Planning Statement (incorporating Design & Access Statement)€¦ · Chesterfield Canal...
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Planning Statement
(incorporating Design & Access Statement)
Chesterfield Canal
Restoration between Eckington Road & Hague Lane, constituting the remainder of
the restoration scheme within Chesterfield Borough
Version 1.00
Date 24th June 2020
Looking away from Staveley along
the line of the Chesterfield Canal
Chesterfield Canal Restoration: Planning Statement (incorporating Design & Access Statement)
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Contents
1 Introduction ....................................................................................................................................... 3
2 Background to the Project ................................................................................................................. 5
3 Site Location ..................................................................................................................................... 6
4 Summary of the Proposal .................................................................................................................. 7
5 Planning Policy .................................................................................................................................. 9
6 Design & Access Statement ............................................................................................................ 12
7 Summary of Supporting Documentation .......................................................................................... 25
8 Conclusions ..................................................................................................................................... 30
Appendix 1: Copy of Pre-Application Meeting Notes .............................................................................. 31
Appendix 2: Copy of EIA Screening Request Decision Notice (CHE/20/00213/EIA) ............................... 34
Looking east from Eckington Road towards
the railway bridge, taken March 2020 when
volunteer work halted due to the Covid-19
pandemic
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1 INTRODUCTION
1.1 This Planning Statement supports a full planning application for the restoration of 2.6km of the
Chesterfield Canal between Eckington Road & Hague Lane. The extents constitute the remaining length
of the Chesterfield Canal to be restored within the boundaries of Chesterfield Borough.
1.2 Starting at Eckington Road, the scheme will briefly consist of:
• crossing the Staveley-Seymour railway line (site of bridge no. 13b)
• construction of Railway Lock (no. 5b)
• construction of the 2.6km of canal channel, including approximately 2.1km on a raised
embankment, with the formerly embanked central section known as the Puddlebank
• construction of 4no. overbridges: Arkwright Trail bridge (no. 13c), Bellhouse Bridge (no. 14),
Packsaddle Bridge (no. 15) and Red Bridge (no. 16)
• construction of a new aqueduct over the river Doe Lea
1.3 To facilitate the works, temporary access roads and compounds will be required. Several lengths of
Public Rights of Way (PROW) will need to be realigned through the scheme.
1.4 The scheme will provide a restored length of canal in furtherance of the partnership goals of multiple
partners as set out in section 2 below, and be another step towards the long term goal of complete
restoration of the Chesterfield Canal in time for the 250th anniversary of the original opening in 2027.
1.5 In preparing this application, pre-application advice was sought from Chesterfield Borough Council (CBC)
as the Local Planning Authority (LPA). This advice is included in Appendix 1 to this statement.
1.6 Prior to submission of this application, a Screening Opinion was sought under the Town and Country
Planning (Environmental Impact Assessment) Regulations 2017. This was submitted to CBC on the 31st
March 2020, planning reference CHE/20/00213/EIA, and a decision notice was issued on 17th April 2020
confirming that the scheme would not be classed as EIA development and therefore this planning
application would not require an accompanying Environmental Statement. A copy of this decision notice
is included in Appendix 2 to this statement.
1.7 The following plans are submitted in support of this application:
Drawing No. Title Drawing Size
9213-42-DCC-PL-100 Site Location Plan A1
9213-42-DCC-PL-101-1 Restoration Proposals – Proposed General Arrangement – June 2020
A1
9213-42-DCC-PL-101-2 Restoration Proposals – Proposed General Arrangement – June 2020
A1
9213-42-DCC-PL-101-3 Restoration Proposals – Proposed General Arrangement – June 2020
A1
9213-42-DCC-PL-101-4 Restoration Proposals – Proposed General Arrangement – June 2020
A1
9213-42-DCC-PL-101-5 Restoration Proposals – Proposed General Arrangement – June 2020
A1
9213-42-DCC-PL-102-1 Drainage – Proposals for Field and Surface Water Drainage – June 2020
A1
9213-42-DCC-PL-102-2 Drainage – Proposals for Field and Surface Water Drainage – June 2020
A1
9213-42-DCC-PL-102-3 Drainage – Proposals for Field and Surface Water Drainage – June 2020
A1
9213-42-DCC-PL-102-4 Drainage – Proposals for Field and Surface Water Drainage – June 2020
A1
9213-42-DCC-PL-102-5 Drainage – Proposals for Field and Surface Water Drainage – June 2020
A1
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Drawing No. Title Drawing Size
9213-42-DCC-PL-103-1 Cross Sections Showing Topography, Embankment Profiles and Drainage Proposals (Canal W/L at 55.8m)
A0
9213-42-DCC-PL-103-2 Cross Sections Showing Topography, Embankment Profiles and Drainage Proposals (Canal W/L at 55.8m)
A0
9213-42-DCC-PL-103-3 Cross Sections Showing Topography, Embankment Profiles and Drainage Proposals (Canal W/L at 55.8m)
A0
9213-42-DCC-PL-103-4 Cross Sections Showing Topography, Embankment Profiles and Drainage Proposals (Canal W/L at 55.8m)
A0
9213-42-DCC-PL-103-5 Cross Sections Showing Topography, Embankment Profiles and Drainage Proposals (Canal W/L at 55.8m)
A0
9213-42-DCC-PL-104-1 Footpath, Bridleway and Trail Network Proposals – June 2020
A1
9213-42-DCC-PL-104-2 Footpath, Bridleway and Trail Network Proposals – June 2020
A1
9213-42-DCC-PL-104-3 Footpath, Bridleway and Trail Network Proposals – June 2020
A1
9213-42-DCC-PL-104-4 Footpath, Bridleway and Trail Network Proposals – June 2020
A1
9213-42-DCC-PL-104-5 Footpath, Bridleway and Trail Network Proposals – June 2020
A1
9213-42-DCC-PL-200-1 Mineral Rail Bridge (13b) and New Canal Lock (5b) General Arrangement
A1
9213-42-DCC-PL-203-1 Doe Lea Aqueduct (Bridge 14a) General Arrangement A1
1.8 The following documentation is also submitted in support of this application. This is summarised for
convenience in section 7 below.
Report No. Title
20190610 Chesterfield Canal Restoration Eckington Road to Hague Lane Phase 1 Habitat Survey & Preliminary Ecological Appraisal
- GCN eDNA (MEGZ Ponds)
CheCa02 Protected Species Surveys, River Doe Lea
CheCa030405 Protected Species Surveys, Puddlebank (Draft)
CKJ-JBAU-XX-00-RP-HM-0001-S1-P02
Flood Risk Assessment
CCTWFD19 Chesterfield Canal Water Framework Directive Assessment
TJC2020.23 Heritage Statement
GML19233 Enhanced Coal Mining Risk Assessment – Chesterfield Canal Restoration Route, Staveley, Derbyshire
GML19233/1/1 Phase I Geo-Environmental Assessment, Chesterfield Canal Restoration Route, Doe Lea Valley
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2 BACKGROUND TO THE PROJECT
The Chesterfield Canal
2.1 The Chesterfield Canal originally opened in 1777. It ran for 46 miles (approx. 74km) from Chesterfield to
West Stockwith on the River Trent north of Gainsborough, passing through the major towns of Worksop
and Retford along with many smaller communities. Commercial traffic on the canal dropped off with the
coming of the railways, and in 1907 a collapse in the Norwood Tunnel close to Kiveton severed the length
from Chesterfield to Killamarsh from the national network. The canal further declined in the early 20th
century, until in 1968 only the 26 miles (approx. 42km) from Worksop to the River Trent was still
navigable.
2.2 Since 1989, 12 miles (approx. 19km) of the canal have been restored, along with 37 locks, 11 major
bridges and 2 new marinas. Navigation has been extended westward from Worksop as far as the eastern
portal of the Norwood Tunnel at Kiveton Park. This section is fully navigable and linked to the national
canal network via the River Trent. In Derbyshire, over 5 miles (8km) has been restored between the start
of the canal in Chesterfield and Eckington Road, Staveley.
2.3 The restoration efforts to date have all been completed by the committed partnerships of local and
national organisations outlined below.
2.4 There remains approximately 8.5 miles (14km) to be restored between Staveley and Kiveton Park. This
planning application is for the remaining 2.6km within Chesterfield Borough.
The Chesterfield Canal Trust (CCT)
2.5 CCT is the successor to the Chesterfield Canal Society, formed in 1976 with the aim of restoring the
Chesterfield Canal to full navigation. It is a membership organisation, currently with over 1900 members
from the local area and all over the world. The formal objectives of CCT are:
• To promote the restoration to good navigable order of as much as is considered possible of the
Chesterfield Canal and to maintain and improve the Waterway for the use and benefit of the public
• To promote the fullest use of the Waterway for the benefit of the public
• To promote, and educate the public, in the history, use of and associated wildlife of the Waterway
The Chesterfield Canal Partnership (CCP)
2.6 CCP is a partnership of organisations that have an interest in achieving the following aims:
• To restore the Chesterfield Canal to full navigation using, wherever possible, the historic route
• To explore the potential to create and develop a new navigable link between the Chesterfield
Canal and the Sheffield & South Yorkshire Navigation
• To protect, conserve and enhance the natural and built heritage of the canal
• To improve and widen all forms of public access to the canal
• To promote the sustainable economic and social regeneration of the Chesterfield Canal corridor in
order to improve the quality of life in the surrounding communities
2.7 The membership of CCP includes CCT, the Canal & River Trust, all District & County level local
authorities along the full route of the canal and the Inland Waterways Association. Previously, CCP has
been the coordinating body managing and delivering on the restoration aims. This role is now
transitioning to CCT due to the ongoing budgetary pressures placed on local authorities.
2.8 Since the CCP was formed in 1995, a significant amount of theoretical work has been done to examine
the practicality and the benefits of the restoration. This has included high-level feasibility studies and
more detailed examination of the technical feasibility, economic and social benefits, hydrology and
ecology.
2.9 The outcome of all of this work was collated into an overall plan for the restoration, presented in two
volumes: Next Navigation West (Staveley to Killamarsh) and Next Navigation East (Killamarsh to Kiveton
Park). These set out all aspects of the restoration in detail and form the backbone to this application and
the wider restoration strategy.
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Why Restore the Chesterfield Canal?
2.10 Waterway projects across the UK have a proven record of delivering substantial benefits to the
communities through which they run and to the wider surrounding region. The evidence collated within
the ‘Next Navigation’ reports demonstrates the significant positive effects that restoration of the
Chesterfield Canal will have on the quality of life in the area, acting as a focus and catalyst for social,
economic and environmental regeneration.
2.11 Social Benefits: the restored Chesterfield Canal will be a waterway for all – a linear water park and
greenspace open and accessible to all. The canal is already well used for walking, cycling, fishing and
canoeing – all activities which will be enhanced and developed as the project proceeds. Dedicated events
such as the Chesterfield Canal Festival and the Walking Festival also encourage local communities to
enjoy the canal, or they can take a trip on the two trip boats that the Chesterfield Canal Trust operates in
the area (from Tapton Lock and Hollingwood).
2.12 Economic Benefits: the restored Chesterfield Canal creates a range of economic opportunities. The
developments at Staveley Town Basin (proposals being led by Derbyshire County Council), the Staveley
Works corridor and the Chesterfield Waterside site all take advantage of a waterside location to improve
the attractiveness of businesses and residential properties. Katey’s Coffee Shop, which operates out of
the Chesterfield Canal Trust’s headquarters at Hollingwood Hub, is a small but very successful example
of the economic benefits.
2.13 Whilst direct economic benefit is unlikely from the proposed scheme, the application is a key link to
getting the remainder of the Chesterfield Canal restored and realising the significant benefits of the
completed project. Smaller economic benefits are possible through cycle/boat hire and similar activities.
2.14 Environmental Benefits: ‘artificial’ waterways have been integral elements of the landscape for almost
250 years. They form both routes and barriers, and their presence has strongly influenced the
environment in which we live. Restoring the rural stretch of canal from Staveley to Renishaw will
contribute to the protection and enhancement of the local landscape, whilst also providing an increased
diversity of inter-connected terrestrial and aquatic habitats. This connectivity is why waterways form an
integral part of the green infrastructure of multi-functional open spaces and natural assets.
3 SITE LOCATION
3.1 For further details, refer to the site location plan (drawing 9213-42-DCC-PL-100).
3.2 The isolated length of the existing restored Chesterfield Canal runs approximately north-east from
Chesterfield, passing through Brimington and Hollingwood to Staveley, in the east of the Borough. This
scheme will connect to and extend the isolated length to the limits of Chesterfield Borough.
3.3 The proposed works start at Eckington Road (OS Grid Ref SK 43574 75333) and proceed initially east.
The site lies between Staveley and the Hartington Industrial Estate, and runs alongside and under Ireland
Close and the Staveley-Seymour railway line. The environment becomes progressively more rural and
from the northern tip of Bellhouse Lane (OS Grid Ref SK 43888 75323) the proposals are in open
countryside.
3.4 At the northern tip of Bellhouse Lane, the canal alignment turns roughly north-east, and crosses the Doe
Lea valley on a raised embankment. Remains of the historic embankment are still visible, particularly
adjacent to the River Doe Lea. Several deep cuts have been made through the embankment for services
and to open out the river (which used to flow through twin brick culverts under the canal), and the whole
valley has suffered due to mining subsidence. The result is that the original embankment is now up to 3m
lower than it was originally and will require raising as part of the proposed works.
3.5 From Bellhouse Lane to the junction with the Norbriggs Cutting (OS Grid Ref SK 44642 75994), the canal
forms the natural divide between the arable farmland to the north west and the Norbriggs Flash Local
Nature Reserve to the south east. The majority of the adjacent length of the Nature Reserve is farmed.
3.6 From the junction with the Norbriggs Cutting, the canal turns north until it reaches the end of the proposed
works on the south side of the access track from Hague Lane to the sewage treatment works (OS Grid
Ref SK 44476 77148), which is the Borough boundary. Throughout this length, the canal runs through
arable farmland on both sides.
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4 SUMMARY OF THE PROPOSAL
4.1 In broad terms, the intention is to rebuild the length of canal across the Doe Lea valley, where the original
canal route has been seriously affected by mining subsidence and subsequent land use. The priority is to
create a new waterway corridor on the original route, and to endow it with a similar character to that which
the original canal would have had if it had survived.
4.2 The scheme divides into two lengths with different characteristics:
4.3 Between Eckington Road and Bellhouse Lane, the canal is within a short transport corridor, including
the Staveley-Seymour railway line, Staveley Northern Loop Road and the canal. These run in close
proximity and are all crossed by Eckington Road and the disused Great Central Railway route (now the
Trans-Pennine Trail), which taken together make the length heavily engineered, with multiple structures
and hard surfaces.
4.4 From Bellhouse Lane to Hague Lane, the canal is largely on a raised earth embankment in rural
countryside.
4.5 Eckington Road to Bellhouse Lane
4.5.1 This length is dominated by the crossing of the canal and the Staveley-Seymour railway line. The railway
line is currently disused, and the track bed has been taken up, however it is still considered to be live by
Network Rail as various options remain for its re-use. This includes for use as access to the proposed
HS2 Infrastructure Maintenance Depot on the former Staveley Works site.
4.5.2 The historic bridge at this location has recently been excavated under licence from Network Rail in order
to examine its condition. The bridge was infilled by Network Rail following their purchase of the derelict
canal from the British Waterways Board in 1980.
Figure 4.1: Excavation of the existing structure under licence, 20/10/2017
4.5.3 The bridge structure is in sound condition, but as with the surrounding area it has suffered from mining
subsidence. This, combined with the greater loading requirements for modern railways mean that it is no
longer possible to use the structure at the original water level. However, the original bridge abutments will
be reused with a lowered invert level. The rail bridge deck will not be reinstated as part of this scheme,
but it will be possible for it to be so should the line come back into use in the future.
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4.5.4 As such, the water level in this length has been dropped from the historic 55.8mAOD to the current
54.1mAOD. The water level is set by the fall at Staveley Town Lock to the west, which was constructed
by the volunteers of the Chesterfield Canal Trust work party as part of the Staveley Town Basin
development granted planning permission in 2010 (CHE/09/00769/FUL).
4.5.5 Immediately east of the railway, the canal will return to the original water level of 55.8mAOD using a new
lock. The design rationale for this decision is discussed further in section 6 below.
4.5.6 Proceeding east, the canal will then pass underneath a new Trans-Pennine Trail high-level bridge, along
a short length of engineered channel suitable for visitor moorings and underneath a new access bridge at
the northern end of Bellhouse Lane.
4.6 Bellhouse Lane to Hague Lane
4.6.1 Historically, the canal initially followed the contour of the land, before striking out on a raised
embankment, known as the Puddlebank. This carried the canal from one side of the Doe Lea valley to the
other, with the river passing underneath the canal through a pair of brick culverts. The canal then followed
the contours of the land once again from the north end of the Norbriggs cutting.
Figure 4.2: The original Puddlebank, taken May 1970 before the banks were removed
4.6.2 The structure of the Puddlebank largely remains, although it has suffered from mining subsidence and
local breakthroughs for the river and utilities. The banks of the canal were bulldozed out and used in an
attempt to address some of the mining subsidence issues on adjacent farmland. The resulting effect is
that the existing structure is now substantially lower than the original water level, up to 3m in places.
4.6.3 New material will be imported to raise the height of the Puddlebank to the historic 55.8mAOD water level.
This will also mean that the length of embanked canal will be extended in both directions from the original
Puddlebank. The design rationale for that decision is discussed further in section 6 below.
4.6.4 The brick culverts carrying the Doe Lea through the Puddlebank were removed in the 1970s. They will not
be reinstated but replaced by a clear-span aqueduct over the river, in order to suit modern flooding and
ecological requirements.
4.6.5 This section will include a new pedestrian & cycle bridge to connect the towpath to the multi-user trail
along the former Norbriggs cutting, along with a private farm access bridge at Huggester Farm. There will
be a weir and spillway opposite the Norbriggs cutting to return excess water to the river Doe Lea, as per
the historic arrangement at this location.
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5 PLANNING POLICY
5.1 Local Planning Policy
Chesterfield Borough Council Local Plan 2011-2031
5.1.1 The current Local Plan was adopted in July 2013. Restoration of the Chesterfield Canal is a key strategic
objective (S12) and the importance of the canal as integral green infrastructure is noted to the major
development sites at Waterside and the Staveley & Rother Valley Corridor. The specific impact of the
restoration in attracting visitors to the canal and wider borough is also noted.
5.1.2 Strategic Objective S12 states ‘Restore the Chesterfield Canal to a navigable state along all its length
within the borough’. Delivery of the proposed scheme will fully achieve this objective.
5.1.3 Figure 5.1 below shows an extract of the Local Plan ‘Submission Policies Map’ with the scheme proposal
superimposed upon it. The relevant identifiers from the key are included.
Figure 5.1: Extract of the Local Plan ‘Submission Policies Map’ with the proposal superimposed
5.1.4 With the exception of the short length between Eckington Road and the Trans-Pennine Trail Bridge, the
entirety of the scheme is within the green belt as defined by policy CS9 (Green Infrastructure &
Biodiversity). A significant proportion is also within the area of saved policy EVR2 (Development in the
Open Countryside and Other Open Land).
5.1.5 Within the background to policy CS9, the Chesterfield Canal corridor is recognised as a key element of
the borough’s identity. CS9 aims to protect and enhance the green infrastructure corridor, and restoration
of the Chesterfield Canal is entirely in line with the policy aims. It will enhance connectivity and improve
public access to the green infrastructure by formalising and improving the access along the canal, further
increasing opportunities for walking and cycling. Visual access to the local nature reserve will be
significantly enhanced without the need for intrusive access. Restoration of the canal will both conserve
and enhance the distinctive landscape character of this section of the Doe Lea valley, defined as it is by
the historic earth embankment on which the canal used to run.
Green Belt (Green Infrastructure &
Biodiversity) – CS9
Development in the Open Countryside &
Other Open Land – EVR2
Chesterfield – Staveley Regeneration
Route – (Major Transport Infrastructure)
CS21 & (Markham Vale) PS4
Future Extension
(NEDDC)
Restored Chesterfield Canal
Current Application
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5.1.6 Policy EVR2 follows broadly similar lines to that of CS9 but includes further specific conditions for the
types of development that will be permitted within the policy areas. The canal would be classed as
recreation and tourism development under the policy, and so permissible providing it satisfies the
conditions. The primary conditions are that the scale, siting, design, materials and landscape treatment
are such that the visual effect is minimised, and that the proposal does not detract from an area where
the character is vulnerable due to the prominence or narrowness. As the scheme is largely a restoration
and reinstatement of existing features, the only modification to the existing landscape is in terms of the
scale of the embankment, which will remain modest by comparison to the wider landscape setting.
5.1.7 Approximately the first 650m of the scheme, as measured from Eckington Road, is along the line of a
route preserved under policy CS21 (Major Transport Infrastructure). This route was originally preserved
as part of the Staveley Northern Loop Road proposals and it would appear that these have now been
superseded. Indeed, it is notable that in the new Local Plan currently in examination (see below), this
route has been removed from the replacement policy LP24. Notwithstanding that, restoration of the canal
would not preclude development of this road in the future, albeit it would be more complex.
5.1.8 Restoration of the Chesterfield Canal will also support delivery of the plan policies CS14 (Tourism and the
Visitor Economy) and CS19 (Historic Environment). CS14 specifically encourages proposals for tourism
development where they relate to the restoration and enhancement of the Chesterfield Canal, whilst the
restoration will also enhance the setting of the canal in accordance with CS19.
Chesterfield Borough Council Local Plan 2018-2033 (In examination, not yet adopted)
5.1.9 CBC is in the process of preparing a new Local Plan. This was presented for examination in June 2019
and the report of the examiner was issued in May 2020. The emerging plan is therefore well advanced
although not yet currently adopted.
5.1.10 In accordance with paragraph 48 of the National Planning Policy Framework, weight may be given to
relevant policies in the emerging plan according to: the stage of preparation of the emerging plan, the
extent to which there are unresolved objections to relevant policies, and the degree of consistency of the
relevant policies in the emerging plan to the NPPF. With regard to all criteria, on the scale set out in the
NPPF, the current status of the emerging plan means a greater weight can be given to the relevant
policies.
5.1.11 The relevant policies in the emerging plan are therefore presented to provide evidence for the future
direction of thinking with regard to the restoration of the Chesterfield Canal.
5.1.12 Strategic Objective S12 is proposed for retention, unchanged within the new Local Plan. Delivery of the
proposed scheme will fully achieve this objective as stated above.
5.1.13 A new policy is proposed to specifically consider the Chesterfield Canal, LP19. This is an updated and
enhanced version of the 2006 Local Plan policy EVR14 (Restoration of the Chesterfield Canal) which was
subsumed into CS9 as part of the current Local Plan. LP19 will safeguard the route of the Canal against
future development that prejudices the existing character and/or the future potential for improvement and
enhancement. It will also encourage adjacent development to conserve, enhance and restore the canal
along the original route wherever possible.
5.1.14 The key essence of policy CS9 (Green Infrastructure and Biodiversity) relevant to the restoration of the
Chesterfield Canal is proposed for retention within the new policy LP16 (Green Infrastructure).
5.1.15 No specific replacement for policy EVR2 is proposed, but the key essence of the policy is retained within
other proposed policies, including most notably LP1, LP2, LP3 and LP16.
5.1.16 Policy CS14 (Tourism and the Visitor Economy) is proposed for retention as policy LP8. There are two
minor additions proposed to the list of where tourism development will be encouraged, both of which are
relevant to the restoration of the Chesterfield Canal: ‘opportunities to encourage physical activity’ and
‘enhancing and improving access to the Green Belt, Green Wedges and Strategic Gaps’.
5.1.17 Policy CS19 (Historic Environment) is proposed for retention as policy LP22.
5.1.18 As noted above, there is a strip of land between Hall Lane and the borough boundary to the north-east
that is subject to policy CS21 (Major Transport Infrastructure). This area of land is proposed for removal
from the replacement policy LP24.
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Supplementary Planning Documents (SPDs)
5.1.19 There are no SPDs currently published by CBC that are applicable to this scheme.
5.1.20 It is noted that there is an SPD currently in development with regard to the Historic Environment. This
SPD is currently at the scoping stage and therefore no further detail on this is available and the scheme
can only be considered in light of the core Local Plan policies identified above.
Neighbourhood Plans
5.1.21 There are no current areas with a Neighbourhood Plan included in the scheme.
North-East Derbyshire District Council & Rotherham Metropolitan Borough Council
5.1.22 The proposals forming part of this planning application are wholly within the CBC LPA boundary.
However, the restoration project will include future lengths in the North-East Derbyshire (NEDDC) and
Rotherham (RMBC) LPA areas. It is therefore prudent to briefly consider the planning policy relating to
the future restoration works within these areas.
5.1.23 The NEDDC Local Plan was adopted in November 2005. The key planning policy is R12 (The
Chesterfield Canal), although the restoration receives specific mention at various other points throughout
the plan. Policy R12 safeguards the route of the Chesterfield Canal, including the alternative route
through Killamarsh, from development prejudicing future restoration, and permits proposals associated
with the recreational, leisure, nature conservation and historical potential of the Chesterfield Canal along
its route.
5.1.24 NEDDC has submitted a new Local Plan for examination, which recently restarted following a pause
associated with the change in political constitution of the council. The above policy is proposed for
retention as new planning policy ID8 (Chesterfield Canal), with modifications to reflect the revised
alternative route through Killamarsh.
5.1.25 The RMBC Local Plan was adopted in September 2014. It confirms the council’s support for the
restoration of the Chesterfield Canal in line with Strategic Objectives 8 (Landscape, historic environment
and settlement identity) and 9 (Greenspaces, sport and recreation), and policies CS19 (Green
Infrastructure) and CS23 (Valuing the Historic Environment). The Chesterfield Canal is identified as a
Strategic Green Infrastructure Corridor connecting the southern Rother Valley with Wales, Kiveton Park
and through to Worksop in North Nottinghamshire.
5.2 National Planning Policy
5.2.1 Guidance in the latest revision of the National Planning Policy Framework (February 2019) is consistent
with the adopted Chesterfield Borough Council Local Plan and does not require any further consideration
here.
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6 DESIGN & ACCESS STATEMENT
6.1 It must be stated at this point that the guidance about writing Design and Access Statements as schemes
themselves evolved could not be followed in this case. This proposal forms a part of the ongoing process
of connecting the isolated length of the Chesterfield Canal to the national network. As such, the broad
principles of the scheme, and much of the detail, have been in place for many years.
6.2 Design Rationale
6.2.1 As noted above, this length of the Chesterfield Canal restoration is dominated by the Puddlebank, and in
particular by the mining subsidence that has affected it since this length of the canal fell into disuse.
6.2.2 At Staveley Town Basin and at Renishaw, the canal has been restored to its original water level of
55.8mAOD. The canal was constructed on the level all of the way from Hollingwood to Killamarsh, a
distance of over six miles. However, a decision has already been taken to reduce the level underneath
the Staveley-Seymour railway, and the lock constructed at Staveley Town Basin to do so. At the time of
the Staveley Town Basin planning application, it was intended that a second lock would be constructed to
the east of the railway to return to the historic water level.
6.2.3 In the years since that application, further consideration has been given to the design of the Puddlebank
section. In particular this considered whether, given the mining subsidence, it would actually be preferable
to adopt a lower water level throughout this length and site the return lock closer to Renishaw, most likely
at Miner’s Crossing.
6.2.4 In reviewing the design in this manner, a number of design constraints have been evaluated. These
constraints and the impact they have had on the selection of a final design solution are set out below.
Design Constraints
6.2.5 The relevant water levels are 54.1mAOD at Eckington Road and 55.8mAOD at Renishaw (outside of the
boundaries of this application). Therefore, there is a need to raise the water level by 1.7m by means of
one or more locks between these two points.
6.2.6 There are five known utilities that cross the line of the canal between the railway and Bellhouse Lane.
Allowing for 1.5m water depth and 0.4m of additional protection slab over the utility, any service with a
crown level within 1.9m of the proposed water level at the crossing point would need to be diverted. The
five known utility services include: a 450mm diameter sewer with a crown level of approximately
52.8mAOD; a 900mm diameter sewer with a crown level of approximately 53.1mAOD; a 700mm diameter
water pipe with a crown level of approximately 51.5mAOD; a 500mm diameter water pipe with a crown
level of approximately 53.6mAOD and a 200mm diameter gas main with a crown level of approximately
53.7mAOD.
6.2.7 There needs to be a supply of water to the section of canal at Renishaw. The long pound between
Hollingwood and Killamarsh was the low point of this length. Water was predominantly supplied from two
feeds: the River Rother, which supplies the canal in Chesterfield and from where water cascades down
the canal at each lock; and the River Doe Lea, which supplied the canal via a lengthy take-off channel
that fed into the southern end of the Norbriggs Cutting. The latter has suffered from subsidence and
reinstatement of this supply is not currently practical. Therefore, the primary feed to the canal at
Renishaw must come from the canal at Staveley, and so water must be supplied around or through any
dropped pound. This will necessitate a passive siphon or active pumping depending on the scheme.
6.2.8 It is noted that the railway crossing is not considered as a direct constraint to the design of this section
of the canal. The water level at the crossing point was previously set by the Staveley Town Basin
application based on discussions with Network Rail.
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Defining the Design Options
6.2.9 Early development of the design solution for the Puddlebank is discussed in the Next Navigation West
report published by the Chesterfield Canal Partnership and publicly available on the Chesterfield Canal
Trust website. In summary, the choice of water level was never considered and would be set at
55.8mAOD throughout. The focus was instead primarily on the choice of plan alignment, in particular
whether the Puddlebank should be constructed on the original line or a new one. In order to minimise the
visual intrusion on the landscape, it was determined that the construction would be on the original line for
the majority of the length. However, where the canal historically followed the contours of the land to the
north of the Norbriggs Cutting, it was proposed to move the canal alignment to the east in order to
maintain the same relationship with the surrounding landscape.
6.2.10 The current proposals are for the canal to be retained on the original line and not relocated to the east.
This is in response to the preference of the landowners in this area.
6.2.11 As such, the design options defined for evaluation were all assumed to follow the original line and the
primary differences would be in the adopted water level. Three options were evaluated:
• ‘High Level’
Adopt a water level across the Doe Lea valley of 55.8mAOD, matching the historic level. This
would entail installing a lock immediately east of the Staveley-Seymour railway. There would be
no need for diversion of utilities based on the level (it may still be necessary to divert either the
gas main or the smaller water main to enable construction of Bellhouse Lane Bridge). The siphon
pipe planned to feed water from Staveley Town Basin to the Puddlebank could be installed.
• ‘Low Level’
Adopt a water level across the Doe Lea valley of 54.1mAOD to match the current dropped pound
level at Eckington Road. This would require diversion of four of the utility services (all but the
deepest water main). A lock would be installed in the vicinity of Miner’s Crossing, to the north of
this scheme and within the NEDDC LPA. This would necessitate permanent pumping of water
from the 54.1mAOD pound to the 55.8mAOD pound at Renishaw due to the lack of other water
supplies at this point.
• ‘Intermediate Level’
Adopt a water level across the Doe Lea valley of 55.0mAOD, by installing locks at both of the
locations identified above. This would allow the canal to cross the two sewers but would still
necessitate diversion of the smaller water main and the gas pipe. A controlled siphon pipe and a
permanent pumping system would both be necessary.
Selecting an Overall Design Solution
6.2.12 In order to select the most appropriate solution, the three options above were evaluated against the
following criteria:
• Cost, including the initial construction costs and maintenance costs
• Construction impacts
• Programme
• Impact upon installed services
6.2.13 An outline cost comparison was carried out, focussing primarily on the cost differential between the
options. Much of the work required does not vary across the scheme and so this was not included. The
cost comparison therefore focussed on the earth-moving, locks, water control mechanisms and the
diversion of utilities.
6.2.14 The High Level option was the cheapest solution, followed by the Low Level option and with the
Intermediate Level option as the most expensive. The cost comparison is particularly sensitive to two
large unknowns – the cost of purchase of the clay materials required to raise the level of the Puddlebank
and the cost of diverting the two sewers. The former has a significant impact on the cost of the High Level
option and is mitigated by the offer of approximately 95% of the required material free of charge. The
latter has a significant impact on the cost of the Low Level option. Preliminary estimates of £500,000 per
sewer were used in the analysis, and based on budget estimates obtained for the diversion of the smaller
water main and the gas pipe the sewer diversion costs are likely to be under-estimated.
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6.2.15 The resulting effect is that there is greater certainty in the relative cost of the High Level option, whilst the
Low Level option is most likely to get more expensive. Therefore, the High Level option remains
preferable on cost grounds.
6.2.16 In assessing the construction impact, the impact of the construction work on the site is largely
independent of the water level. Instead, the primary consideration is the transport of the clay materials
required to raise the level of the Puddlebank, which dramatically increases as the water level increases.
For the Low Level option, approximately 75,000m3 of clay would need to be imported. This increases to
approximately 175,000m3 of clay for the High Level option.
6.2.17 As noted above, approximately 160,000m3 of clay has been offered to the scheme free of charge. This is
currently sited on the former Foxlow tip site. This material can be transported under the Midland Mainline
freight railway using the existing bridge alongside the River Rother, and then through the north of the
Hartington reclamation scheme and onto the mothballed Staveley-Seymour railway. From this location it
can proceed along the railway and directly onto the construction site, avoiding the use of any public
highways. Preliminary discussions on this proposal have taken place with representatives from Network
Rail who have agreed in principle, subject to detailed discussions.
6.2.18 Being able to transport the significant majority of the clay off the public highway mitigates the primary
construction impacts of the works on the local population. There is therefore little discernible difference
between the construction impacts of the different design options.
6.2.19 The Chesterfield Canal Trust has set a goal of completing restoration of the canal by 2027. To achieve
this ambitious programme, rapid progress needs to be made on this scheme, in order to link the restored
canal at Staveley with the semi-restored canal at Renishaw. It is therefore preferable to proceed with the
design option that can be pursued quickest. In this case, the preference is therefore for the High Level
option, avoiding the lengthy lead-in associated with the utility diversions.
6.2.20 As outlined, above the scheme will impact upon a number of installed utilities. These include the five
identified in paragraph 6.2.6 above, along with an extensive land drainage system installed in the
farmland north of the Norbriggs Cutting.
6.2.21 At Bellhouse Lane, the requisite diversions are set out in paragraph 6.2.11 above. The water main and
gas pipe diversions would be relatively simple, but the sewer diversions are much more complex. These
are large sewers that feed into the treatment plant to the north of the scheme area. To reduce the crown
level would most likely require splitting the pipe into multiple smaller pipes and/or introducing pumping
along the route. Neither of these are ideal for the long-term maintenance of the sewers, and thus avoiding
the need to modify them is the first preference. Taken together with the other utilities, the High Level
option is the first preference, then the Mid Level and lastly the Low Level.
6.2.22 For the land drainage system, the ideal situation would be that the land drainage could discharge directly
into the canal. However, to do this the drains would need to have an invert level higher than the proposed
water level, which is not the case. Therefore, the drains need to pass underneath the canal. Where the
proposed bed level is higher than the land drains, this needs no further consideration. However, if the
drains are within the water depth (i.e. an invert level between canal water level and bed level), either a
siphon or pumped drainage system would be necessary. Both of these would require additional
maintenance and are liable to failure, and as such would not be acceptable to either the canal or the
adjacent landowner. Based on these criteria, the High Level option is the best for mitigating the impacts
upon the drainage, as the Low Level and Mid Level options would both impact upon a portion of the
installed land drainage to the north of the scheme.
6.2.23 In conclusion, the High Level option is the best solution on the grounds of cost, construction programme
and mitigating the effect on utilities. The only major negative to the High Level option would be the
construction impact associated with road haulage of the significant quantities of clay materials required to
raise the Puddlebank, and this has been mitigated by the proposals to transport the clay off-road. As
such, the High Level option is the one adopted in this scheme.
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6.3 Detailed Design, Appearance & Landscaping
6.3.1 The layout and details of the scheme are discussed further below. The text should be read in conjunction
with the scheme drawings listed in the introduction to this Planning Statement.
6.3.2 In general, the scheme is described as if travelling along the canal from the west (Eckington Road),
proceeding first east to Bellhouse Lane, then north-east towards the end of the Norbriggs Cutting and
finally turning north to the end of the scheme at Hague Lane.
6.3.3 More detail on each of the key features of the scheme is given after the general description, and is cross-
referenced by the paragraph number given in brackets.
General Description
6.3.4 The section of the canal forming part of this scheme will extend from the restored canal below Eckington
Road, proceeding east at a water level of 54.1mAOD. Immediately after the end of the existing bridge
structure, the offside (south) bank will revert to a soft bank with sloping sides. The towpath side (north)
will continue as an engineered vertical bank with brick facing and a stone coping.
6.3.5 The canal will narrow through the original railway bridge (6.3.16) and on leaving the footprint of the
railway will immediately enter the new Railway Lock (6.3.21). This will raise the water level back to the
original water level of 55.8mAOD.
6.3.6 At the head of the lock, the Trans-Pennine Trail will cross the canal on a high-level bridge (6.3.29). The
canal will widen out again and continue to run east, with a vertical engineered bank on the towpath side
and soft banks on the offside. The towpath between the lock and Bellhouse Lane will be suitable for
short-term visitor moorings.
6.3.7 At the north end of Bellhouse Lane, the canal will be crossed by a new access bridge (6.3.31). The canal
will start to turn towards the north-east and will follow a gently winding course until it reaches the
Norbriggs Cutting. Immediately to the east of Bellhouse Lane bridge, a winding hole will be constructed at
the location of the former Bellhouse Basin.
6.3.8 The first evidence of the Puddlebank (6.3.12) will start immediately to the east of Bellhouse Lane bridge,
where land levels have dropped due to mining subsidence. This will become more pronounced further
along this length until it reaches Doe Lea Aqueduct (6.3.24). Typically, the channel will retain soft banks
other than across the aqueduct itself and for an approach length either side, which will use engineered
banks.
6.3.9 To the north east of the aqueduct, the canal reaches the junction with the former Norbriggs cutting. A new
pedestrian and cycle bridge, Packsaddle Bridge, will connect the multi-user trail along the cutting with the
towpath (6.3.33).
6.3.10 The canal then turns to the north and follows a gently winding course all the way to Hague Lane. As the
route follows the original line, which has since suffered from mining subsidence, the canal will continue to
be on a low level embankment for the majority of this length. Other than at bridges, soft banks will be
used throughout, with opportunities taken for offside habitat creation through the form of reed shelves.
6.3.11 Throughout the scheme, the towpath will run along the left hand side of the water when viewed as if
travelling from Eckington Road towards Hague Lane. The towpath will be constructed of compacted stone
chippings with a hawthorn hedge separating it from the private farmland.
The Puddlebank
6.3.12 The Puddlebank is the dominating structure of this section. It is a large earth embankment that allows the
canal to cross the Doe Lea valley without having to descend to the valley floor. It was a pioneering
structure when first constructed and is believed to be the last part of the Chesterfield Canal to be
completed in 1777.
6.3.13 Significant elements of the original Puddlebank remain. However, the landscape in this area has suffered
drastically from mining subsidence, and in places the valley floor has dropped by over four metres. In
combination, the canal banks were bulldozed out in the 1970s, with the resulting material used to
compensate for subsidence in the surrounding farmland, and several channels were cut through for
drainage and a pipeline. Together, these mean that extensive earth works are necessary to raise the
height of the Puddlebank to its historic level, making this the largest earth-moving operation in the
restoration of this section of the canal.
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Figure 6.1: Remains of the Puddlebank, viewed from within the Norbriggs Flash LNR
6.3.14 The Puddlebank will begin almost immediately after Bellhouse Lane. Whilst the dominating structure
extends to the junction with the Norbriggs Cutting, the remainder of the section will also be on an
embankment, albeit much smaller.
6.3.15 The raised Puddlebank will utilise imported clay material combined with the existing, subject to detailed
design considerations. Construction will be in accordance with modern requirements for earth-cored
embankments.
Crossing the Staveley-Seymour Railway
6.3.16 When the railway was originally constructed, a bridge was built to carry it over the canal. This was later
widened. After the canal fell into decline, Network Rail purchased the canal underneath the structure to
enable it to remove the steel girder bridges and infill the canal to form an earth embankment.
Figure 6.2: The old railway bridge, viewed looking west towards Eckington Road
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6.3.17 The railway line is currently mothballed and the track removed. In 2017, a licence was obtained by
Derbyshire County Council to enable volunteers of the Chesterfield Canal Trust work party to excavate
and investigate the condition of the original bridge structure. It has been found to be in excellent
condition, only requiring some minor remedial repairs.
6.3.18 Given the condition, it is proposed to reuse the original structure. As with much of the ground in this area,
it is lower than previously due to mining subsidence. Additionally, it is likely that any reinstatement of the
railway would require a thicker bridge deck structure and ballasting arrangement than previously.
Together these have dictated the lowering of the water level through the structure.
6.3.19 A new engineered channel will be constructed between the walls of the original structure to ensure that
the lowered invert does not compromise the structural integrity of the existing abutments. This will also
allow for an increased towpath width to suit the requirements of the Trans-Pennine Trail and for the
installation of the siphon pipe.
6.3.20 There is no intention to reinstate a railway bridge deck as part of this scheme.
Railway Lock (No. 5b)
6.3.21 The new lock will be located immediately east of the railway bridge. A standard 22m x 2.3m chamber will
allow for a single full-length narrowboat to rise by 1.7m from the dropped pound at 54.1mAOD to the
historic pound level of 55.8mAOD.
6.3.22 The siting of the lock allows for the historic pound level to be regained prior to the crossing of a cluster of
utilities between the proposed Trans-Pennine Trail Bridge and Bellhouse Lane. Four of these utilities
would need to be diverted if the lock were located any further to the east.
6.3.23 The lock construction will be very similar in appearance to that of the recently completed Staveley Town
Lock (no. 5a), located approximately 450m to the west at Staveley Town Basin. A reinforced concrete
foundation and walls will be faced in red-brick and topped off with a stone coping. Lock gates will be
constructed in timber, with mitred double gates at the bottom end and a single gate at the top end.
Figure 6.3: Staveley Town Lock (no. 5a), at Staveley Basin. Railway Lock (no. 5b) will be similar in
construction and appearance
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Doe Lea Aqueduct (No. 14a)
6.3.24 Originally, a pair of small brick-lined culverts were constructed to convey the River Doe Lea through the
Puddlebank. These were removed in the 1970s after the canal had fallen derelict, leaving the river in an
open channel.
6.3.25 Modern requirements for flood mitigation and ecological connectivity preclude reinstatement of the
original culverts. The canal will therefore cross the river on a new aqueduct. This will have a 37m clear
span across the existing opening, in order to maintain the current embankment profile. Retaining the
existing profile means that the flood profiles remain unchanged and the existing habitat connectivity either
side of the Puddlebank will not be affected by the scheme.
6.3.26 The new aqueduct will be constructed from concrete or steel subject to detailed design and contractor
involvement. It will bear onto piled foundations at either end and will have no intermediate piers. The
towpath will be integral to the aqueduct, and as such this will replace the existing steel footbridge across
the river at this location.
Bridges
6.3.27 There will be four new bridges over the canal along this section:
• Trans-Pennine Trail Bridge (No. 13c)
• Bellhouse Bridge (No. 14)
• Packsaddle Bridge (No. 15)
• Red Bridge (No. 16)
6.3.28 The scheme starts at Eckington Road Bridge (No. 13) which is existing. Additionally, the planning
drawings also show White Bridge (No. 17). The latter is outside of the planning boundary and will form
part of a future application to NEDDC, but is included on the scheme drawings for reference to aid
understanding of the future connectivity.
6.3.29 The Trans-Pennine Trail Bridge (No. 13c) will cross the canal just beyond the head of Railway Lock
(No. 5b). This will provide a route for pedestrians, cyclists and equestrians between the Arkwright Trail to
the south and the Trans-Pennine Trail (TPT) to the north, replacing the existing circuitous system of
ramps and paths that crosses the canal line at approximate towpath level. Note that the existing
connection between the TPT and the canal towpath will be re-routed along the towpath through the
railway bridge and up to the side of the lock and thus will not cross the canal to the west of the railway.
6.3.30 This bridge will be a high-level bridge, approximately six metres above the canal. It will replace the
original Great Central Railway bridge that has been demolished, although it will be very different in style.
Instead, the structure will be similar in appearance to the existing canal bridges at Constitution Hill,
Staveley and Foundry Bridge, Renishaw, albeit it will have a longer span and minimal abutments.
Figure 6.4: The original GCR bridge, shown here in 1987 after the canal had been infilled. The
bridge has since been replaced by a system of ramps
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6.3.31 Bellhouse Bridge (No. 14) will be located at the end of Bellhouse Lane. It will replace an original bridge
that has since been demolished. Its primary purpose is to facilitate landowner access to the farmland to
the north of the canal, but it will also provide pedestrian, cycle and maintenance vehicle access from
Bellhouse Lane onto the canal towpath and also to the TPT.
6.3.32 The bridge will be suitable for agricultural vehicles, requiring a wide bridge with a relatively flat deck. The
structure will be constructed from reinforced concrete with a brick facing, similar to the style previously
used for the reinstatement of Bilby Lane bridge.
Figure 6.5: Bilby Lane bridge, constructed in 2002 to remove the last obstacle to navigation
between Chesterfield and Staveley, will form the template for both Bellhouse Bridge
(no. 14) and Red Bridge (no. 16)
6.3.33 Packsaddle Bridge (No. 15) is located across the main line of the canal at the junction with the
Norbriggs Cutting. It replaces an original bridge that has since been demolished, and will be a pedestrian
and cycle bridge to connect the multi-user trail along the Norbriggs Cutting to the canal towpath. It will be
similar in style to Foundry Bridge, Renishaw, with a reinforced concrete structure faced in red-brick, and
ramped approaches.
Figure 6.6: The original Packsaddle Bridge, which has since been removed, will be replaced by a
raised bridge suitable for navigation
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Figure 6.7: Renishaw Foundry Bridge, opened in 2009 on the isolated section of canal restored at
Renishaw. This will form the template for Packsaddle Bridge (no. 15), and a similar
deck style will be used for the longer span Trans-Pennine Trail Bridge (no. 13c).
Photo © Eckington Parish TV
6.3.34 Red Bridge (No. 16) will be sited on the existing farmer’s access track north of the Norbriggs Cutting. It
replaces an old bridge that has since been demolished. It will be very similar in style and construction to
Bellhouse Bridge. An access track will be included linking the towpath around the bridge, which will only
be utilised by maintenance vehicles that cannot access under the bridge. There will be no public access
to the farmland.
Water Control
6.3.35 Fundamental to the operation of the canal is the supply and management of water. The pound between
Railway Lock and Killamarsh will be a high spot on the canal which has no natural water supply.
Therefore, water will be supplied via a siphon pipe from Staveley Town Basin. A weir will be included at
Norbriggs.
6.3.36 The siphon pipe will allow the existing supplies to Staveley Town Basin to continue beyond Railway
Lock. A buried pipe will be installed from the head of Staveley Town Lock to the head of Railway Lock.
There is existing provision for this pipe in the structures of the Ireland Close bridge and the Eckington
Road bridge. Provision is made in the design for the installation of this pipe through the Staveley-
Seymour railway bridge (6.3.16). An outlet for periodic flushing of the siphon will be included alongside
the existing Hartington side weir, which will be the low point of the pipe.
6.3.37 Opposite the Norbriggs Cutting, there are the remains of an original weir. As with the entirety of the canal
in this area, it has suffered from mining subsidence and so a replacement weir will be constructed. This
will allow excess water to drain back to the Doe Lea. The towpath will be carried over the weir on a
concrete slab, similar to the arrangement at the existing Hartington side weir. Water will discharge onto a
concrete or brick lined spillway before discharging to an open channel along the foot of the Puddlebank.
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Drainage
6.3.38 The central section of the Puddlebank is well established from the historical construction. However, due
to the mining subsidence referred to previously, it will be necessary to extend the embanked length of
canal to the North and to the South-West of the original embankment. This will interrupt the existing
surface water flows and introduce the potential for ponding or water-logged ground within the existing
arable farmlands.
6.3.39 Additionally, there is extensive land drainage already installed at Huggester Farm and it is essential that
the canal restoration does not prevent this from operating.
6.3.40 On the farmland to the South-West, where there have been no records or evidence of existing land
drainage discovered, a new ditch will be provided at the base of the embankment. A piped section will be
installed under the access ramp from Bellhouse Lane bridge. The ditch will discharge at two points. At the
western-most low point, a piped discharge will take water underneath the embankment and feed the flood
compensation area, which will be excavated deeper than required in order to retain some water in the
permanent state. At the eastern extents, the ditch will run out into the existing wetlands adjacent to the
river.
6.3.41 Where the existing land drainage is installed at Huggester Farm this will be protected and enhanced as
necessary. The existing drainage will typically be left in-situ underneath the embankment, but new
connections and collector drains will be installed upslope. Additionally, a new collector drain will be
installed at the base of the embankment on the downslope to ensure that run-off from the embankment
does not run directly across the farmland.
6.3.42 All new drainage will use existing discharge points.
6.4 Access
6.4.1 Waterways, and especially navigable ones where boats enliven the scene, are enduringly popular
features of both urban and rural England. It is crucial, therefore, that the proposals for restoring this
section of the Chesterfield Canal make full allowance for the public to gain access to enable them to
enjoy what will be an important asset to the area. The canal may be historic, and partial access to it
already available, but this scheme will be a step change and so this section of the statement will consider
access in its widest terms.
‘Inward Access’ from outside the area
6.4.2 The primary purpose of restoring any waterway is to make it accessible to boats. Whilst historically these
would have been solely working boats, in the modern age leisure craft will dominate.
6.4.3 Until the entirety of the restoration scheme is completed and the isolated length of canal between
Chesterfield and Renishaw is connected to the rest of the network, boat users are likely to be limited to
the Chesterfield Canal Trust trip boats and the occasional visiting trailable boat. The latter can access the
canal using slipways constructed at Staveley Town Basin and at Tapton Lock, and no further access
provision is required as part of this scheme.
6.4.4 Leisure boating access may increase in the medium-term, prior to the completion of the remainder of the
restoration scheme, if one or both of the proposed marinas at Staveley Town Basin and the Staveley
Works site (as part of the Chatsworth Settlement Trust proposals) are developed. This is particularly likely
if one or both of the proposed marinas include the option for residential moorings. Such boats would be
lifted into the canal by crane, for which there is dedicated provision already made at Staveley Town Basin
and so no further access provision is required as part of this scheme.
6.4.5 Visiting boaters generally need little in the way of facilities, with the main requirements being for the
provision of drinking water and the disposal of domestic waste and sewage. Dedicated facilities are
already provided below Tapton Lock, and additional facilities will be provided in due course at Staveley
Town Basin. There is no need, nor is it appropriate for the setting, to consider additional facilities within
the scheme proposed here.
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6.4.6 Dedicated visitor moorings will be available at Bellhouse Lane for short-term visitors. These will have
bollards and/or rings to enable boaters to tie up. Bollards will additionally be provided at lock mooring
points, to enable boaters to tie up temporarily whilst setting the lock. There is typically little restriction on
mooring locations on a canal, but elsewhere boaters will use their own metal spikes driven into the bank
in order to secure their ropes.
6.4.7 Typical canal narrowboats, and indeed many trailable boats, are longer than the standard width of the
canal. It is therefore necessary to ensure that there are suitable points for them to turn (known as
‘winding’). Winding holes are proposed at the site of the former Bellhouse Basin, at the junction with the
Norbriggs Cutting and at the northern end of the scheme. No winding holes are provided at the western
end of the scheme as it will be connected to the navigable canal already restored which includes suitable
provisions, including the widening known as Hartington Harbour immediately west of the proposed
scheme.
6.4.8 The re-opening of a restored canal will bring boaters into areas that many of them would not otherwise
have visited. Additionally, there is always an initial surge in boating upon opening as boaters take the
opportunity to explore a new length of the navigable network. In both cases, the surrounding area profits
from the money spent by boaters in local shops, pubs and restaurants. The canal therefore makes the
surrounding area more accessible to the wider public and ultimately more prosperous.
Access for the general public
6.4.9 Towpaths on English waterways are typically a shared space, with walkers and boaters often sharing the
path with cyclists, anglers and, in some instances, horses. The latter may be ridden or used to tow boats,
which, whilst relatively rare today, was the original purpose of a towpath.
6.4.10 The towpath from Bellhouse Lane to Hague Lane will primarily be used by walkers, as the Trans-Pennine
Trail provides an alternative and preferable route for cyclists and mounted horses. However, some cycling
use is to be expected from users joining the towpath at Packsaddle Bridge (from the existing multi-user
trail along the Norbriggs Cutting). A 3m wide towpath is therefore proposed for the cycle route proceeding
north from Packsaddle Bridge (since this is expected to dominate), with a slightly narrower 2.5m wide
towpath across the Puddlebank in order to minimise the earth-moving required.
6.4.11 The canal towpath is dedicated as the Cuckoo Way for the entirety of the 46 miles of the Chesterfield
Canal. For the majority of this scheme, the footpath is a public right of way, dedicated as Staveley
Footpath No. 71.
6.4.12 Throughout this length of canal, the towpath will be on the left of the canal when travelling from Eckington
Road towards Renishaw. This maintains the historic relationship with the canal but does mean that the
towpath is on the far side of the canal from the primary adjacent housing areas at Lowgates and Mastin
Moor. The water therefore forms a barrier to ready access from these communities, and so dedicated
access points will be provided. This has the benefit of controlling access and not encouraging deviation
from the existing footpaths, which is especially beneficial in the Norbriggs Flashes local nature reserve.
6.4.13 In total, there are six access nodes into the scheme:
• Canal west of Eckington Road
• Franklyn Drive
• Trans-Pennine Trail & Arkwright Trail
• Bellhouse Lane
• Packsaddle Bridge
• White Bridge
6.4.14 For more detail of all of the modifications proposed to the existing public rights of way and undedicated
routes discussed below, refer also to the scheme drawings referenced in the introduction to this Planning
Statement.
6.4.15 From the restored canal west of Eckington Road, access will continue along the towpath directly from
the previously restored canal. This is the existing Staveley FP1 and part of the Trans-Pennine Trail (TPT),
also for use by horses and cyclists.
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6.4.16 From Franklyn Drive, there is an existing undedicated path connecting the canal corridor with the
junction between Franklyn Drive and Eckington Road. This will be partially realigned during the scheme
and connect into the canal towpath and the TPT. It will be suitable for pedestrians, horses and cyclists.
6.4.17 The existing access arrangements from the Trans-Pennine Trail (TPT) and the Arkwright Trail will be
the most altered as part of the scheme. At present, the length of the canal towpath designated as part of
the TPT connects to the Arkwright Trail via Staveley FP50 & Staveley FP49. Together they connect to the
northbound TPT via Staveley BW48. As part of the scheme, Staveley FP50 will be diverted through the
railway crossing to connect with Staveley FP71 (the canal towpath heading east). The existing
connections from Staveley FP71 to the northbound TPT will be reprofiled, and a new access bridge will
be constructed to connect the Arkwright Trail to the northbound TPT. Therefore, access and will be
maintained for all routes and the connections from the Arkwright Trail and the canal towpath to the
northbound TPT will be simplified. All of these connections will be suitable for pedestrians, horses and
cyclists.
6.4.18 At the northern end of Bellhouse Lane, access will be available to pedestrians and cyclists over
Bellhouse Bridge, connecting into the canal towpath. This will also maintain the existing connectivity
between Bellhouse Lane and the TPT.
6.4.19 At the junction with the Norbriggs Cutting, Packsaddle Bridge will be constructed. This will allow
pedestrians and cyclists to cross over the canal and connect to the towpath from Staveley FP22. The
latter is the multi-user trail along the Norbriggs Cutting, and other footpaths within the nature reserve and
surrounding farmland connect into this prior to its junction with the main line of the Chesterfield Canal.
6.4.20 White Bridge is located immediately to the north of the scheme. The bridge itself is within the NEDDC
LPA and is not included in this scheme. At present, the access track from Hague Lane to the sewage
treatment plant is designated as Eckington FP153 and the canal towpath continuing north is designated
as Eckington FP162. Access to both will be available from the end of the restored canal path and will be
maintained when White Bridge is constructed as part of any future scheme.
6.4.21 Throughout, there will be no steps along any of the routes and gradients will be restricted to a maximum
of 1 in 20 to allow for wheelchair access. The paths will typically be constructed from compacted stone
similar to the towpath on the existing restored lengths of canal.
Maintenance Access
6.4.22 The restored canal will require access for routine maintenance, typically including grass cutting and
vegetation clearance, bin emptying, management of water control and statutory inspections. Additionally,
lock gates typically need replacing every 25-40 years.
6.4.23 Throughout the scheme, the towpath will be suitable for maintenance vehicles. The access points for
these will be gated and padlocked to ensure that no unauthorised vehicles can access the towpath.
Where bridges would not have sufficient vertical clearance for maintenance vehicles, alternative access
will be provided around them. This is shown on the scheme drawings at Packsaddle Bridge and Red
Bridge. At the latter, the access links to the farmland will be for maintenance vehicles only and there will
be no public access of any kind.
6.4.24 Bellhouse Lane is also currently used for maintenance access to the Trans-Pennine Trail. This route will
be preserved, but in order to minimise regular interaction between maintenance vehicles and users of the
footpaths, a separate access route will be provided between Bellhouse Lane and the TPT, which will be
for maintenance vehicles only. The area between this maintenance access route and the Bellhouse Lane
moorings will be retained for silt deposition in the course of routine dredging works along the canal.
6.4.25 Access to Railway Lock for the purposes of replacing lock gates will be available from Bellhouse Lane.
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Construction Access
6.4.26 The primary construction access points will be from the south-western corner of the scheme, divided into
transport of clay along the railway, as noted in 6.2.17 above, and road access from Ireland Close (A6192
Northern Loop Road). From these access points, materials will be moved along the route of the canal.
6.4.27 If it is not possible to transport clay along the railway, e.g. due to refusal by Network Rail or technical
limitations, the clay would need to be transported by road. The road route would be to turn left out of the
Foxlow tip site, using the existing signal-controlled junction, then turn left at the roundabout between Hall
Lane and Ireland Close, before left turning into site. This would not route lorries through the town. It is
noted that part of the route (along Ireland Close) would be shared with the Hartington Reclamation route
and require coordination within a suitable Traffic Management Plan.
6.4.28 Additional road access may be obtained from the northern limit of the scheme off Hague Lane. This is an
existing access route used for lorries into the Sewage Treatment Plant so is suitable by inspection. It will
require coordination within a suitable Traffic Management Plan, and it is suggested that this should form a
planning condition that can be approved in coordination with the chosen contractor when appointed.
6.4.29 To allow construction works to take place east of the river without significant transport of material by road,
a temporary access bridge is proposed over the Doe Lea to the north of the aqueduct construction site.
This will be subject to the appropriate consent process with the Environment Agency alongside the permit
for the permanent works.
6.4.30 No construction access will occur along Bellhouse Lane other than that already approved under scheme
CHE/18/00602/FUL for the Chesterfield Canal Trust volunteer work party compound.
6.5 Conclusion
6.5.1 The re-building of the last section of the canal in Chesterfield borough represents an important step in the
restoration of the Chesterfield Canal to a fully navigable standard throughout its 46-mile length, ultimately
bringing added prosperity and health benefits to the area. The design will ensure that the original
character of this lost section of canal will be re-created, adding a high-quality landscape, leisure and
environmental asset to the Staveley area. The design will also ensure that the canal can be enjoyed by all
sectors of the community via easy access to and along the towpath.
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7 SUMMARY OF SUPPORTING DOCUMENTATION
7.1 For full details, refer to the supporting documentation referenced in each section below. This summary is
provided for convenience only.
7.2 Ecology
Phase 1 Habitat Survey and Preliminary Ecological Appraisal (PEA)
7.2.1 The Phase 1 survey was carried out in Summer 2018. This identified where appropriate mitigation works
could be determined directly and where further survey work would be required.
7.2.2 Additional survey work was recommended for a number of Protected Species as listed below. These
surveys have been completed or are in progress at the time of application.
• Great Crested Newts (eDNA sampling complete, population survey ongoing – refer to ‘Protected
Species Surveys – Great Crested Newts’ below)
• Otter (survey complete – refer to ‘Protected Species Surveys – Doe Lea’ below)
• Water Vole (survey complete – refer to ‘Protected Species Surveys – Doe Lea’ below)
• White-Clawed Crayfish (survey complete – refer to ‘Protected Species Surveys – Doe Lea’ below)
• Badger (survey complete – refer to both ‘Protected Species Surveys – Doe Lea’ and ‘Protected
Species Surveys – Puddlebank’ below)
• Reptiles (survey complete – refer to ‘Protected Species Surveys – Puddlebank’ below)
• Bats (survey ongoing – refer to ‘Protected Species Surveys – Puddlebank’ below)
Protected Species Surveys – Great Crested Newts
7.2.3 As recommended within the PEA, further survey work was carried out to identify whether Great Crested
Newts (GCN) are present within 500m of the scheme. Identified ponds are shown on the map in figure 7.1
below. The survey work was carried out in two stages, using environmental DNA (eDNA) testing followed
up with a full population survey in the event of a positive eDNA result.
7.2.4 The first phase of eDNA testing was carried out on all identified ponds in spring 2019, with the exception
of the single pond owned by the Coal Authority which denied access on health and safety grounds. They
did not possess any details for GCN activity in this pond and so it has not been possible to confirm the
presence or absence of GCN at this location. This pond is located over 200m from the canal, separated
by the TPT, access to the sewage works and active farmland. It is therefore considered unlikely that the
canal restoration scheme would have any impact on GCN activity at this pond, should there be any.
7.2.5 During separate surveys conducted on the Puddlebank in early 2020, additional standing water bodies
were identified in the farmed areas of the Norbriggs Flash LNR. Additional eDNA testing was carried out
on these in spring 2020.
7.2.6 One pond (referred to as ‘Pond 1’ on Figure 7.1 and in the detailed report), the main water body within the
Norbriggs Flash LNR, returned a positive eDNA test. A full population class assessment is therefore
being conducted on this pond in spring 2020. This survey is ongoing at the time of submission of the
planning application and the results will be updated when available.
7.2.7 A negative eDNA result was returned for all other ponds tested.
7.2.8 The results of the GCN surveys are included in two parts:
• Ponds labelled as ‘MEGZ Pond xx’ in figure 7.1 were tested as part of ongoing surveys being
carried out for the Markham Vale development, which includes the Staveley Basin site. These
results are included in the document titled ‘GCN eDNA (MEGZ Ponds)’
• All other survey results are included in the Protected Species Survey report for the Puddlebank
(see below)
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Figure 7.1: Location of identified ponds (note Pond 3 is an isolated length of the canal at
Renishaw and does not relate to this scheme)
Protected Species Surveys – Doe Lea (White-Clawed Crayfish, Water Vole, Otter &
Badgers)
7.2.9 From the PEA, a first group of surveys were identified clustering on the river Doe Lea, including White-
Clawed Crayfish, Water Vole and Otters. As Badgers could be active on any part of the extended site,
they were also included in this phase.
7.2.10 A 450m stretch of the river was surveyed, centred on the site of the Doe Lea aqueduct. Surveys were
undertaken in July and October 2019.
7.2.11 There was no evidence of White-Clawed Crayfish or the non-native Signal Crayfish. On closer
inspection, a large majority of the river was found to be unsuitable for White-Clawed Crayfish. No further
survey work or mitigation was recommended.
7.2.12 There was evidence of historic Water Vole presence but no signs of recent occupation. As such, an
inspection prior to the start of site works has been recommended to confirm any recent occupation.
7.2.13 Evidence was identified to suggest Otters are active in the area, although there was no evidence that
they are resting in the vicinity of the works. Suitable construction mitigations to avoid a barrier to otter
movement and prevent them from entering the site are recommended.
7.2.14 Badger survey work was limited due to vegetation growth. Additional survey work was recommended,
and this is incorporated in the Puddlebank surveys below.
Future Extension
(NEDDC)
Current Application
Zone within 500m
of application
Pond 1
Pond 2
Pond 4
Restored
Chesterfield
Canal
MEGZ Pond VI MEGZ Pond V
Ponds within MEGZ
surveys found to be dry
Additional standing water
bodies identified in 2020
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Protected Species Surveys – Puddlebank (Reptiles, Bats & Badgers)
7.2.15 The second group of surveys identified from the PEA followed the restoration route, including Reptiles,
Bats & Badgers.
7.2.16 Surveys for this element started in January 2020. Reptile and Badger surveys concluded in May 2020.
Bat surveys are due to conclude in Summer 2020 along with the population class assessment for GCN. A
draft report is included with this application and will be updated on conclusion of the final surveys.
7.2.17 Badger information is confidential and so is not discussed here. Mitigation methods are proposed.
7.2.18 There was no specific evidence of Reptiles found during the surveys, although the possibility of their
presence remains strong. A precautionary method statement is suggested for the construction, to include
how to proceed if reptiles are discovered.
7.2.19 Bat surveys were divided into two stages. A ground level tree assessment was carried out to determine
trees or other features with the potential to provide suitable bat roosts. From this, a total of seven trees
were identified, three of which had a potential greater than ‘low’ and were thus recommended for further
surveys. Activity surveys are currently ongoing on these three trees and the results will be included in the
updated report when completed.
Summary
7.2.20 In conclusion, the ecology reports have identified that the impact of the canal restoration on the local
biodiversity is very low, subject to the mitigation and compensation measures identified being
implemented.
7.2.21 The reports further highlight that the canal restoration is an excellent opportunity to increase the
biodiversity value of the area and provide a green corridor for local wildlife.
7.3 Flooding
7.3.1 This section of the canal crosses the Doe Lea valley. Therefore, it is critical to understand the importance
of the canal restoration works on the flood behaviour in the area. The submitted Flood Risk Assessment
(FRA, document reference CKJ-JBAU-XX-00-RP-HM-0001) assesses the impacts in full, with a brief
summary presented here for convenience.
Flooding effects arising due to the scheme
7.3.2 A large majority of the scheme is already sufficiently escarped or embanked to be classified as flood zone
1. Indeed, for much of its length, the canal forms the boundary between flood zones 1 and 2, as indicated
in figure 4-2 within the FRA report. However, where the Puddlebank crosses the Doe Lea, the footprint is
within flood zones 2 and 3. With reference to the CBC SFRA flood maps, the areas within flood zone 3
are classed as flood zone 3b (functional floodplain).
7.3.3 The proposed scheme is considered to be ‘water compatible’ under the NPPF and is thus deemed to be
acceptable in all flood zones.
7.3.4 Flooding behaviour of the Doe Lea upstream of the canal crossing is dominated by the existing profile of
the river channel and the Puddlebank where the historical culverts were removed in the 1970s. Under the
present scheme design, there is no intention to modify the existing profile below the modelled peak flood
levels. The existing opening will be crossed by a single span aqueduct.
7.3.5 As there is no change to the existing profile, there will be no change to the existing flooding behaviour
providing that the soffit of the aqueduct is higher than the modelled peak flood levels. The FRA report
confirms that there will be at least 5.7m clearance in this situation. There is therefore no change to the
existing flooding behaviour.
7.3.6 Raising of the Puddlebank will increase the footprint within the modelled flood events. A flood
compensatory scheme has therefore been designed and included within the FRA report, in order to
ensure that there is no loss of floodplain storage for all modelled events. Compensatory storage areas will
be located south (upstream) and north (downstream) of the Puddlebank, resulting in a net storage volume
gain in both instances. Note that the compensatory scheme presented is for planning purposes only and it
is proposed that the detailed design and approval of these is subject to a planning condition.
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7.3.7 Raising of the Puddlebank will have introduce a barrier to surface water flows from the farmland up-slope
of the site. For details of the appropriate mitigation, refer back to the Design and Access Statement
(6.3.38)
7.3.8 The scheme will not significantly increase surface water runoff rates given that the landscaping will be
fundamentally similar to the existing scenario without significant areas of hardstanding.
Flooding effects acting on the site
7.3.9 The FRA report concludes that the site itself is considered to be at low risk of surface water flooding or
that resulting from sewers or groundwater, owing to the raised profile. Further, the scheme is considered
to be at low risk of flooding from reservoir breach or failure.
7.3.10 Water within the canal will be managed in accordance with standard operational practices for a canal and
the risk to users of flooding from the canal itself is negligible.
7.3.11 In all of the modelled flood events, the canal and the towpath are sited well above the flood level, and will
therefore remain operational and safe for users during such events. Dry access and egress from the site
is possible for all towpath users via the footpaths at White Bridge, Packsaddle Bridge and the multitude of
routes at Eckington Road.
7.4 Water Quality
7.4.1 When the canal is restored along the length of this scheme, operating it will require water. Canals lose
water through evaporation, seepage and operation of locks. Additionally, management of water levels
means it is necessary to discharge water over side weirs at periodic intervals along the canal.
7.4.2 Water for the operation of this section of canal will come from the existing restored length above Staveley
Town Lock, fed via the siphon pipe that will discharge at the head of Railway Lock. This water is supplied
primarily from the River Rother at Chesterfield, along with a smaller supply where Trough Brook
discharges fully into the canal at Hollingwood. No new water supplies will be developed as part of this
application.
7.4.3 Increasing the length of restored canal will have several impacts on the water regime:
• increase in evaporation and seepage losses, potentially requiring higher abstraction quantities at
the primary abstraction point on the river Rother
• altering the discharge patterns from side weirs, particularly reducing the quantities discharged to
the river Rother at Mill Green and Hartington, and introducing a new discharge to the river Doe
Lea at Norbriggs
• increase in losses due to lockage due to the addition of Railway Lock. Due to the operation of the
siphon pipe, only lockage water and minimal side weir losses should occur at Hartington
7.4.4 The changes to the water regime could have an impact on the water quantity and quality in the rivers
Rother and Doe Lea, thence affecting the Water Framework Directive (WFD) status of these water
bodies. An assessment of this impact has been carried out and is submitted in support of this application
(Chesterfield Canal Water Framework Directive Assessment, document reference CCTWFD19).
7.4.5 The WFD assessment used modelling work carried out in an earlier study of the impact on future
restoration of the canal through to Killamarsh on the abstraction from the river Rother. This study
concluded that the existing abstraction is sufficient for the purposes of supplying the current application.
7.4.6 The WFD assessment concludes that the potential impact on water quality is likely to be small. It notes
concerns with the potential impacts on the river Rother at low flows. However, it should be noted that,
given there is no requirement for any greater abstraction than that necessary to feed the currently
restored extents, this is no different to the existing situation. Additionally, the impact of the abstraction on
low flow conditions is being separately managed by the Environment Agency as part of the licensing
process for previously exempt abstractions.
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7.5 Heritage
7.5.1 A Heritage Statement (document reference TJC2020.23) is included in support of this application, in order
to assess the impact of the scheme upon any designated and non-designated heritage assets.
7.5.2 The Heritage Statement concludes that the primary features of historical and archaeological interest are
those directly relating to the canal itself. The remains of structures cleared since the canal fell derelict are
identified as being of local significance, with the Puddlebank being of regional significance owing to its
pioneering engineering and a lack of detailed understanding as to the methods of its construction.
7.5.3 As restoration of the canal is proposed along the original route, the scheme will have a direct impact on
the archaeological resources along the route and will potentially lead to a partial loss or destruction of the
heritage significance. The report highlights that a balanced judgement must be made between the loss of
archaeological resource and the wider benefit to the historic environment associated with the restoration
of the canal.
7.5.4 In particular, the report recommends that archaeological evaluation and recording is carried out in
accordance with the NPPF and policy CS19 of the CBC Local Plan. Particular attention should be paid to
the Puddlebank owing to its enhanced significance and the irreversibility of any changes made during
restoration in order to satisfy modern engineering design standards.
7.5.5 The report does not consider any further archaeological evaluation is necessary prior to determination of
the planning application but recommends that the requirements identified above are secured by a suitable
planning condition.
7.6 Ground Conditions
7.6.1 An initial assessment of the ground conditions has been made via desktop study, in two stages.
7.6.2 A Phase I Geo-Environmental report was commissioned to look at the potential for land contamination.
This noted the potential for contamination where the canal has been backfilled, and particularly around
the former gas works on Bellhouse Lane. With regard to the former point, it should be noted that the
memories of those who were around when the canal was decommissioned across the Puddlebank note
that the primary means of doing so was to bulldoze the banks outwards (rather than infilling the channel),
as the resulting material was used to raise other local areas suffering from mining subsidence. Thus, for
the large part of the route, the actual amount of backfill material is very limited.
7.6.3 The site sits entirely within a Coal Mining Reporting Area, and significant lengths are within a
Development High Risk Area, indicating the potential for shallow mine workings that may present a risk to
surface developments. Given the history of the site and the known effects of mining subsidence to date,
this is not surprising. A desktop enhanced Coal Mining Risk Assessment has been carried out. This
concludes that there remains a risk of surface movement due to recorded and possible unrecorded mine
workings. It makes recommendations for intrusive ground investigations that will be incorporated into the
detailed geotechnical investigations to be undertaken prior to the detailed design.
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8 CONCLUSIONS
8.1 In summary, this planning application seeks to restore 2.6km of the Chesterfield Canal between
Eckington Road & Hague Lane, constituting the remaining length of the Chesterfield Canal to be restored
within the boundaries of Chesterfield Borough.
8.2 Starting at Eckington Road, the scheme will briefly consist of:
• crossing the Staveley-Seymour railway line (site of bridge no. 13b)
• construction of Railway Lock (no. 5b)
• construction of the 2.6km of canal channel, including approximately 2.1km on a raised
embankment, with the formerly embanked central section known as the Puddlebank
• construction of 4no. overbridges: Arkwright Trail bridge (no. 13c), Bellhouse Bridge (no. 14),
Packsaddle Bridge (no. 15) and Red Bridge (no. 16)
• construction of a new aqueduct over the river Doe Lea
8.3 The design has carefully considered all of the constraints, in order to come up with a balanced solution
that is in the best interests of all parties now and into the future.
8.4 Restoration of the Chesterfield Canal is a key strategic objective for Chesterfield Borough Council and the
proposals are in accordance with all of the relevant planning policies. Alongside the strategic and policy
support, the restoration is very well supported politically and by the local population.
8.5 The restoration will have no impact on the flooding characteristics of the Doe Lea or on the water quality
of the Doe Lea or the Rother.
8.6 With appropriate mitigation, the scheme will have a very low impact on the local biodiversity and will
instead be an opportunity for increasing the biodiversity value of the area and enhancing green corridors.
8.7 Restoring this section of the canal will be a significant step forward towards complete restoration of the
Chesterfield Canal and the significant social, economic, health and environmental benefits that that will
bring. Even partially complete, the meanwhile benefits will be extensive.
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APPENDIX 1: COPY OF PRE-APPLICATION MEETING NOTES
Meeting Notes
Date & Time of Meeting 19/06/2019 9:00 – 10:30
Attendees
George Rogers (CCT Development Manager)
Paul Staniforth (CBC Development Management & Conservation Manager)
Aim of Meeting
Pre-application meeting regarding the planning application to CBC.
The planning application will consist of the remainder of the Chesterfield Canal restoration within Chesterfield Borough, from Eckington Road to Hague Lane. This will include the reconstruction of the Puddlebank, construction of 2no accommodation bridges, 2/3no pedestrian/cycle bridges, an aqueduct over the River Doe Lea and the crossing of the Mineral Line, a total distance of approximately 2.6km.
CCT is aiming for completion of restoration by 2027, and this section will be one of the key next elements to be delivered, subject to planning permission, land agreements and funding being resolved.
Meeting Notes
PS explained his knowledge of the canal project.
I then set out the proposed scheme for this application and the key issues associated with the design of the works:
- HS2 - Utility crossings, particularly the Yorkshire Water sewers - Earth moving quantities, particularly with regards to potential clay supply from Foxlow - Position of locks & levels with regards to the above
PS understood CCT’s position in needing to get planning submitted, and reminded us that HS2 would be a consultee as was already understood.
Following internal CCT discussions regarding the impact of wider developments in the Borough on the sewer network in this area, I raised this with PS. He wasn’t able to give any update on whether the sewers are going to be replaced. Additionally, he noted that being so close to the sewage works there may be limited options for lowering.
Earth moving quantities and proposed routes for bringing material to site was discussed. Bellhouse Lane would definitely not be appropriate and options should be explored as much as possible, with a preference to the Fitzwise option, followed by road access from Ireland Close and along the canal route. PS raised whether access at the other end would need to be considered (e.g. through the Ash Renishaw site or similar) but neither him nor I were conversant enough in this area to comment further.
Meeting Notes
In terms of required documentation, I went through the list I had prepared, and we commented as follows:
- Drawings – plans, sections, structural details etc would be required - Planning statement – this should also include outline construction methods and a background to the
design proposals, i.e. the options considered and why whichever is adopted, basically the process I went through in explaining the scheme to him. This should also include information regarding construction traffic (number of trips, routing etc)
- Heritage/archaeology assessment - Coal Mining Risk Assessment - Ground investigation – to understand the risk of contamination from any disturbed ground, even if
staying on site. - Ecology. PS advice is that we should seek an EIA screening opinion as otherwise it is open to
challenge, but he is confident it wouldn’t need to proceed to a full Environmental Statement. PS advises engaging with Environment Agency & Derbyshire Wildlife Trust now, in order that suitable enhancements can be included as part of the scheme.
- Flood Risk Assessment, although PS doesn’t think this need be onerous, and wouldn’t need to consider flood risk associated with the canal water. However, the impact of bringing water in via canal and any impacts on the river etc, which I think in essence is the Water Framework Directive assessment, should be considered. The best we can do here is get some advice from the Environment Agency (I might know more after a similar meeting for Cromford).
PS wasn’t particularly committal on the marina concepts as no proposals were available to look at and discuss. A marina at Bellhouse Lane should consider the impact on traffic / parking / services / amenities etc, so would need that to be well addressed in any application. He didn’t raise any particular concerns re greenbelt.
PS will confirm the Borough boundary at Hague Lane, he needs to check exactly where the line is.
With regards to the compound planning application, this is going before planning committee on Monday 1st July. It will be recommended for approval and Paul doesn’t see anyone on planning committee voting against it.
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APPENDIX 2: COPY OF EIA SCREENING REQUEST DECISION NOTICE
(CHE/20/00213/EIA)