Diageo St. James’s Gate BreweryThe St. James’s Gate Brewery is part of Diageo Global Supply,...

Diageo St. James’s Gate Brewery

IPPC Licence Register No. P0301-01

Annual Environmental Report 2009

March 2010

St. James’s Gate Brewery Annual Environmental Report 2009 Diageo Ireland

Licence Register No. P0301-01 March 2010

Table of Contents

1 INTRODUCTION .......................................................................................................................................... 1

1.1 DESCRIPTION OF ACTIVITY .......................................................................................................................... 1 1.1.1 St. James’s Gate Brewery .................................................................................................................. 1 1.1.2 Beverage Blending Agents Plant ....................................................................................................... 2

1.2 MANAGEMENT STRUCTURES ....................................................................................................................... 2 1.3 ENVIRONMENTAL POLICY ............................................................................................................................ 3 1.4 ORGANISATIONAL STRUCTURE – ENVIRONMENTAL MANAGEMENT ............................................................ 4

2 SUMMARY INFORMATION ...................................................................................................................... 6 2.1 SELF MONITORING DATA ............................................................................................................................. 6

2.1.1 Emissions to Sewer ............................................................................................................................ 6 2.1.1.1 Overview .................................................................................................................................................. 6 2.1.1.2 Non-Compliances ................................................................................................................................... 10

2.1.2 Emissions to Water .......................................................................................................................... 17 2.1.3 Emissions to Atmosphere ................................................................................................................. 18

2.1.3.1 Combined Heat & Power Plant .............................................................................................................. 18 2.1.3.2 Roasthouse .............................................................................................................................................. 20 2.1.3.3 Grain Intake ............................................................................................................................................ 21

2.1.4 Waste Management .......................................................................................................................... 22 2.2 MONITORING AND ENFORCEMENT ............................................................................................................. 30

2.2.1 Agency Site Audit ............................................................................................................................. 30 2.2.2 Agency Monitoring – Emissions to Sewer ....................................................................................... 30 2.2.3 Agency Monitoring – Emissions to Atmosphere ............................................................................. 32 2.2.4 Third-Party Audits ........................................................................................................................... 32

2.2.4.1 ISO 14001 Audits ................................................................................................................................... 32 2.2.4.2 IS 393 Audit ........................................................................................................................................... 32

2.3 ENERGY AND WATER CONSUMPTION ........................................................................................................ 33 2.3.1 Energy Consumption ....................................................................................................................... 33 2.3.2 Water Consumption ......................................................................................................................... 33

2.4 ENVIRONMENTAL INCIDENTS AND COMPLAINTS ....................................................................................... 34 2.4.1 Environmental Incidents .................................................................................................................. 34 2.4.2 Environmental Complaints .............................................................................................................. 36

2.5 AER RETURNS WEBFORM & EUROPEAN POLLUTANT RELEASE AND TRANSFER REGISTER (E-PRTR) .. 37 3 MANAGEMENT OF THE ACTIVITY .................................................................................................... 38

3.1 ENVIRONMENTAL & ENERGY MANAGEMENT PLAN .................................................................................. 38 3.2 ENVIRONMENTAL & ENERGY MANAGEMENT PROGRAMME ..................................................................... 39

3.2.1 Report on Environmental & Energy Management Programme for 2009 ...................................... 39 3.2.2 Environmental and Energy Management Programme for 2010 .................................................... 54

4 LICENCE-SPECIFIC REPORTS ............................................................................................................. 69 4.1 NOISE ......................................................................................................................................................... 69

4.1.1 Noise Survey..................................................................................................................................... 69 4.1.2 Noise Reduction Programme ........................................................................................................... 70

4.2 TESTING AND INSPECTION OF UNDERGROUND TANKS AND PIPELINES ..................................................... 71 4.2.1 Bunding ............................................................................................................................................ 71 4.2.2 Pipelines ........................................................................................................................................... 71

4.3 HYDROGEOLOGICAL INVESTIGATION ........................................................................................................ 72 ANNEX A: AER RETURNS WEBFORM AND EUROPEAN POLLUTANT RELEASE AND TRANSFER

REGISTER


Licence Register No. P0301-01 1 March 2010

1 INTRODUCTION Licensee: St. James’s Gate Brewery Location of Activity: St. James’s Gate, Dublin 8 Licence Register Number: P0301-01 The St. James’s Gate Brewery (SJGB) is based in Dublin at National Grid Reference 3392 E, 1430 N. It covers an area circa 24 hectares. The Brewery was granted an Integrated Pollution Control (IPC) licence on the 4th July 2000. This licence was converted to an Integrated Pollution Prevention and Control (IPPC) Licence on 9th November 2005 through the addition of Amendment A to the licence. Condition 2.9.2 requires the Brewery to prepare an Annual Environmental Report (AER) for submission to the Environmental Protection Agency (EPA). This report, in compliance with condition 2.9.2 of the IPPC licence, details the environmental performance at the site for the period January to December 2009 and has been prepared in accordance with the Guidance Note for Annual Environmental Reports, published in October 2000. 1.1 Description of Activity 1.1.1 St. James’s Gate Brewery The Brewery is engaged in the brewing of stout for the UK, Irish, mainland Europe and North American market. Following the closure of the Guinness Park Royal Brewery in London in mid-2005, all UK stout production was transferred to St. James’s Gate. As a consequence the St. James’s Gate site underwent a capacity expansion programme during 2005. Stout is produced using traditional brewing materials: malt, barley, roast barley, hops, water and yeast. In the Brewhouse, malt and barley are milled into coarse flour (grist), keeping the barley husk material as intact as possible. The milled grist is then mixed with hot water in a process known as mashing, in which the starches in the malt are converted into fermentable sugars. The porridge-like mash is transferred to a kieve and the sweet wort is filtered off to a third vessel, the kettle. In the kettle, hop extract is added and the wort is boiled. The hops are used to give bitterness, aroma, flavour and some preservative value to the beer, while roast barley provides the unique colour and some of the flavour components of Stout. After boiling in the kettle the wort is decanted and pumped, with cooling en route, to the Fermentation Plant. The Fermentation Plant receives chilled stout wort directly from the Brewhouse. Yeast is added to carry out the primary fermentation, converting the sugars in the wort into alcohol and carbon



dioxide, which is a by-product of the fermentation process. Afterwards, stout is centrifuged to remove the yeast and the green beer is matured in Maturation Vessels, clarified and blended to Bright Beer Tanks for subsequent packaging in the Keg Plant or despatch in bulk from the Tank Station. In the Keg Plant, beer from Bright Beer Tanks is pasteurised before racking into four sizes of kegs (60, 50, 30 and 20 litres) for distribution to the domestic and export markets or is dispatched in bulk via tankers to packaging sites within Guinness Supply in Ireland and UK. Beer is produced 24 hours per day and 365 days per year. There are 200 people currently employed at the Brewery in production units. 1.1.2 Beverage Blending Agents Plant The Plant consists of a Brewhouse, evaporation/concentration unit, a storage tank farm and a packaging facility. It is designed to produce a concentrate, which is exported to over 50 countries worldwide. The concentrate is produced using malt, roast barley, yeast, hops and water. It will go on to produce bottle, canned and draught products wherever Guinness stout is sold. The product is exported in Unitanks, flexitanks and road tankers via Dublin port. 1.2 Management Structures The St. James’s Gate Brewery is part of Diageo Global Supply, which in turn is a subsidiary of Diageo plc. The Brewery has a structured management approach to the operation of the business in terms of product quality, environment, process control, safety, training and analytical capability. Management systems for quality, environment, energy, safety, food safety and training are audited on an on-going basis through internal audits and external third-party surveillance audits. Registration to specific management systems has been achieved as follows:

• ISO 9001: 2008 Quality Management 2009 • ISO 14001 Environmental Management 2004 • Training - Excellence Through People (FAS) 1999 • EN 16001:2009 Energy Management Standard 2009 • ISO 22000 Food Safety Management 2007 • OHSAS 18001 OH&S Occupational Health and Safety Management 2008



1.3 Environmental Policy The policy is given below. St. James’s Gate Brewery The St. James’s Gate Brewery will manage its operations, products and services in a way, which supports environmental sustainability and local biodiversity. It will operate in an environmentally responsible way to protect and enhance our people, brands and the communities in which we work and live. It will strive to become a truly sustainable organisation, by reducing our carbon footprint and contribute zero harm to the environment in line with our Destination 2011 strategy. It will:

• comply with the requirements of the Integrated Pollution, Prevention and Control licence.

• comply with all relevant Environmental legislation, legal and other requirements, that

relate to the Environmental Aspects.

• comply with all Diageo corporate policies and procedures.

• minimise energy and water use, minimise solid waste, greenhouse gas, air and effluent emissions at source and optimise CO2 recovery.

• optimise the use of raw materials.

• undertake a programme of continuous improvement in environmental performance,

with an emphasis on pollution prevention.

• train and motivate employees to conduct their work in a environmentally-responsible manner.

• ensure that adequate resources are deployed to enable the environmental policy to be

implemented.

• communicate the environmental policy to all interested parties and make it publicly available.

Our commitment to the Environmental Policy is underpinned by the Company’s core values, which include “Proud of What We Do” and “Be the Best”. Colin O’Brien Operations Manager St. James’s Gate Brewery May 2008



1.4 Organisational Structure – Environmental Management The organisational chart for the Brewery, including the elements of environmental management, is given in Figure 1.

St.James’s Gate Brewery Annual Environmental Report 2009 Diageo Ireland


Figure 1: Environmental and Energy Management Structure

Environmental and Energy Management Structure

TechnicalTrainingManager

Export Warehouse Warehousing-Outside Yard

Head of Logistics

RegulatoryManager

RiskManager

Environment

DirectorProcess Support &

Innovation

BBA Manager

Head ofBeverage

Blending Agents

Third-partyUtilities&

CHP Plant

Third-partyGrain Intake

ContractsManagers

Third-partyWaste

Management

FacilitiesManager

TechnicalSupportManager

BrewingShift

Manager

BrewingManager

Operations Mgr.QA Laboratory

EnvironmentalManager

SystemsManager

PackagingShift

Manager

PackagingProductionManager

Operations ManagerSt. James's Gate

Brewery

Brewing DirectorGuinness & European RTD Supply



2 SUMMARY INFORMATION 2.1 Self Monitoring Data Except where otherwise stated, summary information is provided for the period from January 2009 to December 2009 inclusive, as specified in the EPA’s Guidance Note for Annual Environmental Reports. The information is presented in line with the Guidance Note as an annualised mass emission figure, derived from the average measured mass emission value multiplied by the duration of the emission. 2.1.1 Emissions to Sewer The following sub-sections present the Brewery’s self monitoring data for emissions to sewer at the three emission points (SE-1, SE-2 and SE-3) during 2009. 2.1.1.1 Overview There are three licensed emission points to sewer from the site: SE-1, SE-2 and SE-3. The discharge from SE-1 consists of process effluent and surface water run-off and is screened and then pH-adjusted in the on-site Effluent Neutralisation Plant before being discharged to the Dublin City Council sewer for final treatment in the Ringsend Wastewater Treatment Plant. In late 2005, the process emission from SE-2 was diverted to the Effluent Neutralisation Plant, ultimately discharging via SE-1, and therefore since 2006, only surface water run-off has been discharged via this emission point. The discharge of process emissions from SE-3 was also discontinued in late 2005 and only surface water run-off has been discharged from this point since then. Samples from all three emission points are collected on a 24-hour flow-proportional composite basis and are monitored for the parameters set out in Table 1. Table 1: Monitoring Frequency at SE-1, SE-2 and SE-3

Continuous Daily Monthly Flow BOD Sulphates (as SO4) Temperature COD Fats, oils & grease pH Suspended Solids Detergents (as MBAS) Total nitrogen (as N) Ammoniacal nitrogen Total oxidised nitrogen Total phosphorus (as P)

In November 2009, the Brewery submitted a proposal to the Agency to reduce the frequency of monitoring at SE-2 and SE-3 from daily to monthly. In December 2009, the Agency agreed to this proposal and therefore from 2010 onwards the monitoring frequency for SE-2 and SE-3 will be reduced to a monthly frequency.



Table 2 summarises the discharge from the main emission point to sewer, SE-1, during 2009, with the trend from 2001 to 2009 for BOD, COD and Suspended Solids annual loads shown in Figure 2. In 2009, the annual loads of BOD, COD and Suspended Solids from SE-1 were all below the limits set out in the licence. Table 2: Emissions to Sewer for Reference Point SE-1

Parameter Mass Emission (kg) 2008

Mass Emission (kg) 2009

Licensed Mass Emission (kg)

Volume (m3) 1,059,219 956,429 2,737,500 BOD 2,558,952 2,294,073 5,475,000 COD 4,251,645 3,535,134 10,950,000 Suspended Solids 960,524 720,925 3,832,500 Sulphates (as SO4) 60,761 71,808 1,095,000 Fats, oils and grease 8,950 15,609 273,750 Detergents (as MBAS) 4,029 1,969 273,750

Parameter Average Concentration(mg/l) 2008

Average Concentration(mg/l) 2009

Total Nitrogen (as N) 69.10 35.0 Ammoniacal Nitrogen 15 8.0 Total Oxidised Nitrogen 1.55 1.0 Total Phosphorous (as P) 15.61 22.6

Figure 2: Trend in BOD, COD & SS Annual Load from SE-1

Licence Limit

Licence Limit

Licence Limit

0

2,000

4,000

6,000

8,000

10,000

12,000

BOD COD SS

Ann

ual L

oad

(thou

sand

kg)

Trend in BOD, COD & SS Annual Load from SE-1

200120022003200420052006200720082009



Table 3 summarises the discharge from the emission point to sewer, SE-2, during 2009, with the trend from 2001 to 2009 for BOD, COD and Suspended Solids annual loads shown in Figure 3. In 2009, the annual loads of BOD, COD and Suspended Solids from SE-2 were all below the limits set out in the licence. Table 3: Emissions to Sewer for Reference Point SE-2




Volume (m3) 48,586 58,726 438,000 BOD 1,766 2,972 876,000 COD 4,232 6,552 1,752,000 Suspended Solids 2,684 2,140 175,200 Sulphates (as SO4) 4,104 2,833 175,200 Fats, oils and grease 56.94 58.7 43,800 Detergents (as MBAS) 11.32 9.5 43,800



Total Nitrogen (as N) 11.21 7.6 Ammoniacal Nitrogen 4.1 4.4 Total Oxidised Nitrogen 3.4 2.1 Total Phosphorous (as P) 1.47 1.5


Licence Limit

Licence Limit

Licence Limit

0

200

400

600

800

1,000

1,200

1,400

1,600

1,800

2,000

BOD COD SS

Ann

ual L

oad

(thou

sand

kg)


200120022003200420052006200720082009



Table 4 summarises the discharge from the emission point to sewer, SE-3, during 2009, with the trend from 2001 to 2009 for BOD, COD and Suspended Solids annual loads shown in Figure 4. In 2009, the annual loads of BOD, COD and Suspended Solids from SE-3 were all below the limits set out in the licence. Table 4: Emissions to Sewer for Reference Point SE-3




Volume (m3) 3,944 1,194 401,500 BOD 233 11 803,000 COD 22 74 1,606,000 Suspended Solids 337 52 160,600 Sulphates (as SO4) 21.54 25 160,600 Fats, oils and grease 1.825 1.2 40,150 Detergents (as MBAS) 0.36 0.19 40,150



Total Nitrogen (as N)

6.50 4.6

Ammoniacal Nitrogen 1.10 2.1 Total Oxidised Nitrogen 1.33 1.5 Total Phosphorous (as P) 0.243 0.37


Licence Limit

Licence Limit

Licence Limit

0

200

400

600

800

1,000

1,200

1,400

1,600

1,800

2,000

BOD COD SS

Ann

ual L

oad

(thou

sand

kg)


200120022003200420052006200720082009



2.1.1.2 Non-Compliances Emission Point SE-1 – BOD Table 5 summarises the number of non-compliances for emissions of BOD to sewer at SE-1 in 2009. Table 5: Non Compliances for Emission Point SE-1 – BOD (2009)

BOD Concentration BOD Load Daily Weekly Monthly Annual Daily Weekly Monthly Annual January 0 0 1 - 0 0 0 - February 0 1 1 - 0 0 0 - March 0 1 1 - 0 0 0 - April 0 1 1 - 0 0 0 - May 0 0 0 - 0 0 0 - June 0 0 0 - 0 0 0 - July 0 0 0 - 0 0 0 - August 0 0 0 - 0 0 0 - September 0 0 0 - 0 0 0 - October 0 0 0 - 0 0 0 - November 0 0 1 - 0 0 0 - December 0 0 0 - 0 0 0 - January – December

0 3 5 1 0 0 0 0

Note 1: Compliance is assessed in accordance with Condition 3.3.2 of the licence. As in 2008, in 2009 the annual BOD load has continued to reduce through implementation of the Effluent Reduction Programme. However, as shown in Table 5, there were a total of eight non-compliances in relation to the BOD concentration during 2009. These non-compliances were attributable to a combination of factors, including our reduction in effluent flow arising from our water usage reduction initiatives, which results in higher concentration effluent; production activities (e.g. accidental release of small quantities of product); and the growth of biomass in the effluent plant, for which we have implemented a corrective action plan. There were no non-compliances in relation to BOD load. A number of initiatives under the Effluent Reduction Programme continued in 2009 which contributed to continuing reduction in BOD load. Figure 5 shows the average daily BOD concentration since 2001 and Figure 6 shows the average daily BOD load since 2001.



Figure 5: Annual Trend in Average Daily BOD Concentration

0

500

1,000

1,500

2,000

2,500

3,000

3,500

4,000

4,500

2001 2002 2003 2004 2005 2006 2007 2008 2009

BO

D C

once

ntra

tion

(mg/

l)Average Daily BOD Concentration at SE-1

Figure 6: Annual Trend in Average Daily BOD Load

0

5

10

15

20

2001 2002 2003 2004 2005 2006 2007 2008 2009

BO

D L

oad

(tonn

es/d

ay)

Average Daily BOD Load at SE-1



Emission Point SE-1 – COD There were no non-compliances in relation to emissions of COD from SE-1 during 2009, as summarised in Table 6. Table 6: Non Compliances for Emission Point SE-1 – COD (2009)

COD Concentration COD Load Daily Weekly Monthly Annual Daily Weekly Monthly Annual January 0 0 0 - 0 0 0 - February 0 0 0 - 0 0 0 - March 0 0 0 - 0 0 0 - April 0 0 0 - 0 0 0 - May 0 0 0 - 0 0 0 - June 0 0 0 - 0 0 0 - July 0 0 0 - 0 0 0 - August 0 0 0 - 0 0 0 - September 0 0 0 - 0 0 0 - October 0 0 0 - 0 0 0 - November 0 0 0 - 0 0 0 - December 0 0 0 - 0 0 0 - January – December

0 0 0 0 0 0 0 0

Note 1: Compliance is assessed in accordance with Condition 3.3.2 of the licence.



Emission Point SE-1 – Suspended Solids Table 7 summarises the number of non-compliances for Suspended Solids emissions to sewer at SE-1 in 2009. Table 7: Non Compliances for Emission Point SE-1 – Suspended Solids (2009)

Concentration Load January 0 0 February 1 0 March 0 0 April 3 0 May 0 0 June 0 0 July 0 0 August 0 0 September 0 0 October 0 0 November 0 0 December 0 0 January – December 4 0

Note 1: Compliance is assessed in accordance with Condition 3.3.2 of the licence. Note 2: Since May 2009, the emission limit value on suspended solids at SE-1 has increased from 1,400 mg/l

to 2,000 mg/l following agreement from both the Local Authority and the Agency. There were a total of four non-compliances in relation to Suspended Solids at emission point SE-1 in 2009, compared to five in 2008, seven in 2007, six in 2006 and twelve in 2005. The non-compliances in 2009 were attributed to the biomass growth in the effluent plant, for which we have implemented a corrective action plan.



Emission Point SE-1 – pH There were no non-compliances in relation to pH at SE-1 during 2009, as summarised in Table 8. Table 8: Non Compliances for Emission Point SE-1 – pH (2009)

Daily pH January 0 February 0 March 0 April 0 May 0 June 0 July 0 August 0 September 0 October 0 November 0 December 0 January – December 0

Note 1: Compliance is assessed in accordance with Condition 3.3.2 of the licence. Emission Point SE-1 – Sulphates, Detergents & Fats, Oils & Grease There were no non-compliances in relation to sulphates, detergents or fats, oils & grease at SE-1 during 2009, as summarised in Table 9. Table 9: Non Compliances for Emission Point SE-1 – SO4, MBAS & OFG (2009)

Sulphates Detergents Fats, Oils & Grease Concentration Load Concentration Load Concentration Load January 0 0 0 0 0 0 February 0 0 0 0 0 0 March 0 0 0 0 0 0 April 0 0 0 0 0 0 May 0 0 0 0 0 0 June 0 0 0 0 0 0 July 0 0 0 0 0 0 August 0 0 0 0 0 0 September 0 0 0 0 0 0 October 0 0 0 0 0 0 November 0 0 0 0 0 0 December 0 0 0 0 0 0 January – December

0 0 0 0 0 0




Emission Point SE-2 In November 2005 the process effluent flow to SE-2 was diverted to SE-1 and this has improved compliance with the limits set out in our licence for this emission point. Table 10 summarises the number of non-compliances for emissions to sewer at SE-2 in 2009. Table 10: Non Compliances for Emission Point SE-2 (2009)

pH BOD COD SS SO4 MBAS OFG January 0 0 0 0 0 0 0 February 0 0 0 0 0 0 0 March 0 0 0 0 0 0 0 April 0 0 0 0 0 0 0 May 1 1 1 1 0 0 0 June 0 0 0 0 0 0 0 July 0 0 0 0 0 0 0 August 0 0 0 0 0 0 0 September 0 0 0 0 0 0 0 October 0 0 0 0 0 0 0 November 0 0 0 0 0 0 0 December 0 0 0 0 0 0 0 January – December 1 1 1 1 0 0 0

Note 1: Compliance is assessed in accordance with Condition 3.3.2 of the licence. The non-compliances in relation to pH, BOD, COD and suspended solids in May 2009 were attributed to the accidental release of product from a unitank in the vicinity of SE-2; this area has since been designated as a non-storage location to avoid a recurrence of this event. There were no non-compliances in relation to sulphates, detergents or fats, oils & grease at SE-2 during 2009.



Emission Point SE-3 The process effluent flow to SE-3 has been diverted to SE-1 and this has improved compliance with the limits set out in our licence for this emission point. There were no non-compliances in relation to emissions to sewer at SE-3 during 2009, as summarised in Table 11. Table 11: Non Compliances for Emission Point SE-3 (2009)

pH BOD COD SS SO4 MBAS OFG January 0 0 0 0 0 0 0 February 0 0 0 0 0 0 0 March 0 0 0 0 0 0 0 April 0 0 0 0 0 0 0 May 0 0 0 0 0 0 0 June 0 0 0 0 0 0 0 July 0 0 0 0 0 0 0 August 0 0 0 0 0 0 0 September 0 0 0 0 0 0 0 October 0 0 0 0 0 0 0 November 0 0 0 0 0 0 0 December 0 0 0 0 0 0 0 January – December 0 0 0 0 0 0 0




2.1.2 Emissions to Water There is a single licensed emission point to water from the site, SW-1, which discharges to the River Liffey. Up to March 2007, this emission point discharged cooling water which originated from an underground well at the site. However, in March 2007, the discharge of cooling water ceased and since then only surface water has been discharged via an interceptor at SW-1. The licence requires that flow, temperature and pH are monitored on a continuous basis; that BOD and COD are monitored on a monthly basis; that suspended solids, sulphates (as SO4), fats, oils and grease, detergents (as MBAS), ammoniacal nitrogen, total oxidised nitrogen, total phosphorus (as P) and heavy metals are monitored on a quarterly basis; and that pesticides and biocides are monitored annually at SW-1. In addition, the licence requires monitoring at two locations in the river upstream (ASW-2) and downstream (ASW-3) of SW-1. However, since there is no longer any process emission to surface water from SW-1, monitoring at this location has been discontinued. The Brewery continues to carry out monitoring at the two ambient monitoring locations (ASW-2 and ASW-3) in accordance with the conditions set out in the licence. The results of this monitoring are summarised in Table 12. Table 12: Ambient Water Monitoring at ASW-2 and ASW-3 (2009)

Parameter Monitoring Frequency

Average Annual Value ASW-2 ASW-3

pH Monthly 7.95 8.00 BOD (mg/l) Monthly 2.4 2.8 COD (mg/l) Monthly 18.5 20.8 Suspended Solids (mg/l) Monthly 9.8 9.6 Fats, Oils & Grease (mg/l) Quarterly 1 1 Detergents (as MBAS) (mg/l) Quarterly 0.09 0.08 Ammonia (as N) Quarterly 0.23 0.21 Total Oxidised Nitrogen (mg/l) Quarterly 1.34 1.40 Total Phosphorous (as P) (mg/l) Quarterly 0.09 0.13 Sodium (mg/l) Quarterly 251 203



2.1.3 Emissions to Atmosphere The following subsections summarise the emissions to atmosphere from our licensed emission points at the Combined Heat & Power Plant (A1-3, A1-4, A1-5, A1-6 and A1-7), the afterburners in the Roasthouse (A2-1 and A2-2) and the grain intake area (A2-3, A2-4 and A2-5). 2.1.3.1 Combined Heat & Power Plant There are three main emission points associated with the three CHP turbines (A1-3, A1-4 and A1-5), each of which is monitored for Nitrogen Oxides (as NO2) on an annual basis. There is also a bypass stack on Turbine 1 (A1-6) and a stand-by boiler (A1-7), which are also monitored for Nitrogen Oxides on an annual basis. Monitoring of the emissions from emission points A1-3, A1-4, A1-5 and A1-7 was carried out in February 2009 and monitoring at emission point A1-6 was carried out in July 2009. Table 13 summarises the monitoring results. Table 13: Emissions to Atmosphere from CHP Plant (2009)

Emission Point NOX Concentration (mg/Nm3)

Licence Limit (mg/m3)

Mass Emission (kg) Note 2

Licence Limit (kg/year)

A1-3 40 80 20,584 43,836 A1-4 61 80 24,366 43,836 A1-5 78 Note 1 80 17,886 43,836 A1-6 33 80 * Note 3 43,836 A1-7 59 66 35 13,754

Note 1: Monitoring of the emission from A1-5 was repeated in November 2009 following a monitoring survey carried out on behalf of the Agency (refer to Section 2.2.3). The results of the November survey showed a NOX concentration of 58 mg/Nm3.

Note 2: The mass emission is based upon the measured concentration, the maximum volumetric flow rate and the operational hours for each stack.

Note 3: A1-6 is the bypass stack on Turbine 1 (A1-3) and only operates at low load. There were no non-compliances of emissions to atmosphere from the CHP plant during 2009, with a small reduction in NOX mass emission for all stacks except A1-5, which returned to the 2007 level. Table 14 summarises the performance of the CHP plant during 2009. Table 14: CHP Plant Summary (2009)

2008 2009 NOX emissions (kg) 57,072 62,871 Energy input (MWh) 321,667 300,723 Electricity generated (MWh) 74,635 73,362 CO2 emissions (tonnes) 57,521 57,821



Figure 7 shows the historical mass emissions of NOX from the CHP plant from 2001 to 2009. Figure 7: Mass Emissions of NOX to Atmosphere from CHP Plant (2001 to 2009)

Licence Limit Licence Limit Licence Limit Licence Limit

Licence Limit

0

5,000

10,000

15,000

20,000

25,000

30,000

35,000

40,000

45,000

50,000

A1-3 A1-4 A1-5 A1-6 A1-7

NOX

Annu

al L

oad

(kg/

year

)

Emissions to Atmosphere from CHP Plant (NOX)

2001 2002 2003 2004 2005 2006 2007 2008 2009



2.1.3.2 Roasthouse There are two licensed emission points from the afterburners on the roasthouse (A2-1 and A2-2) each of which is monitored for Total Organics and Nitrogen Oxides on an annual basis. The annual monitoring was carried out in October 2009 and the results are summarised in Table 15. Table 15: Emission to Atmosphere from Roasthouse Afterburners (2009)

Emission Point

Parameter Measured Value

Licence Limit

Mass Emission (kg/year)

Licence Limit (kg/year)

A2-1

Total Organics (as C) (kg/h)

0.06 0.2 526 1,752

Nitrogen Oxides (as NO2) (mg/m3)

32 61 1,436 2,880

A2-2

Total Organics(as C) (kg/h)

0.08 0.4 701 3,504

Nitrogen Oxides (as NO2) (mg/m3)

37 75 1,659 3,541

There were no non-compliances in relation to emissions to atmosphere from either A2-1 or A2-2 during 2009. Figure 8 and Figure 9 show the annual mass emissions from A2-1 and A2-2 from 2001 to 2009, respectively. Figure 8: Mass Emission to Atmosphere from A2-1 (2001 to 2009)

Licence Limit

Licence Limit

0

2,000

4,000

6,000

8,000

10,000

12,000

Total Organics (as C) Nitrogen Oxides (as NO2)

Annu

al M

ass

Emis

sion

(kg/

year

)

Mass Emission to Atmosphere from A2-1

2001

2002

2003

2004

2005

2006

2007

2008

2009



Figure 9: Mass Emission to Atmosphere from A2-2 (2001 to 2009)

Licence Limit Licence Limit

0

2,000

4,000

6,000

8,000

10,000

12,000

Total Organics (as C) Nitrogen Oxides (as NO2)

Annu

al M

ass

Emis

sion

(kg/

year

)Mass Emission to Atmosphere from A2-2

2001

2002

2003

2004

2005

2006

2007

2008

2009

2.1.3.3 Grain Intake There are three licensed emission points at the grain intake area (A2-3, A2-4 and A2-5), each of which is monitored for total particulate matter on an annual basis. The annual monitoring was carried out in September and October 2009 and the results are summarised in Table 16. Table 16: Emission to Atmosphere of Total Particulates from Grain Intake (2009)

Emission Point

Total Particulate

Matter (mg/Nm3)

Licence Limit

(mg/Nm3)

Volumetric Flow Rate (Nm3/h)

Licence Limit

(Nm3/h)

Mass Emission (kg/year)

Licence Limit

(kg/year)

A2-3 4.2 50 21,951 28,900 807.6 12,658 A2-4 <1 50 21,406 24,450 187.5 10,709 A2-5 4.0 50 14,078 14,650 493.3 6,417

There were no non-compliances in relation to emissions to atmosphere from the grain intake area during 2009.



2.1.4 Waste Management Condition 8.3 of the licence requires the Brewery to maintain a waste register to record the following details:

(a) The names of the agent and transporter of the waste. (b) The name of the persons responsible for the ultimate disposal / recovery of the waste. (c) The ultimate destination of the waste. (d) Written confirmation of the acceptance and disposal / recovery of any hazardous

waste consignments sent off-site. (e) The tonnages and EWC Code for the waste materials listed in Schedule 4(i)

Hazardous Wastes for Disposal / Recovery and Schedule 4(ii) Other Wastes for Disposal / Recovery, sent off-site for disposal / recovery.

(f) Details of any rejected consignments. Table 17 presents a summary of the annual waste arisings for hazardous and non-hazardous wastes at the Brewery. There were no rejected consignments in 2009.



Table 17: Summary of Annual Waste Arisings for 2009

EWC HAZ (Y/N)

Description of Waste Quantity (tonnes/ annum, unless otherwise

specified)

Method of Disposal/ Recovery

Location of Disposal/ Recovery

Name of Waste Disposal/ Recovery

Contractor (if applicable)

Waste Collectors

Permit Number

02 07 01 N Waste grain 107.8 R3 (b) Miltown Composting Ltd., Fethard, Co. Tipperary

A Quick Sharp Ltd., T/A AQS Environmental Solutions

WCP-MO-09-0292-01

02 07 04 N Waste essences & flavourings

0.70 R13 (c) ATM, Rotterdam, Netherlands

Indaver Ireland / Quay Logistics

WCP- DC-08-1121-01

02 07 04 N Waste essences & flavourings

0.59 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

02 07 05 N Effluent Plant Screenings 137 R3 (b) Ormonde Organics, Co. Waterford

Ormonde Organics Limited

WCP-OY-08-0595-01

02 07 99 N Lab smalls 0.08 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

02 07 99 N Spent Grains 71,352 Not applicable (animal feed)

Note 1

Not applicable (animal feed) Note 1

KW Forage Systems Ltd. Not applicable (animal feed)

Note 1 02 07 99 N Black Spent Grain 13,711 R10 (b) Bord Na Móna, Kildare KW Forage Systems

Ltd/Agrilife CP D240/2

02 07 99 N Surplus Yeast (FBP) 9,919 Not applicable (animal feed)

Note 1



Note 1 02 07 99 N Barley Screenings / Dust

(Roasthouse and GFE) 1,124 R10 (b) Bord Na Móna, Kildare KW Forage Systems

Ltd./Michael Dunne WCP-DC-08-

1146-01 02 07 99 N Sample Beers (Technology

House & QA Department) 3.2 D8 (b) Dublin Dublin City Council N/A

02 07 99 N Wort Sample (Technology House & QA Department)

0.03 D8 (b) Dublin Dublin City Council N/A

02 07 99 N Concentrated Product Samples (Tech. House)

0.04 D8 (b) Dublin Dublin City Council N/A



Table 17: Summary of Annual Waste Arisings for 2009 (cont/d)

EWC HAZ (Y/N)


specified)





Waste Collectors

Permit Number

02 07 99 N Spent Grain (Technology House)

1,934 Not applicable (animal feed)

Note 1



Note 1 15 01 02 N Plastic 1.7 R5 (b) Greyhound Recycling,

Clondalkin, Dublin. Greyhound Recycling and Recovery Ltd.

WCP-DC-08-1154-01

15 01 03 N Wood 35.1 R3 (b) Greyhound Recycling, Clondalkin, Dublin.

Greyhound Recycling and Recovery Ltd.

WCP-DC-08-1154-01

15 01 04 N Waste kegs 37.2 R4 (b) P. Carney Ltd., Kells, Co. Meath

P. Carney Ltd. CP D 1003/7

15 02 03 N Spent carbon 6.2 R3 (b) Waddock Composting, Carlow

A Quick Sharp Ltd., T/A AQS Environmental Solutions

WCP-MO-09-0292-01

17 04 07 N Scrap Metal 56.7 R4 (b) Greyhound Recycling, Clondalkin, Dublin.


WCP-DC-08-1154-01

20 01 01 N Paper 28.2 R3 (b) Greyhound Recycling, Clondalkin, Dublin.


WCP-DC-08-1154-01

20 01 01 N Cardboard 34.4 R3 (b) Greyhound Recycling, Clondalkin, Dublin.


WCP-DC-08-1154-01

20 01 02 N Glass 43.5 R5 (b) Quinn Glass, Derrylin, Co. Fermanagh, N. Ireland

Glassco Recycling Limited (Rehab Recycling)

WCP-DC-08-1150-01

20 01 08 N General Waste 245 R3 (b) Greyhound Recycling, Clondalkin, Dublin


WCP-DC-08-1154-01

20 01 08 N General Waste 162 R1 (b) Greyhound Recycling, Clondalkin, Dublin


WCP-DC-08-1154-01

20 01 25 N Waste Catering Oil 1.55 R9 (c) Frylite, Strabane, Co. Tyrone

Frylite Ireland Ltd. WCP-MO-09-0624-01




EWC HAZ (Y/N)


specified)





Waste Collectors

Permit Number

06 01 02 Y Waste fluoride 0.03 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

06 01 06 Y Waste acids 0.05 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

06 01 06 Y Waste acids 0.04 D10 (c) Indaver NV, Antwerp, Belgium


WCP- DC-08-1121-01

06 01 06 Y Waste acids 0.05 D10 (c) AVG, Hamburg , Germany

Indaver / WM Cyril McGuinness

WCP-DC-08-1139-01

06 02 04 Y Waste caustic 0.21 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

08 01 11 Y Waste paint tins 0.13 D10 (c) AVG, Hamburg , Germany


WCP-DC-08-1139-01

08 03 12 Y Waste ink cartridges 0.36 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

11 01 13 Y Kerosene (degreaser) 0.05 R2 (c) Solvent Recovery Management Ltd, West Yorkshire, United Kingdom

Safety Kleen, Unit 5 Airton Road, Tallaght, Dublin 24

CP D83/1

13 02 08 Y Waste oil 3.7 R9 (b) ENVA Ireland Ltd., Portlaoise, Co. Laois

Enva Ireland Ltd. WCP-DC-08-1116-01

13 05 07 Y Interceptor Waste 26.6 D6 (b) ENVA Ireland Ltd., Portlaoise, Co. Laois


13 07 01 Y Waste diesel 0.40 R9 (b) ENVA Ireland Ltd., Portlaoise, Co. Laois


14 06 01 Y Waste refrigerant 0.05 R3 (c) Harp International Ltd., Pontypridd, United Kingdom

Smart Waste Solutions Ltd./

CP D566/4

14 06 02 Y Dichloromethane 0.34 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01




EWC HAZ (Y/N)


specified)





Waste Collectors

Permit Number

14 06 02 Y Dichloromethane 0.07 D10 (c) Indaver NV, Antwerp, Belgium


WCP- DC-08-1121-01

14 06 03 Y Waste methanol 0.21 D10 (c) Indaver NV, Antwerp, Belgium


WCP- DC-08-1121-01

14 06 03 Y Waste alcohol, ethyl acetate & methanol



WCP- DC-08-1121-01

14 06 03 Y Diacetyl 0.06 R13 (c) ATM, Rotterdam, Netherlands


WCP- DC-08-1121-01

15 01 10 Y Empty Plastic Drums 2.39 R5 (b) Rilta Environmental Ltd., Greenogue Business Park, Rathcoole, Co. Dublin.

Rilta Environmental Ltd. WCP-DC-09-1192-01

15 01 10 Y Empty Steel Drums 0.38 R4 (b) Rilta Environmental Ltd., Greenogue Business Park, Rathcoole, Co. Dublin.

Rilta Environmental Ltd. WCP-DC-09-1192-01

15 01 10 Y Waste ink cartridges 0.08 R13 (b) Rehab Recycling, Tallaght


WCP-DC-08-1139-01

15 01 10 Y Waste empty drums 0.01 R3 (c) Nehlsen GmbH & Co. KG., Germany


WCP- DC-08-1121-01

15 01 10 Y Waste empty drums 0.004 R3 (c) Nehlsen GmbH & Co. KG., Germany


WCP-DC-08-1139-01

15 01 10 Y Waste empty drums 0.001 R1 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

15 01 10 Y Empty plastic containers 0.02 R5 (b) Leinster Environmentals, Dundalk, Co. Louth


15 01 10 Y Empty metal containers 0.22 R4 (b) MSM Recycling, Co. Kilkenny


15 01 10 Y Ink cartridges 0.22 R13 (b) Rehab Recycling, Tallaght


WCP-DC-08-1139-01




EWC HAZ (Y/N)


specified)





Waste Collectors

Permit Number

15 02 02 Y Solid oily waste 2.46 R1 (c) Lindenschmidt Unweltservice, Krombach, Germany


16 01 07 Y Oil filters 0.24 R4 (c) RD Recycling NV, Houthalen, Belgium


16 03 03 Y Optisperse 0.09 D10 (c) Indaver NV, Antwerp, Belgium


WCP- DC-08-1121-01

16 03 05 Y Chlorine contaminated waste 0.08 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

16 05 04 Y Waste aerosol cans 0.04 R4 (c) SBH Sonderabfallentsorgung und -behandlung Hohenlohe GmbH, Germany


16 05 06 Y Lab smalls (containing mercury thermometers)



WCP- DC-08-1121-01

16 05 07 Y Lab smalls 0.27 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

16 05 07 Y Lab smalls 0.02 D10 (c) Indaver NV, Antwerp, Belgium


WCP- DC-08-1121-01

16 05 07 Y Waste desiccant 0.23 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

16 05 07 Y Waste cortrol 0.01 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

16 05 08 Y Lab smalls 0.14 D10 (c) AVG, Hamburg , Germany


WCP- DC-08-1121-01

16 05 08 Y Waste disinfectant 0.04 D10 (c) Indaver NV, Antwerp, Belgium


WCP- DC-08-1121-01




EWC HAZ (Y/N)


specified)





Waste Collectors

Permit Number

16 06 01 Y Batteries 0.04 R4 (c) Campine NV, Beerse, Belgium


16 07 08 Y Oil contaminated waste 0.23 R1 (c) Lindenschmidt Unweltservice, Krombach, Germany


16 07 09 Y Contaminated plastic 0.9 R1 (c) Lindenschmidt Unweltservice, Krombach, Germany


17 06 01 Y Asbestos Waste 1.29 D1 (c ) Buhck Landfill, Germany

Rilta Environmental Ltd. (using BIS Willich Industrial Services Ltd)

WCP-DC-08-1124-01

18 01 03 Y Medical waste 0.23 D10

D10

(c) AGR, RZR Herten / Im Linen, Germany, (c) Indaver Medical Services, Leuven, Belgium

SRCL Ltd. WCP-DC-09-1178-01

18 01 03 Y Medical waste 0.96 D9 (b) Sterile Technologies, Naas Road, Dublin

SRCL Ltd. WCP-DC-09-1178-01

19 08 06 Y Waste resin 15.9 R12 (c) ATM, Netherlands Indaver Ireland / Transport Partners

WCP- DC-08-1121-01

19 08 06 Y Waste resin 4.1 R12 (c) ATM, Netherlands Indaver Ireland / Quay Logistics

WCP- DC-08-1121-01

20 01 21 Y Fluorescent Tubes 0.41 R4/R5 (b) Irish Lamp Recycling Co., Athy, Co. Kildare

Irish Lamp Recycling Co. Ltd.

WCP-DC-08-1115-01

20 01 21 Y Fluorescent Tubes 0.01 R4/R5 (b) Rehab Recycle, Tallaght Rehab Recycling WCP CP D353/3

20 01 23 Y WEEE 0.30 R4/R5 (b) Rehab Recycle, Tallaght Rehab Recycling WCP CP D353/3




EWC HAZ (Y/N)


specified)





Waste Collectors

Permit Number

20 01 35 Y WEEE 4.85 R4/R5 (b) Rehab Recycle, Tallaght Rehab Recycling WCP CP D353/3

Note 1: As advised by the Agency, these materials are recorded under recovery code R11 in the Pollutant Release and Transfer Register. (a) = On-Site (b) = Off-Site (Ireland) (c) = Off-Site (Abroad)



2.2 Monitoring and Enforcement 2.2.1 Agency Site Audit On 10th July 2009, the Agency carried out an Audit at the site. The Agency’s Audit Report of 18th August 2009 identified three non-compliances in relation to the conditions of the licence, and a total of five observations. The Brewery responded to the Agency’s Audit Report on 14th September 2009, setting out corrective actions for each of the non-compliances and observations, including the target date for completion and the status of the actions that had already been closed out. 2.2.2 Agency Monitoring – Emissions to Sewer The Agency visited the site in February, April, August and October 2009 and collected grab samples from emission points SE-1, SE-2 and SE-3. The results of these grab samples are summarised in Table 18, with the corresponding results from the Brewery’s analysis also shown. No sample was collected from SE-2 in August 2009. All of the results determined by the EPA, the Brewery laboratory and the Third Party laboratory were below their respective limits set out in the licence. While there is some variation between the results obtained by the EPA and those from the Brewery’s monitoring programme, in general the two sets of results are consistent with one another. In September 2002, the Brewery joined the EPA laboratory inter-calibration scheme. Results to date for the Brewery in the scheme have indicated that the Brewery is analysing at the same level versus its peers in the scheme.



Table 18: Comparison of EPA Grab Samples and Brewery Monitoring Programme at SE-1, SE-2 and SE-3

BOD (mg/l) COD (mg/l) SS mg/l) Ammonia (mg/l) Total Oxidised Nitrogen (mg/l)

Fats, Oils & Grease (mg/l)

Sulphates (mg/) Total Phosphorous

(mg/l) SJG1 EPA SJG EPA SJG EPA Alt2 EPA Alt EPA Alt EPA Alt EPA Alt EPA

February 2009 SE-1 2,820 2,542 4,635 4,360 984 822 1 0.25 6.9 0.5 3 nr 340 36.7 2,574 2,700 SE-2 7 10 51 25 76 10 8 3.8 2.4 2.1 1 10 82 50 1,010 891 SE-3 18 5 39 25 12 68 0.2 0 1.3 1.3 1 10 28 29.5 120 62 April 2009 SE-1 2,850 2,603 4,305 4,860 824 728 3 0.25 38 0.1 3 38 14.6 24.6 22.6 22.4 SE-2 32 31 88 94 36 48 6 4 10 2.6 1 10 30.1 27.9 0.95 0.78 SE-3 9 14 69 76 20 27 0.95 1 6 1.2 1 10 14.1 12.5 0.1 0.07 August 2009 SE-1 5,929 5,445 9,020 10,270 652 588 0.35 0.37 0.2 0.2 1 nm 107.3 98.3 35.7 28.2 SE-2 19 30 80 75 16 22 13.6 8.9 0.74 0.3 1 10 48.6 20 2.74 2.4 SE-3 - - - - - - - - - - - - - - - - October 2009 SE-1 3,150 766 4,170 4,870 400 461 0.28 0.01 0.2 0.1 10 nm 58.1 >20 19.3 15.35 SE-2 17 23 40 41 6 10 4.5 5.8 0.84 0.7 1 15 64.6 >20 2.21 1.93 SE-3 2 6 36 21 12 10 0.2 0.07 0.82 0.8 1 10 36.1 >20 84.6 38

Note 1: The samples are analysed in the Brewery’s laboratory for BOD, COD and Suspended Solids as part of the Brewery’s monitoring programme. Note 2: The samples are analysed in a Third Party laboratory for Ammonia, Total Oxidised Nitrogen, Fats, Oils & Grease, and Total Phosphorous as part of the Brewery’s

monitoring programme.



2.2.3 Agency Monitoring – Emissions to Atmosphere On 11th June 2009, Euro Environmental Services carried out monitoring of the emissions to atmosphere at three emission points (A1-4, A1-5 and A2-2) on behalf of the Agency. The results of this monitoring are summarised in Table 19. Table 19: Agency Monitoring of Emissions to Atmosphere

Parameter A1-4 A1-5 A2-2 Nitrogen Oxides (as NO2) (mg/m3)

73.2 85.6 16.4

Total Organic Compounds (as TOC) (kg/h)

n/a n/a 0.27

The parameters monitored at emission points A1-4 and A2-2 were below the limits set out in the licence. The concentration of Nitrogen Oxides at A1-5 was above the limit set out in the licence. The Brewery investigated the cause of this high concentration and notified the Agency of the corrective action plan. Subsequent monitoring at A1-5 in November 2009 showed that the corrective action plan had been successful in reducing the concentration of Nitrogen Oxides to below the licence limit (measured at 58 mg/m3). The Monitoring Report from Euro Environmental Services also identified an observation in relation to the measurement of velocity, temperature and pressure of the emissions to atmosphere at the CHP plant. The Brewery is assessing the options to address this observation. 2.2.4 Third-Party Audits There were three Third-Party audits carried out by Certification Europe during 2009: two in relation to the Environmental Management System standard ISO 14001 and one in relation to the Energy Management System standard IS 393 (replaced by IS EN 16001). The three audits were carried out over a total of four days. 2.2.4.1 ISO 14001 Audits On 24th and 29th April 2009, Certification Europe carried out a Re-Certification Audit of the Environmental Management System. The audit identified a single non-conformance and two observations / comments. Certification Europe re-certified the Brewery to ISO 14001:2004. On 25th November 2009, Certification Europe carried out a Surveillance Audit on the EMS. The audit identified a single non-conformance and a single observation / comment. The Brewery maintained its certification to ISO 14001:2004. 2.2.4.2 IS 393 Audit On 4th November 2009, Certification Europe carried out a Surveillance Audit on the Energy Management System against the Irish Energy Management System standard IS 393 and the European standard IS EN 16001 (the replacement to IS 393). The audit identified no non-conformances but did identify a total of 11 observations / comments. The Brewery maintained its certification to the Irish Standard IS 393 and was subsequently certified to the European Standard IS EN 16001 at the end of November 2009.



2.3 Energy and Water Consumption 2.3.1 Energy Consumption Steam and electricity are generated in the Combined Heat and Power (CHP) Plant operated on site by Gatepower Ltd. In addition, the Brewery imports electricity from the grid. Table 20 summarises the energy consumption at the site in 2009, while Table 21 summarises the energy inputs to and outputs from the CHP plant. Table 20: Energy Consumption (MWh) (2009)

Energy Source 2009 Natural Gas for CHP Plant 300,723Natural Gas for Roasthouse 10,782Total Natural Gas 311,505Diesel for CHP Plant 0Electricity imported from the grid 180Total Site Energy Consumption 311,685

Table 21: Summary of Energy Inputs to and Outputs from the CHP Plant (MWh) (2009)

Energy Source 2009 Inputs Natural Gas for electricity exported to grid 71,990Natural Gas for electricity & steam exported to the Brewery 228,733Total Natural Gas input 300,723 Outputs Electricity exported to the grid 28,796Electricity exported to the Brewery 44,566Steam exported to the Brewery 127,557

Overall energy usage fell in 2009 compared to 2008. A focused energy efficiency programme, coupled with the on-going certification to the Energy Management Standard IS EN 16001 drove the decrease in energy usage on the site. A number of energy efficiency projects were delivered in 2009, and this programme will continue into 2010. 2.3.2 Water Consumption Water (Town and Service) is supplied to the site by Dublin City Council. Town (Potable) Water is used during the brewing process. Service Water is used in fire hoses and other ancillary activities. Historically, cooling water has been drawn from an underground well on site; however, since March 2007 this cooling water has no longer been in use, with the cooling water replaced by an alternative cooling medium. Water consumption at the site is summarised in Table 22.



Table 22: Water Usage (2009)

Source 2008 (m3) 2009 (m3) Town 1,945,043 1,779,106 Service (Canal) 642,276 277,190 Cooling 0 0 Total 2,587,319 2,056,296

2.4 Environmental Incidents and Complaints 2.4.1 Environmental Incidents Table 23 summarises the environmental incidents that occurred during 2009, setting out the cause and corrective action, and identifying the relevant authorities that were notified of the incident. Table 23: Environmental Incidents (2009)

Month Number Description Authorities Contacted

January 3 • The in-line pH probe at SE-3 gave erratic readings over the weekend of 10th/11th January. The probe was replaced. The composite samples for pH over the weekend were within the licence limits.

• The flow proportional sampler at SE-2 failed to collect

a sample between 19th and 20th January due to low flow at the emission point. A grab sample was collected and the tubing for the sampler was re-instated in the flow. The results of the grab sample were compliant with the licence limits.

• The in-line pH probe at SE-1 failed on 23rd January.

The probe was replaced on 24th January. The pH result for the composite samples on 23rd and 24th January were within the licence limits.

EPA

EPA

EPA

February 1 • The licence limit on concentration of suspended solids at SE-1 was exceeded on 15th February (1,720 mg/l -v- 1,400 mg/l). The exceedance was due to the biomass growth in the WWTP tanks, for which a corrective action plan is in place, and a fault in one of the production areas.

EPA

April 2 • The licence limit on concentration of suspended solids at SE-1 was exceeded on 18th April (1,860 mg/l -v- 1,400 mg/l). The exceedance was due to the biomass growth in the WWTP tanks, for which a corrective action plan is in place.

• The in-line temperature probe at SE-2 failed on 26th

April. The fault occurred with the controller, which was replaced on 27th April. The results of the composite sample for the period were within the licence limits.

EPA

EPA



Table 23: Environmental Incidents (2009)


May 1 • A small leak of product from a tank in the vicinity of SE-2 resulted in the results for pH (5.08 -v- 6), COD (23,950 mg/l -v- 4,000 mg/l), BOD (8,561 mg/l -v- 2,000 mg/l) and suspended solids (904 mg/l -v- 400 mg/l) exceeding the licence limits. The daily loads for COD, BOD and suspended solids were within the licence limits. The area has been designated as a non-storage location to prevent a recurrence.

EPA

June 3 • The in-line pH probe at SE-2 started to give low readings over the weekend of 6th/7th June. The probe was replaced on 8th June. The pH result from the composite sample was within the licence limits.

• The flow proportional sampler at SE-2 failed to collect

a sample between 10th and 11th June due to low flow at the emission point. A grab sample was collected and the tubing for the sampler was re-instated in the flow. The results of the grab sample were compliant with the licence limits.

• The flow proportional sampler at SE-3 was not

available to collect a sample on 10th or 11th June due to a CCTV survey of the drains in the vicinity. The sampler was returned to operation following completion of the CCTV survey.

EPA

EPA

EPA

August

2 • The flow proportional sampler at SE-3 was taken out of operation on 4th August and the emission point was blocked to prevent debris entering the drain during works carried out by Iarnród Éireann at the site. The emission point was unblocked and the sampler returned to operation following completion of the on-site works.

• The in-line pH probe at SE-2 gave erratic readings on

19th August. The probe was replaced on 20th August. The composite sample for pH was within the licence limit.

EPA

EPA

September 1 • The in-line temperature probe at SE-1 failed on 6th September due to a fault with a cable on the transmitter. The fault was repaired and the probe returned to operation.

EPA

November 1 • The in-line pH probe at SE-1 gave erratic readings on 29th November. A fault with the automatic probe washer was diagnosed, the fault was repaired and the probe returned to operation. The pH result from the composite sample was within the licence limit.

EPA



Table 23: Environmental Incidents (2009)


December 1 • A fire occurred at the site on 21st December on the roof of disused storage area during maintenance works. Dublin Fire Brigade responded and extinguished the fire.

EPA Dublin City

Council

TOTAL 15 2.4.2 Environmental Complaints In 2009, there were three incidents at the Brewery that gave rise to complaints. Table 24 summarises the complaints received, the identified cause and the corrective actions taken. Table 24: Summary of Complaints Received in 2009

Date Complaint Cause Corrective Action 22/05/2009 A resident from the

apartment building adjacent to the Effluent Plant complained of an increase in odour from the plant.

The complainant could not be contacted and therefore the exact cause of the increase in odour was not identifiable. The activities carried out at the plant were reviewed to identify potentially causes of an increase in odour. One of the potential causes identified was cleaning of the tanks during which the hatches are open to provide ventilation. A second potential cause was from the skips containing the grain screened from the effluent.

The plant was inspected to determine whether its operation on the day of the complaint could have caused an increase in odour. No particular cause was identified. The option of providing covers on the skips containing the screened material was investigated with the contractor that provides the skips and covers have since been installed.

08/09/2009 A resident from the apartments adjacent to the CHP plant complained of a high level of noise from the CHP plant during the morning of 8th September, and again during the night of 8th September.

The noise from the plant was due to a fault in the operating mode of two of the turbines while the third turbine was undergoing its statutory inspection which resulted in the venting of steam from the plant.

The two turbines were operated at minimum output during the inspection of the third turbine to minimise the venting of steam. The operational settings on the two turbines were corrected to permit operation in the alternative mode required during inspections.



Table 24: Summary of Complaints Received in 2009 (cont/d)

Date Complaint Cause Corrective Action 25/12/2009 Four residents from the

apartments adjacent to the CHP plant complained of a high level of noise from the CHP plant during the early hours of 25th December.

Due to the low temperature at the time, a pressure transmitter froze causing the system to vent steam.

The transmitter was replaced and the pipeline was lagged to prevent further freezing. It is planned to install trace heating on the primary low pressure transmitter and to reassess the operation of the control system on the plant.

2.5 AER Returns Webform & European Pollutant Release and Transfer

Register (E-PRTR) The AER Returns Webform and European Pollutant Release and Transfer Register for the Brewery is attached in Annex A to this report. An electronic copy of the AER Returns Webform and the E-PRTR was uploaded to the Agency’s website prior to submission of this Annual Environmental Report.



3 MANAGEMENT OF THE ACTIVITY 3.1 Environmental & Energy Management Plan St. James’s Gate Brewery is certified to the International Standard for Environmental Management Systems (ISO 14001), and to the Energy Management System standard IS EN 16001. The Environmental & Energy Management Plan for 2010 is a combined plan covering both Environmental and Energy targets. It defines a set of objectives and targets for the company to work towards. Of its nature, it is liable to alteration in the light of changing circumstances and the company’s future plans. It is also subject to revision from time to time and proposals, plans, targets and goals may vary accordingly. Therefore, progress on a particular objective or target is subject to change. Progress on the objectives and targets achieved during the previous year is reported in the Annual Environmental Report. In addition to the EEMP, a Register of Opportunities (or Ideas Log) is maintained for potential Energy Usage reduction initiatives. The process by which ideas are generated, sourced, captured, reviewed and assessed for progression is shown in Figure 10. Figure 10: Flow Chart for Register of Opportunities for Energy Usage

Register of OPPORTUNITIES

– IS393

Evaluate alternativesQuantify savingsPropose actions Steam

/ Fuel WaterElec/Refg Others

Project based

Operational changes

Mainenance/Repair/replace

CONTINUOUSIMPROVEMENT

MeasureSustain

KPI improvementBenchmark

SolutionDelivery

Management Review

IDEA SourcesMeasurement

Process & Product development

AuditsBenchmarksStaff Ideas

External consultantsSuppliers

Brewhouse

FBP

Keg Plant

BBa

Utilities

Facilities

Local champion and Ideas Log per Area.



The Plan is prepared in accordance with the requirements of ISO 14001, IS EN 16001 and with Conditions 2.2, 2.3 and Schedule 6 (i) of the IPPC licence. It has also been developed taking into account the guidance set out in the Agency’s Guidance Note for Annual Environmental Reports, the Register of Environmental Aspects and Impacts, the Register of Energy Aspects and Impacts, and in particular the significant impacts identified in these Registers. 3.2 Environmental & Energy Management Programme This section sets out the Environmental & Energy Management Programme for Diageo Ireland (St. James’s Gate Brewery). The programme is broken down into a number of categories as follows:

2.1 Soil, Surface Water and Groundwater 2.2 Emissions to Atmosphere 2.3 Waste Reduction 2.4 Management and Control of Effluent Discharges 2.5 Noise 2.6 Resource Usage 2.7 Energy Usage 2.8 Awareness and Training

For each of these headings the following information is outlined:

• Objective • Rationale behind objective • Specific target to achieve objective • Plan to achieve targets • Timescale • Persons / department responsible

3.2.1 Report on Environmental & Energy Management Programme for 2009 The following tables proved a report on our Environmental and Energy Management Programme for 2009.



Objective 1.0

To protect soil, surface waters and groundwater from pollution.

Rationale

Specific requirements relating to the protection of groundwater and surface water are contained in Guinness Ireland’s (St. James’s Gate Brewery) IPPC Licence Reg. No. P0301-01.

No. Target Time scale Comment 1.1 To carry out a comprehensive

hydrogeological monitoring programme for the site to identify any soil and groundwater contamination.

Ongoing until October 2010 and then review with the

Agency.

The long-term monitoring programme that had been agreed with the agency has been implemented. This involves quarterly sampling of the groundwater on site for a suite of parameters. Overall, the water quality has not deteriorated in terms of the general suite parameters. Variations in concentrations between sampling rounds occurs for all parameters, although there are no obvious trends for any parameter.

1.2 To undertake a programme of remedial work on foul sewer pipelines and storage tanks.

December 2009 Phase 1 of the survey has been completed, including a survey of the manholes. The scope for Phase 2 is being developed, including a CCTV survey. Remedial work will be carried out in light of the findings from Phase 1.

1.3 Rationalise the number of points of emission to sewer from the site.

July 2009 A proposal to reduce the frequency of monitoring at emission points SE-2 and SE-3 was submitted to the Agency in November 2009. The Agency approved the reduction in monitoring frequency in December 2009; monitoring at emission points SE-2 and SE-3 will be carried out on a monthly basis.

1.4 To protect soil, surface waters and groundwater from contamination from materials stored on the site.

Ongoing The schedule of bunds was updated during 2009 to take account of changes in bund usage. The next round of bund testing is due to commence in 2010.



Objective 2.0 To improve control of air emissions from the site.

Rationale Conditions 5 and 11 of Guinness Ireland’s (St. James’s Gate Brewery) IPPC Licence requires the company to prepare proposals for the reduction of

certain emissions to atmosphere and prepare air quality monitoring programmes.

No. Target Time scale Comment 2.1 To prepare proposals for the reduction of

emissions of nitrogen oxides from the CHP Plant

Ongoing

The annual monitoring programme indicated that NOX emissions from three of the emission points decreased from those in 2008. The Brewery requested clarification from the Agency in 2009 on the format and content of a submission that would satisfy the requirements of its licence and is awaiting feedback.

2.2 To sustain the improved ratio of CO2 recovery to enable the site to sell approximately 3,500 tonnes of excess CO2 per annum.

December 2009

The target of 3,500 tonnes was achieved in 2009.

2.3 To reduce the environmental impact of employees travelling to work.

December 2009

The cycle to work scheme was successfully rolled out during 2009 and will continue into 2010.



Objective 3.0 To implement the site Waste Management Strategy 2006-2007.

Rationale In line with European and Irish waste management policy Guinness is striving to introduce the prevention and reduction of waste as far as practical.

Condition 8.3 of Guinness Ireland’s IPC Licence (Reg. No. P0301-01) required the company to develop and maintain a site management record.

No. Target Time scale Comment 3.1 To ensure that the situation achieved in

2004/5/6/7/8 of zero waste to landfill is fully maintained. Continue to build employee awareness of the principles of Reduce, Reuse, Recycle. Ensure full awareness of waste streams and disposal routes by including key information in: • Environmental Newsletter • E-mail bulletins across the site. • Presentations to teams Introduce a 4 waste stream system in Dublin Brewery to facilitate better segregation at source. This will involve communications and awareness to the teams on waste management.

Ongoing

December 2009

No production waste from the site was sent to landfill during 2009. A small quantity of a asbestos containing material was disposed of at a purpose built hazardous waste landfill designed for this type of hazardous waste. Segregation bins are now in place for 4 waste streams for the brewing/TFS, KRP, Systems, BBA and Logistics areas.

3.2 To establish more detailed waste reporting and performance indices. To increase our recycling figures by 10% from the 2007 figure (16%).

December 2009.

Building specific reports were provided to the Environmental Department during 2009. In 2009, 29% of wastes were recycled.

3.3 To undertake the auditing of waste contractors who remove waste material from the site.

Ongoing Four waste contractors were audited during 2009.




Rationale In line with European and Irish waste management policy Guinness is striving to introduce the prevention and reduction of waste as far as practical. Condition 8.3 of Guinness Ireland’s IPC Licence (Reg. No. P0301-01) required the company to develop and maintain a site management record.

No. Target Time scale Comment 3.4 Continue rollout of best practice waste

management to specific business units or buildings.

June 2009 The rollout of best practice waste management continued during 2009, including segregation of wastes at source (3.1) and the ongoing reporting of waste from specific buildings.

3.5 To review the disposal route for process wastes from the BBA process.

June 2009 Review is ongoing with our partners and potential users.



Objective 4.0 To improve the management and control of effluent discharges from the site.

Rationale: Condition 6 of Guinness Ireland’s IPPC Licence (Ref. No. P0301-01) requires the monitoring and management of effluent discharges from the site.

No. Target Time scale Comment

4.1 To further reduce the effluent load from the Brewing areas to sustain improvements. FBP area to target 0.29 kg BOD/hl and Brewhouse to target 0.12 kg BOD/hl.

December 2009 The FBP area achieved an effluent load of 0.26 kg BOD/hl. The Brewhouse achieved an effluent load of 0.10 kg BOD/hl.

4.2 Manage effluent emissions from the Keg Plant to maintain the performance achieved in 2008 of less than 0.045 kg BOD/hl.

December 2009 The Keg Plant achieved an effluent load of 0.035 kg BOD/hl.

4.3 To monitor and utilise the real time information available relating to effluent performance.

December 2009 Two TOC meters were installed for monitoring total organic carbon; one in the upper level and one in the lower level. An effluent reduction programme was established to focus on reducing BOD load from the site. The areas identified in the programme included the Brewhouse, FBP and BBA areas.

4.4 Establish a baseline for GFE 2effluent flow to help reduce the level of process waste in the BBA area.

December 2009 Data was gathered on losses to drain, product metering and stock control during 2009 on which a baseline for GFE 2 effluent can be established. This data collection will be continued during 2010.



Objective 5.0 To monitor the level of noise emissions on site, at the boundary of Guinness Ireland and at noise sensitive locations off site.

Rationale To ensure that the activities at the St. James's Gate Brewery do not have any adverse impact on the surrounding residential areas. Condition 9 of

Guinness Ireland’s IPPC Licence (Reg. No. P0301-01) requires that a noise survey of the site operations be carried out annually.

No. Target Time scale Comment 5.1 To review the level of noise at noise

sensitive locations. Review the findings from the 2008 annual noise survey and identify areas of focus to carry out a detailed noise survey. The next phase of the implementation of the Noise Reduction Programme will be established and a further reduction programme established if necessary.

March 2009

December 2009

A detailed noise survey was carried out to determine the optimum noise control options and from this, Phase 3 of the Noise Reduction Programme was established.



Objective 6.0 To increase the efficiency of resource use on site.

Rationale In accordance with good environmental practice and section 2.10 of the site IPPC licence, the Brewery is introducing measure to improve efficiency of

resource and energy use on the site.

No. Target Time scale Comment 6.1 Maintain caustic usage ratio in the keg plant

at 0.1 kg/keg and acid usage at 0.0095 litres/keg.

December 2009 The Keg Plant achieved a caustic usage ratio of 0.09 kg/keg and an acid usage ratio of 0.011 kg/keg in 2009.

6.2 Maintain lubricant usage ratio in the keg plant at 0.0028 litres/keg.

December 2009 The Keg Plant achieved a lubricant usage ratio of c. 0.0016 kg/keg in 2009. A dry lubricant was introduced in the Keg Plant during 2009, which also assisted in the reduction of water usage at the site.

6.3 Sustain usage in 2009 on chemical detergent used in the Brewing Department based on 2008 targets.

December 2009 Acid and sterilant usage were maintained below the 2008 targets in 2009. Caustic usage was above the target 2009 due to special to improve microcleaning. The target for 2010 has been updated accordingly. Old target 0.494; 0.65 caustic came in at 0.61 0.028 kg/hl acid in 0.015 0.04 in at 0.041 kg/hl for sterilant

6.4 To optimise extract recovery in the Brewhouse by achieving in excess of 96.5% extract from raw materials again in 2009.

On-going

An extract recovery rate of 97% was achieved in 2009.



Objective 7.0 To improve the energy efficiency of the Brewery site.

Rationale: To reduce the energy use by the St. James’s Gate Brewery site and improve the energy efficiency of site operations. This will reduce greenhouse gas

emissions from the business.

No. Target Time scale Comment 7.1 To sustain the ratio of water consumption

per hl of beer produced to 4.6:1:

• Towns water usage ratio to be improved from 3.6:1 to 3.5:1.

• Service (canal) water usage to be improved from 1.2:1 to 1.1:1.

December 2009 An overall water consumption ratio of 3.87:1 was achieved in 2009.

• The ratio for Town water was 3.35:1. • The ratio for Canal water was 0.52:1.

7.2 Sustain the consumption of electricity to 31 MJ/hl of beer (or 8.6 kWh/hl).

December 2009 An electricity consumption ratio of 8.4 kWh/hl was achieved in 2009 (30.4 MJ/hl).

7.3 Sustain the consumption of steam below 100 MJ/hl of beer (or 27.78 kWh/hl).

December 2009 A steam consumption ratio of 24 kWh/hl was achieved in 2009.

7.4 In the BBA, target a further reduction in water usage by focussing on a water reduction initiative in 2009.

December 2009 The areas with the potential for a reduction in water usage within the BBA area were investigated during 2009.

7.5 To improve the energy efficiency in the Technology House and the Pilot Plant.

December 2009

The Brewery assessed the option of replacing the single glazing in the Technology House and Pilot Plant with double glazing; approval for this project has been sought for 2010.



Objective 8.0 To reduce gas and steam use from direct firing of waste heat boilers (i.e. to reduce additional gas use not required for CHP).

Rationale When site steam demands exceed defined limits additional steam is raised in the waste heat boilers by direct addition of natural gas. By controlling site

steam use more actively this ‘direct fired steam and natural gas’ can be reduced.

No. Target Time scale Comment 8.1 Sustain the Direct Fired Steam use of less

than 8 GWh per year for 2009.

December 2009. Direct Fired Steam usage in 2009 was less than 8 GWh.



Objective 9.0 Reduce cooling load and hence refrigeration electrical demand to refrigeration compressors by 10%.

Rationale: There are 3 refrigeration systems in use at St James Gate Brewery Dublin.


9.1 Sustain reductions made in 2007/8 on site electrical demand for refrigeration.

December 2009

A total of 1,476 MWh of electricity was saved in electrical demand for refrigeration in 2009.



Objective 10.0 Reduce site electrical use for compressed air generation by utilising ‘spill air’ from the nitrogen production process and routing this into the

compressed air system.

Rationale There are 3 air systems on site wet air, high pressure air and central air. The objective is to feed spill air from the nitrogen plant compressors into the central air system to reduce electrical consumption on the central air compressors. It is envisaged that the upper level air compressors for central air (JG air compressors) can then be turned off.

No. Target Time scale Comment 10.1 Sustain operation of the nitrogen spill air

project to deliver the electrical savings seen in 2007.

December 2009 Annual savings of 2,500 MWh of electricity was achieved in 2009.



Objective 11.0 Optimisation of the keg plant external keg washers.

Rationale The external keg washers provide a hot cleaning function for kegs returned from trade. This operation occurs before internal cleaning, sterilisation and

filling with beer. There are 2 washers which use fresh water, recovered water, cleaning chemicals and steam for heating. The basis of the saving is to reduce cold fresh water addition which has savings in water, effluent, steam and cleaning chemicals.

No. Target Time scale Comment 11.1 Investigate an accurate way to measure

water usage for KRP and RB area and monitor in 2009.

December 2009

A number of projects were carried out in 2009 that achieved significant water savings at the Keg Plant washing area, including reducing water usage in the pre-rinse stage and increasing the quantity of water recovered from the process. The overall savings amounted to c. 1,600 m3 per week by the end of 2009.



Objective 12.0 Process waste reduction.

Rationale By reducing waste from plant trials that contributes to overall waste streams, by finding alternative route or reduction at source.


12.1 To sustain the reductions in process waste identified in 2008.

Ongoing.

The system for purchasing raw materials was improved during 2009, with improved inventory management ensuring that only raw materials required for trials were purchased.



Objective 13.0 To improve awareness of the environmental controls and systems on site.

Rationale It is essential that all employees who have a role in the Environmental Management System on site are aware of the consequences of their role and the

consequences of deviating from set procedures. Condition 2.7 of Guinness Ireland’s (St. James’s Gate Brewery) IPPC Licence (Ref. No. P0301-01) requires that procedures for identifying training needs are established and maintained. There are also requirements in place to ensure that appropriate training is provided to all personnel whose work can have a significant effect on the environment.

No. Target Time scale Comment 13.1 To inform all production employees

regarding the requirements of the IPPC licence for the Brewery.

On-going A programme of environmental training was carried out during 2009.

13.2 To ensure that all employees and contractors remain fully aware of their obligations regarding waste handling on site

On-going This was continued through: • Inclusion at training sessions, • awareness through the WasteWatchers Newsletter, and • the Environmental Week held during 2009.



3.2.2 Environmental and Energy Management Programme for 2010 In the following tables we set out our Environmental and Energy Management Programme for 2010. This programme includes continuing the ongoing targets across the site and the introduction of new targets that were identified during 2009.



Objective 1.0

To protect soil, surface waters and groundwater from pollution.

Rationale

Specific requirements relating to the protection of groundwater and surface water are contained in Guinness Ireland’s (St. James’s Gate Brewery) IPPC Licence Reg. No. P0301-01.

No. Target Plan Time scale Responsibility Department 1.1 To carry out a comprehensive

hydrogeological monitoring programme for the site to identify any soil and groundwater contamination.

Phase 3: Implement the two-year monitoring programme that has been agreed with the Agency. Bi-annual monitoring. Review October 2010.

On-going until October 2010 and then review

with the Agency.

Environmental Manager Overall site

1.2 To undertake a programme of remedial work on foul sewer pipelines and storage tanks.

Continue to implement a programme of remedial work on foul sewer pipelines and storage tanks in St. James’s Gate. Phase 1 (of 3) of the investigation work is complete for all pipelines. Manholes and underground tanks have been included in the scope. Remedial work as a result of the CCTV investigation to be completed.

December 2010 Environmental Manager/ Business Engineering

Overall site

1.3 To protect soil, surface waters and groundwater from contamination from materials stored on the site.

The 3-yearly bund survey of the site is due for review in 2010.All new bunds on site will comply with new procedures in place. Bund log to be reviewed and second round of integrity testing to be initiated.

On-Going Environmental Manager Overall Site

1.4 To improve the identification of the foul sewer system from the surface water drainage system.

To implement a programme of colour coding all manholes on site as proposed by the agency in January 2010

December 2010 Environmental Manager/ Business Engineering

Overall Site



Objective 2.0 To improve control of air emissions from the site.

Rationale Conditions 5 and 11 of Guinness Ireland’s (St. James’s Gate Brewery) IPPC Licence requires the company to prepare proposals for the reduction of

certain emissions to atmosphere and prepare air quality monitoring programmes.

No. Target Plan Time scale Responsibility Department 2.1 Continue to monitor emissions of

nitrogen oxide from the CHP plant. Carry out NOX monitoring as per licence. Ongoing Gatepower/Diageo

contract Manager/ Environmental Manager

Overall Site

2.2 To sustain the improved ratio of CO2 recovery to enable the site to sell maximise the sale of excess CO2 per annum.

Sustain improved Fermentation control through better yeast management and tighter process control. Maximise FBP CO2 recovery to RWE CO2 collection plant to enable sales target to be achieved. Put measurement mechanism in place.

December 2010 CI Manager/ Third-party Utilities Site Manager/

Fermentation Department

Fermentation Department/ Third-party

Utilities Company

2.3 To reduce the Environmental impact of employees travelling to work.

Roll out the cycle to work scheme for 2010.

December 2010 Environmental Manager/Facilities

Compliance Manager/HR Solutions

Overall site




Rationale In line with European and Irish waste management policy Guinness is striving to introduce the prevention and reduction of waste as far as practical.

Condition 8.3 of Guinness Ireland’s IPPC Licence (Reg. No. P0301-01) required the company to develop and maintain a site waste management record.

No. Target Plan Time scale Responsibility Department 3.1 To ensure that the situation

achieved in 2004-2009 of zero waste to landfill is fully maintained.

Continue to build employee awareness of the principles of Reduce, Reuse, Recycle. Ensure full awareness of waste streams and disposal routes by including key information in: • Environmental Newsletter (‘WasteWatchers’) • E-mail bulletins across the site. • Presentations to teams Continue the rollout of the 4 waste stream system across the site to facilitate better segregation at source. Use the GreenIQ as the forum to improve communications and awareness on waste management.

Ongoing Facilities and Environmental Management

Overall Site

3.2 To establish more detailed waste reporting and performance indices. To increase our recycling figures by 10% from the 2007 figure (16%).

Review the building-specific waste reports and implement continuous improvement performance targets for these areas. Extend out training and awareness to the Demand side of the business. This will be part of the roll out of the 4 waste streams.

December 2010 Facilities and Environmental Management

Overall site

3.3 To undertake the auditing of waste contractors who remove waste material from the site.

Continue with the ongoing programme for the auditing of waste contractors

Ongoing Environmental Manager/ Diageo Supply

Procurement Team

Overall site




Rationale In line with European and Irish waste management policy Guinness is striving to introduce the prevention and reduction of waste as far as practical. Condition 8.3 of Guinness Ireland’s IPPC Licence (Reg. No. P0301-01) required the company to develop and maintain a site waste management record.

No. Target Plan Time scale Responsibility Department 3.4 Continue to rollout of best practice

waste management to specific business units or buildings.

Establish the Brewing/BBA Department as a best practice building for waste management –. Look at the possibility of setting targets and improving against those targets month on month.

June 2010 Brewing Manager / BBA Production Manager

Brewing

3.5 Introduce the Demand company to the waste segregation policy.

Use the GreenIQ forum to improve visibility of the Environmental agenda, specifically waste segregation. Roll out the 4 waste steam segregation system into the office buildings.

December 2010 Environmental Manager Demand

3.6 Establish a robust waste management Strategy for the site.

Review current Waste Management Strategy and determine what, if any, updating is required.

December 2010 Environmental Manager Overall site





No. Target Plan Time scale Responsibility Department

4.1 To further reduce the effluent load from the Brewing areas to sustain improvements. FBP area to target 0.29 kg BOD/hl and Brewhouse to target 0.12 kg BOD/hl.

Review vessel and line pushouts further, as part of the effluent reduction programme. Continue to Investigate any further improvements in effluent reduction in the brewing departments through the use of n-line TOC meters. Use the effluent reduction meeting and the Manufacturing Excellence forum to continue to drive awareness.

December 2010 Brewing Shift Manager/ Nominated Brewer

Brewing

4.2 Manage effluent emissions from the Keg Plant to maintain the performance achieved in 2008 of less than 0.045 kg BOD/hl.

Review other opportunities for the reduction of liquid effluent that may come out of the effluent reduction project.

December 2010 Packaging Production Manager/ Packaging

Shift Manager

Keg Plant

4.3 To monitor and utilise the real-time information available relating to effluent performance.

Utilise the two TOC meters on site giving real time information on brewery effluent to investigate high readings and root cause any issues. Implement findings as part of the effluent reduction programme.


4.4 Establish a baseline for GFE 2 Effluent flow to help reduce the level of process waste in the BBA area.

Continue to focus on losses to drain, product metering and stock control. Support effluent reduction programme in 2010.

December 2009 BBA Production Manager

BBA





No. Target Plan Time scale Responsibility Department4.5 To reduce the effluent load from the

BBA department.

Increase efficiency of raw material usage to reduce BOD to drain. Review findings from effluent reduction investigation. Set meaningful targets and draw up improvement plan.

December 2010 BBA Production Manager

BBA



Objective 5.0 To monitor the level of noise emissions on site, at the boundary of Guinness Ireland and at noise sensitive locations off site.

Rationale To ensure that the activities at the St. James’s Gate Brewery do not have any adverse impact on the surrounding residential areas. Condition 9 of

Guinness Ireland’s IPPC Licence (Reg. No. P0301-01) requires that a noise survey of the site operations be carried out annually.

No. Target Plan Time scale Responsibility Department 5.1 To review the level of noise at

noise sensitive locations. Review the findings from the 2009 Annual noise Survey. Progress the implementation of the next phase of the Noise Reduction Programme.




Objective 6.0 To increase the efficiency of resource use on site.

Rationale In accordance with good environmental practice and section 2.10 of the site IPPC licence, the Brewery is introducing measure to improve efficiency of

resource and energy use on the site.

No. Target Plan Time scale Responsibility Department 6.1 Maintain caustic usage ratio in the

keg plant at 100 kg/1,000 kegs and acid usage at 10 kg/1,000 kegs.

Optimise the use of caustic/acid detergents, by working closely with the detergent and machine suppliers. Focus monitoring to a shift-by-shift basis.

December 2009 Packaging Production Manager / Packaging

Shift Manager

Keg Plant

6.2 Improve lubricant usage ratio in the keg plant from 2.9 kg/1,000 kegs.

Extend use of Dry Lube across all remaining areas of the Keg plant. This will also reduce water usage.

December 2010 Packaging Production Manager / Packaging

Shift Manager

Keg Plant

6.3 Sustain usage in 2010 on chemical detergent used in the Brewing Department based on 2008 targets.

Target for 2010 is:

• Acid usage 0.028 kg/hl • Caustic usage 0.65 kg/hl • Sterilant usage 0.04 kg/hl

December 2010 Brewing Manager Brewing Shift Managers

Brewing

6.4 In the BBA monitor CIP usage against targets. Identify areas for potential savings.

Target for 2010 is

• Acid usage 0.020 kg/hl • Caustic usage 0.75 kg/hl • Sterilant usage 0.09 kg/hl

December 2010 Production Manager BBA

6.5 To optimise extract recovery in the Brewhouse by achieving in excess of 96.5% extract from raw materials again in 2010.

Optimise brewing performance at raw material change-over by conducting more brewing trials. Reduce losses to drain in BH.

Ongoing Brewing Manager Brewing Shift Manager

Brewing




Rationale: To reduce the energy use by the St. James’s Gate Brewery site and improve the energy efficiency of site operations. This will reduce greenhouse gas

emissions from the business.

No. Target Plan Time scale Responsibility Department 7.1 To reduce the ratio of water

consumption per hl of beer produced to 3.9:1 • Towns water usage ratio to be

improved from 3.5:1 to 3.32:1 • Service (Canal) Water usage to

be improved from 1.1:1 to 0.57:1

• Continue with the water use reduction programme.

• Keg plant to roll out Drylube trial. • Condensate recovery projects. • Conduct feasibility study in BBA

production area to identify areas of improvement.

December 2010 Contract Manager/ Third-party Utilities Site

Manager

Technical Support

Department/ Third-party

Utilities Company

7.2 Sustain the consumption of electricity to 31 MJ/hl of beer. (or 8.6 kWh/hl)

• Sustain the recommendations implemented in 2007 from the Site Energy Audit.

• Review of energy study required in 2010.

• Continue to run new Refrigeration plant in on a single circuit whenever possible.

• Install New air compressor unit. • Scope of electrical metering to be

increased to give on-line monitoring for up to 76% of site usage.

(Refer also to Objectives 8 – 12)

December 2010 Contract Manager/ Third-party Utilities Site

Manager

Technical Support


Utilities Company

7.3 Sustain the consumption of Steam below 100 MJ/hl of beer (or 27.78 kWh/hl).

Sustain the recommendations implemented in 2007 from the site energy study.

December2010 Contract Manager/ Third-party Utilities Site

Manager

Technical Support


Utilities Company




Rationale: To reduce the energy use by the St. James’s Gate Brewery site and improve the energy efficiency of site operations. This will reduce greenhouse gas emissions from the business.

No. Target Plan Time scale Responsibility Department 7.4 In the BBA, target a further

reduction in water usage by focusing on a water reduction initiative in 2010.

Further investigate the possible areas to reduce water usage in the BBA – CIP, Evaporator, Water Pasteuriser.

December 2010 BBA Operations Manager

BBA

7.5 To have departmental objectives that will drive improvement in energy efficiency.

• Draw up targets and objectives specific to the departments.

• Link departmental objectives into the overall site objectives.

December 2010 Contracts Manager/ Engineering Manager /

Departmental Area Engineers

Site / BBA/Brewing

/ Packaging



Objective 8.0 To reduce gas and steam use from direct firing of waste heat boilers (i.e to reduce additional gas use not required for CHP).

Rationale: When site steam demands exceed defined limits additional steam is raised in the waste heat boilers by direct addition of natural gas. By controlling

site steam use more actively this ‘direct fired steam and natural gas’ can be reduced.

No. Target Plan Time scale Responsibility Department 8.1 Direct Fired Steam use of less than

7 GWh per year for 2010 (based on Gatepower Contract 137 + 7Gw).

• Sustain improvements for use of reduced direct firing.

• Introduce 6% kettle and RMX boil in brewhouse to reduce overall energy use.

December 2010 Technical Support Team and Operations Team

Operations and Technical

support



Objective 9.0 Reduce cooling load and hence refrigeration electrical demand to refrigeration compressors.

Rationale: There are 3 refrigeration systems in use at St James Gate Brewery Dublin.

No. Target Plan Time scale Responsibility Department

9.1 Sustain reductions made in 2007/8/9 on site electrical demand for refrigeration.

• Sustain reductions made in 2008/2009. • Continue to run glycol section of recirc

chiller on single circuit. • Reduce parasitic load.

December 2010 Contracts Manager/Technical

Support Team

Technical Support



Objective 10.0 Reduce site electrical use for compressed air generation by utilising ‘spill air’ from the nitrogen production process and routing this into the

compressed air system.

Rationale: There are 3 air systems on site wet air, high pressure air and central air. The objective is to feed spill air from the nitrogen plant compressors into the central air system to reduce electrical consumption on the central air compressors. It is envisaged that the upper level air compressors for central air (JG air compressors) can then be turned off.

No. Target Plan Time scale Responsibility Department 10.1 Sustain operation of the nitrogen

spill air project to deliver the electrical savings seen in 2007.

• Deliver Site Energy Awareness Campaign.

• Continue to carry out compressed air leakage survey twice yearly.

December 2010 Contracts Manager and RWE Utilities

Technical Support



Objective 11.0 To improve awareness of the environmental controls and systems on site.

Rationale: It is essential that all employees who have a role in the Environmental Management System on Site are aware of the consequences of their role and the

consequences of deviating from set procedures. Condition 2.7 of Guinness Ireland’s (St. James’s Gate Brewery) IPPC Licence (Ref. No. P0301-01) requires that procedures for identifying training needs are established and maintained. There are also requirements in place to ensure that appropriate training is provided to all personnel whose work can have a significant effect on the environment.

No. Target Plan Time scale Responsibility Department 11.1 To inform all employees regarding

the requirements of the IPPC licence for the Brewery.

Continue the implementation of the training programme level1. Roll out to new recruits, contractors on site, Logistics and Demand and provide refresher training as necessary. Roll out Environmental Training at team days on effluent alarms and TOC meters on site.

Ongoing Training Manager / Environmental Manager

Overall site

11.2 To ensure that all employees and contractors remain fully aware of their obligations regarding waste handling on site

Continue this through:

• Inclusion at training sessions • Awareness through the WasteWatchers

Newsletter • Environmental week. • The GreenIQ team

Ongoing Facilities Manager / Environmental Manager

Overall site



4 LICENCE-SPECIFIC REPORTS This section summarises the results from the Licence Specific Reports completed during 2009. 4.1 Noise 4.1.1 Noise Survey The annual noise survey was carried out in September 2009 in accordance with Condition 9 of the licence. The results of the monitoring are summarised in Table 25. The day-time readings were taken on 29th September and the night-time readings were taken on 29th and 30th September. Table 25: Summary of Noise Survey Results

Location Daytime Night-time LAeq

(30 min) dB(A)

LA90 dB(A)

SNLNote 1

dB(A) LAeq

(15 min) dB(A)

LA90 dB(A)

SNL dB(A)

1 Ellis Quay 66 60 NDNote 2 63 49 <49 2 Bonham St. / Watling St. 61 54 <54 55 49 49 3 Watling St. 71 55 <55 57 49 49 4 School St./Taylor’s Lane 61 51 ND Note 2 52 42 <42 5 Marrowbone Lane 59 50 <50 50 39 ND Note 2 6 Bond St. 63 54 <54 60 42 <42 7 Echlin St. 70 59 ND Note 2 60 48 48 8 Inside boundary at Watling St. 59 58 58 60 59 59 9 Inside boundary at Presbytery 63 59 59Note 3 60 56 56 Note 3

Note 1: Specific Noise Level (the noise level attributable to site activity). Note 2: Not detected. Note 3: The actual specific noise level at the Presbytery is calculated to be 3 dB(A) lower than the measured

level, taking into account façade effect sound build up. Condition 9.3 of the licence requires that activities on-site shall not give rise to noise levels off-site, at noise sensitive locations, which exceed the following sound pressure limits, subject to Condition 3 of this licence: Daytime: 55 dB(A) Leq, 30 minutes Night-time: 45 dB(A) Leq, 15 minutes Locations 1 to 7 in Table 25 are designated as Noise Sensitive Locations. Due to the location of the Brewery within a city centre, noise levels measured at these locations may not all be attributable to site activity. Therefore, the noise survey identifies the specific noise level which is the noise that is attributable to activities at the site. The specific noise level is used as the basis for determining compliance with the limits set out in the licence. The results of the 2009 survey indicate that the daytime noise limit of 55 dB(A) was complied with at each of the seven Noise Sensitive Locations (locations 1 to 7). The results also indicate that the night-time noise limit of 45 dB(A) was complied with at locations 4, 5 and 6, but that is was exceeded, albeit marginally, at locations 1, 2, 3 and 7. There were no tonal or impulsive components to the noise measured at any of the Noise Sensitive Locations.



A comparison of the night-time specific noise levels from 2000 to 2009 at the seven Noise Sensitive Locations is shown in Figure 11. Figure 11: Historical Night-time Specific Noise Levels

0

10

20

30

40

50

60

70

Location 1 Location 2 Location 3 Location 4 Location 5 Location 6 Location 7

Spec

ific

Nois

e Le

vel (

dB(A

))

Night-time Specific Noise Level (2000 to 2009)

2000

2001

2002

2003

2004

2005

2006

2007

2008

2009

4.1.2 Noise Reduction Programme In January 2009, a review of the noise sources in the CHP area was carried out, which identified a number of measures to reduce noise levels, including the installation of acoustic panels on the steam valves. The installation of these panels has reduced the noise level in this area, measured at a distance of 5 m, by 5 dB. The overall reduction in noise at the closest Noise Sensitive Location to the CHP plant is estimated to be in the order of 3 to 4 dB. Additional noise reduction measures are planned for 2010 to further reduce the impact of noise from the site at the Noise Sensitive Locations.



4.2 Testing and Inspection of Underground Tanks and Pipelines 4.2.1 Bunding A bund integrity survey was completed in late 2006. A total of 130 bunds and bunded areas were inspected and data sheets for each area were compiled. Twenty-one priority items and forty-one other actions were identified from the survey, with the remedial work completed in 2007. As part of the bund integrity programme, bund integrity tests commenced in 2007 and were completed in 2008. During 2009, the bund data sheets were reviewed and updated in light of changes in their use in recent years. The next round of bund integrity testing is due to commence in 2010. 4.2.2 Pipelines In 1995, the Brewery embarked on an extensive programme of inspection of the underground effluent pipelines within the St. James’s Gate Brewery site. Subsequently, a significant programme of remediation and repair work was instigated and this has been completed. This repair work focused primarily on upgrading large sections of internal sub-floor drainage, which at the time was found to be defective. (Reference: report 1890-50-RP-001; PM Ltd.). An additional programme of inspection and testing, directed at the external underground pipeline network and underground tanks, has also been undertaken. To facilitate the work, the site was divided into eight zones. During 2002, inspection and testing was completed on five of the zones and the remaining three zones were completed in 2003. The compilation of the detailed report commenced in December 2003 and was completed in February 2004. The report identified 100 sewer lines and 105 manholes that were in need of remedial work and this work commenced in 2005. The purpose of the drainage and remediation works is to secure the process effluent drainage system in order to protect the receiving environment of the River Liffey and to allow the site to function in an efficient compliant manner in terms of its requirements under the IPPC licence and statutory legislation. Furthermore, the site must remain operational during the course of the remedial works, and therefore it is proposed to use non-invasive renovation options where possible. During 2009, Phase 1 of the remedial works programme on the foul sewer pipelines was completed, which included a survey of all of the manholes previously identified. In light of the works from Phase 1, the programme for Phase 2 is being developed, which will include a CCTV survey and completion of additional remedial works identified during Phase 1.



4.3 Hydrogeological Investigation In compliance with Condition 10.3.3 of the licence, a hydrogeological investigation of the site took place between November 2005 and January 2006. Soil samples and groundwater samples were collected, the results were reviewed, and a submission made to the Agency regarding ongoing monitoring. A programme of quarterly sampling for a range of potential contaminants was agreed with the Agency. Following the monitoring programme in 2008, O’Neill Groundwater Engineering (OGE), the contractor carrying out the monitoring programme, recommended that the frequency of the programme be reduce from quarterly to biannually. This biannual programme was carried out in April and October 2009 and will continue until October 2010, at which point it will be reviewed with the Agency. The conclusions from sampling round 13 of the programme (October 2009) are set out below (from OGE Report No. 0470901).

• There are no monitoring wells in which concentrations of all heavy metal parameters showed definite increasing or decreasing trends over a number of sampling rounds. The concentrations over the thirteen sampling rounds still remain highly variable for all heavy metal parameters with the exception of Cadmium. There is an overall trend of the peaks of certain parameters declining e.g. Selenium and Copper.

• There were notable increases in Copper and Chromium levels in a number of up gradient, down gradient and centrally located monitoring wells. Heavy metal concentrations have historically been highly variable and therefore further monitoring will be required to identify possible trends.

• Cadmium concentrations have appeared to stabilise over the last two years of sampling. Nine of the eleven monitoring wells have been consistently under the Dutch S-Value.

• Selenium and Nickel concentrations have seen an overall reduction compared to the previous sampling round. However, all the wells still exceed the Dutch S-Value for Selenium and eight of the eleven for Nickel.

• Mineral oil has consistently been non detectable up until Sample Round 13. The last round when any mineral oils were detected was Round 8. This was undertaken in December 2007. There have been a number of detections in both up gradient and down gradient monitoring wells in this round [Round 13]. It is too early to be definitive as to whether or not these are anomalous results.

• Heavy metal, DRO and Mineral Oil Contamination shows no spatial pattern within the site.

• Elevated levels of PAHs over the Dutch Intervention & Target values are predominantly associated with MW2 and MW3 which are both up gradient monitoring wells. There has been a significant increase in PAH compounds in both wells. MW3 is most notable in this sampling round [Round 13].



• There is a notable absence in PAH detection in MW10 in comparison to the previous

sampling round, which is positive. However, continued sampling will be required to determine if this is an overall decreasing trend.

*****


Licence Register No. P0301-01 March 2010

Annex A

AER Returns Webform

and

European Pollutant Release and Transfer Register

Sheet : Facility ID Activities AER Returns Worksheet 30/3/2010 14:45

| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 |

Version 1.1.10REFERENCE YEAR 2009

1. FACILITY IDENTIFICATIONParent Company Name Diageo Ireland

Facility Name Diageo IrelandPRTR Identification Number P0301

Licence Number P0301-01

Waste or IPPC Classes of ActivityNo. class_name

2.1The operation of combustion installations with a rated thermal input equal to or greater than 50MW

Address 1 St. James Gate BreweryAddress 2 James StreetAddress 3 Dublin 8Address 4

Country IrelandCoordinates of Location -6.28779 53.343

River Basin District IEEANACE Code 1105

Main Economic Activity Manufacture of beer

AER Returns Worksheet

| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | Page 1 of 2

Main Economic Activity Manufacture of beerAER Returns Contact Name Fiona McLoone

AER Returns Contact Email Address [email protected] Returns Contact Position Environmental Manager

AER Returns Contact Telephone Number 01-4714798/086 3880533MOBAER Returns Contact Mobile Phone Number

AER Returns Contact Fax Number 0Production Volume 0.0

Production Volume UnitsNumber of Installations 0

Number of Operating Hours in Year 0Number of Employees 0

User Feedback/CommentsWeb Address

2. PRTR CLASS ACTIVITIESActivity Number Activity Name1(c) Thermal power stations and other combustion installations

3. SOLVENTS REGULATIONS (S.I. No. 543 of 2002)Is it applicable? No

Have you been granted an exemption ?If applicable which activity class applies (as per

Schedule 2 of the regulations) ?


Sheet : Facility ID Activities AER Returns Worksheet 30/3/2010 14:45

Is the reduction scheme compliance route being used ?

| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | Page 2 of 2| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | Page 2 of 2

Sheet : Releases to Air AER Returns Worksheet 30/3/2010 14:46

4.1 RELEASES TO AIR | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | 30/03/2010 14:468 12 20 20 28 29 6 13 6 6 6 10 28

SECTION A : SECTOR SPECIFIC PRTR POLLUTANTS

QUANTITYA1-3 A1-4 A1-5 A1-6 A1-7 A2-1 A2-2 Brewing Dept.

No. Annex II Name M/C/E Method Code Designation or Description Emission Point 1 Emission Point 2 Emission Point 3 Emission Point 4 Emission Point 5 Emission Point 6 Emission Point 7Emission Point 8

T (Total) KG/Year

A (Accidental) KG/Year

F (Fugitive) KG/Year

08 Nitrogen oxides (NOx/NO2) M OTH Fluegas analyser 20584.0 24366.0 17886.0 0.0 35.0 1436.0 1659.0 0.0 65966.0 0.0 0.003 Carbon dioxide (CO2) C MAB Mass balance 27791978.0 21572016.0 12384278.0 0.0 86560.0 1108390.0 1108390.0 9650910.0 74296431.6 0.0 593909.606 Ammonia (NH3) E Estimate 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 394.0 0.0 394.004 Hydro-fluorocarbons (HFCs) E Estimate 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.014 Hydrochlorofluorocarbons (HCFCs) E Estimate 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 13.0 0.0 13.0

* Select a row by double-clicking on the Pollutant Name (Column B) then click the delete button

SECTION B : REMAINING PRTR POLLUTANTS

QUANTITY

No. Annex II Name M/C/E Method Code Designation or Description Emission Point 1 T (Total) KG/Year A (Accidental) KG/Year F (Fugitive) KG/Year0.0 0.0 0.0 0.0


SECTION C : REMAINING POLLUTANT EMISSIONS (As required in your Licence

QUANTITYA2-1 A2-2 A2-3 A2-4 A2-5

Pollutant No. Name M/C/E Method Code Designation or Description Emission Point 1 Emission Point 2 Emission Point 3 Emission Point 4 Emission Point 5 T (Total) KG/YearA (Accidental) KG/Year


351 Total Organic Carbon (as C) M OTH Bernath portable FID 526.0 701.0 0.0 0.0 0.0 1641.9 0.0 414.9

244 Total Particulates M OTH Method based on ISO 9096 0.0 0.0 807.6 187.5 493.3 1488.4 0.0 0.0* Select a row by double-clicking on the Pollutant Name (Column B) then click the delete button

Additional Data Requested from Landfill operators

Landfill: Diageo IrelandPlease enter summary data on the quantities of methane flared and / or utilised

additional_pollutant_no T (Total) kg/Year M/C/E Method CodeDesignation or

DescriptionFacility Total Capacity m3

per hourTotal estimated methane generation (as pe

site model) 0.0 N/AMethane flared 0.0 0.0 (Total Flaring Capacity)

Methane utilised in engine/s 0.0 0.0 (Total Utilising Capacity)Net methane emission (as reported in Section

A above) 0.0 N/A

Method Used

Method Used

RELEASES TO AIRPOLLUTANT METHOD

Method Used

POLLUTANT

RELEASES TO AIR

RELEASES TO AIRMETHOD

POLLUTANT METHODMethod Used

For the purposes of the National Inventory on Greenhouse Gases, landfill operators are requested to provide summary data on landfill gas (Methane) flared or utilised on their facilities to accompany the figures for total methane generated. Operators should only report their Net methane (CH4) emission to the environment under T(total) KG/yr for Section A: Sector specific PRTR pollutants above. Please complete the table below:

| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | Page 1 of 1| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | Page 1 of 1

Sheet : Releases to Waters AER Returns Worksheet 30/3/2010 14:46

4.2 RELEASES TO WATERS | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | 30/03/2010 14:468 8 16 16 24 24 6 6 6

SECTION A : SECTOR SPECIFIC PRTR POLLUTANTS Data on ambient monitoring of storm/surface water or groundwater, conducted as part of your licence requirements, should NOT be submitted under AER / PRTR Reporting as this on

QUANTITY



SECTION B : REMAINING PRTR POLLUTANTS

QUANTITY



SECTION C : REMAINING POLLUTANT EMISSIONS (as required in your Licence)

QUANTITY

Pollutant No. Name M/C/E Method Code Designation or Description Emission Point 1 T (Total) KG/Year A (Accidental) KG/Year F (Fugitive) KG/Year0.0 0.0 0.0 0.0


RELEASES TO WATERS

Method Used

RELEASES TO WATERS

RELEASES TO WATERS

Method Used

POLLUTANTMethod Used

POLLUTANT

POLLUTANT


Sheet : Releases to Wastewater or Sewer AER Returns Worksheet 30/3/2010 14:46

4.3 RELEASES TO WASTEWATER OR SEWER | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Re 30/03/2010 14:468 13 21 26 6 8 6 8

SECTION A : PRTR POLLUTANTS

QUANTITYSE-1 SE-2 SE-3

No. Annex II Name M/C/E Method Code Designation or Description Emission Point 1 Emission Point 2 Emission Point 3 T (Total) KG/Year



79 Chlorides (as Cl) M CRM

3rd Party UKAS accredited laboratory method (TM 097D based on USEPA Method 525.1/2) 29.86 3.16 0.32 33.34 0.0 0.0

20 Copper and compounds (as Cu) M CRM

3rd Party UKAS accredited laboratory method (TM 152D by ICPMS) 13.96 0.63 0.44 15.03 0.0 0.0

12 Total nitrogen M CRM

3rd Party UKAS accredited laboratory method (TM 102D based on AWWA/APHA 20th Edition - Method 4500) 33475.0 446.3 5.49 33926.79 0.0 0.0

13 Total phosphorus M CRM


76 Total organic carbon (TOC) (as total C or COD/3) M CRM


24 Zinc and compounds (as Zn) M CRM

3rd Party UKAS accredited laboraotry method (TM 107D using Dr Lange Kit) 194.8 5.94 0.07 200.81 0.0 0.0


SECTION B : REMAINING POLLUTANT EMISSIONS (as required in your Licence

QUANTITYSE-1 SE-2 SE-3

Pollutant No. Name M/C/E Method Code Designation or Description Emission Point 1 Emission Point 2 Emission Point 3 T (Total) KG/Year



3rd Party UKAS accredited

OFFSITE TRANSFER OF POLLUTANTS DESTINED FOR WASTE-WATER TREATMENT OR SEWER

OFFSITE TRANSFER OF POLLUTANTS DESTINED FOR WASTE-WATER TREATMENT OR SEWER

Method Used

Method Used

POLLUTANT METHOD

POLLUTANT METHOD

Page 1 of 1

303 BOD M CRM

3rd Party UKAS accredited laboratory method (TM 045D based on MEWAM BOD5 2nd Edition 1988/AWWA/ APHA 20th Edition - Method 5210B) 2294073.0 2972.0 11.0 2297056.0 0.0 0.0

306 COD M CRM

3rd Party UKAS accredited laboraotry method (TM 107D using Dr Lange Kit) 3535134.0 6552.0 74.0 3541760.0 0.0 0.0

308 Detergents (as MBAS) M OTH 3rd Party laboraotry method 1969.0 9.5 0.19 1978.69 0.0 0.0

314 Fats, Oils and Greases M OTH 3rd Party laboraotry method 15609.0 58.7 1.2 15668.9 0.0 0.0

343 Sulphate M CRM

3rd Party UKAS accredited laboratory method (TM 098D by Kone Analyser) 71808.0 2833.0 25.0 74666.0 0.0 0.0

240 Suspended Solids M CRM

3rd Party UKAS accredited laboratory method (TM 022D by Gravimetric Determination based on BS 2690:Part 120:1981) 720925.0 2140.0 52.0 723117.0 0.0 0.0


Page 1 of 1

Sheet : Releases to Land AER Returns Worksheet 30/3/2010 14:46

4.4 RELEASES TO LAND | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | 30/03/2010 14:468 8 16 16 6 6 6 6

SECTION A : PRTR POLLUTANTS

QUANTITY

No. Annex II Name M/C/E Method Code Designation or Description Emission Point 1 T (Total) KG/Year A (Accidental) KG/Year0.0 0.0 0.0


RELEASES TO LANDPOLLUTANT METHOD

Method Used


SECTION B : REMAINING POLLUTANT EMISSIONS (as required in your Licence)

QUANTITY

Pollutant No. Name M/C/E Method Code Designation or Description Emission Point 1 T (Total) KG/Year A (Accidental) KG/Year0.0 0.0 0.0


POLLUTANT METHODMethod Used

RELEASES TO LAND


Sheet : Treatment Transfers of Waste AER Returns Worksheet 30/3/2010 14:47

5. ONSITE TREATMENT & OFFSITE TRANSFERS OF WASTE | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2009.xls | Return Year : 2009 | 30/03/2010 14:475 75 0

Quantity (Tonnes per

Year)

Haz Waste : Name and Licence/Permit No of Next Destination Facility Non Haz Waste:

Name and Licence/Permit No of Recover/Disposer

Haz Waste : Address of Next Destination Facility

Non Haz Waste: Address of Recover/Disposer

Name and License / Permit No. and Address of Final Recoverer / Disposer

(HAZARDOUS WASTE ONLY)

Actual Address of Final Destination i.e. Final Recovery / Disposal Site (HAZARDOUS WASTE ONLY)

Transfer DestinationEuropean Waste

Code Hazardous Quantity T/Year Description of Waste

Waste Treatment Operation M/C/E Method Used

Location of Treatment Name and Licence / Permit No. of Recoverer / Disposer / Broker Address of Recoverer / Disposer / Broker Name and Address of Final Destination i.e. Final Recovery / Disposal Site (HAZARDOUS WASTE ONLY) Licence / Permit No. of Final Destination i.e. Final Recovery / Disposal Site (HAZARDOUS WASTE ONLY)

Within the Country 02 07 01 No 107.8 Waste grain R3 M Weighed Onsite in Ireland

Miltown Composting Ltd. ,WM-WP-28-03

Fethard ,.,.,Co. Tipperary,Ireland

To Other Countries 02 07 04 No 0.7 Waste essences & flavourings R13 M Weighed AbroadIndaver Ireland Ltd.,W0036-01

Tolka Quay Road ,Dublin Port ,Dublin ,.,Ireland

To Other Countries 02 07 04 No 0.59 Waste essences & flavourings D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01


Within the Country 02 07 05 No 137.0 Effluent Plant Screenings R3 M Weighed Offsite in IrelandOrmonde Organics,W0237-01

Killowen ,Portlaw ,County Waterford.,.,Ireland

To Other Countries 02 07 99 No 0.08 Lab smalls D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01


Within the Country 02 07 99 No 71352.0 Spent grains R11 M Weighed Offsite in IrelandKW Forage Systems Ltd.,N/A (animal feed)

Ballymountain ,Waterford ,.,.,Ireland

Within the Country 02 07 99 No 13711.0 Black Spent Grains R10 M Weighed Offsite in IrelandBord Na Móna Kilberry Compost Facility,W0198-01

Kilberry,Co. Kildare,.,.,Ireland

Within the Country 02 07 99 No 9919.0 Surplus Yeast (FBP) R11 M Weighed Offsite in IrelandKW Forage Systems Ltd.,N/A (animal feed)


Within the Country 02 07 99 No 1124.0Barley Screenings / Dust (Roasthouse and GFE) R10 M Weighed Offsite in Ireland

Bord Na Móna Kilberry Compost Facility,W0198-01

Kilberry,Co. Kildare,.,.,Ireland

Within the Country 02 07 99 No 3.2Sample Beers (Technology House & QA Department) D8 M Weighed Offsite in Ireland Dublin City Council,N/A

Ringsend WWTP,Dublin 2,.,.,Ireland

Within the Country 02 07 99 No 0.04Concentrated Product Samples (Tech. House) D8 M Weighed Offsite in Ireland Dublin City Council,N/A

Ringsend WWTP,Dublin 2,.,.,Ireland

Within the Country 02 07 99 No 1934.0 Spent Grain (Technology House) R11 M Weighed Offsite in IrelandKW Forage Systems Ltd.,N/A (animal feed)


Within the Country 15 01 02 No 1.7 Plastic R5 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01

Knockmitten Lane ,Western Industrial Estate ,Dublin 12,County Dublin,Ireland

Within the Country 15 01 04 No 37.2 Waste kegs R4 M Weighed Offsite in Ireland P. Carney Ltd.,P0402-01Crossakiel ,Kells ,Co. Meath.,.,Ireland

Within the Country 15 02 03 No 6.2 Spent carbon R3 M Weighed Offsite in IrelandWaddock Composting Ltd.,WP 01/02 WP 11/04

.,.,Carlow,Co. Carlow.,Ireland

Method Used

Within the Country 17 04 07 No 56.7 Scrap Metal R4 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 01 No 28.2 Paper R3 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 01 No 34.4 Cardboard R3 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 02 No 43.5 Glass R5 M Weighed Offsite in IrelandQuinn Glass Ltd.,NR1998 250

Derrylin ,Co. Fermanagh.,BT92 9AW,.,United Kingdom

Within the Country 20 01 08 No 245.0 General Waste R3 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 08 No 162.0 General Waste R1 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


To Other Countries 20 01 25 No 1.55 Waste catering oil R9 M Volume Calculation Abroad Frylite Ltd.,LN/08/11

Orchard Road Industrial Estate,Orchard Road,Strabane,Co. Tyrone BT82 9FR,United Kingdom




Year)












Method Used

To Other Countries 06 01 02 Yes 0.03 Waste flouride D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01


AVG Abfall-Verwertungs-Gesellshaft,11/05/2005 IB2234/AVG-GENB-2,Borgistrasse 2 ,D-22113 ,Hamburg ,.,Germany

Borgistrasse 2 ,D-22113 ,Hamburg ,.,Germany

To Other Countries 06 01 06 Yes 0.1 Waste acids D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 06 01 06 Yes 0.04 Waste acids D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01


Indaver NV,MLAV1/9800000485/MV/bd,Poldervlietweg ,B-2030 Antwerpen ,.,.,Belgium

Poldervlietweg ,B-2030 Antwerpen ,.,.,Belgium

To Other Countries 06 02 04 Yes 0.21 Waste caustic D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 08 01 11 Yes 0.13 Waste paint tins D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 08 03 12 Yes 0.36 Waste ink cartridges D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 11 01 13 Yes 0.05 Kerosene (degreaser) R2 M Weighed AbroadSafety Kleen Ireland Ltd.,W0099-01

Unit 5,Airton Road,Tallaght,Dublin 24,Ireland

Solvent Recovery Manager Ltd.,AG8462/BY 4106,Weeland Road ,Knottingley ,West Yorkshire ,WF11 8DZ ,United Kingdom

Weeland Road ,Knottingley ,West Yorkshire ,WF11 8DZ ,United Kingdom

Enva Ireland Ltd.,W0184-01 Clonminam Industrial Clonminam Industrial Estate

Within the Country 13 02 08 Yes 3.7 Waste oil R9 M Weighed Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

01,Clonminam Industrial Estate ,Portlaoise ,Co. Laois,.,Ireland

Clonminam Industrial Estate ,Portlaoise ,Co. Laois,.,Ireland

Within the Country 13 05 07 Yes 26.6 Interceptor Waste D6 M Weighed Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

Enva Ireland Ltd.,W0184-01,Clonminam Industrial Estate ,Portlaoise ,Co. Laois,.,Ireland


To Other Countries 14 06 01 Yes 0.05 Waste refrigerant R3 M Weighed AbroadSmart Waste Solutions Ltd.,WPR042

Environmental Services Centre ,Unit 2 ,Whitestown Industrial Estate ,Dublin 24 ,Ireland

Harp International Ltd.,SIU3/91/24,Gellihirion Industrial Estate,Pontypridd,Rhondda Cynon Taff,CF37 5SX,United Kingdom

Gellihirion Industrial Estate,Pontypridd,Rhondda Cynon Taff,CF37 5SX,United Kingdom

To Other Countries 14 06 02 Yes 0.34 Dichloromethane D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 14 06 02 Yes 0.07 Dichloromethane D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 14 06 03 Yes 0.21 Waste methanol D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01







Year)












Method Used

To Other Countries 14 06 03 Yes 1.9 Waste alcohol, ethyl acetate & methanol D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 14 06 03 Yes 0.06 Diacetyl R13 M Weighed AbroadIndaver Ireland Ltd.,W0036-01


ATM,821780 02/3762 AWE/2002.3784,PO Box 30 ,NI-4780 AA Moerdijk ,Vlasweg 12 ,4782PW Moerdijk ,Netherlands

PO Box 30 ,NI-4780 AA Moerdijk ,Vlasweg 12 ,4782PW Moerdijk ,Netherlands

Within the Country 15 01 10 Yes 2.39 Empty Plastic Drums R5 M Weighed Offsite in IrelandRilta Environmental Ltd.,W0192-02

Block 402 Greenogue Business Park ,Rathcoole ,Co. Dublin.,.,Ireland

Rilta Environmental Ltd.,W0192-02,Block 402 Greenogue Business Park ,Rathcoole ,Co. Dublin.,.,Ireland


Within the Country 15 01 10 Yes 0.38 Empty Steel Drums R4 M Weighed Offsite in IrelandRilta Environmental Ltd.,W0192-02


Rilta Environmental Ltd.,W0192-02,Block 402 Greenogue Business Park ,Rathcoole ,Co. Dublin.,.,Ireland


Within the Country 15 01 10 Yes 0.08 Waste ink cartridges R13 M Weighed Offsite in IrelandIndaver Ireland Ltd.,W0036-01


Rehab Enterprises Ltd. T/A Rehab Recycle,WPRO33/2,77 Broomhill Road ,Tallaght ,Dublin 24 ,.,Ireland

77 Broomhill Road ,Tallaght ,Dublin 24 ,.,Ireland

To Other Countries 15 01 10 Yes 0.014 Waste empty drums R3 M Weighed AbroadIndaver Ireland Ltd.,W0036-01


Nehlsen Gmbh & Co. KG,N/A,NL Nehlsen-Plump ,Betriebsstatte Bremen ,Louis-Krages-Strasse D-08280 Aue ,.,Germany

NL Nehlsen-Plump ,Betriebsstatte Bremen ,Louis-Krages-Strasse D-08280 Aue ,.,Germany

To Other Countries 15 01 10 Yes 0.001 Waste empty drums R1 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




Leinster Environmentals Ltd.,WP008-06,Clermont Business Park Clermont Business Park

Within the Country 15 01 10 Yes 0.02 Empty plastic containers R5 M Weighed Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

Business Park ,Haggardstown ,Dundalk ,Co. Louth.,Ireland

Clermont Business Park ,Haggardstown ,Dundalk ,Co. Louth.,Ireland

Within the Country 15 01 10 Yes 0.22 Empty metal containers R4 M Weighed Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

Midland Scrap Metal & Crane Hire Co. Ltd.,WMP005/D,Harbour Street,Mountmellick,Co. Laois,.,Ireland

Harbour Street,Mountmellick,Co. Laois,.,Ireland

Within the Country 15 01 10 Yes 0.22 Ink cartridges R13 M Weighed Offsite in IrelandIndaver Ireland Ltd.,W0036-01


Rehab Enterprises Ltd. T/A Rehab Recycle,WPRO33/2,77 Broomhill Road ,Tallaght ,Dublin 24 ,.,Ireland

77 Broomhill Road ,Tallaght ,Dublin 24 ,.,Ireland

To Other Countries 15 02 02 Yes 2.46 Solid oily waste R1 M Weighed Abroad Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

Lindenschmidt Unweltservice Krombach Germany,04 714 98089,Krombacher Strasse 43-46 ,57223 Kreuztal-Krombach ,.,.,Germany

Krombacher Strasse 43-46 ,57223 Kreuztal-Krombach ,.,.,Germany

To Other Countries 16 01 07 Yes 0.24 Oil filters R4 M Weighed Abroad Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

RD Recycling NV,023.03.10/V2005NO14639,Centrum Zuid 3017,3530 Houthalen,.,.,Belgium

Centrum Zuid 3017,3530 Houthalen,.,.,Belgium

To Other Countries 16 03 03 Yes 0.09 Optisperse D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01







Year)












Method Used

To Other Countries 16 03 05 Yes 0.08 Chlorine contaminated waste D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 16 05 04 Yes 0.04 Waste aerosol cans R4 M Weighed Abroad Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

SBH Sonderabfallentsorgung und -behandlung Hohenlohe GmbH,D/067/BW/08126,Austrasse 5,D-74238 Krautheim,.,.,Germany

Austrasse 5,D-74238 Krautheim,.,.,Germany

To Other Countries 16 05 06 Yes 0.01Lab smalls (containing mercury thermometers) D10 M Weighed Abroad

Indaver Ireland Ltd.,W0036-01




To Other Countries 16 05 07 Yes 0.27 Lab smalls D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01








To Other Countries 16 05 07 Yes 0.23 Waste desiccant D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 16 05 07 Yes 0.01 Waste cortrol D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




AVG Abfall-Verwertungs-Gesellshaft 11/05/2005



Gesellshaft,11/05/2005 IB2234/AVG-GENB-2,Borgistrasse 2 ,D-22113 ,Hamburg ,.,Germany


To Other Countries 16 05 08 Yes 0.04 Waste disinfectant D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 16 06 01 Yes 0.04 Batteries R4 M Weighed Abroad Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

Campine NV,06.5-1 6b-e,Nijverheidsstraat 2 ,B - 2340 ,Beerse ,.,Belgium

Nijverheidsstraat 2 ,B - 2340 ,Beerse ,.,Belgium

To Other Countries 16 07 08 Yes 0.23 Oil contaminated waste R1 M Weighed Abroad Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland



To Other Countries 16 07 09 Yes 0.9 Contaminated plastic R1 M Weighed Abroad Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland



To Other Countries 17 06 01 Yes 1.29 Asbestos Waste D1 M Weighed AbroadRilta Environmental Ltd.,W0192-02


Buhck Umweltservices GmbH & Co. KG,eg0019,Hamurg,.,.,.,Germany Hamurg,.,.,.,Germany




Year)












Method Used

To Other Countries 18 01 03 Yes 0.23 Medical waste D10 M Weighed Abroad SRCL Ltd.,W055-02

420-430 Beech Road ,Western Industrial Estate ,Naas Road ,Dublin 12,Ireland

AGR mbH,E56252039,RZR Herten/ImLinen.,.,.,.,Germany

RZR Herten/ImLinen.,.,.,.,Germany

Within the Country 18 01 03 Yes 0.96 Medical waste D9 M Weighed Offsite in Ireland SRCL Ltd.,W055-02


SRCL Ltd.,W055-02,420-430 Beech Road ,Western Industrial Estate ,Naas Road ,Dublin 12,Ireland


To Other Countries 19 08 06 Yes 20.0 Waste resin R12 M Weighed AbroadIndaver Ireland Ltd.,W0036-01


ATM,821780 02/3762 AWE/2002.3784,PO Box 30 ,NI-4780 AA Moerdijk ,Vlasweg 12 ,4782PW Moerdijk ,Netherlands

PO Box 30 ,NI-4780 AA Moerdijk ,Vlasweg 12 ,4782PW Moerdijk ,Netherlands

Within the Country 20 01 21 Yes 0.41 Fluorescent tubes R4 M Weighed Offsite in IrelandIrish Lamp Recycling Company,02/2000B

Woodstock Industrial Estate,Kilkenny Road,Athy,Co. Kildare,Ireland

Midland Scrap Metal & Crane Hire Co. Ltd.,WMP006,Harbour Street,Mountmellick,Co. Laois,.,Ireland

Harbour Street,Mountmellick,Co. Laois,.,Ireland

Within the Country 20 01 21 Yes 0.01 Fluorescent tubes R4 M Weighed Offsite in Ireland Rehab Recycling,WP98120

The Rehab Building,Kylemore Road,Ballyfermot,Dublin 10,Ireland

Rehab Recycling,WP98120,The Rehab Building,Kylemore Road,Ballyfermot,Dublin 10,Ireland


Within the Country 20 01 23 Yes 0.3 WEEE R4 M Weighed Offsite in Ireland Rehab Recycling,WP98120




Within the Country 20 01 35 Yes 4.85 WEEE R4 M Weighed Offsite in Ireland Rehab Recycling,WP98120




Within the Country 02 07 99 No 0.03 Wort sample D8 M Weighed Offsite in Ireland Dublin City Council,N/ARingsend WWTP,Dublin 2,.,.,Ireland

Greyhound Recycling andKnockmitten Lane ,Western Industrial Estate Dublin

Within the Country 15 01 03 No 35.1 Wood R3 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01

Industrial Estate ,Dublin 12,County Dublin,Ireland

Within the Country 13 07 01 Yes 0.4 Waste Diesel R9 M Weighed Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

Enva Ireland Ltd.,W0184-01,Clonminam Industrial Estate ,Portlaoise ,Co. Laois,.,Ireland


* Select a row by double-clicking the Description of Waste then click the delete button


Date post:	23-May-2020
Category:	Documents
Upload:	others
View:	7 times
Download:	0 times

Diageo St. James’s Gate BreweryThe St. James’s Gate Brewery is part of Diageo Global Supply,...

Documents