Diageo St. James’s Gate Brewery · 2014-12-16 · In July 2010, kegging of all stout ales and lagers in the Island of Ireland Diageo portfolio was transferred from the St. Francis

Diageo St. James’s Gate Brewery

IPPC Licence Register No. P0301-01

Annual Environmental Report 2010

March 2011

St. James‟s Gate Brewery Annual Environmental Report 2010

Diageo Ireland

Licence Register No. P0301-01 March 2011

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 .......................................................................................................... 27

2.2.1 Agency Site Audit .......................................................................................................................... 27 2.2.2 Agency Monitoring – Emissions to Sewer ..................................................................................... 27 2.2.3 Agency Monitoring – Emissions to Atmosphere ........................................................................... 29 2.2.4 Third-Party Audits ........................................................................................................................ 29

2.2.4.1 ISO 14001 Audit .................................................................................................................................. 29 2.2.4.2 IS 393 Audit ......................................................................................................................................... 29

2.3 ENERGY AND WATER CONSUMPTION...................................................................................................... 30 2.3.1 Energy Consumption..................................................................................................................... 30 2.3.2 Water Consumption ...................................................................................................................... 30

2.4 ENVIRONMENTAL INCIDENTS AND COMPLAINTS ..................................................................................... 31 2.4.1 Environmental Incidents ............................................................................................................... 31 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 2010 ..................................... 39 3.2.2 Environmental and Energy Management Programme for 2011 ................................................... 51

4 LICENCE-SPECIFIC REPORTS ........................................................................................................... 63

4.1 NOISE ...................................................................................................................................................... 63 4.1.1 Noise Survey ................................................................................................................................. 63 4.1.2 Noise Reduction Programme ........................................................................................................ 64

4.2 TESTING AND INSPECTION OF UNDERGROUND TANKS AND PIPELINES .................................................... 65 4.2.1 Bunding ......................................................................................................................................... 65 4.2.2 Pipelines ....................................................................................................................................... 65

4.3 HYDROGEOLOGICAL INVESTIGATION ...................................................................................................... 66 ANNEX A: AER RETURNS WEBFORM AND EUROPEAN POLLUTANT RELEASE AND TRANSFER

REGISTER


Diageo Ireland

Licence Register No. P0301-01 1 March 2011

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 2010 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


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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.

In July 2010, kegging of all stout ales and lagers in the Island of Ireland Diageo portfolio was

transferred from the St. Francis Abbey Brewery, Kilkenny, and the Great Northern Brewery,

Dundalk, to the St. James‟s Gate Brewery. High gravity beer is now blended, nitrogenated

and carbonated en route from the Fermentation Plant to the Keg Plant. As a result of the

consolidation of keg plant operations, the logistics operations were reorganised to cater for

the increase in activity.

Beer is produced 24 hours per day and 365 days per year. There are 40 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 2008

EN 16001:2009 Energy Management Standard 2009

ISO 22000 Food Safety Management 2009

OHSAS 18001 OH&S Occupational Health and Safety Management 2008


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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 Corporate strategy.

It will:

Comply with the requirements of the Integrated Pollution, Prevention and Control

licence and the Environmental Management Standard ISO14001.

Comply with all relevant Environmental legislation, legal and other requirements, that

relate to the Environmental Aspects

Have a framework for establishing and reviewing site specific KPI‟s which are

aligned with Diageo Global KPI‟s

Comply with all Diageo corporate policies and procedures, such as the Global Risk

Management Standards and the Global Environmental Policy

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

Sept 2010


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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 2010

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Figure 1: Environmental and Energy Management Structure

Site PA/Admin

Local Scheduler

Production KDR

Inventory Controller

Planning Mgr (4)

20 x Process Brewers

15 x Craft Technicians

10 x Quality Technicians

5 x Quality Process Technician

5 x Process Technicians TFS

5 x Production Shift Mgrs

2 x CI Process Brewers

2 x Day Production Shift Mgrs

Bhse/FBP

1 x Process Brewer GFE2

1 Day Production Shift Mgr BBA

Production Mgr (62)

10 x Process Technicians KP

10 x Craft Technicians

4 x Palletiser Technicians

5 x Packaging Shift Mgrs

1 x CI Process Technician

1 x Day PSM

Packaging Mgr (37)

3 x QA Day Technicians

1 x Quality Ops Mgr

1 x Environmental Mgr

1 x Systems Admin/KDR

Systems Mgr (7)

1 x Systems Engineer

1 x Training/Comms Mgr

2 x CI Brewers

1 x CI Team Leader

Technical Manager (6)

4 x Production Engineers

BBA/BHSE/FBP/KP

10 x Craft Apprentices

4 x CI Craft Technicians

2 x Maintenance/KDR Planners

1 x Contracts Mgr

1 x Health & Safety Mgr

1 x Painter

1 x Engineering Mgr (24)

Operations Mgr (142)


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2 SUMMARY INFORMATION

2.1 Self Monitoring Data

Except where otherwise stated, summary information is provided for the period from January

2010 to December 2010 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 2010.

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. 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.

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 has been reduced to a monthly frequency.

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 Note 1

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) Note 1:

Daily monitoring for BOD, COD and Suspended Solids takes place at SE1; these parameters are

monitored for at SE2 and SE3 on a monthly basis.


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Table 2 summarises the discharge from the main emission point to sewer, SE-1, during 2010,

with the trend from 2002 to 2010 for BOD, COD and Suspended Solids annual loads shown

in Figure 2. In 2010, 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)

2009

Mass Emission (kg)

2010

Licensed Mass

Emission (kg)

Volume (m3) 956,429 983,611 2,737,500

BOD 2,294,073 2,626,691 5,475,000

COD 3,535,134 3,881,552 10,950,000

Suspended Solids 720,925 617,445 3,832,500

Sulphates (as SO4) 71,808 142,550 1,095,000

Fats, oils and grease 15,609 10,021 273,750

Detergents (as MBAS) 1,969 685 273,750

Parameter Average Concentration

(mg/l) 2009

Average Concentration

(mg/l) 2010

Total Nitrogen (as N) 35.0 24.4

Ammoniacal Nitrogen 8.0 1.4

Total Oxidised Nitrogen 1.0 0.27

Total Phosphorous (as P) 22.6 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

An

nu

al L

oad

(th

ou

san

d k

g)

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

2002

2003

2004

2005

2006

2007

2008

2009

2010


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Table 3 summarises the discharge from the emission point to sewer, SE-2, during 2010, with

the trend from 2002 to 2010 for BOD, COD and Suspended Solids annual loads shown in

Figure 3. In 2010, the annual loads of BOD, COD and Suspended Solids from SE-2 were all

below the limits set out in the licence.



2009

Mass Emission (kg)

2010

Licensed Mass

Emission (kg)

Volume (m3) 58,726 94,127 438,000

BOD 2,972 2,615 876,000

COD 6,552 5,615 1,752,000

Suspended Solids 2,140 1,879 175,200

Sulphates (as SO4) 2,833 3,640 175,200

Fats, oils and grease 58.7 121 43,800

Detergents (as MBAS) 9.5 1.9 43,800


(mg/l) 2009


(mg/l) 2010






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

An

nu

al L

oad

(th

ou

san

d k

g)


2002

2003

2004

2005

2006

2007

2008

2009

2010


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Table 4 summarises the discharge from the emission point to sewer, SE-3, during 2010, with

the trend from 2002 to 2010 for BOD, COD and Suspended Solids annual loads shown in

Figure 4. In 2010, the annual loads of BOD, COD and Suspended Solids from SE-3 were all

below the limits set out in the licence.



2009

Mass Emission (kg)

2010

Licensed Mass

Emission (kg)

Volume (m3) 1,194 1,269 401,500

BOD 11 24 803,000

COD 74 291 1,606,000

Suspended Solids 52 97 160,600

Sulphates (as SO4) 25 37 160,600

Fats, oils and grease 1.2 1.9 40,150

Detergents (as MBAS) 0.19 0.9 40,150


(mg/l) 2009


(mg/l) 2010






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

An

nu

al L

oad

(th

ou

san

d k

g)


2002

2003

2004

2005

2006

2007

2008

2009

2010


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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 2010.

Table 5: Non Compliances for Emission Point SE-1 – BOD (2010)

BOD Concentration BOD Load

Daily Weekly Monthly Annual Daily Weekly Monthly Annual

January 0 0 0 - 0 0 0 -

February 0 2 1 - 0 0 0 -

March 0 3 1 - 0 0 0 -

April 0 2 1 - 0 0 0 -

May 0 0 1 - 0 0 0 -

June 0 0 0 - 0 0 0 -

July 0 0 0 - 0 0 0 -

August 0 0 1 - 0 0 0 -

September 0 0 1 - 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 7 7 1 0 0 0 0

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

The non-compliances shown in Table 5 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; and production activities (e.g. accidental

release of small quantities of product). There were no non-compliances in relation to BOD

load.

A number of initiatives under the Effluent Reduction Programme continued in 2010.

Figure 5 shows the average daily BOD concentration since 2002 and Figure 6 shows the

average daily BOD load since 2002.


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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

2002 2003 2004 2005 2006 2007 2008 2009 2010

BO

D C

on

cen

trati

on

(m

g/l)

Average Daily BOD Concentration at SE-1

Figure 6: Annual Trend in Average Daily BOD Load

0

5

10

15

20

2002 2003 2004 2005 2006 2007 2008 2009 2010

BO

D L

oad

(to

nn

es/d

ay)

Average Daily BOD Load at SE-1


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Emission Point SE-1 – COD

There were no non-compliances in relation to emissions of COD from SE-1 during 2010, as

summarised in Table 6.

Table 6: Non Compliances for Emission Point SE-1 – COD (2010)

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



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Emission Point SE-1 – Suspended Solids

Table 7 summarises the number of non-compliances for Suspended Solids emissions to sewer

at SE-1 in 2010.

Table 7: Non Compliances for Emission Point SE-1 – Suspended Solids (2010)

Concentration Load

January 0 0

February 0 0

March 0 0

April 0 0

May 0 0

June 0 0

July 0 0

August 0 0

September 0 0

October 0 0

November 0 0

December 1 0

January – December 1 0


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 was a single non-compliance in relation to Suspended Solids at emission point SE-1 in

2010, compared to four in 2009, five in 2008, seven in 2007, six in 2006 and twelve in 2005.

The non-compliance in 2010 was attributed to the use of grit during the cold weather in

December 2010.


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Emission Point SE-1 – pH

There were no non-compliances in relation to pH at SE-1 during 2010, as summarised in

Table 8.

Table 8: Non Compliances for Emission Point SE-1 – pH (2010)

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


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 2010, as summarised in Table 9.

Table 9: Non Compliances for Emission Point SE-1 – SO4, MBAS & OFG (2010)

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



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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.

There were no non-compliances in relation to emissions to sewer at SE-2 during 2010, as


Table 10: Non Compliances for Emission Point SE-2 (2010)

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



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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 2010, as


Table 11: Non Compliances for Emission Point SE-3 (2010)

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



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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 (2010)

Parameter Monitoring

Frequency

Average Annual Value

ASW-2 ASW-3

pH Monthly 8.15 8.18

BOD (mg/l) Monthly 3.08 3.08

COD (mg/l) Monthly 26.7 22.1

Suspended Solids (mg/l) Monthly 16.1 21.3

Fats, Oils & Grease (mg/l) Quarterly 1.0 1.0

Detergents (as MBAS) (mg/l) Quarterly <0.47 <0.21

Ammonia (as N) Quarterly 0.53 0.17

Total Oxidised Nitrogen (mg/l) Quarterly 1.43 1.47

Total Phosphorous (as P) (mg/l) Quarterly 96.5 99.9

Sodium (mg/l) Quarterly 1,128 1,165


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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, A1-6 and A1-7 was

carried out in March 2010. Table 13 summarises the monitoring results.

Table 13: Emissions to Atmosphere from CHP Plant (2010)

Emission Point NOX Concentration

(mg/Nm3)

Licence Limit

(mg/m3)

Mass Emission

(kg) Note 1

Licence Limit

(kg/year)

A1-3 30 80 15,312 43,836

A1-4 73 80 8,470 43,836

A1-5 69 80 33,894 43,836

A1-6 21 80 * Note 2

43,836

A1-7 12 66 15 13,754

Note 1: The mass emission is based upon the measured concentration, the maximum volumetric flow rate and

the operational hours for each stack.

Note 2: 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 2010,

with an overall reduction in NOX mass emissions of approximately 10%, compared to 2009.

Table 14 summarises the performance of the CHP plant during 2010.

Table 14: CHP Plant Summary (2010)

2009 2010

NOX emissions (kg) 62,871 57,691

Energy input (MWh) 300,723 289,241

Electricity generated (MWh) 73,362 69,899

CO2 emissions (tonnes) 57,821 55,295


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Figure 7 shows the historical mass emissions of NOX from the CHP plant from 2002 to 2010.

Figure 7: Mass Emissions of NOX to Atmosphere from CHP Plant (2002 to 2010)

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

NO

XA

nn

ual

Lo

ad

(kg

/year)

Emissions to Atmosphere from CHP Plant (NOX)

2002 2003 2004 2005 2006 2007 2008 2009 2010


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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 November 2010 and the results are summarised in

Table 15.

Table 15: Emission to Atmosphere from Roasthouse Afterburners (2010)

Emission

Point

Parameter Measured

Value

Licence

Limit

Mass Emission

(kg/year)

Licence Limit

(kg/year)

A2-1

Total Organics (as

C) (kg/h)

0.17 0.2 1,489 1,752

Nitrogen Oxides

(as NO2) (mg/m3)

40 61 1,789 2,880

A2-2

Total Organics(as

C) (kg/h)

0.1 0.4 876 3,504

Nitrogen Oxides

(as NO2) (mg/m3)

39 75 1,738 3,541

There were no non-compliances in relation to emissions to atmosphere from either A2-1 or

A2-2 during 2010. Figure 8 and Figure 9 show the annual mass emissions from A2-1 and

A2-2 from 2002 to 2010, respectively.

Figure 8: Mass Emission to Atmosphere from A2-1 (2002 to 2010)

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)

An

nu

al

Mass E

mis

sio

n (

kg

/year)

Mass Emission to Atmosphere from A2-1

2002

2003

2004

2005

2006

2007

2008

2009

2010


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Figure 9: Mass Emission to Atmosphere from A2-2 (2002 to 2010)

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)

An

nu

al

Mass E

mis

sio

n (

kg

/year)

Mass Emission to Atmosphere from A2-2

2002

2003

2004

2005

2006

2007

2008

2009

2010

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 2010 and the results are summarised in Table 16.

Table 16: Emission to Atmosphere of Total Particulates from Grain Intake (2010)

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 3 50 24,009 28,900 631.0 12,658

A2-4 <1 50 22,402 24,450 196.2 10,709

A2-5 <1 50 11,580 14,650 101.4 6,417

There were no non-compliances in relation to emissions to atmosphere from the grain intake

area during 2010.


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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 2010.


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Table 17: Summary of Annual Waste Arisings for 2010

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 03 01 N Kieselguhr 9.26 R3 (b) Waddock Composting,

Carlow

Ormonde Organics

Limited

WCP-OY-08-

0595-01

02 07 05 N Effluent Plant Screenings 330.6 R3 (b) Waddock Composting,

Carlow

Ormonde Organics

Limited

WCP-OY-08-

0595-01

02 07 99 N Barley Screenings / Dust

(Roasthouse, GFE & Malt

Intake)

947 R10 (b) Bord Na Móna, Kildare KW Forage Systems

Ltd./Michael Dunne

WCP-DC-08-

1146-01

02 07 99 N Black Spent Grain 11,505 R10 (b) Bord Na Móna, Kildare KW Forage Systems

Ltd/Agrilife

CP D240/2

02 07 99 N Spent Grain (Technology

House)

0.2 Not applicable

(animal feed) Note 1

Not applicable (animal feed) Note 1

KW Forage Systems Ltd. Not applicable


02 07 99 N Spent Grains 66,828 Not applicable





02 07 99 N Surplus Yeast (FBP) 10,207 Not applicable





15 01 02 N Plastic 2.1 R3 (b) Greyhound Recycling,

Clondalkin, Dublin.

Greyhound Recycling

and Recovery Ltd.

WCP-DC-08-

1154-01

15 01 03 N Wood 48.0 R3 (b) Greyhound Recycling,

Clondalkin, Dublin.

Greyhound Recycling

and Recovery Ltd.

WCP-DC-08-

1154-01

15 01 04 N Waste kegs 27.2 R4 (b) P. Carney Ltd., Kells,

Co. Meath

P. Carney Ltd. CP D 1003/7

15 02 03 N Spent carbon 4.9 R3 (b) Waddock Composting,

Carlow

A Quick Sharp Ltd., T/A

AQS Environmental

Solutions

WCP-MO-09-

0292-01


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Table 17: Summary of Annual Waste Arisings for 2010 (cont/d)

EWC HAZ

(Y/N)


(tonnes/ annum,

unless otherwise

specified)

Method of

Disposal/

Recovery


Recovery

Name of Waste

Disposal/ Recovery

Contractor (if

applicable)

Waste

Collectors

Permit

Number

16 01 03 N Waste tyres 6.99 R3 (b) Crumb Rubber, Dundalk

(b) Crossmore Transport

Ltd.

Crumb Rubber, Dundalk WCP-DC-08-

1136-01

17 01 07 N Construction & demolition

waste

82.0 R5 (b) Pac on Waste,

Balbriggan, Co. Dublin

(b) Premier Waste

Management, Dublin 22.

Greyhound Recycling

and Recovery Ltd.

WCP-DC-08-

1154-01

17 04 07 N Scrap Metal 51.0 R4 (b) Greyhound Recycling,

Clondalkin, Dublin.

Greyhound Recycling

and Recovery Ltd.

WCP-DC-08-

1154-01

20 01 01 N Cardboard 24.6 R3 (b) Greyhound Recycling,

Clondalkin, Dublin.

Greyhound Recycling

and Recovery Ltd.

WCP-DC-08-

1154-01

20 01 01 N Paper 21.8 R3 (b) Greyhound Recycling,

Clondalkin, Dublin.

Greyhound Recycling

and Recovery Ltd.

WCP-DC-08-

1154-01

20 01 02 N Glass 47.3 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 210.6 R3 (b) Greyhound Recycling,

Clondalkin, Dublin

Greyhound Recycling

and Recovery Ltd.

WCP-DC-08-

1154-01

20 01 08 N General Waste 177.2 R1 (b) Greyhound Recycling,

Clondalkin, Dublin

Greyhound Recycling

and Recovery Ltd.

WCP-DC-08-

1154-01

20 01 25 N Waste Catering Oil 2.31 R9 (c) Frylite, Strabane, Co.

Tyrone

Frylite Ireland Ltd. WCP-MO-09-

0624-01

06 04 04 Y Lab smalls 0.004 D10 (c) AVG, Hamburg ,

Germany

Indaver Ireland / Quay

Logistics

WCP- DC-08-

1121-01

07 01 03 Y Waste dichloromethane 0.14 D10 (c) AVG, Hamburg ,

Germany


Logistics

WCP- DC-08-

1121-01

08 03 12 Y Waste ink cartridges 0.1 D10 (c) AVG, Hamburg ,

Germany


Logistics

WCP- DC-08-

1121-01


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EWC HAZ

(Y/N)


(tonnes/ annum,

unless otherwise

specified)

Method of

Disposal/

Recovery


Recovery

Name of Waste

Disposal/ Recovery

Contractor (if

applicable)

Waste

Collectors

Permit

Number

13 02 08 Y Waste oil 2.0 R9 (b) ENVA Ireland Ltd.,

Portlaoise, Co. Laois

Enva Ireland Ltd. WCP-DC-08-

1116-01

13 05 07 Y Interceptor Waste 15.3 D6 (b) ENVA Ireland Ltd.,



1116-01

13 07 03 Y Waste diesel 0.2 R9 (b) ENVA Ireland Ltd.,



1116-01

13 08 02 Y Oily waste 1.0 R9 (b) ENVA Ireland Ltd.,



1116-01

14 06 02 Y Iso-octane waste 0.07 D10 (c) Indaver NV, Antwerp,

Belgium


Logistics

WCP- DC-08-

1121-01

14 06 03 Y Laboratory waste 0.44 D10 (c) AVG, Hamburg ,

Germany

(c) Indaver NV, Antwerp,

Belgium


Logistics

WCP- DC-08-

1121-01

15 01 10 Y Empty plastic containers 0.1 R3 (b) Leinster Environmentals,

Dundalk, Co. Louth


1116-01

15 02 02 Y Solid oily waste 5.13 R1 (c) Lindenschmidt

Unweltservice, Krombach,

Germany


1116-01

15 02 02 Y Used spill kits 0.09 D10 (c) AVG, Hamburg ,

Germany


Logistics

WCP- DC-08-

1121-01

16 05 04 Y Waste aerosol cans 0.36 R4 (c) Remondis Industrie

Service GmbH & Co. KG


1116-01

16 06 01 Y Batteries 0.1 R4 (c) Campine NV, Beerse,

Belgium


1116-01


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EWC HAZ

(Y/N)


(tonnes/ annum,

unless otherwise

specified)

Method of

Disposal/

Recovery


Recovery

Name of Waste

Disposal/ Recovery

Contractor (if

applicable)

Waste

Collectors

Permit

Number

16 07 08 Y Oil contaminated waste 1.7 R1 (c) Lindenschmidt

Unweltservice, Krombach,

Germany


1116-01

18 01 03 Y Medical waste 0.03 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 1.05 D9 (b) Sterile Technologies,

Naas Road, Dublin

SRCL Ltd. WCP-DC-09-

1178-01

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)


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2.2 Monitoring and Enforcement

2.2.1 Agency Site Audit

On 26th

February 2010, the Agency carried out an Audit at the site. The Agency‟s Audit

Report of 31st May 2010 identified four 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 16th

June, 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 March, May, August and November 2010 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. At the time of preparing this AER, the results from the Agency for the samples

collected in August and November had not been received by the Brewery.

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.


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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 Alt

2 EPA Alt EPA Alt EPA Alt EPA Alt EPA

March 2010

SE-1 2,955 - 4,665 - 632 - 4.21 - 1.0 - 8 - 87.2 - 22 -

SE-2 1 NT 25 23 3 NR 3.2 1.6 1.16 1.2 1 10 39.2 NM 1.05 1.06

SE-3 4 NT 23 23 9 NR 0.2 0.09 0.47 0.4 1 10 12.6 39.2 0.054 0.003

May 2010

SE-1 3,585 3,855 4,445 5,535 584 510 7.9 0.47 0.4 0.9 12 0 390 - 30.6 30.75

SE-2 45 39 106 76 10 10 3.5 3.2 0.1 0.6 1 10 38.7 34.7 24 1.97

SE-3 17 15 66 54 20 11 0.3 0.27 0.68 0.6 2 10 9 7.2 0.11 0.05

August 2010

SE-1 4,140 - 5,365 - 544 - 0.58 - 0.1 - 9 - 71.7 - 25.4 -

SE-2 50 - 127 - 48 - 1.1 - 0.15 - 1 - 47.2 - 33.2 -

SE-3 7 - 36 - 48 - 0.9 - 0.68 - 10 - 14 - 0.14 -

November 2010

SE-1 3,485 - 4,250 - 400 - 0.27 - 0.1 - 9 - 572 - 17.9 -

SE-2 12 - 36 - 18 - 6 - 0.99 - 1 - 59.4 - 2.04 -

SE-3 4 - 19 - 0.01 - 0.2 - 0.37 - 1 - 23.2 - 0.07 -

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.

NT: Not tested

NM: Not measured


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2.2.3 Agency Monitoring – Emissions to Atmosphere

On 10th

March 2010, Euro Environmental Services carried out monitoring of the emissions to

atmosphere at three emission points (A1-3, 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 A1-3 A1-5 A2-2

Nitrogen Oxides (as NO2) (mg/m3)

18.9 54.5 n/a

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

n/a n/a 0.1

The parameters monitored at all three emission points were below their respective limits.

2.2.4 Third-Party Audits

There were two Third-Party audits carried out by Certification Europe during 2010: one in

relation to the Environmental Management System standard ISO 14001 and one in relation to

the Energy Management System standard IS EN 16001. The audits were carried out over a

total of four days.

2.2.4.1 ISO 14001 Audit

On 20th

and 21st September 2010, Certification Europe carried out a Re-Certification Audit of

the Environmental Management System. The audit identified four non-conformances and

three observations/comments. Certification Europe re-certified the Brewery to

ISO 14001:2004.

2.2.4.2 IS 393 Audit

On 15th

and 16th

April 2010, Certification Europe carried out a Reassessment Audit on the

Energy Management System against the European standard IS EN 16001. The audit

identified four non-conformances and a single observation/comment. The Brewery

maintained its certification to the European Standard IS EN 16001.


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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 2010, while Table 21 summarises the

energy inputs to and outputs from the CHP plant.

Table 20: Energy Consumption (MWh) (2010)

Energy Source 2010

Natural Gas for CHP Plant 289,241

Natural Gas for Roasthouse 9,739

Total Natural Gas 298,980

Diesel for CHP Plant 73

Diesel / gas oil for logistics 2,323

Electricity imported from the grid 763

LPG for forklift trucks 342

Total Site Energy Consumption 302,481

Table 21: Summary of Energy Inputs to and Outputs from the CHP Plant (MWh) (2010)

Energy Source 2010

Inputs

Natural Gas for electricity exported to grid 68,790

Natural Gas for electricity & steam exported to the Brewery 220,451

Total Natural Gas input 289,241

Outputs

Electricity exported to the grid 27,516

Electricity exported to the Brewery 42,383

Total electricity generated 69,899

Steam exported to the Brewery 121,469

Overall energy usage fell in 2010 compared to 2009. A focused energy efficiency

programme, coupled with the on-going implementation of the Energy Management System

drove the decrease in energy usage on the site. A number of energy efficiency projects were

delivered in 2010, and this programme will continue into 2011.

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.


Diageo Ireland


Table 22: Water Usage (2010)

Source 2009 (m3) 2010 (m

3)

Town 1,779,106 1,805,135

Service (Canal) 277,190 239,262

Cooling 0 0

Total 2,056,296 2,044,397

2.4 Environmental Incidents and Complaints

2.4.1 Environmental Incidents

Table 23 summarises the environmental incidents that occurred during 2010, setting out the

cause and corrective action, and identifying the relevant authorities that were notified of the

incident.

A total of 51 incidents occurred during 2010, 24 of which arose due to higher than normal

temperatures at SE-1. As a result of successfully implementing a number of initiatives to

reduce water usage at the site over the last number of years, the cooling buffering capacity at

SE-1 has been reduced. A team has been established to identify and assess the options for

recovering heat from the high temperature sources, primarily the hot medium used in the

cleaning programmes. The team is also investigating the potential for temperature quenching

prior to effluent entering the Waste Water Treatment plant.

Table 23: Environmental Incidents (2010)

Month Number Description Authorities

Contacted

January 0 None

-

February 3 The mean weekly BOD concentration for week 6

exceeded the licence limit (3,048 mg/l -v- 3,000 mg/l)

as a result of a loss of product to drain from a failed

valve. The valve was repaired.

The mean weekly BOD concentration for week 7


as a result of a loss of product to drain due to an error

in the brewing programme.

The mean monthly BOD concentration at SE-1

exceeded the licence limit (3,076 mg/l -v- 2,500 mg/l).

This was attributed to the events in weeks 6 and 7.

EPA

EPA

EPA

March 4 The mean weekly BOD concentration for week 9


due to a minor fault on the evaporator.


(3,001 mg/l -v- 3,000 mg/l) and for week 11

(3,226 mg/l -v- 3,000 mg/l) exceeded the licence limit

due to low volume flow.

EPA

EPA


Diageo Ireland


Table 23: Environmental Incidents (2010) (cont/d)


Contacted

March

(cont/d)



This was attributed to the events in weeks 9 to 11.

EPA

April 3 The mean weekly BOD concentration for week 15


due to higher volumes of returned product discharged

to drain.



due to a loss of product to drain at the tanker station.



This was attributed to the events in weeks 15 and 16.

EPA

EPA

EPA

May 1 The mean monthly BOD concentration at SE-1


This was attributed to loss of product to drain from a

faulty valve.

EPA

June 4 On 14th

June, one of the samples collected as part of

the groundwater monitoring programme was found to

have an abnormal appearance. The cause was

attributed to cleaning of one of the underground

effluent balance tank prior to its scheduled inspection.

A corrective action plan was put in place.

On 25th

, 28th

and 29th

June, the temperature at SE-1

exceeded 42°C, with maximum temperatures of

44.5°C, 43.7°C and 44.5°C, respectively. An

investigation identified the cause to be the warmer

ambient temperatures combined with high

temperatures used during routine plant cleaning.

EPA

EPA

July 9 The temperature at SE-1 exceeded 42°C:

o Between 3rd

and 4th

July, on three occasions.

o On 6th

July (a maximum recorded

temperature of 43.5°C)

o On 11th



o On 12th



o On 14th


temperature of 43°C)

o On 19th



o On 25th


temperature of 45°C).

An investigation identified the causes to be the

warmer ambient temperatures combined with high

EPA


Diageo Ireland



Contacted

temperatures used during routine plant cleaning.

On 18th

July, a fault occurred on the pH probe at SE-3.

The probe was replaced and returned to normal

operation. A grab sample taken during the period

showed that the licence limit was not exceeded.

On 26th

July, the in-line pH probe at SE-3 failed and

was subsequently replaced. There was no flow via

SE-3 during this period.

EPA

EPA

August 7 Between 6th

and 7th

August, the temperature at SE-1

exceeded 42°C intermittently, with a maximum

recorded temperature of 44°C. During this period,

restrictions on the water supply to the Brewery due to

a leak in the Dublin City Council water supply

resulted in a lower effluent flow and therefore a lower

cooling effect on the small volumes of hot condensate

generated during the brewing process. The burst

water main was repaired.

On 10th

August, the temperature at SE-1 exceeded

42°C, with a maximum recorded temperature of 43°C.

The cause was attributed to two processes that release

hot liquid to drain coinciding with a fault with a valve

in the CHP plant, which caused a boiler blow down.

The valve in the CHP plant was repaired and the

brewing programme was reviewed to prevent two

brewing processes occurring simultaneously.

On 15th


42°C intermittently, with a maximum recorded

temperature of 44°C. This was attributed to a fault

with the evaporator which resulted in larger volumes

of hot condensate being released to drain. The

evaporator was taken out of service and repaired.

On 19th


42°C, with a maximum recorded temperature of 44°C.

This was caused by a small overflow from the warm

and hot water storage tanks, for which corrective

actions were taken.

On 21st and 22

nd August, the temperature at SE-1

exceeded 42°C intermittently, with maximum

recorded temperatures of 43.7°C and 46.8°C,

respectively. An investigation identified the causes to

be the warmer ambient temperatures combined with

high temperatures used during routine plant cleaning.

The monthly mean BOD concentration at SE-1


Two losses of beer during the month, due to a pump

and a valve failure, contributed to the higher than

normal concentration. In both cases, the equipment

was replaced.

EPA

EPA

EPA

EPA

EPA

EPA


Diageo Ireland



Contacted

September 6 On 11th

September, the temperature at SE-1 exceeded

42°C. The cause was attributed to the release of

excess hot condensate coinciding with routine

cleaning. A low effluent flow reduced the overall

cooling buffering capacity.

On 12th


42°C. The cause was attributed to an inefficient heat

exchanger on the evaporator. A new plate pack was

ordered and subsequently installed.

On 13th


42°C. The cause was attributed to the fault with the

heat exchanger (from above) combined with draining

of hot water from the boiler in the CHP plant as part of

its normal start-up process.

On 15th


42°C, caused by the fault with the heat exchanger

(from above).

On 15th

September, the in-line pH probe at SE-2

recorded high pH levels, with a maximum reading of

11.2. No process drains discharge via SE-2. A CCTV

survey was conducted to identify the drains that

discharge via SE-2.

The monthly mean BOD concentration exceeded the

licence limit (2,594 mg/l -v- 2,500 mg/l) caused by a

loss of product to drain due to a fault with the flow

meter and evaporator. Both items were repaired.

EPA

EPA

EPA

EPA

EPA

EPA

October 5 On 1st October the evaporator heat exchanger in the

BBA department caused a high temperature at SE-1.

The maximum temperature recorded was 43.5°C. A

project to fix the heat exchanger and prevent the

release of excess hot condensate to drain was

commenced.

On 2nd

October, the temperature at SE-1 exceeded

42°C from 16.40 until 17.51. No specific cause was

identified, other than normal process cleaning which

was underway at the time.

On 4th

October, the temperature at SE-1 was elevated

from 00.38 until 01.23. The maximum temperature

recorded during this period was 45.1°C. A normal

stream-cleaning programme in the Brewhouse was

underway at the time using hot caustic, which was

found to be the cause of the elevated temperature.

The in-line pH probe at SE-2 failed on 5th

October.

The failure arose from a loose electrical connection

during routine cleaning of the probe. The connection

was repaired and the probe returned to service.

On 5th

October, the temperature at SE-1 exceeded

EPA

EPA

EPA

EPA

EPA


Diageo Ireland



Contacted

42°C, with a maximum recorded temperature of

43.8°C. . No specific cause was identified, other than

normal process cleaning which was underway at the

time.

November 2 The in line pH probe at SE-1 gave erratic readings on

1st November. The pH probe was cleaned and the

readings returned to normal. A second, backup, in-

line pH probe showed that during the period of erratic

readings, the pH was within the emission limit value.

The monthly mean BOD concentration exceeded the

licence limit (2,758 mg/l -v- 2,500 mg/l), caused by a

loss of product to drain from a fault with a valve and

freezing of equipment due to the adverse cold weather.

The valve was repaired and the options for preventing

future freezing of equipment are being assessed.

EPA

EPA

December 5 On 10th

December, the pH probe at SE-2 recorded a

high pH level for a period of 30 minutes. The cause

was investigated and was attributed to the large

volume of melting snow at the time.

On 11th

December, a fault occurred on the in-line pH

probe at SE-1, which incorrectly recorded low pH

results. The backup pH probe was used to monitor

pH, which showed the pH level to be within the

licence limits. The probe was repaired and replaced.

On 16th

December, a fault occurred on the continuous

pH and temperature probes at SE-1, resulting in a loss

of readings. The fault was caused by a blown fuse,

which was replaced. The composite samples for the

period met the licence limits.

As a result of the adverse cold weather, no composite

sample could be taken at SE-1 between 25th

and 27th

December. The automatic pH probe wash at SE-1 also

froze, resulting in irregular pH readings between 26th

and 27th

December.

On 28th

December, the suspended solids concentration

exceeded the licence limit (3,540, mg/l -v- 1,400 mg/l)

due to the use of grit on the roadways at the site during

the adverse cold weather and the increase in surface

water following a leak in the water main.

EPA

EPA

EPA

EPA

EPA

Total 51


Diageo Ireland


2.4.2 Environmental Complaints

In 2010, there were six 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 2010

Date Complaint Cause Corrective Action

25/01/2010 A complaint was received

from a local resident in

relation to a noise from the

rear of the spent grain yard.

The source of the noise was

identified as an auger on one

of the dust skips.

The skip was removed from

service and was subsequently

removed from the site for

repair by the supplier. The

skip was returned to the site

and to service once it was

repaired.


from a local resident in

relation to a noise from the

rear of the spent grain yard.


identified as an auger on one

of the dust skips.

The skip was removed from

service and was subsequently

removed from the site for

repair by the supplier. The

supplier set out the actions

required to prevent a

recurrence of this noise and

the skip was returned to the

site and to service once it

was repaired.


from a local resident

regarding noise levels from

the spent grain yard.

Upon investigation, no noise

source was identified.

The complaint was closed to

the satisfaction of the

complainant following

communication of the

Brewery‟s investigation and

the outcome.


from residents in the

apartments adjacent to the

site, relating to noise

emanating from the CHP

plant.


identified as the lifting of a

pressure relief valve on the

CHP plant which, in turn,

was attributed to a power

outage in the vicinity of the

site.

The relief valve returned to

normal operation following

the restoration of power to

the area. The operators of

the CHP plant investigated

the root cause of the

activation to prevent a

recurrence.


from a local resident relating

to a „banging‟ noise from the

spent grain yard.

Due to the extremely cold

weather at the time, the slide

valves controlling the

transfer of grain to the

production area had frozen.

To free the valves, the

maintenance team had

„banged‟ the valves and the

vessels.

The maintenance teams were

reminded to consider the

effect of their actions and the

Brewery‟s responsibilities to

its neighbours in relation to

noise.


from a local resident about a

loud banging coming from

the spent grain yard

The cause was found to be a

faulty gearbox in one of the

dust skips.

The skip was taken out of

service and the gearbox was

repaired.


Diageo Ireland


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.


Diageo Ireland


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

EN 16001. The Environmental & Energy Management Plan for 2011 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

– IEN16001

Evaluate alternatives

Quantify savings

Propose actionsSteam

/ FuelWater

Elec/

RefgOthers

Project based

Operational

changes

Mainenance/

Repair/replace

CONTINUOUS

IMPROVEMENT

Measure

Sustain

KPI improvement

Benchmark

Solution

Delivery

Management

Review

IDEA Sources

Measurement

Process & Product

development

Audits

Benchmarks

Staff Ideas

External consultants

Suppliers

Brewhouse

FBP

Keg Plant

BBa

Utilities

Facilities

Local champion and Ideas Log per Area.


Diageo Ireland


The Plan is prepared in accordance with the requirements of ISO 14001, 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 2010

The following tables proved a report on our Environmental and Energy Management

Programme for 2010.


Diageo Ireland


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.

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 2010 Remediation work recommended as part of the Phase 1 CCTV survey is on-

going, as access to drains in production areas are made available. Phase 2 (of 3)

of the CCTV survey is complete and Phase 3 is underway. Recommendations

from Phase 2 and Phase 3 will be initiated on receipt of the final report.

1.3 To protect soil, surface waters and

groundwater from contamination from

materials stored on the site.

Ongoing The planned approach to bund integrity testing was signed off in December

2010. Integrity testing of bunds under this approach commenced in January

2011, and will be undertaken on a phased process.

1.4 To improve the identification of the foul

sewer system from the surface water

drainage system.

December 2010 A review of the site drainage system was undertaken. Approximately 1,200

manholes and 800 gullies were identified. The project proposal to colour code

all manholes is currently being developed by the Business Engineering

Department.


Diageo Ireland


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.


2.1 Continue to monitor emissions of nitrogen

oxide from the CHP plant.

Ongoing

Air monitoring is carried out as per licence and emissions of nitrogen oxide

have remained below the emission limit value set out in the licence.

2.2 To sustain the improved ratio of CO2

recovery to enable the site to sell maximise

the sale of excess CO2 per annum.

December 2010

Since July 2010, the Great Northern Brewery and St Francis Abbey Brewery no

longer require CO2. Fermentation control has been maximised and the

installation of an additional meter has improved quantification of secondary

CO2.

2.3 To reduce the Environmental impact of

employees travelling to work.

December 2010

The cycle to work scheme was successfully rolled out in 2010.


Diageo Ireland


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.


3.1 To ensure that the situation achieved in

2004-2009 of zero waste to landfill is fully

maintained.

Ongoing St James Gate continues to strive to achieve zero waste to landfill. The

GreenIQ team rolled out waste segregation site wide in non-production areas.

A programme of communication ran in tandem to increase employee awareness.

Communication tools, such as Insight Magazine and the Facilities newsletter,

have been used to promote the programme. An Environmental day was held in

May 2010 to promote awareness to all employees.

3.2 To establish more detailed waste reporting

and performance indices.

To increase our recycling figures by 10%

from the 2007 figure (16%).

December 2010

Individual building waste reporting was found to be excessively labour

intensive. Waste reporting for the site has been reviewed to ensure complete

visibility around cradle to grave management of waste.

3.3 To undertake the auditing of waste

contractors who remove waste material from

the site.

Ongoing The central Governance team carry out a programme of supplier audits, which

includes waste contractors. An audit of the site‟s main waste management

provider was under taken by an independent auditor on behalf of Diageo and a

series of face to face communications with the service provider are being

undertaken to address all issues raised during the audit.

3.4 Continue rollout of best practice waste

management to specific business units or

buildings.

June 2010 Waste management continues to be a particular area of focus and has now been

rolled out site-wide.

3.5 Introduce the Demand company to the waste

segregation policy.

December 2010 The GreenIQ team rolled out waste segregation site wide in the Demand

organisation. A programme of communication ran in tandem to increase

employee awareness (see also Target 3.1).

3.6 Establish a robust waste management

Strategy for the site.

December 2010 A review of the waste management was carried out and the recommendations

from the review are being prioritised.


Diageo Ireland


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.


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 2010 Potential losses from vessel and line push-outs were minimised in the Brewing

areas. Diageo reviewed its brewing practices in Ireland and in July 2010

kegging activities from all sites in Ireland were consolidated at St James Gate.

Management of returned beer for Ireland was also centralised at St James Gate.

As a result of the increase in beer volumes and beer types, the effluent load

increased. Work is on-going to identify the sources of the increased effluent.

In-line effluent samplers were removed from the drains to facilitate drain repair

and therefore the BOD loads for specific areas are not available. The KPIs will

be agreed with the brewing areas for 2011.

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 2010 Keg plant activities changed significantly in 2010 as a result of the kegging

consolidation. An increase in the number of product changeovers has increased

the effluent from push-outs. A project team is reviewing push-outs to minimise

losses to drain.

4.3 To monitor and utilise the real time

information available relating to effluent

performance.

December 2010 Effluent is monitored using two TOC meters. High BOD concentrations trigger

an alert to the shift mangers, prompting investigations into potential leaks.

4.4 Establish a baseline for GFE 2effluent flow

to help reduce the level of process waste in

the BBA area.

December 2010 Push-outs in the BBA were optimised to reduce process waste.

4.5 To reduce the effluent load from the BBA

department.

December 2010 Raw materials usage was optimised to reduce the effluent from the process.

Maximum extraction without adverse effect on quality was achieved.


Diageo Ireland


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.


5.1 To review the level of noise at noise

sensitive locations.

December 2010 Recommendations from the 2009 noise survey were completed. Key areas of

the site will be targeted for a detailed noise survey in 2011.


Diageo Ireland


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.


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.

December 2010 Caustic usage was on track at 80.62 kg/1000 kegs.

Average acid usage was above target at 14.5 kg/1000 kegs.

A change of chemical supplier is underway for the site and targets will be

agreed with new supplier.

6.2 Improve lubricant usage ratio in the keg

plant from 2.9 kg/1,000 kegs.

December 2010 Lubricant usage was on track at 2.14 kg/1000 kegs.

The use of dry lube was trialled for 6 months. However, the dry lube was

deemed not to be appropriate for use in the keg plant.

6.3 Sustain usage in 2010 on chemical detergent

used in the Brewing Department based on

2008 targets.

December 2010 Acid use met the target.

Caustic usage was off target, due to a number of issues requiring special CIPs.

Sterilant usage was slightly above the target due to dosing issues and increased

special CIP requirements.

6.4 In the BBA monitor CIP usage against

targets. Identify areas for potential savings.

December 2010

As a result of chemical supplier changeover mid-year, results are were not

available for the chemical usage at the time of preparing the AER.

6.5 To optimise extract recovery in the

Brewhouse by achieving in excess of 96.5%

extract from raw materials again in 2010.

Ongoing The target on extract recovery was achieved.


Diageo Ireland


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.


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

December 2010 An overall water consumption ratio of 3.74:1 was achieved in 2010.

The ratio for Town water was 3.3:1.

The ratio for Canal water was 0.44:1.

7.2 Sustain the consumption of electricity to

31 MJ/hl of beer (or 8.6 kWh/hl).

December 2010 An electricity consumption ratio of 28 MJ/hl was achieved in 2010.

7.3 Sustain the consumption of steam below

100 MJ/hl of beer (or 27.78 kWh/hl).

December 2010 The steam consumption ratio target of less than 100 MJ/hl was achieved in

2010.

7.4 In the BBA, target a further reduction in

water usage by focussing on a water

reduction initiative in 2010.

December 2010 The validation of water meters in BBA was carried out. KPIs were reviewed on

a weekly basis at the Energy Savings initiatives meeting and deviations from

predicted usage were investigated.

7.5 To have departmental objectives that will

drive improvement in energy efficiency.

December 2010 A 5% utilities reduction plan was drawn up with proposals for Departmental

savings. Departmental targets were reviewed weekly at the Energy Savings

initiatives meeting and deviations from predicted usage were investigated.


Diageo Ireland


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.


8.1 Direct Fired Steam use of less than 7 GWh

per year for 2010 (based on Gatepower

Contract 137 + 7GW).

December 2010 Direct fired steam usage was off track for 2010. The actual usage for the year

was 11.2 GWh. Usage was on target for the first third of 2010, but changes in

production outside the control of the Utilities Department resulted in increased

steam consumption.


Diageo Ireland


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.


9.1 Sustain reductions made in 2007/8/9 on site

electrical demand for refrigeration.

December 2010 Reductions in electrical demand for refrigeration have been sustained. The

recirculation chiller performance was reviewed on a weekly basis at the Energy

Savings initiatives meeting and deviations from predicted usage were

investigated.


Diageo Ireland


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.


10.1 Sustain operation of the nitrogen spill air

project to deliver the electrical savings seen

in 2007.

December 2010 Compressed air leak surveys were carried out in May and November 2010 and

repairs were carried out as identified in the reports.


Diageo Ireland


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.


11.1 To inform all production employees

regarding the requirements of the IPPC

licence for the Brewery.

On-going Environmental Awareness training was held for all production teams and

contract companies.

11.2 To ensure that all employees and contractors

remain fully aware of their obligations

regarding waste handling on site

On-going Contractors were reminded of their obligations regarding waste handling,

through environmental awareness training and face to face communications.

Environmental issues were raised at daily production meetings and team

briefings. Other communication tools, such as the Insight magazine and

Environmental Days were used to increase employee awareness.

The GreenIQ team rolled out environmental initiatives across the site.


Diageo Ireland


3.2.2 Environmental and Energy Management Programme for 2011

In the following tables we set out our Environmental and Energy Management Programme

for 2011. This programme includes continuing the ongoing targets across the site and the

introduction of new targets that were identified during 2010.


Diageo Ireland


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.

Continue with the bi-annual sampling

programme. Review sampling requirements with

the Agency.

On-going sampling as

per current agreement

with EPA.

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.

Carry out repair work from Phases 2 & 3 of the

CCTV survey.

On-going Environmental Manager

/Business Engineering

Overall site

1.3 To protect soil, surface waters and

groundwater from contamination

from materials stored on the site.

Initiate the second round of the 3-yearly bund

survey. Ensure all new bunds on site comply with

the new procedure. Review the bund log.

December 2011 Environmental Manager Overall Site

1.4 To improve the identification of the

foul sewer system from the surface

water drainage system

Implement a programme of colour coding of all

manholes on site as proposed by the Agency in

January 2010.

December 2011 Environmental Manager


Overall Site

1.5 Reduce the potential for

uncontrolled release from the site.

Identify unmonitored emission points from the

site and implement a procedure for protection of

these outfalls from uncontrolled releases.

December 2011 Environmental Manager


Overall Site


Diageo Ireland


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.


2.1 To sustain the improved ratio of

CO2 recovery to enable the site to

maximise the sale of excess CO2

per annum.

Sustain improved fermentation control and

maximise FBP CO2 recovery to the CO2

collection plant.

Explore options to find external buyer of CO2.

December 2011 Contracts Manager /

Third Party Utilities Site

Manager

Brewing /

Third-party

Utilities

Company


Diageo Ireland




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.


3.1 Strive to achieve zero waste to

landfill.

Continue to build employee awareness of the

principles of Reduce, Reuse, Recycle.

Use the GreenIQ team to communicate through

Insight magazine, the facilities Newsletter and the

Environmental Day.

Work with waste contract companies to ensure

waste is routed away from landfill.

Ongoing Facilities Manager /

Environmental Manager

Overall Site

3.2 Reduce overall quantities of waste

on the site. Increase proportion of

waste recycled.

Replace non-recyclable cups with reusable cups

across the site.

Establish a clear reporting system which

differentiates the 4 waste streams. Measure

improvements in recycling rates.

December 2011 Facilities and

Environmental Manager

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.

Work with key waste contract company to ensure

findings raised during 2010 audit are closed out.

Ongoing Environmental

Manager/Diageo Supply

Procurement Team

Overall site

3.4 Introduce the Demand company to

Environmental waste initiatives.

Use the GreenIQ forum to improve visibility of

the Environmental agenda.

December 2011 Environmental Manager Demand


Diageo Ireland




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.


3.5 Establish a robust Waste

Management Strategy for the site.

Prioritise the recommendations and initiate the

key recommendations made in the proposal for a

Waste Management review, which was drawn up

in 2010 to help drive the waste management

strategy.

December 2011 Environmental Manager Overall site

3.6 Look for opportunities for recycling

waste that is beneficial to the

business.

Identify recycling facilities that require waste as a

raw material e.g. plastic wastes.

December 2011 Facilities/Environmental

Manager/Operations

Overall site


Diageo Ireland


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.


4.1 To further reduce the effluent load

from the Brewing areas to sustain

improvements.

Improve the TOC alert system by setting up TOC

load alert system.

Use the Manufacturing Excellence forum to drive

the effluent reduction programme.

December 2011 Brewing Shift Manager Brewing

4.2 Reduce effluent emissions from the

Keg Plant.

Quantify the waste beer from the keg plant, which

increased as a direct result of the consolidation of

kegging at SJG, identify the key sources of the

effluent, implement improvements and include

effluent emissions in the keg plant waste report.

Review how BOD is currently measured for the

keg plant

December 2010 Packaging Production

Manager/Packaging Shift

Manager

Keg Plant

4.3 To reduce the effluent load from the

BBA department.

Draw up effluent reduction plan with BBA based

on information logged through Push Outs &

Water Chases in GFE1 & GFE2.

December 2011 BBA Day Shift Manager BBA

4.4 Manage effluent arising from

Returned Beer Store.

Replace Returned Beer flow meter to determine

percent of site load attributable to Returned Beer

store.

Agree site effluent KPI‟s for F12. Adopt separate

KPIs for Total Site and the site excluding

Returned Beer.

June 2011 Environmental

Manager/Day Production

Shift Manager

Keg Plant


Diageo Ireland


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.


5.1 To review the level of noise at

noise sensitive locations.

Carry out detailed noise survey at specific noise

sensitive locations on site to identify key areas

attributing the noise. Develop next phase of

Noise Reduction Plan based on the findings from

the survey.

June 2011 Environmental Manager Overall site


Diageo Ireland






6.1 Maintain caustic usage ratio in the

keg plant at 100 kg/1000 kegs and

acid usage at 10 kg/1000 kegs.

Agree targets with new chemical supplier and

track against target. Re-establish monthly review

with supplier. Monitor usage on a shift by shift

basis.



Manager

Keg Plant

6.2 Improve lubricant usage ratio in the

keg plant from 2.9 kg/1000 keg.




basis.



Manager

Keg Plant

6.3 Sustain usage of chemical

detergents used in the Brewing

Department.

Agree targets for chemical detergents with the

new chemical supplier.

June 2011 Brewing

Manager/Brewing Shift

Manager

Brewing

6.4 To optimise extract recovery in the

Brewhouse by achieving in excess

of 96.5% extract from raw materials

again in 2011.

Optimise mill performance.

Align mashing recipes across streams.

Dec 2011 Brewing

Manager/Brewing Shift

Manager

Brewing


Diageo Ireland






6.5 To reduce the ratio of water

consumption per hl of beer

produced from 2010 levels (3.74:1)

Reduce towns water usage

ratio from 3.3:1.

Reduce Service (Canal) Water

usage from 0.44:1.

Implement condensate recovery projects in

the keg plant and BBA.

Improve water usage in the evaporator by

10% by optimising run up & run down.

Implement CO2 plant water washer project.

Optimise cooling water run time and quantify

water savings in BBA.

Optimise cleaning efficiency (by Third Party

utilities company).

Report on potential water savings ideas (by

Third Party utilities company).

December 2011 Contract Manager/ Third

Party Utilities Site

Manager

Technical

Support

Department/

Third-party

Utilities

Company

6.6 Maintain caustic usage ratio in the

keg plant at 100 kg/1000 kegs and

acid usage at 10 kg/1000 kegs.




basis.



Manager

Keg Plant


Diageo Ireland






7.1 Sustain the consumption of

electricity at 32 MJ/hl of beer.

(or 8.6 kWh/hl)

Complete the review of the energy study.

Continue to run new Refrigeration plant on a

single circuit, where possible.

Complete electrical metering project to give

on-line monitoring for up to 76% of site

usage.

June 2011

December 2011

Contract Manager/RWE

Utilities Site Manager

Technical

Support

Department /

Third-party

Utilities

Company

7.2 Sustain the consumption of steam

below 100 MJ/hl of beer (or

27.78 KWh/hl = 37 kW steam/hl of

beer).

Implement condensate recovery projects in

keg plant and BBA.

June 2011 Contract Manager/RWE

Site Manager

Technical

Support /

Third-party

Utilities

Company

7.3 To reduce gas and steam use from

direct firing of waste heat boilers

(i.e. to reduce additional gas use not

required for CHP).

Review feasibility of 2010 target for direct

fired steam use of less than 7 GWh per year.

Review the reinstatement of 6% boil off

project

June 2010 Technical Support Team

and Operations Team

Operations

and Technical

support

7.4 Reduce cooling load and hence

refrigeration electrical demand to

refrigeration compressors.

Continue to run the second glycol cooling

circuit only when required.

Continue to monitor the recirculation chiller

performance on single circuit, and investigate

any deviations from the predicted load.

December 2011 Contracts

Manager/Technical

Support Team

Technical

Support


Diageo Ireland






7.5 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.

Feed spill air from the nitrogen

plant compressors into the central

air system to reduce electrical

consumption on the central air

compressors.

Continue to carry out compressed air leakage

survey twice yearly and repair leaks in the

system.

December 2011 Contracts Manager/RWE

Utilities

Technical

Support


Diageo Ireland


Objective 8.0 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.


8.1 To inform all employees regarding

the requirements of the IPPC

licence for the Brewery.

Develop an e-learning environmental awareness

training package for roll out in Q3 2011 to

support the implementation of the Environmental

training programme level 1.

Roll out the training to new recruits, contractors

on site, logistics and Demand, and provide

refresher training as necessary.

June 2011 Training

Manager/Environmental

Manager

Overall site

8.2 To ensure that all employees and

contractors remain fully aware of

their obligations regarding waste

handling on site.

Continue awareness programmes through:

The GreenIQ team

Face-to face meetings with Contractors

Ongoing Facilities

Manager/Environmental

Manager

Overall site


Diageo Ireland


4 LICENCE-SPECIFIC REPORTS

This section summarises the results from the Licence Specific Reports completed during

2010.

4.1 Noise

4.1.1 Noise Survey

The annual noise survey was carried out in December 2010 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 9th

December and the night-time readings were taken on 9th

and 10th

December.

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 69 63 ND Note 2

66 55 ND Note 2

2 Bonham St. / Watling St. 58 53 <53 55 50 <50

3 Watling St. 75 53 53 56 49 49

4 School St./Taylor‟s Lane 64 51 ND Note 2

57 45 ND Note 2

5 Marrowbone Lane 54 49 <49 49 44 44

6 Bond St. 66 56 ND Note 2

55 44 <44

7 Echlin St. 65 57 ND Note 2

59 51 <51

8 Inside boundary at Watling St. 60 58 58 60 58 58

9 Inside boundary at Presbytery 69 61 61 Note 3

60 58 58 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 2010 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 1, 4,

5 and 6, but that is was exceeded at locations 2, 3 and 7. There were no tonal or impulsive

components to the noise measured at any of the Noise Sensitive Locations.


Diageo Ireland


A comparison of the night-time specific noise levels from 2001 to 2010 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

Sp

ecif

ic N

ois

e L

evel

(dB

(A))

Night-time Specific Noise Level (2001 to 2010)

2001

2002

2003

2004

2005

2006

2007

2008

2009

2010

4.1.2 Noise Reduction Programme

During 2010, two areas were identified for acoustic screening to further reduce the noise

impact from the site. The two areas were:

The extract fan at first floor level of the roasthouse building.

The external equipment at the northwest corner of GFE1 (the „blow-down pot‟).

The screening in these areas was completed during 2010 and the actions taken to reduce the

noise arising from these areas were identified and implemented.

As part of the Brewery‟s continuous Noise Reduction Programme, the following areas of the

Brewery will be targeted for noise assessment and, where identified, noise reduction during

2011:

A detailed noise survey in the Spent Grain Yard, to identify the key areas and

equipment causing noise in the area.

Noise modelling in the logistics yard on the lower level to identify the areas for noise

reduction/improvement.


Diageo Ireland


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.

In 2010, the bund integrity testing programme was reviewed and updated. The next round of

testing will commence in 2011.

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. Phase 2 of

the programme was developed during 2010, which included a CCTV survey and completion

of additional remedial works identified during Phase 1. Approximately 70% of the remedial

work was completed during 2010; the remainder is scheduled for completion during 2011 as

production areas become available to gain access to the drains in these areas.

The report on the remediation works completed under Phase 2 will be completed during

2011. The CCTV survey under Phase 3 of the programme will take place during the second

quarter of 2011.


Diageo Ireland


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 June and November 2010.

During the June 2010 monitoring round, elevated pH, temperature and conductivity were

recorded at MW8 and was notified to the Agency as outlined in Table 23. Additional

monitoring was undertaken at this location and an investigation and remediation programme

was initiated, which will continue during 2011.

The conclusions from the latest monitoring round (November 2010) are set out below (from

OGE Report No. 0411002).

The results from the heavy metal sampling indicate an improvement over June 2010.

The elevated levels of Mineral Oils and DROs from MW1 are anomalous.

Overall, the PAH concentrations are reducing.

The remedial works on the well heads appears to have addressed the issue of surface

runoff potentially contaminating the sample point.

MW8 continues to be the subject of a separate investigation.

In OGE‟s opinion the concentrations of many of the parameters are at or below

background levels. Continued monitoring during 2011 should establish the

background value ranges for many of the parameters. Seasonal effects may also

become apparent as the water table rises and falls in response to recharge.

*****


Diageo Ireland

Licence Register No. P0301-01 March 2011

Annex A

AER Returns Webform

and

European Pollutant Release and Transfer Register

Sheet : Facility ID Activities AER Returns Workbook 31/3/2011 9:21

| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 |

Guidance to completing the PRTR workbook

Version 1.1.11REFERENCE YEAR 2010

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

7.3.1

Brewing (including cider and perry production) in installations where the production capacity exceeds 25 million litres per year, not included in paragraph 7.8.

7.3.1

Brewing (including cider and perry production) in installations where the production capacity exceeds 25 million litres per year, not included in paragraph 7.8.

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

Country IrelandCoordinates of Location -6.28683 53.3427

AER Returns Workbook

| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | Page 1 of 2

Coordinates of Location 6.28683 53.3427River Basin District IEEA

NACE Code 1105Main Economic Activity Manufacture of beer

AER Returns Contact Name Fiona McLooneAER Returns Contact Email Address [email protected]

AER Returns Contact Position Environmental ManagerAER Returns Contact Telephone Number 01-4714798/086 3880533MOB

AER Returns Contact Mobile Phone NumberAER Returns Contact Fax Number 0

Production Volume 0.0Production Volume Units

Number of Installations 0Number of Operating Hours in Year 0

Number of Employees 0User Feedback/Comments

Web Address

2. PRTR CLASS ACTIVITIESActivity Number Activity Name50.1 General8(b)(ii) Vegetable raw materials

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 Workbook 31/3/2011 9:21

Is the reduction scheme compliance route being used ?

| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | Page 2 of 2| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | Page 2 of 2

Sheet : Releases to Air AER Returns Workbook 31/3/2011 9:22

4.1 RELEASES TO AIR Link to previous years emissions data | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | 31/03/2011 09:228 11 19 19 27 28 6 13 6 6 6 10 9

SECTION A : SECTOR SPECIFIC PRTR POLLUTANTSPlease enter all quantities in this section in KGs

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 analyse 15312.0 8470.0 33894.0 0.0 15.0 1789.0 1738.0 0.0 61218.0 0.0 0.003 Carbon dioxide (CO2) C ETS 25235302.0 5736702.0 24285886.0 0.0 37111.0 1001169.0 1001169.0 9957466.0 77566271.0 0.0 10311466.006 Ammonia (NH3) E ESTIMATE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 640.0 0.0 640.004 Hydro-fluorocarbons (HFCs) E ESTIMATE 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 30.0 0.0 30.0

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

SECTION B : REMAINING PRTR POLLUTANTSPlease enter all quantities in this section in KGs

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/Year14 Hydrochlorofluorocarbons (HCFCs) E ESTIMATE 0.0 5.0 0.0 5.0


SECTION C : REMAINING POLLUTANT EMISSIONS (As required in your Licence)Please enter all quantities in this section in KGs

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 1489.0 876.0 0.0 0.0 0.0 2779.9 0.0 414.9

244 Total Particulates M OTH Method based on ISO 9096 0.0 0.0 631.0 196.2 101.4 928.6 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 per sit

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

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:

Method Used

Method Used

RELEASES TO AIRPOLLUTANT METHOD

Method Used

POLLUTANT

RELEASES TO AIR

RELEASES TO AIRMETHOD

POLLUTANT METHOD

| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | Page 1 of 1| PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | Page 1 of 1

Sheet : Releases to Waters AER Returns Workbook 31/3/2011 9:22

4.2 RELEASES TO WATERS Link to previous years emissions data | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | 31/03/2011 09:228 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 thPlease enter all quantities in this section in KGs

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 B : REMAINING PRTR POLLUTANTSPlease enter all quantities in this section in KGs

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)Please enter all quantities in this section in KGs

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 Workbook 31/3/2011 9:23

4.3 RELEASES TO WASTEWATER OR SEWER Link to previous years emissions data | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Re 31/03/2011 09:238 13 21 26 6 8 6 8

SECTION A : PRTR POLLUTANTSPlease enter all quantities in this section in KGs

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) 31.06 4.8 0.2 36.06 0.0 0.0

20 Copper and compounds (as Cu) M CRM

3rd Party UKAS accredited laboratory method (TM 152D by ICPMS) 21.17 2.73 0.04 23.94 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) 24000.0 658.9 3.81 24662.71 0.0 0.0

13 Total phosphorus M CRM


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

3rd Party UKAS accredited laboraotry method (TM 107D using Dr Lange Kit) 1293851.0 1871.7 97.0 1295819.7 0.0 0.0

24 Zinc and compounds (as Zn) M CRM



SECTION B : REMAINING POLLUTANT EMISSIONS (as required in your Licence)Please enter all quantities in this section in KGs

QUANTITY

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

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

Method Used

POLLUTANT METHOD

POLLUTANT METHOD

Link to previous years emissions data Page 1 of 2

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



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) 2626691.0 2615.0 24.0 2629330.0 0.0 0.0

306 COD M CRM

3rd Party UKAS accredited laboraotry method (TM 107D using Dr Lange Kit) 3881552.0 5615.0 291.0 3887458.0 0.0 0.0

308 Detergents (as MBAS) M OTH 3rd Party laboraotry method 685.0 1.9 0.9 687.8 0.0 0.0

314 Fats, Oils and Greases M OTH 3rd Party laboraotry method 10021.0 121.0 1.9 10143.9 0.0 0.0

343 Sulphate M CRM

3rd Party UKAS accredited laboratory method (TM 098D by Kone Analyser) 142550.0 3640.0 37.0 146227.0 0.0 0.0

Method UsedPOLLUTANT METHOD

Link to previous years emissions data Page 1 of 2

Sheet : Releases to Wastewater or Sewer AER Returns Workbook 31/3/2011 9:23

240 Suspended Solids M CRM

3rd Party UKAS accredited laboratory method (TM 022D by Gravimetric Determination based on BS 2690:Part 120:1981) 617445.0 1879.0 97.0 619421.0 0.0 0.0


Link to previous years emissions data Page 2 of 2Link to previous years emissions data Page 2 of 2

Sheet : Releases to Land AER Returns Workbook 31/3/2011 9:23

4.4 RELEASES TO LAND Link to previous years emissions data | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | 31/03/2011 09:238 8 16 16 6 6 6 6

SECTION A : PRTR POLLUTANTSPlease enter all quantities in this section in KGs

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)Please enter all quantities in this section in KGs

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 Workbook 31/3/2011 9:23

5. ONSITE TREATMENT & OFFSITE TRANSFERS OF WASTE | PRTR# : P0301 | Facility Name : Diageo Ireland | Filename : P0301_2010.xls | Return Year : 2010 | 31/03/2011 09:235 40 Please enter all quantities on this sheet in Tonnes 3

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 03 01 No 9.26 Kieselguhr R3 M Weighed Offsite in IrelandOrmonde Organics,W0237-01

Killowen ,Portlaw ,County Waterford.,.,Ireland

Within the Country 02 07 05 No 330.6 Effluent plant screenings R3 M Weighed Offsite in IrelandOrmonde Organics,W0237-01

Killowen ,Portlaw ,County Waterford.,.,Ireland

Within the Country 02 07 99 No 947.0 Barley screenings & dust R10 M Weighed Offsite in IrelandBord Na Móna Kilberry Compost Facility,W0198-01 Kilberry,Co. Kildare,.,.,Ireland

Within the Country 02 07 99 No 11505.0 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 66828.2 Spent grains R11 M Weighed Offsite in IrelandKW Forage Systems Ltd. (animal feed),N/A

Ballymountain ,Waterford ,.,.,Ireland

Within the Country 02 07 99 No 10207.0 Surplus yeast R11 M Weighed Offsite in IrelandKW Forage Systems Ltd. (animal feed),N/A

Ballymountain ,Waterford ,.,.,Ireland

Within the Country 15 01 02 No 2.1 plastic packaging R3 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 03 No 48.0 wooden packaging R3 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 15 01 04 No 27.2 Waste kegs R4 M Weighed Offsite in Ireland P. Carney Ltd.,P0402-01Crossakiel ,Kells ,Co. Meath.,.,Ireland

Within the Country 15 02 03 No 4.9 Spent carbon R3 M Weighed Offsite in IrelandWaddock Composting Ltd.,WP 01/02 WP 11/04

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

Within the Country 16 01 03 No 6.99 Waste tyres R3 M Weighed Offsite in Ireland Crumb Rubber,WP 2007/01Mooretown,Dromiskin,Dundalk,Co. Louth,Ireland

Greyhound Recycling andKnockmitten Lane ,Western Industrial Estate Dublin

Method Used

Within the Country 17 01 07 No 82.0 Construction & demolition waste R5 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01

Industrial Estate ,Dublin 12,County Dublin,Ireland

Within the Country 17 04 07 No 51.0 Scrap metal R4 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 01 No 24.6 Cardboard R3 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 01 No 21.8 Paper R3 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 02 No 47.3 Waste glass R5 M Weighed Offsite in Ireland Quinn Glass Ltd.,N/ADerrylin ,Co. Fermanagh.,.,.,Ireland

Within the Country 20 01 08 No 210.6 General waste R3 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 08 No 177.2 General waste R1 M Weighed Offsite in IrelandGreyhound Recycling and Recovery Ltd.,W0095-01


Within the Country 20 01 25 No 2.31 Waste catering oil R9 M Weighed Offsite in Ireland Frylite Ltd.,LN/08/11

298 Melmount Road ,Strabane ,.,Co. Tyrone,United Kingdom




Year)



Recover/Disposer










Method Used

To Other Countries 06 04 04 Yes 0.004 Lab smalls D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01

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

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 07 01 03 Yes 14.0 Waste dichloromethane D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




To Other Countries 08 03 12 Yes 0.1 Waste ink cartridges D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




Within the Country 13 02 08 Yes 2.0 Waste oil 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

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

Within the Country 13 05 07 Yes 15.3 Interceptor waste D6 M Volume Calculation Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland



Within the Country 13 07 03 Yes 0.2 Waste diesel R9 M Weighed Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland



Within the Country 13 08 02 Yes 1.0 Oily waste R9 M Weighed Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland



Indaver

To Other Countries 14 06 02 Yes 0.07 Iso-octane waste 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 14 06 03 Yes 0.44 Laboratory waste D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01




Within the Country 15 01 10 Yes 0.1 Empty plastic containers R3 M Weighed Offsite in Ireland Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

Leinster Environmentals Ltd.,WP008-06,Clermont Business Park ,Haggardstown ,Dundalk ,Co. Louth.,Ireland

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

To Other Countries 15 02 02 Yes 5.13 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 15 02 02 Yes 0.09 Used spill kits D10 M Weighed AbroadIndaver Ireland Ltd.,W0036-01







Year)



Recover/Disposer










Method Used

To Other Countries 16 05 04 Yes 0.36 Waste aerosol cans R4 M Weighed Abroad Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

REMONDIS Industrie Service GmbH & Co. KG,***************,Niederlassung Krautheim,Austraße 5,74238 Krautheim,.,Germany

Niederlassung Krautheim,Austraße 5,74238 Krautheim,.,Germany

To Other Countries 16 06 01 Yes 0.1 Used batteries R4 M Weighed Abroad Enva Ireland Ltd.,W0184-01Clonminam Industrial Estate ,Portlaoise ,.,.,Ireland

Campine NV,********************,Nijverheidsstraat 2 ,B - 2340 ,Beerse ,.,Belgium

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

To Other Countries 16 07 08 Yes 1.7 Oil contaminated wastes R1 M Volume Calculation 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 18 01 03 Yes 0.03 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/Im Linen.,.,.,.,Germany

RZR Herten/Im Linen.,.,.,.,Germany

Within the Country 18 01 03 Yes 1.05 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


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


Documents

Diageo St. James’s Gate Brewery · 2014-12-16 · In July 2010, kegging of all stout ales and lagers in the Island of Ireland Diageo portfolio was transferred from the St. Francis