GSK Experiences in Life Cycle Inventory and...

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GSK Experiences in Life Cycle Inventory and Assessment Conchita Jiménez-González and David J C Constable* Operational Sustainability Corporate Environment, Health, Safety and Sustainability * Now Lockheed Martin Green Chemistry and Green Engineering Conference Washington, DC. June 2009

Transcript of GSK Experiences in Life Cycle Inventory and...

Page 1: GSK Experiences in Life Cycle Inventory and Assessmentacs.confex.com/recording/acs/green09/pdf/free/4db... · GSK Experiences in Life Cycle Inventory and Assessment Conchita Jiménez-González

GSK Experiences in Life Cycle Inventory and AssessmentConchita Jiménez-González and David J C Constable*Operational Sustainability Corporate Environment, Health, Safety and Sustainability* Now Lockheed Martin

Green Chemistry and Green Engineering ConferenceWashington, DC. June 2009

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OutlineAbout GSKLCI/A in GSK:– CtG LCA of an API– LCI/A in the GSK Sustainability Tools

Solvent Selection GuideFLASCGreen Technology GuideWRAP

– Other applicationsFuture Work on LCI/A at GSK

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GSK EHS Plan for Excellence

Sustainabilityin Environment, Health and SafetyPlan for Excellence Engages through

collaborationEmbraces GSK principlesAligns with the GSK key business driversSets strategic objectivesSets EHS themes year by year to sharpen focusBuilds our momentum

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LCI/A Program in GSK

MATERIALS

PRODUCTION

TRANSPORT

USEEND OF LIFE

MATERIALS

PRODUCTION

TRANSPORT

USEEND OF LIFE

MATERIALS

PRODUCTION

TRANSPORT

USEEND OF LIFE

MATERIALS

PRODUCTION

TRANSPORT

USEEND OF LIFE

Waste Treatment

Solvents

Respiratory Devices

APIs

Packaging

Technologies

Sustainable by DesignSustainability Tools:

FLASCWRAPSSGGTG

Bioprocesses

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Cradle-to-gate LCA of a GSK APIFunctional Unit: 1 kg of APIGSK process studied has 7 stages26 materials directly used in GSK processTo make these 26 materials requires the manufacture of a total of 119 materials (125 including GSK’s intermediates)Cradle-to-Gate Analysis involved:– Process:

MaterialsEnergyTransportation

– Treatment:wastewater treatment,incineration, and Solid waste disposal.

Source: Jimenez-Gonzalez, Curzons, Constable, Cunningham, 2004. Int J LCA 9(2) 114-121Source: Jimenez-Gonzalez, Curzons, Constable, Cunningham, 2004. Int J LCA 9(2) 114-121

MATERIALS

PRODUCTION

TRANSPORT

USEEND OF LIFE

MATERIALS

PRODUCTION

TRANSPORT

USEEND OF LIFE

MATERIALS

PRODUCTION

TRANSPORT

USEEND OF LIFE

MATERIALS

PRODUCTION

TRANSPORT

USEEND OF LIFE

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WASTE TREATMENT ANDENERGY MODULES

Total Cradle-to-Gate Emissions = Materials + Treatment + Energy

H25 (g)

150 C

8 (l)

9 (l)Reactor, 150 C Co

lum

n,15

0 C

P-A

C1

C2

C3C4

C7

C8

S1S2

GSKprocess

GSK LCA METRICS

Factors to convertEmissions to Impacts

Materials required for a process, chemical trees with GSK-LCA metrics

Hydrochloric acid, HCl

Chlorine, Cl2Ethylene, C2H6

Water, H2O

Water, H2O

Sodium Chloride, NaCl

Naphtha Refinery

Salt Rock Petroleum Reserve

Hydrochloric acid, HCl

Chlorine, Cl2Ethylene, C2H6

Water, H2O

Water, H2O

Sodium Chloride, NaCl

Naphtha Refinery

Salt Rock Petroleum Reserve

Hydrochloric acid, HCl

Chlorine, Cl2Ethylene, C2H6

Water, H2O

Water, H2O

Sodium Chloride, NaCl

Naphtha Refinery

Salt Rock Petroleum Reserve

Hydrochloric acid, HCl

Chlorine, Cl2Ethylene, C2H6

Water, H2O

Water, H2O

Sodium Chloride, NaCl

Naphtha Refinery

Salt Rock Petroleum Reserve

Hydrochloric acid, HCl

Chlorine, Cl2Ethylene, C2H6

Water, H2O

Water, H2O

Sodium Chloride, NaCl

Naphtha Refinery

Salt Rock Petroleum Reserve

Hydrochloric acid, HCl

Chlorine, Cl2Ethylene, C2H6

Water, H2O

Water, H2O

Sodium Chloride, NaCl

Naphtha Refinery

Salt Rock Petroleum Reserve

Hydrochloric acid, HCl

Chlorine, Cl2Ethylene, C2H6

Water, H2O

Water, H2O

Sodium Chloride, NaCl

Naphtha Refinery

Salt Rock Petroleum Reserve

Methodology

Total Gate-to-Gate pre-treatment emissions=

Process + Energy emissions

UTILITY MODULES

Energy Emissions (kg/kg product)

Process Emissions (kg/kg product)

H25 (g)

150 C

8 (l)

9 (l)Reactor, 150 C Co

lum

n,15

0 C

P-A

C1

C2

C3C4

C7

C8

S1S2

Source: Jimenez-Gonzalez, Kim, Overcash, 2000. Int J LCA 5(3) 153-159Source: Jimenez-Gonzalez, Kim, Overcash, 2000. Int J LCA 5(3) 153-159

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LCA of API pre-treatment resultsCradle-to-gate pre-treatment contributions:

Solvents, Chemicals, Internal

0% 20% 40% 60% 80% 100%

Total cradle materials (kg)

Energy (MJ)

TOC (kg)

POCP (kg-et)

GHG (CO2-eq)

Acidification (SO2-eq)

Eutrophication (PO4-3-eq.)

Chemicals Solvents Internal

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Key Learnings of LCI/A of an API

Solvent use (excluding incineration) is the major contributor to: – Energy (ca. 75%)– Resource utilisation (about 80%)– Photochemical Ozone Creation Potential (ca. 70%)– Green House Gases (about 50%)– associated impacts when compared to GSK processes, transport

and manufacture of other raw materials.The energy required to incinerate solvent wastes not recovered is approximately equivalent to a total of: – 60% of the energy used to produce the API– 50% of the post-treatment Green House Gas emissions

WW treatment does not significantly increase overall life cycle profile.Transport contribution to overall impacts is low

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LCI/A in GSK’s Sustainability Tools

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Sustainability by DesignGSK Eco-Design Toolkit

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Wasterecoverability and recyclabilitydisposal issues (waste water treatment and incineration)VOC

Impact - fate and effects to air and water

Health -OEL, EU risk phrases and risk of exposure

Safety -compatibility, flammability, process risk, conductivity

Life Cycle - cradle to gate environmental impacts for manufacture

Source: Eco-Design ToolkitMethodology:

Curzons AD, Constable DJC, Cunningham VL. 1999 Clean Products and Processes 1:82-90 and Jiménez-González C, Curzons AD, Constable DJC, Cunningham VL. 2005 J. of Clean Tech. and Env..Pol 7:42-50,

Source: Eco-Design ToolkitMethodology:

Curzons AD, Constable DJC, Cunningham VL. 1999 Clean Products and Processes 1:82-90 and Jiménez-González C, Curzons AD, Constable DJC, Cunningham VL. 2005 J. of Clean Tech. and Env..Pol 7:42-50,

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The links contain the

information for each solvent

For example, clicking in

2-propanol we get...

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Streamlined LCI/A in GSK: FLASC™

Fast Lifecycle Assessment of Synthetic Chemistry

A simple to use web-based tool and methodology to determine and benchmark the relative sustainability of chemicals used in synthetic processes for API production

Based on the cradle-to-gate LCA impacts associated with the manufacture of chemicals used in a typical pharmaceutical process.

Source: Eco-Design Toolkit Methodology: Curzons, Jimenez-Gonzalez, Duncan, Constable, Cunningham, 2007, IJLCA, 12(4)272-280, Source: Eco-Design Toolkit Methodology: Curzons, Jimenez-Gonzalez, Duncan, Constable, Cunningham, 2007, IJLCA, 12(4)272-280,

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Streamlined LCI/A in GSK: FLASC™

FLASC = Fast Life cycle Assessment for Synthetic Chemistry

Used in GSK to:Evaluate greennessCompare routesIn R&D Green MetricsIn Manufacturability CriteriaProcess-Related Materials ReviewsIn CEO Award entries

Used in GSK to:Evaluate greennessCompare routesIn R&D Green MetricsIn Manufacturability CriteriaProcess-Related Materials ReviewsIn CEO Award entries

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Data generated

Measure of chemistry efficiency

Measure of resource efficiency

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Detailed Report

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What if Analysis

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FLASCTM by the Numbers

More than 500 FLASC assessments completed to date229 materials currently in FLASC db. – ~70 additional LCIs completed, to be added during 2008– For materials not in the database, average data is inserted

based on classification of the raw materials into 14 groups of chemicals having related LCI impact profiles

22 GSK benchmark processes used to developed FLASC methodology and score 10 screening questions to identify opportunities for process improvement are included5-to-1 Score (low is bad, high is good)2 sets of data required as input: route’s BOM (materials and masses) & API’s MW

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LCI/A in GSK’s Green Technology Comparisons

Source: Eco-Design ToolkitMethodology:

– Jimenez-Gonzalez, Constable, Curzons, Cunningham, 2002. Clean. Tech. Environ. Policy 4:44–53 and – Jiménez-González, Curzons, Constable, Overcash, Cunningham. 2001. Clean Prod and Proc 3:35-41

Source: Eco-Design ToolkitMethodology:

– Jimenez-Gonzalez, Constable, Curzons, Cunningham, 2002. Clean. Tech. Environ. Policy 4:44–53 and – Jiménez-González, Curzons, Constable, Overcash, Cunningham. 2001. Clean Prod and Proc 3:35-41

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For instance…

LCI/A comparison for:– recovery of THF– Dehydration of alcohols– Resolution of enantiomers– Concentration of mother liquors– And more…

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Green Packaging Guide - WRAP

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Other LCI/A Applications in GSK

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End-of-Life: Waste Treatment Modules

Source:Jimenez-Gonzalez, Overcash and Curzons, 2001, J. Chem. Technol. Biotechnol. 71:707-716Source:Jimenez-Gonzalez, Overcash and Curzons, 2001, J. Chem. Technol. Biotechnol. 71:707-716

SolventRecovery

IncineratorWWTP

Manufacturing Plant

Manufacturing Plant

LCA ImpactsEnergyGWPPOCPAcidificationEutrophication

LCA ImpactsEnergyGWPPOCPAcidificationEutrophicationSOLVENT

MANUFACTURING

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Example – THF Solvent Recovery vs Energy Recovery

Manufacturing PlantCase 1

Incinerator with 50%Energy Recovery

1,000 kg THF

~ 3,570 kg CO2-eq~ 3,570 kg CO2-eq

Approx Estimated Savings ~12,000 kg CO2-eq

Manufacturing PlantCase 2

1,000 kg THF

~ 1,060 kg CO2-eq~ 1,060 kg CO2-eq

Incineratorw/EnergyRecovery200 kg

Solvent Recovery

800 kg THF

~ 10,000 kg CO2-eq SAVINGS from manufacturing~ 10,000 kg CO2-eq SAVINGS from manufacturing

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Bio-processes, closing the cycle – A sustainable vision?

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Bio-Processes GSK Case Study –LCA of 7ACA

Chemical Process

Materials(FLASC)

Energy production

Waste treatment

API production, formulation, distribution and consumption

Enzymatic Process

Energy production

Waste treatment

Materials(FLASC)

7-ACA

7-ACA

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Comparing Chemical (C) and Enzymatic (E) Routes

Source:Henderson, Jimenez-Gonzalez, Preston, Constable, Woodley, 2008, Industrial Biotechnology 4(2):180-192Source:Henderson, Jimenez-Gonzalez, Preston, Constable, Woodley, 2008, Industrial Biotechnology 4(2):180-192

Energy

Mass

GWP POCP

Acidification Eutrophication

E

C

E

C

E

C

E

C

E

C

E

C

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LCA of Delivery Devices

MATERIALS PRODUCTION TRANSPORT USE END OF LIFE

It includes raw material extractionand transformation

It comprises theproduction andassembly process

It accounts for transport from suppliers and tomarkets

It includes Device use

It accounts fortreatment, Disposal and recycling

MATERIALS PRODUCTION TRANSPORT USE END OF LIFE

It includes raw material extractionand transformation

It comprises theproduction andassembly process

It accounts for transport from suppliers and tomarkets

It includes Device use

It accounts fortreatment, Disposal and recycling

Assessing the environmental life cycle impacts of products. Evaluate Devices for opportunities to reduce their environmental footprintGSK Pilot Program for Delivery Device Recycling

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LCA impacts applied to in GSK-CH’sMission and Targets

WaterPackaging SustainableIngredients

Our Environmental Sustainability Mission: Grow our business whilst continuously improving our environmental impact

WasteEnergy & Emissions

-25% packaging weight100% recyclable packs50% recycled content

Sustainable sourcing strategy for

major ingredients

-1% / year non-hazardous

solid waste

-20% Water Usage Ratio

-20%Energy usage &

Global Warming Potential

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The Road Ahead

Continue embedding LCI/A in evaluations and tools:– NCEs and Key products, – processes with fermentation and enzymation– End of life considerations

Enhance and Update our tools– Solvent Selection Guide– FLASC– Green Packaging Guide

Benchmark– With other Pharma (e.g. AZ)– Other industries Analysis

In the longer term need to incorporate – human health, – ecotoxicity, – principles of inherent safety, – and economics.

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Acknowledgements

Alan Curzons, GSK CEHSS, ret.Rebecca DeLeeuwe, GSK CEHSSGraham Geen, GSK R&DJohn Hayler, GSK R&DRichard Henderson, GSK CEHSSBen Holladay, GSK Corporate ITGiuseppe Lo Biundo, GSK R&D Jim McCann, GSK Corporate IT Teresa Oliveira, GSK R&DMark Rhodes, GSK CEHSSBrian Rohrback, Infometrix Tom Roper, GSK R&D Clare Ruddick, GSK R&D GSK’s Sustainable Processing TeamGSK’s staff in Corporate EHSS and Chemical Development

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Any Questions?

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Back up slides

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Sustainability by Design

If we want to make the biggest impacts to products, services and costs, we have to start from the ground up.

If we want to build sustainability into the design of products and services we have to think differently about the what and how of R&D.

Increasing demands and decreasing budgets are likely to mean greater reliance on easily accessible company-wide tools that provide early assessments and highlight sustainability issues.

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Key Deliverables of LCI/A of APIA generic ‘life cycle approach’ applicable to:– strategic decision making, – business processes and – other processes and tools

Generic learnings on life cycle and Pharmaceuticals

A documented Simplified methodology

A LCI/A component for the Solvent Selection Guide

FLASC - Fast Life cycle Assessment of Synthetic Chemistry

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LCA of API pre-treatment results

Cradle-to-Gate LCA paroxetine contributions

0% 20% 40% 60% 80% 100%

Total cradle materials (678.11 kg)

Energy (8,359.5 MJ)

TOC (14.8 kg)

POCP (3.96 kg-et)

GHG (979 CO2-eq)

Acidif ication (8.36 SO2-eq)

Eutrophication (2.75 PO4-3-eq.)

Process Energy Transport

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LCA of API post-treatment results

Cradle-to-Gate LCA paroxetine contributions (post-treatment)

-60% -40% -20% 0% 20% 40% 60% 80% 100%

Total cradle materials (799.46 kg)

Energy (13,084 MJ)

TOC (2.1 kg)

POCP (2.18 kg-et)

GHG (1,836 CO2-eq)

Acidification (9.08 SO2-eq)

Eutrophication (1.32 PO4-3-eq.)

Spent solvent (154 kg)

Process Energy Transport Treatment

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How FLASCTM was developedEight core impact categories established

Mass Energy POCP Eutro Acidif Oil use GHG TOC

Life Cycle based environmental data were first developed for materials (NCSU’s Modular Approach), then for processes to a large number of GSK’s APIs

This data set is used as a benchmark for assessing new processes using a comparative scoring process

Process Mass Energy POCP Acid Eutr Oil GHG TOC1 100 855 5 1 2 80 8 52 150 800 4 15 3 50 5 83 200 1500 9 11 1 125 12 12

Process Score 1 Score 2 Score 3 Score 4 Score 5 Score 6 Score 7NEW 4 4.1 1.9 4.5 3.9 4.1 3.8

Combined single ‘FLASCTM’ score is generated, corrected for COMPLEXITY of drug substance molecule

4.1

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Detailed Report (biggest contributors)

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Developing the LCA Dataset

Cradle-to-gate LCI in GSK’s guide

LCA using GSK’s metrics– Net mass of materials used (kg) – Energy required (MJ) – Greenhouse gas equivalents (GHG, kg of CO2-

equivalents) – Oil and natural gas depletion for materials

manufacture (kg) – Acidification potential (AP, kg of SO2 equivalents) – Eutrophication potential (EP, kg of (PO4)-3 equivalents) – Photochemical ozone creation potential (POCP, kg of

ethylene-equivalents) – Total organic carbon (TOC) load before waste

treatment

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Relationship between FLASCTM and MP

0.00

0.50

1.00

1.50

2.00

2.50

3.00

3.50

4.00

4.50

5.00

0.00 0.50 1.00 1.50 2.00 2.50 3.00 3.50

Mass Productivity (%)

FLASC score

Solvent acceptability score

•FLASC tracks MP very well for most processes (real value of measuring MP)

•Two key advantages of FLASC – it takes into account starting material and product complexity.

•Where SMs are complex FLASC takes this into account - this is why there are outliers.

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PCA for selected inorganic materials

Factor2

Factor1

Factor3

Sodium methoxide

Sodium nitriteMagnesium sulphateCalcium carbonate

Potassium hydroxide

LithalAluminium chloride

Lithium

Lithium carbonate

Ammonium fluoride

Lithium chloride

Sodium hydroxide

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FLASC rating

% Relative to the average

Comments.

5.0 12% 4.3 20% 4.0 25% For a FLASCTM score = 4, the total Life Cycle mass and

energy associated with the materials used is 25% of that associated with an average route.

3.8 30% 3.4 40% 3.1 50% 2.9 60% 2.7 70% 2.5 80% 2.4 90% 2.3 100% 25 GSK routes developed during 1990 to 2000 were assessed.

The average Life Cycle environmental impact was assigned a rating of 2.3.

2.1 110% 2.0 120% For a FLASCTM score = 2 the total Life Cycle mass and

energy use associated with the materials is 120% relative to the average route

1.9 130% 1.7 150% 1.4 200% 1.0 300% For a score = 1 the life cycle mass and energy associated with

the materials is 300% relative to the average route

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~ 1,380 kg CO2-eq~ 1,380 kg CO2-eq

Example 2 –Recovery, Segregation and Treatment

Manufacturing PlantCase 1

Incinerator withoutEnergy Recovery

500 kg DCM 500 kg MeOH/Water

(50:50)

SolventRecovery

Incineratorw/o ER

SolventRecovery

WWTP

Manufacturing PlantCase 2

500 kg DCM

500 kg MeOH/Water (50:50)

125 kg DCM

56 kg MeOH

25 kg MeOH 169 kg MeOH

375 kg DCM

~ 370 kg CO2-eq~ 370 kg CO2-eq

Approx Estimated Savings ~1,000 kg CO2-eq

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GSK’s R&D Green Metrics

Set of agreed green metrics for synthetic route development:FLASC ScoreSolvent ScoreMass ProductivityReaction Mass EfficiencyMass Intensity Number and mass of solventsMaterials of ConcernMass of waterMajor contributors to total mass

Calculated and communicated at every Pilot Plant CampaignProvides Benchmark of routes in same stage of developmentIncludes guidance and targets

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Process Related Materials Review

•A single file with the EHS information for a whole process•Provides EHS information and key issues for synthetic routes

•Captures an agreed set of green metrics, including FLASC & Solvent Score, MP, RME•Is produced at 3 milestones of product development.

•A single file with the EHS information for a whole process•Provides EHS information and key issues for synthetic routes

•Captures an agreed set of green metrics, including FLASC & Solvent Score, MP, RME•Is produced at 3 milestones of product development.

Gene-function-target

association

Target to tractable hit

Tractable hit to

candidatePre-clinical FTIH to

PoCPhase III

File & launch

Life cycle manage-

ment

Disease selection

Target family

selection

PoC to commit to Phase

III

Phase I Phase II Phase III

SecondPP campaign

SiteSourcing

ValidationBatches

•Preliminary measure of EHS/green chemistry performance.•Identifies and communicates issues and opportunities for more sustainable chemistry and technology

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GSK CEO’s EHS Excellence Awards

Promotes improvements in GSK’s use of human, environmental and economic resourcesRecognizes innovation, effective over the long-term, that can be shared within GSKThree categories– EHS Community

Partnership– Green Chemistry /

Technology– EHS Initiative (H&S)

•FLASC & Solvent Scores are common metrics used by the teams submitting Award entries in the Green Chemistry / Green Technology category

•FLASC & Solvent Scores are common metrics used by the teams submitting Award entries in the Green Chemistry / Green Technology category

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1.9

2.8

3.53.9

1.0

1.5

2.0

2.5

3.0

3.5

4.0

4.5

5.0

CS FTIH FTIH P C P C CP III Ph III

FLA

SC

ave

towards full scale

commercialisationPre-clinical

Measuring Progress: Development Portfolio

27% of the Life Cycle impact of the

average GSK process*

37% of the Life Cycle impact of the average GSK

process*

65% of the Life Cycle impact of the

average GSK process*

130% of the Life Cycle impact of the average GSK

process*

* The average performance of the benchmark routes (1990-2000) was assigned a FLASC score of 2.3* The average performance of the benchmark routes (1990-2000) was assigned a FLASC score of 2.3

The environmental life cycle impact of all new processes post-PoC is potentially much lower than

for current processes in manufacturing

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Results: Materials Impacts

Using GSK’s FLASC™ tool to compare the two routes