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William Grant & Sons Irish Manufacturing Application for an IPPC Licence Attachments to Application
Doc. Ref. 472-X0004 July 2013
Attachment B.5 Planning Permissions & Applications
This attachment contains the following:
B5.1 A copy of the Planning Permission Reference No. 12/261
B5.2 A copy of the Planning Inspector’s Report
B5.3 A copy of the Screening Statement for Appropriate Assessment (extracted from the EIS)
B5.4 A copy of the Environmental Impact Statement (as a separate attachment)
B5.5 A list of the Planning Applications lodged and Permissions granted for the site
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William Grant & Sons Irish Manufacturing Application for an IPPC Licence Attachments to Application
Doc. Ref. 472-X0004 July 2013
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EPA Export 09-07-2013:23:41:35
| OCTOBER 2012 | ENVIRONMENTAL IMPACT STATEMENT FOR WILLIAM GRANT & SONS LTD.
Appropriate Assessment Screening Statement
10.2.1.Introduction
Kelleher Ecology Services Ltd. was commissioned by McCutcheon
Halley Walsh planning consultants, on behalf of William Grant & Sons, to
undertake a screening statement for a proposed distillery development at
Clonminch, Tullamore, Co. Offaly. This assessment was undertaken a
planning application for a proposed distillery, where European
designated conservation sites are present in the surrounding area.
A screening assessment is undertaken to establish if any proposed plan
or project is likely to have a significant effect on any site that has been
designated under the E.U. Habitats Directive (92/43/EEC), i.e. a Special
Area of Conservation (SAC), or the E.U. Birds Directive (2009/147/EC),
i.e. a Special Protection Area (SPA). Collectively, SAC’s and SPA’s are
known as Natura 2000 sites. The Natura 2000 sites under consideration
here are Charleville Wood SAC, River Barrow and Nore SAC and Clara
Bog SAC. The conservation objectives of Natura 2000 sites have been
compiled by the National Parks & Wildlife Service (NPWS) in relation to
the habitats and species for which the sites are selected. These
conservation objectives are referred to when carrying out appropriate
assessments for plans and projects that might impact on these sites. So
in this case, the conservation objectives of Charleville Wood SAC, River
Barrow and Nore SAC and Clara Bog SAC have been considered in the
following assessment and report.
A screening assessment is part of an appropriate assessment process
that consists of up to four stages, where each stage follows on from the
preceding one. In Stage 1, a screening process is undertaken to identify
whether significant1 impacts on a Natura 2000 site are likely to arise from
the project or plan in question. If significant impacts are likely to occur,
then the process moves on to Stage 2 where an appropriate assessment
(AA) considers potential mitigation measures for adverse impacts. If it is
considered that mitigation measures will not be able to satisfactorily
reduce potential adverse impact on a Natura 2000 site then an
assessment of alternative solutions is considered in Stage 3. This is then
followed by Stage 4 in the event that adverse impacts remain and the
proposed activity or development is deemed to be of Imperative Reasons
of Overriding Public Interest (IROPI), allowing an assessment of
compensatory measures to be considered. The outcome of a Stage 2
and higher assessment is presented in a report known as a Natura
Impact Statement (NIS).
1EPA (2003) define significant impact as “An impact which, by its character, magnitude, duration
or intensity alters a sensitive aspect of the environment.”
This report presents the outcome of a Stage 1 screening assessment to
identify whether significant impacts are likely to arise from the proposed
development on the Natura 2000 sites in question. This report has been
completed as part of a planning application by the client to Offaly County
Council for a proposed distillery. The following guidelines were used in
the completion of this assessment;
Assessment of Plans and Projects Significantly Affecting Natura 2000 Sites – European Commission Methodical Guidance on the provisions of Article 6(3) and 6(4) of the ‘Habitats’ Directive 92/43/EEC (European Commission 2001)
Appropriate Assessment of Plans and Projects in Ireland – Guidance for Planning Authorities (DoEHLG 2009)
10.2.2 Stage 1: Screening
The development will comprise the construction of a distillation plant and
whiskey maturation warehouses, a visitor/marketing centre and
ancillaries on a site area of c. 23 hectares (56.8 acres), which is to be
built in three phases. The proposed distillery site is located to the south
of the town of Tullamore, on the north side of the N52 in County Offaly,
with a number of Natura 2000 sites in the surrounding area (see Figure
2.1). At present, the site is in use as commercial forestry to the west and
as pasture farmland to the east. The southern boundary adjoins the N52,
from which an access will be provided to the site.
This first phase, which is intended to be operational in 2014, will involve
clearance of the existing site, re-grading the ground levels as necessary,
the formation of new access roads, hardstanding areas and car parks,
the provision of services and drainage and the construction of the main
distillery building, the co-products and boiler house building, a filling
store, gatehouse, two warehouses and various tanks, silos, cooling
towers and associated landscaping. A pond and pumping station will be
formed to provide fire fighting water and a means of attenuation to control
the discharge of storm water from the site.
The second phase is intended to commence in 2019 and be completed
by 2021. Apart from the two new warehouses, the other new buildings in
this phase are within the foot print of the first phase. However, piling
operations and service connections will be required. The proposed
warehouses included in this phase are located on the agricultural land to
the east which will need to be cleared and graded.
The third phase is intended to commence in 2021 and be completed in
2022. This phase is entirely associated with the construction of a further
seven warehouses. This will involve the clearance and re-grading of
ground levels, the formation of new access roads and service yards, the
provision of services and drainage including the construction of a further
attenuation pond which will be linked to the original pond.
As part of the overall project design, a site drainage system that is
cognisant of existing site conditions and drainage will be designed and
installed. Surplus topsoil and peat that are excavated during the
construction phase will be retained in mounds, which will be engineered
to ensure long term stability.
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ENVIRONMENTAL IMPACT STATEMENT for WILLIAM GRANT & SONS LTD. | October 2012 |
Figure 2.1 - Location of Distillery Site & Natura 2000 Sites
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EPA Export 09-07-2013:23:41:35
| OCTOBER 2012 | ENVIRONMENTAL IMPACT STATEMENT FOR WILLIAM GRANT & SONS LTD.
The proposed development site is not located within any designated
conservation site. There is one Natura 2000 site, Charleville Wood SAC
(site code 000571), within 1 km of the proposed development site at
Clonminch. There are a further two Natura 2000 sites, River Barrow and
River Nore SAC (site code 002162) and Clara Bog SAC (site code
000572) within 10 km of the proposed development.
The proposed development site is drained by two field drain systems
which ultimately discharge to two swallow holes towards the Tullamore
River, one 800m to the northwest of the site and a second 600m north of
the site. Site drainage may influence designated sites potentially
associated with the drainage system after it discharges from the site. In
this case, Charleville Wood SAC may potentially be affected by site
drainage as this site has an aquatic aspect and is located to the
northwest, beyond the swallow holes. The two other Natura 2000 sites in
question are not drained by the proposed development site.
Table 2.1 summarises the main conservation characteristics of each site,
as well as the approximate distance from the proposed development site,
and Figure 2.1 shows the location of these designated sites in relation to
the site boundary. The conservation objectives of Charleville Wood SAC
relate to the presence of the habitat, Old sessile oak woods with Ilex and
Blechnum in the British Isles and for a population of rare snail, Vertigo
moulinsiana. In the case of River Barrow and Nore SAC, the
conservation objectives apply to a range of different habitats including;
Alluvial forests with Alnus glutinosa and Fraxinus excelsior and Petrifying
springs with tufa formation (Cratoneurion), and associated species
including; Otter (Lutra lutra) and Freshwater pearl mussel (Margaritifera
margaritifera). While for Clara Bog SAC the objectives include a range of
habitats, such as Active raised bogs and Bog woodland, and for the
Marsh Fritillary butterfly (Euphydryas (Eurodryas, Hypodryas) aurinia).
Detailed site synopses and conservation objectives for these Natura
2000 sites are available in Appendix A.
Table 2.1 - Summary of Natura 2000 Sites
10.2.3 Stage 1: Assessment Criteria
The proposed development site is not located within any of the Natura
2000 sites in question nor does it require any resources from them,
thereby ruling out any direct habitat loss of these conservation sites.
Indirect habitat loss or deterioration of Natura 2000 sites within the
surrounding landscape can occur through hydrological or water quality
impacts such as increased siltation, nutrient release and/ or
contaminated run-off arising from the distillery site and into the aquatic
environment. However, this requires connectivity between the distillery
site and the Natura 2000 sites in question through watercourses and / or
drainage. The proposed development site is located in a low lying and
relatively poorly draining area. The site is currently drained by two field
drain systems which ultimately discharge to two swallow holes towards
the Tullamore River, one 800m to the northwest of the site and a second
600m north of the site. Site drainage may potentially impact on
Charleville Wood SAC after it discharges from the site as this SAC has
an aquatic aspect and is located to the northwest, beyond the swallow
holes. A rare snail, Vertigo moulinsiana, is one of the key species listed
for Charleville SAC. This snail is dependent on wet, humid conditions in
suitable, ungrazed and tall vegetation habitats. Successful management
for this species is dependent on the maintenance of even
hydrogeological conditions, as the snail is sensitive to any change in
drainage patterns which may occur (Moorkeens & Killeen, 2011). In this
case, V. moulinsiana associated with Charleville Wood SAC may
potentially be affected by changes to site drainage as a result of the
proposed development.
However, the current poorly draining nature of the site means that rainfall
predominantly runs-off to the existing surface water drainage system at
present. It is therefore considered that the presence of the proposed
distillery will not significantly increase rainfall run-off rates from the
developed site. In addition the implementation of mitigation measures as
part of the proposed drainage design of the developed site will further
reduce potential risks arising from any hydrological or water quality
impacts on the SAC. These measures include the use of surface water
retention ponds designed to a 1 in 200 year rainfall event and swales to
ensure maintenance of the current greenfield surface water discharge
rates from the site while controlling suspended solids & contaminants,
interceptors to collect hydrocarbons arising from vehicles associated with
the site, bunded fuel tanks to ensure adequate fuel storage ability and a
pumped drainage system to an existing culverted drain associated with
the N52 to the south west of the site to over-ride the proposed gravity
drained system to the north during extreme events such as an excessive
flood. While the pumped drainage system to the south may potentially
drain into Charleville Wood SAC, it is worth noting that this system will
only be in place for extreme events on a short-term basis and that
suspended solids and contaminants will still be controlled. None of the
Natura 2000 Site
Site Code Conservation Significance Distance From Site
(Km)
Charleville Wood
SAC 000571
Charleville Wood is one of the most important ancient Oak woodland sites in Ireland. Old Oak
woodland is a habitat listed on Annex I of the EU Habitats Directive. It also supports a large population of the rare snail species, Vertigo
moulinsiana, which is listed on Annex II of this directive, several rare Myxomycete species and wetland areas with associated bird populations. The conservation objectives of Charleville Wood
SAC relate to the presence of the habitat old sessile oak woods with Ilex and Blechnum in the British Isles and for a population of rare snail, V.
moulinsiana.
SAC: 0.81
River Barrow and River Nore
SAC 002162
The site supports alluvial wet woodlands and petrifying springs, priority habitats on Annex I of the E.U. Habitats Directive. The site also has old oak woodlands, floating river vegetation, estuary,
tidal mudflats, Salicornia mudflats, Atlantic salt meadows, Mediterranean salt meadows, dry
heath and eutrophic tall herbs - all habitats listed on Annex I of the E.U. Habitats Directive. The
site also supports several species listed on Annex II of the same directive - inlcuding Freshwater Pearl Mussel, Nore Freshwater Pearl Mussel.
The conservation objectives for The River Barrow and Nore SAC, apply to a range of different
habitats (i.e Alluvial forests with Alnus glutinosa and Fraxinus excelsior and Petrifying springs with
tufa formation (Cratoneurion)) and associated fauna (i.e Otter (Lutra lutra) and Freshwater pearl
mussel (Margaritifera margaritifera).
8.47
Clara Bog SAC
000572
Clara Bog has long been regarded as one of the most important lowland raised bogs in the
country, being the largest remaining example of the true Midland sub-type. It has well developed hummock and hollow complexes and one of the
few remaining soak systems. It also supports several rare invertebrate species, the rare moss
Tetraplodon angustatus, and various bird species of significance including Merlin, which is listed on
Annex I of the EU Birds Directive. The conservation objectives for Clara Bog SAC apply to a range of habitats (i.e. Active raised bogs and
Bog woodland) and for the Marsh Fritillary butterfly (Euphydryas (Eurodryas, Hypodryas)
aurinia).
SAC: 9.15
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EPA Export 09-07-2013:23:41:35
ENVIRONMENTAL IMPACT STATEMENT for WILLIAM GRANT & SONS LTD. | October 2012 |
other Natura 2000 sites potentially receive drainage from the distillery
site.
A peat slip or landslide event has the potential to deposit soils and
associated material directly onto surrounding designated sites and/ or
indirectly through the release of soils and associated material into
watercourses / drainage systems that potentially connect to designated
sites- Charleville Wood SAC and pNHA in this case. This could have a
negative impact on this designated site through loss or damage of habitat
and/ or mortality of associated species. In this proposed development,
surplus topsoil and peat that are excavated as part of the construction
phase will be retained in mounds within designated areas. Detailed
consideration of the potential impact of peat slippage was taken into
account for both the excavation works and design of the mounds to
mitigate any risk of slippage and ensure long term stability. The detailed
construction design proposed as part of the project will ensure that there
is a zero to negligible risk of any peat slippage. As a consequence, it is
anticipated that a peat slide or landslide event will not arise as a result of
the proposed distillery.
Activities associated with the construction and operation of a proposed
development has the potential to disturb and/or displace faunal species
through noise and/or visual cues. In the case of Charleville Wood SAC
the primary conservation objectives relate to the rare Vertigo moulinsiana
snail and old sessile oak woods with Ilex and Blechnum in the British
Isles and not highly mobile terrestrial based faunal species that may be
vulnerable to disturbance arising from activities in the surrounding
landscape. This is combined with the fact that this SAC is at enough of a
distance (c. 800m) from the distillery site to further dismiss potential
disturbance and/or displacement effects through noise and/or visual cues
away. Similarly the primary conservation objectives of the other two
Natura 2000 sites are not concerned with highly mobile terrestrial based
fauna and are located at considerable distances (> 8km) away from the
development site.
Taking the above into consideration – i.e. the nature of the key
conservation objectives involved, lack of highly mobile terrestrial fauna
associated with the SAC’s conservation objectives, distances to the
distillery site, lack of drainage to two Natura 2000 sites in question and
use of mitigation measures that will ensure that site drainage will
essentially remain the same as the current situation and peat slippage
will be of zero to negligible risk in relation to Charleville Wood SAC- - it is
felt that there are no elements of the project likely to impact on the
Natura 2000 sites in questions.
10.2.4 Likely Impacts of the Project on the Natura 2000 Sites
The proposed development site is of c. 23 hectares (56.8 acres) in area,
none of which is part of the Natura 2000 sites in question. Consequently
the size, scale and land-take of the proposed development are of no
concern for the conservation sites.
Charleville Wood SAC is c. 800m northwest of the proposed
development, where its primary conservation objectives relate to its
habitats and a rare snail species. The distillery site potentially drains into
this Natura 2000 site. However, as already outlined above, rainfall
predominantly runs-off to the existing surface water drainage system at
present and mitigation measures proposed as part of the design of the
distillery will ensure that site drainage remains the same and peat
slippage risk will be zero to negligible. None of the other Natura 2000
sites potentially receive drainage from the distillery site.
Taking the above into consideration, activities associated with the
proposed development are of no concern for the SACs in question.
Water will be piped to the proposed distillery from the current daily supply
of abstracted water for the Tullamore Water Supply Scheme. This water
is abstracted from Clodiagh River, which flows through Charleville Wood
SAC. However, the abstraction point on the Clodiagh River is some 15
km upstream of Charleville Wood SAC, at Clonaslee Co. Laois. In
addition, there will be no increase in current abstraction rates at this
location to facilitate the distillery’s needs and works at the intake point
are not required.
Therefore the abstraction regime from the Clodiagh River is not expected
to impact on Charleville Wood SAC as the current status quo will remain
the same. There are no other resources required by the proposed
distillery. Consequently there is no concern in relation to resource
requirements of the proposed works and the Natura 2000 sites.
As part of the construction phase, the first operations to be undertaken
will be the clearance of all excess timber and tree stumps using diesel
powered, all terrain excavators, and dumpers. This material will be
processed on site with diesel or petrol powered plant to create a mulch
for subsequent re-use.
After the site has been cleared of timber, stumps and vegetation, the
remaining topsoil and peat will be stripped out from the areas required in
each phase, and retained in mounded earth forms within the designated
areas indicated on the plans. Detailed consideration of the potential
impact of peat slippage was taken into account in designing the structure
of the mounds to mitigate any risk. The topsoil and peat mounds shall be
engineered to ensure long term stability. The mounds will have side
slopes slope of around 1 vertical to 4 horizontal and, with the maximum
height proposed as four metres, the width of the slopes will be up to 16m
wide. The material within the side slopes will be stabilised as determined
necessary using geotechnical testing of the material properties. The
stabilisation will be achieved by mixing the topsoil and peat with other
soils or by the established techniques of lime and cement stabilisation of
peat which control moisture content and demonstrably increase the shear
strength of the materials. The face of the slopes and mounds will be
topped with a growing medium to the landscape architect's specifications
to allow subsequent planting and vegetation. This detailed construction
design will ensure that there is a zero to negligible risk of any peat
slippage.
Other general excavations and filling operations will then be undertaken
to form platform levels, for the new buildings and hard standing areas.
Where existing materials are softer in nature, soil improvements will be
made by mixing in chemicals such as cement or lime. It will utilise
excavated soils to be mixed with cement or lime to allow the material to
be re-used, along with crushed stone or demolition material, as a base
below roads and hard standing areas.
The public utilities and Offaly County Council will bring power,
communications and drainage to the site. Water will be piped to the
proposed distillery from the current daily supply of abstracted water for
the Tullamore Water Supply Scheme. This water is abstracted from
Clodiagh River, which flows through Charleville Wood SAC. However,
the abstraction point on the Clodiagh River is some 15 km upstream of
Charleville Wood SAC, at Clonaslee Co. Laois. In addition, there will be
no increase in current abstraction rates at this location to facilitate the
distillery’s needs and works at the intake point are not required.
Therefore the abstraction regime from the Clodiagh River is not expected
to impact on Charleville Wood SAC as the current status quo will remain
the same.
Once operational, the proposed distillery will be involved in the
manufacturing of whiskey, including the brewing, fermentation and
distillation processes and spirit aging in casks. The brewing process
takes up to 4 days while spirit aging takes a minimum of 3 years but
typically longer. During the manufacturing process any waste will be
segregated and a comprehensive system for reduction and recycling will
be employed. The proposed distillery is to be developed in three phases,
which will be linked to different output demands over time. It is intended
that infrastructure and buildings required to facilitate the maximum
production anticipated will be developed within a ten year period. Final
output capacity (million litres of alcohol produced per annum) may not be
reached until after the construction period has been completed and will
be determined by market demands.
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| OCTOBER 2012 | ENVIRONMENTAL IMPACT STATEMENT FOR WILLIAM GRANT & SONS LTD.
As already discussed above – i.e. site distances, nature of the key
conservation objectives involved, lack of highly mobile terrestrial fauna
associated with the SAC’s conservation objectives, lack of drainage to
two Natura 2000 sites in question and use of mitigation measures that
will ensure that site drainage will essentially remain the same as the
current situation and peat slippage will be of zero to negligible risk in
relation to Charleville Wood SAC- activities associated with the proposed
distillery are of no particular concern with regard to the Natura 2000 sites.
There is the potential for emissions to the atmosphere during the
construction of the development. In particular, the construction activities
may generate quantities of dust. Construction vehicles, generators etc.,
will also give rise to some exhaust emissions. However, due to the size
and nature of the construction activities, exhaust emissions during
construction will have a negligible impact on local air quality. In addition,
a dust minimisation plan will be formulated for the construction phase of
the project.
A detailed air modelling assessment undertaken as part of the EIS for the
proposed distillery has concluded that the impact associated with the
operational phase of the development will have a negligible impact on
local air quality. Therefore emissions relating to the proposed distillery
are of no particular concern with regard to the Natura 2000 sites.
The surface water drains flowing to the north ultimately discharge to
groundwater via two sink holes. To mitigate against the impact of
increasing the surface water run-off rate it is proposed to construct two
retention ponds at the site. One will be constructed in Phase 1 and the
other in Phase 3. The retention ponds have been sized to ensure that in
the event of a 1 in 200 year rainfall event the greenfield run-off rate to the
north is maintained to the surface water drainage system. In the event of
an extreme event such as an excessive flood, a pumped drainage
system to an existing culverted drain to the south west of the site will
over-ride the proposed gravity drained system to the north. While the
pumped drainage system to the south may potentially drain into
Charleville Wood SAC, it is worth noting that this system will only be in
place for extreme events on a short-term basis and that suspended
solids and contaminants will still be controlled. Therefore the potential
effects of surface run-off from the proposed development on Charleville
Wood SAC are negligible (none of the other Natura 2000 sites potentially
receive drainage from the distillery site). In addition, all surface water
run-off to hard stand and parking areas will discharge to the retention
lagoons via interceptors to mitigate against the risk of discharging fuel
leaks or spills or oily run-off into the surface water drainage system. A
Construction and Environmental Management Plan (CEMP) will be
developed to mitigate the risk of accidental leaks or spills during this
phase. Best practice measures will be incorporated into the development
of the CEMP based on guidance from Construction Industry Federation
and the UK Construction Industry Research and Information Association
(CIRIA).
After the site has been cleared of timber, stumps and vegetation, the
topsoil and underlying subsoil will be excavated to construction formation
level. In some areas, where unsuitable peat or very soft subsoils are
present, it will be necessary to excavate below formation level, for
example to form the retention ponds and where underground services
are required. In such cases the excavated soils may be either reused in
landscape works, for example in perimeter berms or in the case of peat
placed in permanent and bunded storage areas.
The principal wastes/spoils generated during the construction will be will
be stored in bulk on the site to be reused, recycled and/or disposed of
accordance with the facilities Waste Management Plan and in an
authorised facility. Re-fuelling of plant or vehicles will be undertaken in
fully contained areas, The quantities of hazardous waste (i.e. waste oils,
residual chemicals, batteries) generated at the facility will be relatively
small. However, all such wastes will be stored in appropriately size
bunded storage and will be disposed of in accordance with the IPPC
license requirements and the facilities Waste Management Plan. All solid
materials with the potential to cause contamination, such as lime or
cement, will be stored internally away from rainfall or other water or liquid
sources.
The principal wastes/spoils, paper and packaging generated during the
operational disposed will be disposed of or recycled in accordance with
the facilities waste management policy.
Wastewater (including sewage) associated with the distillery will be
disposed into Tullamore Wastewater Treatment Plant & Sludge
Treatment Centre (WTP & STC). This is a newly commissioned plant that
has a capacity of 45,000 population equivalen (PE) biological treatment
and 80,000PE sludge treatment, which is operated under Environmental
Protection Agency (EPA) licence. The Tullamore WTP & STC has
adequate capacity to treat wastewater associated with the proposed
distillery within the scope of the EPA licence. There is therefore no
impact to assess in respect of the outflow from the Tullamore WTP &
STC.
As all emissions associated with the proposed development will be
appropriately controlled, there is no concern in relation to emissions
associated with the proposed distillery and the Natura 2000 sites.
It is proposed that permanent access to the site will be provided by a new
roundabout, situated adjacent to the west boundary of the site, on the
N52. It is hoped that the roundabout is completed before the start of the
construction works, however if not, then a temporary construction access
will be formed from the N52. This may involve the provision of temporary
road widening and the creation of a temporary priority junction for
construction access only. Temporary traffic management arrangements
will have to be agreed with Offaly County Council.
During the construction phase of the proposed development it is
estimated that throughout phase 1 the maximum daily construction traffic
is estimated at 69 return trips per vehicle per day (including HGVs and
light vehicles). By phase 2 and 3 the daily peak of return vehicle journeys
is estimated to involve 35 HGVs and light vehicles.
Operational output will increase over time and full output may not be
achieved until some time after construction has been completed. It is
estimated that there will be 21 employees on completion of phase 1 in
2014 which is to increase to 69 by 2025. There will be approximately 825
heavy vehicles and 21 private cars accessing the site per annum in 2014.
This is estimated to increase to 3800 heavy vehicles and 69 private cars
per annum by 2025. During the operational stage articulated trucks will
be used to transfer casks to and from the warehouses and forklifts will be
used for cask movement on site. In addition, it is estimated that the visitor
centre will attract up to 40,000 visiters per annum.
None of the above transportation requirements occur within the Natura
2000 sites. Consequently there is no particular concern in relation to
transportation requirements associated with the proposed development
and the SACs in question.
The development will comprise the construction of a distillation plant and
whiskey maturation warehouses, a visitor/marketing centre and
ancillaries on a site area of c. 23 hectares (56.8 acres), which is to be
built in three phases. The first phase is intended to be operational by
2014. The second phase is intended to commence in 2019 and be
completed by 2021 and the third phase is intended to commence in 2021
and be completed in 2022. The site will operate at normal hours for
construction works, defined as being between 07:00hrs and 19:00hrs
Monday to Friday and between 7:30hrs and 13:00hrs on Saturdays.
The number of construction workers on site will vary between each
phase and stage of construction. The estimated average and peak of
construction workers required for each phase is:-
Phase 1, - Average number of construction workers is 28 per day; Peak of 58 per day
Phase 2, - Average number of construction workers is 18 per day; Peak of 42 per day
Phase 3, - Average number of construction workers is 20 per day; Peak of 38 per day
Once operational (from 2014), the majority of staff will work from 9.00am
to 5:30pm daily. Process operation staff will work on a shift basis
ensuring that the distillery remains operational 24 hours per day, 7 days
per week. There is normally four weeks’ shut-down throughout the year
to undertake maintenance of plant on site.
Activities associated with the proposed distillery both during construction
and operational phases will not occur within the SAC. Consequently
there is no particular concern in relation to the duration of operations
associated with the proposed development and the Natura 2000 sites.
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ENVIRONMENTAL IMPACT STATEMENT for WILLIAM GRANT & SONS LTD. | October 2012 |
Taking the above into consideration, it is felt that there are no elements
of the project likely to impact (regardless of significance) on the Natura
2000 site. The key considerations that contributed towards this
conclusion are summarised as follows;
The proposed development site is not part of the Natura 2000 sites and does not require any resources from these designated sites.
The site potentially drains into Charleville Wood SAC via two existing field drain systems which ultimately discharge to two swallow holes north and northwest of the site. In this case, Charleville Wood SAC may potentially be affected by site drainage as this site has an aquatic aspect and is located to the northwest, beyond the swallow holes. However, considering the existing high run-off rate and poor drainage pattern at the site and the mitigation measures proposed to be implemented in relation to maintaining site drainage, controlling suspended solids & contaminants in surface water run-off and avoiding peat slippage, activities associated with the proposed development are of no concern to this SAC. None of the other Natura 2000 sites potentially receive drainage from the distillery site and are of no concern in this regard either.
Due to the nature of the key conservation objectives of the Natura 2000 sites with a lack of highly mobile terrestrial fauna combined with site distance, activities associated with the proposed development will not cause disturbance through noise and/or visual cues on habitats / species associated with the key conservation objectives the Natura 2000 sites.
As it is felt that the proposed development and associated activities do
not have any impact on the Natura 2000 sites in question, therefore,
there is no potential for impacts on these designated sites through
cumulative and in-combination with other known plans or projects.
10.2.5 Likely Changes to the Natura 2000 Sites
Habitat reduction is not anticipated in light of the following key
considerations;
The proposed development site is not part of the Natura 2000 sites and does not require any resources from these designated sites.
The site potentially drains into Charleville Wood SAC via two existing field drain systems which ultimately discharge to two swallow holes north and northwest of the site. In this case, Charleville Wood SAC may potentially be affected by site drainage as this site has an aquatic aspect and is located to the northwest, beyond the swallow holes. However, considering the existing high run-off rate and poor drainage pattern at the site and the mitigation measures proposed to be implemented in relation to maintaining site drainage, controlling suspended solids & contaminants in surface water run-off and avoiding peat slippage, activities associated with the proposed development are of no concern to this SAC. None of the other
Natura 2000 sites potentially receive drainage from the distillery site and are of no concern in this regard either.
Due to the nature of the key conservation objectives of the Natura 2000 sites with a lack of highly mobile terrestrial fauna combined with site distance, activities associated with the proposed development will not cause disturbance through noise and/or visual cues on habitats / species associated with the key conservation objectives the Natura 2000 sites.
No disturbance to key species is anticipated in light of the following key
considerations;
The proposed development site is not part of the Natura 2000 sites and does not require any resources from these designated sites.
The site potentially drains into Charleville Wood SAC via two existing field drain systems which ultimately discharge to two swallow holes north and northwest of the site. In this case, Charleville Wood SAC may potentially be affected by site drainage as this site has an aquatic aspect and is located to the northwest, beyond the swallow holes. However, considering the existing high run-off rate and poor drainage pattern at the site and the mitigation measures proposed to be implemented in relation to maintaining site drainage, controlling suspended solids & contaminants in surface water run-off and avoiding peat slippage, activities associated with the proposed development are of no concern to this SAC. None of the other Natura 2000 sites potentially receive drainage from the distillery site and are of no concern in this regard either.
Due to the nature of the key conservation objectives of the Natura 2000 sites with a lack of highly mobile terrestrial fauna combined with site distance, activities associated with the proposed development will not cause disturbance through noise and/or visual cues on habitats / species associated with the key conservation objectives the Natura 2000 sites.
No habitat or species fragmentation are anticipated in light of the
following key considerations;
The proposed development site is not part of the Natura 2000 sites and does not require any resources from these designated sites.
The site potentially drains into Charleville Wood SAC via two existing field drain systems which ultimately discharge to two swallow holes north and northwest of the site. In this case, Charleville Wood SAC may potentially be affected by site drainage as this site has an aquatic aspect and is located to the northwest, beyond the swallow holes. However, considering the existing high run-off rate and poor drainage pattern at the site and the mitigation measures proposed to be implemented in relation to maintaining site drainage, controlling suspended solids & contaminants in surface water run-off and avoiding peat slippage, activities associated with the proposed development are of no concern to this SAC. None of the other Natura 2000 sites potentially receive drainage from the distillery site and are of no concern in this regard either.
Due to the nature of the key conservation objectives of the Natura 2000 sites with a lack of highly mobile terrestrial fauna combined with site distance, activities associated with the proposed development will not cause disturbance through noise and/or visual cues on habitats / species associated with the key conservation objectives the Natura 2000 sites.
A reduction in species density is not anticipated in light of the following
key considerations;
The proposed development site is not part of the Natura 2000 sites and does not require any resources from these designated sites.
The site potentially drains into Charleville Wood SAC via two existing field drain systems which ultimately discharge to two swallow holes north and northwest of the site. In this case, Charleville Wood SAC may potentially be affected by site drainage as this site has an aquatic aspect and is located to the northwest, beyond the swallow holes. However, considering the existing high run-off rate and poor drainage pattern at the site and the mitigation measures proposed to be implemented in relation to maintaining site drainage, controlling suspended solids & contaminants in surface water run-off and avoiding peat slippage, activities associated with the proposed development are of no concern to this SAC. None of the other Natura 2000 sites potentially receive drainage from the distillery site and are of no concern in this regard either.
Due to the nature of the key conservation objectives of the Natura 2000 sites with a lack of highly mobile terrestrial fauna combined with site distance, activities associated with the proposed development will not cause disturbance through noise and/or visual cues on habitats / species associated with the key conservation objectives the Natura 2000 sites.
Changes in key indicators of conservation value are not anticipated in
light of the following key considerations;
The proposed development site is not part of the Natura 2000 sites and does not require any resources from these designated sites.
The site potentially drains into Charleville Wood SAC via two existing field drain systems which ultimately discharge to two swallow holes north and northwest of the site. In this case, Charleville Wood SAC may potentially be affected by site drainage as this site has an aquatic aspect and is located to the northwest, beyond the swallow holes. However, considering the existing high run-off rate and poor drainage pattern at the site and the mitigation measures proposed to be implemented in relation to maintaining site drainage, controlling suspended solids & contaminants in surface water run-off and avoiding peat slippage, activities associated with the proposed development are of no concern to this SAC. None of the other Natura 2000 sites potentially receive drainage from the distillery site and are of no concern in this regard either.
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| OCTOBER 2012 | ENVIRONMENTAL IMPACT STATEMENT FOR WILLIAM GRANT & SONS LTD.
Due to the nature of the key conservation objectives of the Natura 2000 sites with a lack of highly mobile terrestrial fauna combined with site distance, activities associated with the proposed development will not cause disturbance through noise and/or visual cues on habitats / species associated with the key conservation objectives the Natura 2000 sites.
10.2.6 Likely Impacts on the Natura 2000 Sites as a Whole
Interference with the key relationships that define the structure of the
Natura 2000 sites is not anticipated in light of the following key
considerations;
The proposed development site is not part of the Natura 2000 sites and does not require any resources from these designated sites.
The site potentially drains into Charleville Wood SAC via two existing field drain systems which ultimately discharge to two swallow holes north and northwest of the site. In this case, Charleville Wood SAC may potentially be affected by site drainage as this site has an aquatic aspect and is located to the northwest, beyond the swallow holes. However, considering the existing high run-off rate and poor drainage pattern at the site and the mitigation measures proposed to be implemented in relation to maintaining site drainage, controlling suspended solids & contaminants in surface water run-off and avoiding peat slippage, activities associated with the proposed development are of no concern to this SAC. None of the other Natura 2000 sites potentially receive drainage from the distillery site and are of no concern in this regard either.
Due to the nature of the key conservation objectives of the Natura 2000 sites with a lack of highly mobile terrestrial fauna combined with site distance, activities associated with the proposed development will not cause disturbance through noise and/or visual cues on habitats / species associated with the key conservation objectives the Natura 2000 sites.
Interference with the key relationships that define the function of the
Natura 2000 sites is not anticipated in light of the following key
considerations;
The proposed development site is not part of the Natura 2000 sites and does not require any resources from these designated sites.
The site potentially drains into Charleville Wood SAC via two existing field drain systems which ultimately discharge to two swallow holes north and northwest of the site. In this case, Charleville Wood SAC may potentially be affected by site drainage as this site has an aquatic aspect and is located to the northwest, beyond the swallow holes. However, considering the existing high run-off rate and poor drainage pattern at the site and the mitigation measures proposed to be implemented in relation to maintaining site drainage, controlling suspended
solids & contaminants in surface water run-off and avoiding peat slippage, activities associated with the proposed development are of no concern to this SAC. None of the other Natura 2000 sites potentially receive drainage from the distillery site and are of no concern in this regard either.
Due to the nature of the key conservation objectives of the Natura 2000 sites with a lack of highly mobile terrestrial fauna combined with site distance, activities associated with the proposed development will not cause disturbance through noise and/or visual cues on habitats / species associated with the key conservation objectives the Natura 2000 sites.
10.2.7 Indicators of Significance as a Result of the Identification of Effects Set Out Above
Not applicable.
Fragmentation
Not applicable.
Not applicable.
Not applicable.
Not applicable.
10.2.8 Elements of the Project Likely to Significantly Impact on the Natura 2000 Sites or where the Scale or Magnitude of Impacts are Unknown
Taking the above into consideration, it can be objectively concluded that
no significant effects arising from the proposed distillery are likely to
occur in relation to the Natura 2000 sites; Charleville Wood SAC, River
Barrow and Nore SAC and Clara Bog SAC.
10.2.9 Finding of No Significant Effects Report
Name and location of the Natura 2000 sites.
Charleville Wood SAC (site no. 000571)
River Barrow and Nore SAC (site no 002162)
Clara Bog SAC (site no: 000572)
Description of the project or plan.
The development will comprise the construction of a distillation plant and whiskey maturation warehouses, a visitor/marketing centre and ancillaries on a site area of c. 23 hectares (56.8 acres), at Clonminch, Tullamore, Co. Offaly. The development is to be built in three phases. The first phase is intended to be operational in 2014.
Is the Project or Plan directly connected
No.
with or necessary to the management of the site (provide details)?
Are there other projects or plans that together with the project of plan being assessed could affect the site (provide details)?
No. Considering the key conclusion that the proposed distillery site and all the activities associated with it will not impact on the Natura 2000 site in first place, this must also hold for cumulative and in-combination effects with other plans or projects.
The Assessment of Significant Effects
Describe how the project or plan (alone or in combination) is likely to affect the Natura 2000 site.
The proposed distillery development is unlikely to affect the Natura 2000 sites due to the reasons explained in the following section.
Explain why these effects are not considered significant.
No significant effects are envisaged to affect the Natura 2000 site as result of activities associated with the dismantling site due to the following considerations;
The proposed development site is not part of the Natura
2000 sites and does not require any resources from these
designated sites.
The site potentially drains into Charleville Wood SAC via
two existing field drain systems which ultimately discharge
to two swallow holes north and northwest of the site. In
this case, Charleville Wood SAC may potentially be
affected by site drainage as this site has an aquatic aspect
and is located to the northwest, beyond the swallow holes.
However, considering the existing high run-off rate and
poor drainage pattern at the site and the mitigation
measures proposed to be implemented in relation to
maintaining site drainage, controlling suspended solids &
contaminants in surface water run-off and avoiding peat
slippage, activities associated with the proposed
development are of no concern to this SAC. None of the
other Natura 2000 sites potentially receive drainage from
the distillery site and are of no concern in this regard
either.
Due to the nature of the key conservation objectives of the
Natura 2000 sites with a lack of highly mobile terrestrial
fauna combined with site distance, activities associated
with the proposed development will not cause disturbance
through noise and/or visual cues on habitats / species
associated with the key conservation objectives the Natura
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ENVIRONMENTAL IMPACT STATEMENT for WILLIAM GRANT & SONS LTD. | October 2012 |
2000 sites.
List of agencies consulted.
The National Parks & Wildlife Service through Development Applications Unit, DAU, and Ms. Ciara Flynn, DCO of NPWS
Bat Conservation Ireland
Inland Fisheries Ireland
Waterways Ireland
Birdwatch Ireland
Irish Raptor Study Group
Irish Wildlife Trust
An Taisce
Offaly County Council Heritage Officer
All of the above were consulted as part of the associated EIS for the proposed distillery.
Response to consultation.
See Appendix B of this report for detailed responses received as part of the associated EIS for the proposed distillery. In relation to this appropriate assessment screening report the following comments were made by NPWS, no other specific comments were received;
In particular the impact of the proposed development should be assessed, where applicable, with regard to, Natura 2000 sites, i.e. Special Areas of Conservation (SAC) designated under the EC Habitats Directive (Council Directive 92/43/EEC) and Special Protection Areas designated under the EC Birds Directive (Directive 2009/147 EC).
In accordance with article 6.3 of the Habitats Directive, this project should be subject to appropriate assessment screening and if necessary appropriate assessment. You are referred to the Departmental guidance document on Appropriate Assessment, which is available on the NPWS web at http://www.npws.ie/media/npws/publications/codesofpractice/AA%20Guidance%2010-12-09.pdf. You are also referred to the EU Commission guidance entitled “Assessment of plans and projects significantly affecting Natura 2000 sites. Methodological guidance on the provisions of Article 6(3) and (4) of the Habitats Directive 92/43/EEC”
which can be downloaded from http://ec.europa.eu/environment/nature/natura2000/management/docs/art6/natura_2000_assess_en.pdf
In order to carry out the appropriate assessment screening and/or prepare a NIS you will need to collect information about the relevant Natura 2000 sites including their conservation objectives. Details of designated sites and species can be found on www.npws.ie while conservation objectives, if not yet available on our web site, can be obtained by requesting them by completing the data request form on our website at http://www.npws.ie/media/npws/publications/Data%20request%20form.doc
The Department recommends that you consult with the relevant Local Authorities to determine if there are any projects or plans which alone or in combination could impact on any Natura sites.
Data Collected to Carry out the Assessment
Who carried out the
assessment Sources of Data
Level of assessment completed
Where can the full results of the
assessment be accessed and
viewed
Dr. Katherine Kelleher of Kelleher Ecology Services Ltd.
BSc & PhD Zoology & MIEEM
Michelle O’Neill of Cluain Ecology Ltd.
BSc Ecology &
IEEM
Pers. comm. McCutcheon Halley Walsh
Associated documentation including the EIA
National Biodiversity Data Centre (NBDC) online mapping
EPA online river mapping data
NPWS online designated site data & mapping
NBN online database
References (incl. EIS Ecology chapter)
Desktop study & field surveys of distillery site; am satisfied that this has yielded enough information to adequately complete Stage 1 Screening.
Full results of the assessment are available in the above screening statement report.
10.2.10 References
Department of Environment, Heritage & Local Government (DoEHLG).
2009. Appropriate Assessment of Plans and Projects in Ireland –
Guidance for Planning Authorities. DoEHLG, Dublin.
European Commission. 2001. Assessment of Plans and Projects
Significantly Affecting Natura 2000 Sites – European Commission
Methodical Guidance on the provisions of Article 6(3) and 6(4) of the
‘Habitats’ Directive 92/43/EEC. European Commission DG Environment,
Oxford UK.
Environmental Protection Agency (EPA). 2003. Advice Notes on Current
Practice (in the preparation of Environmental Impact Statements). EPA,
Wexford.
Moorkens, E.A. & Killeen, I.J. 2011 Monitoring and Condition
Assessment of Populations of Vertigo geyeri, Vertigo angustior and
Vertigo moulinsiana in Ireland. Irish Wildlife Manuals, No. 55.
National Parks and Wildlife Service, Department of Arts, Heritage and
Gaeltacht, Dublin, Ireland.
SITE NAME CHARLEVILLE WOOD SAC; SITE CODE: 000571
Charleville Wood is a large Oak woodland surrounded by estate parkland
and agricultural grassland located about 3 km south-west of Tullamore.
The site, which is underlain by deep glacial deposits, includes a small
lake with a wooded island, and a stream runs along the western
perimeter. The woodland is considered to be one of very few ancient
woodlands remaining in Ireland, with some parts undisturbed for at least
200 years.
Some 10% of the woodland has been underplanted with conifers and
other exotic trees, but the rest of the area is dominated by Pedunculate
Oak (Quercus robur). Apart from Oak, there is much Ash (Fraxinus
excelsior) and scattered Wych Elm (Ulmus glabra), while Birch (Betula
spp.) is a feature of the boggier margins. The shrub layer is composed
largely of Hazel (Corylus avellana), Hawthorn (Crataegus monogyna)
and Blackthorn (Prunus spinosa). The ground layer is varied, including
damp flushed slopes with Ramsons (Allium ursinum) and drier, more
open areas with a moss sward composed largely of Rhytidiadelphus
triquetris. The fungal flora of the woodland is notable for the presence of
several rare Myxomycete species, namely Hemitrichia calyculata,
Perichaena depressa, Amaurochaete atra, Collaria arcyrionema,
Stemonitis nigrescens and Diderma deplanata. A number of unusual
insects have also been recorded in Charleville Wood, notably Mycetobia
obscura (Diptera), a species known from only one other site in Ireland.
The site is also notable for the presence of a large population of the rare
snail species, Vertigo moulinsiana. Extensive swamps of Bulrush (Typha
latifolia) and Bottle Sedge (Carex rostrata) have developed in the lake
shallows. The lake is an important wildfowl habitat – it supports
populations of Mute and Whooper Swan and a number of duck species,
including Teal, Wigeon, Shoveler, Pochard and Tufted Duck. The
wooded island at its centre is famed for its long history of non-
disturbance. Hazel, Spindle (Euonymus europaeus) and Ivy (Hedera
helix) reach remarkable sizes here.
Charleville Wood is one of the most important ancient woodland sites in
Ireland. The woodland has a varied age structure and is relatively intact
with both areas of closed canopy and open areas with regenerating
saplings present. The understorey and ground layers are also well
represented. Old Oak woodland is a habitat listed on Annex I of the EU
Habitats Directive, while the rare snail species, Vertigo moulinsiana, is
listed on Annex II of this directive. The wetland areas, with their
associated bird populations, the rare insect and Myxomycete species
contribute further to the conservation significance of the site.
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| OCTOBER 2012 | ENVIRONMENTAL IMPACT STATEMENT FOR WILLIAM GRANT & SONS LTD.
SITE NAME: RIVER BARROW AND RIVER NORE SAC; SITE CODE:
002162
This site consists of the freshwater stretches of the Barrow/Nore River
catchments as far upstream as the Slieve Bloom Mountains and it also
includes the tidal elements and estuary as far downstream as Creadun
Head in Waterford. The site passes through eight counties – Offaly,
Kildare, Laois, Carlow, Kilkenny, Tipperary, Wexford and Waterford.
Major towns along the edge of the site include Mountmellick,
Portarlington, Monasterevin, Stradbally, Athy, Carlow, Leighlinbridge,
Graiguenamanagh, New Ross, Inistioge, Thomastown, Callan,
Bennettsbridge, Kilkenny and Durrow. The larger of the many tributaries
include the Lerr, Fushoge, Mountain, Aughavaud, Owenass, Boherbaun
and Stradbally Rivers of the Barrow and the Delour, Dinin, Erkina,
Owveg, Munster, Arrigle and King’s Rivers on the Nore. Both rivers rise
in the Old Red Sandstone of the Slieve Bloom Mountains before passing
through a band of Carboniferous shales and sandstones. The Nore, for a
large part of its course, traverses limestone plains and then Old Red
Sandstone for a short stretch below Thomastown. Before joining the
Barrow it runs over intrusive rocks poor in silica. The upper reaches of
the Barrow also runs through limestone. The middle reaches and many
of the eastern tributaries, sourced in the Blackstairs Mountains, run
through Leinster Granite. The southern end, like the Nore runs over
intrusive rocks poor in silica. Waterford Harbour is a deep valley
excavated by glacial floodwaters when the sea level was lower than
today. The coast shelves quite rapidly along much of the shore.
The site is a candidate SAC selected for alluvial wet woodlands and
petrifying springs, priority habitats on Annex I of the E.U. Habitats
Directive. The site is also selected as a candidate SAC for old oak
woodlands, floating river vegetation, estuary, tidal mudflats, Salicornia
mudflats, Atlantic salt meadows, Mediterranean salt meadows, dry heath
and eutrophic tall herbs, all habitats listed on Annex I of the E.U. Habitats
Directive. The site is also selected for the following species listed on
Annex II of the same directive - Sea Lamprey, River Lamprey, Brook
Lamprey, Freshwater Pearl Mussel, Nore Freshwater Pearl Mussel,
Crayfish, Twaite Shad, Atlantic Salmon, Otter, Desmoulin’s Whorl Snail
Vertigo moulinsiana and the Killarney Fern.
Good examples of Alluvial Forest are seen at Rathsnagadan, Murphy’s of
the River, in Abbeyleix estate and along other shorter stretches of both
the tidal and freshwater elements of the site. Typical species seen
include Almond Willow (Salix triandra), White Willow (S. alba), Grey
Willow (S. cinerea), Crack Willow (S. fragilis), Osier (S. viminalis), with
Iris (Iris pseudacorus), Hemlock Water-dropwort (Oenanthe crocata),
Angelica (Angelica sylvestris), Thin-spiked Wood-sedge (Carex strigosa),
Pendulous Sedge (C. pendula), Meadowsweet (Filipendula ulmaria),
Valerian (Valeriana officinalis) and the Red Data Book species Nettle-
leaved Bellflower (Campanula trachelium). Three rare invertebrates
have been recorded in this habitat at Murphy’s of the River. These are:
Neoascia obliqua (Diptera: Syrphidae), Tetanocera freyi (Diptera:
Sciomyzidae) and Dictya umbrarum (Diptera: Sciomyzidae).
A good example of petrifying springs with tufa formations occurs at
Dysart Wood along the Nore. This is a rare habitat in Ireland and one
listed with priority status on Annex I of the EU Habitats Directive. These
hard water springs are characterised by lime encrustations, often
associated with small waterfalls. A rich bryophyte flora is typical of the
habitat and two diagnostic species, Cratoneuron commutatum var.
commutatum and Eucladium verticillatum, have been recorded.
The best examples of old Oak woodlands are seen in the ancient Park
Hill woodland in the estate at Abbeyleix; at Kyleadohir, on the Delour,
Forest Wood House, Kylecorragh and Brownstown Woods on the Nore;
and at Cloghristic Wood, Drummond Wood and Borris Demesne on the
Barrow, though other patches occur throughout the site. Abbeyleix
Woods is a large tract of mixed deciduous woodland which is one of the
only remaining true ancient woodlands in Ireland. Historical records
show that Park Hill has been continuously wooded since the sixteenth
century and has the most complete written record of any woodland in the
country. It supports a variety of woodland habitats and an exceptional
diversity of species including 22 native trees, 44 bryophytes and 92
lichens. It also contains eight indicator species of ancient woodlands.
Park Hill is also the site of two rare plants, Nettle-leaved Bellflower and
the moss Leucodon sciuroides. It has a typical bird fauna including Jay,
Long-eared Owl and Raven. A rare invertebrate, Mitostoma
chrysomelas, occurs in Abbeyleix and only two other sites in the country.
Two flies Chrysogaster virescens and Hybomitra muhlfeldi also occur.
The rare Myxomycete fungus, Licea minima has been recorded from
woodland at Abbeyleix.
Oak woodland covers parts of the valley side south of Woodstock and is
well developed at Brownsford where the Nore takes several sharp bends.
The steep valley side is covered by Oak (Quercus spp.), Holly (Ilex
aquifolium), Hazel (Corylus avellana) and Birch (Betula pubescens) with
some Beech (Fagus sylvatica) and Ash (Fraxinus excelsior). All the trees
are regenerating through a cover of Bramble (Rubus fruticosus agg.),
Foxglove (Digitalis purpurea) Wood Rush (Luzula sylvatica) and Broad
Buckler-fern (Dryopteris dilatata).
On the steeply sloping banks of the River Nore about 5 km west of New
Ross, in County Kilkenny, Kylecorragh Woods form a prominent feature
in the landscape. This is an excellent example of a relatively
undisturbed, relict Oak woodland with a very good tree canopy. The
wood is quite damp and there is a rich and varied ground flora. At
Brownstown a small, mature Oak-dominant woodland occurs on a steep
slope. There is younger woodland to the north and east of it.
Regeneration throughout is evident. The understorey is similar to the
woods at Brownsford. The ground flora of this woodland is developed on
acidic, brown earth type soil and comprises a thick carpet of Bilberry
(Vaccinium myrtillus), Heather (Calluna vulgaris), Hard Fern (Blechnum
spicant), Cow-wheat (Melampyrum spp.) and Bracken (Pteridium
aquilinum).
Borris Demesne contains a very good example of a semi-natural broad-
leaved woodland in very good condition. There is quite a high degree of
natural re-generation of Oak and Ash through the woodland. At the
northern end of the estate Oak species predominate. Drummond Wood,
also on the Barrow, consists of three blocks of deciduous woods situated
on steep slopes above the river. The deciduous trees are mostly Oak
species. The woods have a well established understorey of Holly (Ilex
aquifolium), and the herb layer is varied, with Brambles abundant.
Whitebeam (Sorbus devoniensis) has also been recorded.
Eutrophic tall herb vegetation occurs in association with the various
areas of alluvial forest and elsewhere where the flood-plain of the river is
intact. Characteristic species of the habitat include Meadowsweet
(Filipendula ulmaria), Purple Loosestrife (Lythrum salicaria), Marsh
Ragwort (Senecio aquaticus), Ground Ivy (Glechoma hederacea) and
Hedge Bindweed (Calystegia sepium). Indian Balsam (Impatiens
glandulifera), an introduced and invasive species, is abundant in places.
Floating River Vegetation is well represented in the Barrow and in the
many tributaries of the site. In the Barrow the species found include
Water Starworts (Callitriche spp.), Canadian Pondweed (Elodea
canadensis), Bulbous Rush (Juncus bulbosus), Milfoil (Myriophyllum
spp.), Potamogeton x nitens, Broad-leaved Pondweed (P. natans),
Fennel Pondweed (P. pectinatus), Perfoliated Pondweed (P. perfoliatus)
and Crowfoots (Ranunculus spp.). The water quality of the Barrow has
improved since the vegetation survey was carried out (EPA, 1996).
Dry Heath at the site occurs in pockets along the steep valley sides of the
rivers especially in the Barrow Valley and along the Barrow tributaries
where they occur in the foothills of the Blackstairs Mountains. The dry
heath vegetation along the slopes of the river bank consists of Bracken
(Pteridium aquilinum) and Gorse (Ulex europaeus) species with patches
of acidic grassland vegetation. Additional typical species include Heath
Bedstraw (Galium saxatile), Foxglove (Digitalis purpurea), Common
Sorrel (Rumex acetosa) and Bent Grass (Agrostis stolonifera). On the
steep slopes above New Ross the Red Data Book species Greater
Broomrape (Orobanche rapum-genistae) has been recorded. Where
rocky outcrops are shown on the maps Bilberry (Vaccinium myrtillus) and
Wood Rush (Luzula sylvatica) are present. At Ballyhack a small area of
dry heath is interspersed with patches of lowland dry grassland. These
support a number of Clover species including the legally protected
Clustered Clover (Trifolium glomeratum) - a species known from only one
other site in Ireland. This grassland community is especially well
developed on the west side of the mud-capped walls by the road. On the
east of the cliffs a group of rock-dwelling species occur, i.e. English
Stonecrop (Sedum anglicum), Sheep's-bit (Jasione montana) and Wild
Madder (Rubia peregrina). These rocks also support good lichen and
moss assemblages with Ramalina subfarinacea and Hedwigia ciliata.
Dry Heath at the site generally grades into wet woodland or wet swamp
vegetation lower down the slopes on the river bank. Close to the
Blackstairs Mountains, in the foothills associated with the Aughnabrisky,
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ENVIRONMENTAL IMPACT STATEMENT for WILLIAM GRANT & SONS LTD. | October 2012 |
Aughavaud and Mountain Rivers there are small patches of wet heath
dominated by Purple Moor-grass (Molinia caerulea) with Heather
(Calluna vulgaris), Tormentil (Potentilla erecta), Carnation Sedge (Carex
panicea) and Bell Heather (Erica cinerea).
Saltmeadows occur at the southern section of the site in old meadows
where the embankment has been breached, along the tidal stretches of
in-flowing rivers below Stokestown House, in a narrow band on the
channel side of Common Reed (Phragmites) beds and in narrow
fragmented strips along the open shoreline. In the larger areas of salt
meadow, notably at Carrickcloney, Ballinlaw Ferry and Rochestown on
the west bank; Fisherstown, Alderton and Great Island to Dunbrody on
the east bank, the Atlantic and Mediterranean sub types are generally
intermixed. At the upper edge of the salt meadow in the narrow ecotonal
areas bordering the grasslands where there is significant percolation of
salt water, the legally protected species Borrer’s Saltmarsh-grass
(Puccinellia fasciculata) and Meadow Barley (Hordeum secalinum) (Flora
Protection Order, 1987) are found. The very rare Divided Sedge (Carex
divisa) is also found. Sea Rush (Juncus maritimus) is also present.
Other plants recorded and associated with salt meadows include Sea
Aster (Aster tripolium), Sea Thrift (Armeria maritima), Sea Couch
(Elymus pycnanthus), Spear-leaved Orache (Atriplex prostrata), Lesser
Sea-spurrey (Spergularia marina), Sea Arrowgrass (Triglochin maritima)
and Sea Plantain (Plantago maritima).
Salicornia and other annuals colonising mud and sand are found in the
creeks of the saltmarshes and at the seaward edges of them. The
habitat also occurs in small amounts on some stretches of the shore free
of stones.
The estuary and the other Habitats Directive Annex I habitats within it
form a large component of the site. Extensive areas of intertidal flats,
comprised of substrates ranging from fine, silty mud to coarse sand with
pebbles/stones are present. Good quality intertidal sand and mudflats
have developed on a linear shelf on the western side of Waterford
Harbour, extending for over 6 km from north to south between Passage
East and Creadaun Head, and in places are over 1 km wide. The
sediments are mostly firm sands, though grade into muddy sands
towards the upper shore. They have a typical macro-invertebrate fauna,
characterised by polychaetes and bivalves. Common species include
Arenicola marina, Nephtys hombergii, Scoloplos armiger, Lanice
conchilega and Cerastoderma edule.
The western shore of the harbour is generally stony and backed by low
cliffs of glacial drift. At Woodstown there is a sandy beach, now much
influenced by recreation pressure and erosion. Behind it a lagoonal
marsh has been impounded which runs westwards from Gaultiere Lodge
along the course of a slow stream. An extensive reedbed occurs here.
At the edges is a tall fen dominated by sedges (Carex spp.),
Meadowsweet, Willowherb (Epilobium spp.) and rushes (Juncus spp.).
Wet woodland also occurs. This area supports populations of typical
waterbirds including Mallard, Snipe, Sedge Warbler and Water Rail.
The dunes which fringe the strand at Duncannon are dominated by
Marram grass (Ammophila arenaria) towards the sea. Other species
present include Wild Sage (Salvia verbenaca), a rare Red Data Book
species. The rocks around Duncannon ford have a rich flora of seaweeds
typical of a moderately exposed shore and the cliffs themselves support
a number of coastal species on ledges, including Thrift (Armeria
maritima), Rock Samphire (Crithmum maritimum) and Buck's-horn
Plantain (Plantago coronopus).
Other habitats which occur throughout the site include wet grassland,
marsh, reed swamp, improved grassland, arable land, quarries,
coniferous plantations, deciduous woodland, scrub and ponds.
Seventeen Red Data Book plant species have been recorded within the
site, most in the recent past. These are Killarney Fern (Trichomanes
speciosum), Divided Sedge (Carex divisa), Clustered Clover (Trifolium
glomeratum), Basil Thyme (Acinos arvensis), Hemp nettle (Galeopsis
angustifolia), Borrer’s Saltmarsh Grass (Puccinellia fasiculata), Meadow
Barley (Hordeum secalinum), Opposite-leaved Pondweed (Groenlandia
densa), Autumn Crocus (Colchicum autumnale), Wild Sage (Salvia
verbenaca), Nettle-leaved Bellflower (Campanula trachelium), Saw-wort
(Serratula tinctoria), Bird Cherry (Prunus padus), Blue Fleabane
(Erigeron acer), Fly Orchid (Ophrys insectifera), Broomrape (Orobanche
hederae) and Greater Broomrape (Orobanche rapum-genistae). Of
these the first nine are protected under the Flora Protection Order 1999.
Divided Sedge (Carex divisa) was thought to be extinct but has been
found in a few locations in the site since 1990. In addition plants which
do not have a very wide distribution in the country are found in the site
including Thin-spiked Wood-sedge (Carex strigosa), Field Garlic (Allium
oleraceum) and Summer Snowflake (Leucojum aestivum). Six rare
lichens, indicators of ancient woodland, are found including Lobaria
laetevirens and L. pulmonaria. The rare moss Leucodon sciuroides also
occurs.
The site is very important for the presence of a number of EU Habitats
Directive Annex II animal species including Freshwater Pearl Mussel
(Margaritifera margaritifera and M. m. durrovensis), Freshwater Crayfish
(Austropotamobius pallipes), Salmon (Salmo salar), Twaite Shad (Alosa
fallax fallax), three Lamprey species - Sea (Petromyzon marinus), Brook
(Lampetra planeri) and River (Lampetra fluviatilis), the marsh snail
Vertigo moulinsiana and Otter (Lutra lutra). This is the only site in the
world for the hard water form of the Pearl Mussel M. m. durrovensis and
one of only a handful of spawning grounds in the country for Twaite
Shad. The freshwater stretches of the River Nore main channel is a
designated salmonid river. The Barrow/Nore is mainly a grilse fishery
though spring salmon fishing is good in the vicinity of Thomastown and
Inistioge on the Nore. The upper stretches of the Barrow and Nore,
particularly the Owenass River, are very important for spawning.
The site supports many other important animal species. Those which are
listed in the Irish Red Data Book include Daubenton’s Bat (Myotis
daubentoni), Badger (Meles meles), Irish Hare (Lepus timidus hibernicus)
and Frog (Rana temporaria). The rare Red Data Book fish species Smelt
(Osmerus eperlanus) occurs in estuarine stretches of the site. In addition
to the Freshwater Pearl Mussel, the site also supports two other
freshwater Mussel species, Anodonta anatina and A. cygnea.
The site is of ornithological importance for a number of E.U. Birds
Directive Annex I species including Greenland White-fronted Goose,
Whooper Swan, Bewick’s Swan, Bar-tailed Godwit, Peregrine and
Kingfisher. Nationally important numbers of Golden Plover and Bar-
tailed Godwit are found during the winter. Wintering flocks of migratory
birds are seen in Shanahoe Marsh and the Curragh and Goul Marsh,
both in Co. Laois and also along the Barrow Estuary in Waterford
Harbour. There is also an extensive autumnal roosting site in the
reedbeds of the Barrow Estuary used by Swallows before they leave the
country.
Landuse at the site consists mainly of agricultural activities – many
intensive, principally grazing and silage production. Slurry is spread over
much of this area. Arable crops are also grown. The spreading of slurry
and fertiliser poses a threat to the water quality of the salmonid river and
to the populations of Habitats Directive Annex II animal species within the
site. Many of the woodlands along the rivers belong to old estates and
support many non-native species. Little active woodland management
occurs. Fishing is a main tourist attraction along stretches of the main
rivers and their tributaries and there are a number of Angler Associations,
some with a number of beats. Fishing stands and styles have been
erected in places. Both commercial and leisure fishing takes place on
the rivers. There is net fishing in the estuary and a mussel bed also.
Other recreational activities such as boating, golfing and walking,
particularly along the Barrow towpath are also popular. There is a golf
course on the banks of the Nore at Mount Juliet and GAA pitches on the
banks at Inistioge and Thomastown. There are active and disused sand
and gravel pits throughout the site. Several industrial developments,
which discharge into the river, border the site. New Ross is an important
shipping port. Shipping to and from Waterford and Belview ports also
passes through the estuary.
The main threats to the site and current damaging activities include high
inputs of nutrients into the river system from agricultural run-off and
several sewage plants, overgrazing within the woodland areas, and
invasion by non-native species, for example Cherry Laurel and
Rhododendron (Rhododendron ponticum). The water quality of the site
remains vulnerable. Good quality water is necessary to maintain the
populations of the Annex II animal species listed above. Good quality is
dependent on controlling fertilisation of the grasslands, particularly along
the Nore. It also requires that sewage be properly treated before
discharge. Drainage activities in the catchment can lead to flash floods
which can damage the many Annex II species present. Capital and
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| OCTOBER 2012 | ENVIRONMENTAL IMPACT STATEMENT FOR WILLIAM GRANT & SONS LTD.
maintenance dredging within the lower reaches of the system pose a
threat to migrating fish species such as lamprey and shad. Land
reclamation also poses a threat to the salt meadows and the populations
of legally protected species therein.
Overall, the site is of considerable conservation significance for the
occurrence of good examples of habitats and of populations of plant and
animal species that are listed on Annexes I and II of the E.U. Habitats
Directive respectively. Furthermore it is of high conservation value for
the populations of bird species that use it. The occurrence of several
Red Data Book plant species including three rare plants in the salt
meadows and the population of the hard water form of the Pearl Mussel
which is limited to a 10 km stretch of the Nore, add further interest to this
site. 6.10.2006
SITE NAME: CLARA BOG SAC; SITE CODE: 000572
Clara Bog is situated some 2 km south of Clara village. Much of it is
state-owned and designated a statutory Nature Reserve.
Clara Bog has long been regarded as one of the most important lowland
raised bogs in the country, being the largest remaining example of the
true Midland sub-type. It has well developed hummock and hollow
complexes and one of the few remaining soak systems. The bog
vegetation has been much studied and is well known. Variations in the
proportions of Bog moss (Sphagnum spp.), Heather (Calluna vulgaris)
and Cottongrass (Eriophorum spp.) has been related to ecological
features such as pools, soaks and ridges.
Several rare invertebrate species are associated with the soak, including
the midge, Lasiodiamesa sphagnicola, for which Clara Bog is its only
known Irish site, a click beetle, Ampedus pomorum and another midge,
Parhelophilus consimilis. The bog is also important for the rare moss,
Tetraplodon angustatus, at its only known Irish station here.
Clara Bog supports breeding Merlin (1-2 pairs), a scarce species in
Ireland and one that is listed on Annex I of the EU Birds Directive. Red
Grouse also breeds, along with other common bogland species such as
Meadow Pipit and Skylark.
To the east the transition into calcarous woodland, and to the north the
transition to the esker ridge have been retained and some excellent
examples of esker grassland occur in the site. Some peripheral
reclaimed farmland is also included in the site, because management
undertaken in these areas can have a profound effect upon the rest of
the bog.
The site has been divided into a western and an eastern section by a
road. The eastern part of the site has been damaged by previous
drainage attempts, however, restoration work is in progress. Continuing
peat extraction from the southern margins is also damaging and has
potential effect upon much of the internal bog, including the soak system.
Ideally the whole bog should be managed as a hydrological unit.
Active raised bogs, once characteristic of central Ireland, are now rare
and vulnerable, and have been recognised by the European Union as a
habitat of international importance. Ireland has a special responsibility to
conserve the best of its remaining bogs. Further drainage, peat
extraction, burning or attempted land reclamation is not consistent with
this responsibility. 25.2.1999
Conservation Object ives
European and national legislation places a collective obligation on Ireland
and its citizens to maintain habitats and species in the Natura 2000
network at favourable conservation condition. The Government and its
agencies are responsible for the implementation and enforcement of
regulations that will ensure the ecological integrity of these sites.
Favourable conservation status of a habitat is achieved when:
Its natural range, and area it covers within that range, are stable or increasing, and
The specific structure and functions which are necessary for its long�term maintenance exist and are likely to continue to exist for
the foreseeable future, and
The conservation status of its typical species is favourable.
The favourable conservation status of a species is achieved when:
• Population dynamics data on the species concerned indicate that it is
maintaining itself on a long�term basis as a viable component of its natural
habitats, and
The natural range of the species is neither being reduced nor is likely to be reduced for the
foreseeable future, and
There is, and will probably continue to be, a sufficiently large habitat to maintain its populations on a long-term basis.
Objective: To maintain or restore the favourable conservation
condition of the Annex I habitat(s) and/or the Annex II species for
which the SAC has been selected:
The overall aim of the Habitats Directive is to maintain or restore the
favourable conservation status of habitats and species of community
interest. These habitats and species are listed in the Habitats and Birds
Directives and Special Areas of Conservation and Special Protection
Areas are designated to afford protection to the most vulnerable of them.
These two designations are collectively known as the Natura 2000
network. The maintenance of habitats and species within Natura 2000
sites at favourable conservation condition will contribute to the overall
maintenance of favourable conservation status of those habitats and
species at a national level.
Conservation Objectives for Charleville SAC (SITE CODE: 000571)
Objective: To maintain or restore the favourable conservation condition of
the Annex I habitat(s) and/or the Annex II species for which the SAC has
been selected:
1016 Vertigo moulinsiana
91A0 Old sessile oak woods with Ilex and Blechnum in the British Isles
Conservation Objectives for River Nore and Barrow SAC (SITE CODE:
002162)
Objective: To maintain or restore the favourable conservation condition of
the Annex I habitat(s) and/or the Annex II species for which the SAC has
been selected:
* indicates a priority habitat under the Habitats Directive
1016 Desmoulin's whorl snail Vertigo moulinsiana
1029 Freshwater pearl mussel Margaritifera margaritifera
1092 White�clawed crayfish Austropotamobius pallipes
1095 Sea lamprey Petromyzon marinus
1096 Brook lamprey Lampetra planeri
1099 River lamprey Lampetra fluviatilis
1103 Twaite shad Alosa fallax
1106 Atlantic salmon (Salmo salar) (only in fresh water)
1130 Estuaries
1140 Mudflats and sandflats not covered by seawater at low tide
1310 Salicornia and other annuals colonizing mud and sand
1330 Atlantic salt meadows (Glauco�Puccinellietalia maritimae)
1355 Otter Lutra lutra
1410 Mediterranean salt meadows (Juncetalia maritimi)
1421 Killarney fern Trichomanes speciosum
1990 Nore freshwater pearl mussel Margaritifera durrovensis
3260 Water courses of plain to montane levels with the Ranunculion fluitantis and
Callitricho�Batrachion vegetation
4030 European dry heaths
6430 Hydrophilous tall herb fringe communities of plains and of the montane to
alpine levels
7220 * Petrifying springs with tufa formation (Cratoneurion)
91A0 Old sessile oak woods with Ilex and Blechnum in the British Isles
91E0 * Alluvial forests with Alnus glutinosa and Fraxinus excelsior (Alno�Padion,Alnion incanae, Salicion albae)
Conservation Objectives for Clara Bog SAC (SITE CODE: 000572)
Objective: To maintain or restore the favourable conservation condition of
the Annex I habitat(s) and/or the Annex II species for which the SAC has
been selected:
[1065] Euphydryas (Eurodryas, Hypodryas) aurinia
[6210] Semi�natural dry grasslands and scrubland facies on
calcareous substrates (Festuco Brometalia)(*
important orchid sites)
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ENVIRONMENTAL IMPACT STATEMENT for WILLIAM GRANT & SONS LTD. | October 2012 |
[7110] * Active raised bogs
[7120] Degraded raised bogs still capable of natural regeneration
[7150] Depressions on peat substrates of the Rhynchosporion
[91D0] * Bog woodland
NPWS / DAU
From: Manager Dau [mailto:[email protected]] Sent: 14 May 2012 13:31 To: Katherine Kelleher ([email protected]) Subject: Yours 004-02-2012; Ours G Pre00165/2012 Your Ref: 004-02-2012_letter 001 Our Ref: G Pre00165/2012
Dr Katherine Kelleher Principal Ecologist & Director Kelleher Ecology Services Curraghdermot Castlelyons Co Cork
Re: Scoping for Ecology Section of EIS for proposed new distillery in
Tullamore.
A Chara
I refer to your email of 5th April 2012, with attachment.
Please find below the recommendations of the Department of Arts,
Heritage and the Gaeltacht in relation to nature conservation.
With regard to any EIA for this proposed development an ecological
survey should be carried out of the proposed development site to survey
the habitats and species present. Such surveys should be carried out by
suitably qualified persons at an appropriate time of the year depending
on the species being surveyed for. The EIS should include the results of
the surveys. With regard to any existing records the data of the National
Parks and Wildlife Service (NPWS) should be consulted at www.npws.ie
and the data of the National Biodiversity Data Centre at
http://www.biodiversityireland.ie/ . Reference should be made to the
National Biodiversity Plan and any relevant County Biodiversity Plan. The
EIS should also address the issue of invasive alien species, such as
Japanese Knotweeed, and detail the methods required to ensure they
are not accidentally introduced or spread during construction.
The impact of the development on the flora, fauna and habitats present
should be assessed. In particular the impact of the proposed
development should be assessed, where applicable, with regard to:
• Natura 2000 sites, i.e. Special Areas of Conservation (SAC)
designated under the EC Habitats Directive (Council Directive
92/43/EEC) and Special Protection Areas designated under the EC Birds
Directive (Directive 2009/147 EC),
• Other designated sites, or sites proposed for designation, such
as Natural Heritage Areas, Nature Reserves
and Refuges for Fauna or Flora, designated under the Wildlife Acts of
1976 and 2000,
• Habitats listed on annex I of the Habitats Directive,
• Species listed on Annexes II and IV of the Habitats Directive,
• Habitats important for birds,
• Birds listed on Annex I of the EC Birds Directive,
• Species protected under the Wildlife Acts including protected
flora,
• Habitats that can be considered to be corridors or stepping
stones for the purpose of article 10 of the
Habitats Directive,
• Red data book species,
• and biodiversity in general.
In order to assess the above impacts it may be necessary to obtain
hydrological and/or geological data. In particular any impact on water
table levels or groundwater flows may impact on wetland sites some
distance away. The EIA should assess cumulative impacts with other
plans or projects if applicable. Where negative impacts are identified
suitable mitigation measures should be detailed if appropriate.
Where there are impacts on protected species and their habitats, resting
or breeding places, licenses may be required under the Wildlife Acts or
derogations under the Habitats Regulations. In particular bats and otters
are strictly protected under annex IV of the Habitats Directive and a copy
of Circular Letter NPWS 2/07 entitled “Guidance on Compliance with
Regulation 23 of the Habitats Regulations 1997 – strict protection of
certain species/applications for derogation licences” can be found on the
Department's NPWS website at:
http://www.npws.ie/media/npws/publications/circulars/media,6686,en.pdf
In addition, licenses will be required if there are any impacts on other
protected species or their resting or breeding places, such as on
protected plants, badger setts or birds' nests. Hedgerows should be
maintained where possible. Where trees or hedges have to be removed
there should be suitable planting of native species in mitigation. The EIS
should estimate the length of hedgerow that will be lost, if any. Where
possible hedges and trees should not be removed during the nesting
season (i.e. March 1st to August 31st). Birds' nests can only be
intentionally destroyed under licence issued under the Wildlife Acts of
1976 and 2000. In order to apply for any such licenses or derogations as
mentioned above a detailed survey should be submitted to NPWS which
should have been carried out by appropriately qualified person/s.
In accordance with article 6.3 of the Habitats Directive, this project should
be subject to appropriate assessment screening and if necessary
appropriate assessment. You are referred to the Departmental guidance
document on Appropriate Assessment, which is available on the NPWS
web at
http://www.npws.ie/media/npws/publications/codesofpractice/AA%20Gui
dance%2010-12-09.pdf
You are also referred to the EU Commission guidance entitled
“Assessment of plans and projects significantly affecting Natura 2000
sites. Methodological guidance on the provisions of Article 6(3) and (4) of
the Habitats Directive 92/43/EEC”
which can be downloaded from:
http://ec.europa.eu/environment/nature/natura2000/management/docs/ar
t6/natura_2000_assess_en.pdf
In order to carry out the appropriate assessment screening and/or
prepare a NIS you will need to collect information about the relevant
Natura 2000 sites including their conservation objectives. Details of
designated sites and species can be found on www.npws.ie while
conservation objectives, if not yet available on our web site, can be
obtained by requesting them by completing the data request form on our
website at
http://www.npws.ie/media/npws/publications/Data%20request%20form.d
oc
The Department recommends that you consult with the relevant Local
Authorities to determine if there are any projects or plans which alone or
in combination could impact on any Natura sites.
The above observations and recommendations are based on the papers
submitted to this Department on a pre-planning basis and are made
without prejudice to any observations the Minister may make in the
context of any consultation arising on foot of any development application
referred to the Minister, by the planning authority, in his role as statutory
consultee under the Planning and Development Act 2000, as amended.
Please acknowledge receipt by return email. Thank you.
Is mise, le meas
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| OCTOBER 2012 | ENVIRONMENTAL IMPACT STATEMENT FOR WILLIAM GRANT & SONS LTD.
Muiris Ó Conchúir
____________________________________
Manager
Development Applications Unit (DAU) Built Heritage & Architectural Policy Section Dept of Arts, Heritage and the Gaeltacht Newtown Rd Wexford T: 053-911 7387 Other contact nos. in DAU: 053-911 7516/7482/7382 E: [email protected]
IRSG
From: John Lyden [mailto:[email protected]] Sent: 10 April 2012 11:26 To: [email protected] Subject: Distillery at Tullamore Dr Katherine Kelleher
Dear Katherine
I acknowledge receipt of your consultation letter dated 5 April 2012.
The Irish Raptor Study Group has no comments on this development.
Regards John Lyden, Committee Member IRSG, 10 April 2012
OCC – HERITAGE OFFICER
From: Amanda Pedlow [mailto:[email protected]] Sent: 16 May 2012 14:36 To: [email protected] Subject: 004-02-2012-letter 001
Thank you for your letter. I have no specific data relating to the site
outlined.
Amanda Pedlow Offaly Heritage Officer Offaly County Council 057 9346839
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William Grant & Sons Irish Manufacturing Application for an IPPC Licence Attachments to Application
Doc. Ref. 472-X0004 July 2013
B5.5 List of Planning Applications & Permissions
Date of Grant Reference Description
12th February 2013 PL2/12/261 Planning permission for development comprising: A pot & malt distillery building; gate house; employee car park with 52 spaces; weigh bridge; tank farm; cooling towers; co-products building including a boiler-house; cereal silos; filling store; 13 warehouses; a visitors' centre, incorporating a restaurant and shop area; visitor car parking area, including 70 car spaces and 3 coach spaces; an administration building (the three sisters); a small warehouse; a cooperage; a dunnage warehouse; a grain distillery; a barrel yard; receivers; high level pipe bridging; 2 storm & fire water retention ponds; 2 earth mounds; a new roundabout access to the N52; lighting; perimeter fencing and all associated ancillary services, site development works, earthworks, signage and landscaping. Buildings generally range in height from 5.622m to 17.36m apart from the grain distillery which has a stack height of 32.476m. The development will require the demolition of a derelict farmhouse. A stage 1 Appropriate Assessment (AA) screening report has been submitted to the planning authority with the application. An environmental impact statement (E.I.S.) has been submitted to the planning authority with the application. The proposed development is for an establishment to which the major accidents directive will apply and is for the purposes of an activity requiring an integrated pollution prevention and control licence.
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William Grant & Sons Irish Manufacturing Application for an IPPC Licence Attachments to Application
Doc. Ref. 472-X0004 July 2013
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