit impractical, option available.

 

 

1.2 Unsuitable minor road access and the impact upon Local Villages

 

However hard Suffolk County Council tries, WLW-PC does not believe it will be able to prevent traffic accessing the site from the Elmswell / Badwell Ash direction using the C Class road over Golding’s Bridge on The Causeway and then Summer Road. Golding’s Bridge was recently made into a single track road and dates back several centuries. It has already been the subject of monitoring for structural integrity and several cracks are evident underneath the arch. These roads are simply not suitable for more HGV traffic. Witness the verges around Walsham and Badwell Ash which are constantly churned up after two lorries have met and cannot pass as the road is too narrow, and the increase in black rubber skid marks at road junctions.

 

Use of Satellite Navigation systems will pinpoint the shortest distance between two points rather than an SCC recommended route. This could lead to bulk transfer vehicles, HGVs and refuse collection vehicles travelling through the many rural settlements along routes more than the stated three miles from roads included in the Suffolk Lorry Route Network (SLRN). The ‘rat run’ from the A14 to the proposed site via Elmswell, Great Ashfield and Badwell Ash, which cuts 13 miles travel each way off the A14/A143 recommended route, would save both time and fuel for contractors and will continue to be used just as it is now. These longstanding concerns have been the subject of two officially supported traffic censuses in Walsham le Willows.

 

The community’s recent experience with the increased traffic from the County Mulch facility provides ample evidence in support of the previous statements. Despite our best efforts, the operating company and the relevant authorities have failed to make any impact on the problems we are experiencing.

 

Currently we are experiencing the additional ongoing difficulty of the inappropriate overnight parking of HGVs in the heart of the village and on the approach roads to the County Mulch facility. We can foresee a further increase in this aspect of the situation as contractors endeavour to achieve an early delivery of their waste to any new facility – most assuredly affecting the visual quality and unique character of this attractive conservation village and with a detrimental effect for the owners of nearby properties..

 

 

2. The Site and its Strategic position

 

2.1 The Site

 

WCS 07/09 6.2.1  gives an inaccurate description of the site, its previous and current use. The Site Appraisal undertaken by consultants Pick Everard - Waste Facility Site Appraisal 2008 assessed an area which does not include the old Mushroom farm buildings. The site they appraised is north of the site described. The total site area assessed in their report refers to 26 hectares and not the 66.32 hectares referred to in the consultation documents. The WCS 07/09 gives a false impression that the 26 hectare area considered is already built upon - it is not.

WCS 07/09 6.2.2 refers to the proposed IKEA development - this again was on a different area to the original 26ha assessed by Pick Everard.

 

This leads us to conclude that the initial appraisal process is fundamentally flawed in relation to the definition of this new site.

 

This explains the query which WLW-PC raised in its response to Waste Core Strategy Issues & Options (Part 11) Strategic Sites (December 2008); in WCS 07/09 6.2.24 The designated development site is a huge area and the parish council feels that any development should be restricted in its location to the Brown Field area to the north of the site”.

 

The Mushroom farm is outside the area described and is currently in part occupied by County Mulch.

 

The Final Consultation document does not make mention of the ANTI-WASTE planning application (SE/01/2220/P) which was withdrawn following it’s submission in June 2001 due to concerns over bio-aerosols affecting residents and workers. This application proposed the construction of a composting plant to handle 154,000 tonnes per year of green and sorted domestic waste.

 

WCS 07/09 6.2.3 the site selection criteria ranked Site 26 as 7th of those available. This ranking did not take into account the Aquifer locations. See separate note under 3.4 Aquifer. Again the Pick Everard site appraisal is fundamentally flawed in relation to this aspect.

 

Pick Everards site appraisal is further flawed in that it states on the sixth page under Compatibility with Neighbouring Land Use; “No site designation, local plan or proposal plan available for the site”. This statement is incorrect as the site falls within a Local Rural Employment Area.

 

Site 26 is located within a designated low fly zone for local military aircraft and the Statutory Bird Strike Zone surrounding RAF Honington.

 

None of the other sites have this combination of disadvantage.

 

2.2  Distances from major centres

 

The choice of the site must be challenged on the grounds of its distance from major urban centres. In fact Site 26 is 26 miles from Ipswich, 33 from Norwich, 40 from Cambridge and 43 from Lowestoft.

WCS 07/09 6.2.23 states “this site is well located to serve the North and West areas of the county including Bury St Edmunds and Newmarket”. Both these waste generating towns sit right on the A14 corridor and are closer in lorry running times to proposed sites at Ipswich rather than pulling lorries off the trunk roads onto smaller SLN roads. Site 26 gives a geographic spread of facilities but sites should be situated near to waste generation not geographical spread. The Waste Core Strategy itself declares in Chapter 5, point 5.5, the Core Strategy spatial policy approach should ‘seek to ensure that as far as practicable waste is treated as close as possible to its point of origin.

 

2.3  The site and its surrounding topography

 

The site is a plateau approximately 60 metres above sea level and is higher than the surrounding land to which it is adjacent.

 

2.4 Current adjacent site uses and problems

 

The communities adjacent to the site have very real recent experience of the mismanagement of waste facilities already in the area. These are not being managed in accordance with the agreed licenses in place and when this is pointed out to the Environment Agency, and the other relevant authorities, they are powerless to do anything about it. This leads us to question the ability of these self same agencies to effectively police and enforce any further waste treatment licenses granted. These problems currently centre on: traffic, parking, smells, fly infestations, vermin, noise and watercourse contamination.

 

 

3. The negative impact on the environment

 

3.1  Visual Impact

 

Site 26 has a rating of Severe for Visual Impact - Comparative visual impact 9, as stated in Waste Core Strategy Issues and Options (part 11). The site is elevated and surrounded by low lying ground with no significant screening in any direction. The impact of a large industrial facility would have a significant detrimental visual impact. ‘Around the site are areas designated as Special Landscape Areas, County Wildlife Sites and Sites of Special Scientific Interest.’ See Waste Core Strategy (Part II) Strategic Sites.

 

Site 26 has the highest visual impact rating coupled with a major underlying aquifer which, when combined together, significantly reduces the design potential to “sink” any required buildings. 

A structure of this potential size would be seen for miles around. Significantly, reference points used by SCC are for heights of 90 and 45 metres. A site within an industrial area or obscured by natural or man-made features would be less intrusive than in Stanton’s open aspect which is a plateau site at approximately 60 metres, ideal for an airfield requiring all-round visibility, but not for this proposal. “It would be difficult to minimise adverse impacts on landscape quality” (SWLP 2.2.d13) … and all this adjacent to our village which is known as a Conservation Village with a large number of listed buildings of architectural and historical interest, the subject of a year-long study by Architectural Historian, Leigh Alston, and, additionally, the subject of a Tourist Trail book about the village.

 

Depending upon the precise nature of the development we could be faced with an elevated 90 metre structure, festooned with red warning lights at night, and visible from many miles around.

 

The siting of a facility of this nature should be in low flood / low water table areas preferably Zone 1. Site 26 has an exceptionally high water table classified as within Groundwater Source Protection Zone 3. The constraints that the water table level would place on design options should be considered. It would be more difficult and costly to partially dig in the facility below ground level to reduce its visual impact and with the increased risk of contaminating the water table. The Waste Core Strategy (Part II) Strategic Sites itself recognizes that there could be potential for contamination, (see Chapter 3/ Site 26 / Overview 1.6), as the site is close to nearby groundwater abstractions and also located within a Nitrate Vulnerable Zone.

 

3.2  Light and Noise pollution

 

As the site sits upon a raised plateau, the impact of a large facility of this nature will have detrimental Light and Noise pollution. Outside lighting, to enable operation 24/7, would be visible within a significant area, affecting a number of surrounding villages. Additionally, red warning lights attached to the high structure would be visible for many miles in any direction, just as the Mendlesham Mast is already highly visible. Noise of vehicles involved in the delivery of waste and extraction of residual waste would be significant during the day. Additionally, there would be the potential for traffic movements, noise and vibration affecting nearby residential properties as HGVs arrive ‘out of hours’ ready to offload early in the day. These types of disturbance would be significant for the surrounding area and are already happening at the County Mulch site.

 

3.3  Aquifer

 

Site 26 overlies a major aquifer as identified in the Pick Everard Appraisal although this was not considered within the Comparative Criteria by Suffolk County Council. The site features, those of overlying a major aquifer, being close to nearby groundwater abstractions and within Groundwater Source Protection Zone 3:  

  1. Increases the consequences and risks associated with pollution and contaminations
  2. Significantly reduces the opportunity for building design to mitigate against Visual Impact  see 3.2

 

 

4. Sustainable development

 

4.1 Employment

 

In the WCS 07/09, page 41, it is stated that ‘the results of the SA (Sustainability Appraisal) showed that this site scored very positively against SA objective(s) 12 (To maximize opportunities for new/additional employment) in the short term’. In Appendix 5, page 134, it states that construction will create short term jobs. We question whether there will be much job creation as major building contractors, who are likely to gain a contract, are more likely to ship in their own existing workforce to work on the plant. We also question how this prospect relates to the St Edmundsbury District Plan that designates the Shepherds Grove Industrial Estate as a ‘Rural Employment Zone? The WCS 07/09 does not recognise this issue.

SCC makes much of the fact that permission had already been given for a large facility on this site, the IKEA Distribution Centre. However, this proposal was expected to create around 300 new jobs which is far in excess of WCS projections for this development.

 

This is contrary to Policy E1 of the current St Edmundsbury Local Plan (SE1 - Existing Employment Land and Premises).

 

The site is designated as light industrial use. A waste facility, in whatever form it takes, will not fall into this category.

 

Recent evidence in relation to the problems on the County Mulch site with smells, vermin and flies would lead us to think that another much larger waste facility would be likely to attract even more problems. This would have an adverse impact on the prospects of the businesses on the rest of the Industrial Estate and could well deter new business moving in with further detrimental effects on the provision of local employment.

 

4.2 Sources and types of waste material

 

SCC will potentially be allowing commercial waste operators to determine the type of, and scale of, waste treatment technology for any given site. If the Industry decide that we need an incinerator then we know that the plant will have to be run at a certain level of ‘throughput’ to maintain efficiency and if the throughput drops because the people of Suffolk reduce their waste output then waste will have to be sourced from further afield. We have already seen County Mulch expanding their business and taking in waste from outside their recognised area so are well aware of the problems of increased traffic that will be generated by such a move.

 

In order to maintain the efficient running of the plant and the return on their investment the operators may even resort to burning waste material which should sit further up the waste hierarchy. This will be a commercial decision not one based on environmental grounds.

In WCS Chapter 8, 8.51, the statement is made that ‘there may be a need to collect, transfer, store, process and treat hazardous waste in the County before being sent for final disposal or treatment’. Policy WCS18 makes it clear that facilities for this transfer and storage would be acceptable on existing waste management sites where hazardous waste would only represent a small proportion of waste managed on site. Once again, we are brought back to the fact that SCC is seeking approval for a scheme in principle only, an umbrella application with no detail as to what may follow from private contractors at a later date.

 

4.3  Waste Reduction

 

We believe that SCC should be making plans to increase levels of recycling above 65% before 2015 and that far greater effort should be put into increasing the current recycling levels.

 

4.4 Impact on our way of life

 

St Edmundsbury’s Core Strategy Submission Document for the LDF states, under Strategy for the Rural Areas 7.2Rural St Edmundsbury has attractive villages and large swathes of unspoilt countryside. Our rural residents report that one of the best things about living in the countryside is its peaceful nature. The beauty and peace of the countryside offer an excellent quality of life.

In 7.6 it statesThrough the various stages of developing the Core Strategy it is clear that residents value the history, visual quality and unique character of the towns, villages and countryside in the Borough. Retaining the local character and distinctiveness of the built environment will be an important prerequisite of new development proposals.’ The Parish Council is well aware that we are part of Mid Suffolk but are in a location closer to the proposed site than many members of St Edmundsbury. We have the same rights and share the same views as stated in the above document – we too enjoy the peace and beauty of our countryside; we too value the history, visual quality and the unique character of Walsham le Willows. We can foresee the local character of our area being changed by traffic movements of large numbers of large vehicles and the attendant wear and tear on parts of our village infrastructure; noise and light pollution which will be exceedingly noticeable in a relatively quiet and dark area; the potential for a decrease in air quality with the attendant possibility of hazards to health; the visual impact of a development far removed from the local character of our environment and the devaluation of land and properties by close proximity to this proposed development.

Policy WCS21 declares that Waste Management Facilities will be considered favourably where they incorporate safe and convenient access for all potential users, and measures which will protect, preserve and where practicable enhance the natural and built environment. We challenge the use of this site when compared to these criteria.

 

 

5. Health concerns

 

As a Parish council we find it close to impossible to make an informed comment on the Health risks associated with a waste site development not least because we don’t know to what use the site may be put, Energy From Waste or MBT, however it remains a major concern of our parishioners as evidenced by their statements at our Open Meeting Consultation held on 16th September 2009.

This concern is not alleviated by the comments in the WCS 07/09  

WCS 07/09 6.2.7  “modeling carried out by the consultants suggests that air quality could be maintained above guidelines” and secondly;

WCS 07/09 6.2.11 “An additional requirement will be to carry out a Health Impact Assessment in support of a planning application for a strategic Residual Waste Treatment Facility at this site”.

 

These two comments give no confidence to local residents in Suffolk County Council’s knowledge of either the subject area or long term safety issues. The British Society of Ecological Medicine (BSEM) has directly challenged the only report to be produced in support of the incinerator solution but without any notable response from the Health Protection Agency and the BSEM conclude that no more incinerators should be built.

 

What we have learnt about the ‘incinerator option’ is that it must be run at 90% efficiency otherwise the likelihood of toxic emissions is greatly increased. These include dioxins, PCB particles; ammonia, acid and fine dust which represent very serious health risks.

 

Air quality would be monitored by the EA but monitoring does not mean absolute 100% prevention of air pollution. This is demonstrated by Allington Quarry Waste Management Facility Community Liaison Committee notes of the 16th of June 2009 where air quality limits are broken and reported as such.

 

We have yet to learn what the long term health impact of this development could be on local residents.

 

Conclusion

 

To summarise, in our view, whilst supporting the County’s over-all strategy, we cannot see how the Stanton site can satisfy SCC criteria because of

  • Its serious intrusion into the landscape.
  • Its serious impact on road traffic on the A143.
  • Significant increase in the use of our minor roads as ‘rat runs’ for heavy vehicles escaping from your ‘approved network’.
  • Its distance from major centres.
  • The effects of light and noise pollution.
  • Employment issues.

 

The Environmental Protection section of the SWLP itself states “Waste development will not be acceptable where impacts cannot be satisfactorily controlled.” We seriously question whether SCC will be able to control all these impacts once a developer has been found. By which time, when further plans are unveiled, it will be too late to opt out, merely to challenge minutiae rather than the ‘bigger picture’.