22
Systeemisellä ymmärryksellä kestävyyttä ja liiketoimintaa yhdyskuntajätteiden käsittelyyn Kiinassa ja Brasiliassa 16.1.2017 Mika Horttanainen Lappeenranta University of technology

ARVI Systeemisellä ymmärryksellä kestävyyttä ja liiketoimintaa yhdyskuntajätteiden käsittelyyn Kiinassa ja Brasiliassa, Horttanainen

Embed Size (px)

Citation preview

Systeemisellä ymmärryksellä kestävyyttä ja liiketoimintaa yhdyskuntajätteidenkäsittelyyn Kiinassa ja Brasiliassa

16.1.2017Mika HorttanainenLappeenranta University of technology

Objectives and Implementation

• The overall objective of the MSW theme was • to increase understanding of the municipal solid waste

management systems (and nitrogen recovery from sludge),• thus increasing the value of the recovery and • facilitating sustainability • in different business environments.

• Implementation• Systems analysis in different operation environments

• South Karelia, Hangzhou, Sao Paulo• Environmental LCA as the main method• Organization of MSW management and money flows• Co-operation with business analysis

Systems analysis for MSW management of Hangzhou city in

ChinaJouni HavukainenMiia LiikanenMika HorttanainenLappeenranta University of Technology,Sustainability Science

Systems analysis for MSW management of Hangzhou city in China

Objectives• Analyzing the current MSW management system of Hangzhou city• Analyzing the possibilities to improve environmental sustainability with

WtE solutions including Finnish technology– SRF production – Avoiding coal use

Environmental impact analysis with LCA methodProducing SRF from mixed MSWGHG emissions and emissions causing acidification and eutrophicationComparing to current mixed MSW co-combustion with coal

Study region: Hangzhou city• Inhabitants: 7 million• Capital city of Zhejiang province• Stark increase in MSW generation

0,000,501,001,502,002,503,003,504,004,50

2000 2005 2010 2015

MSWPopulationGDP

MSW per person− 2003: 142 kg/inhab./a− 2013: 432 kg/inhab./a

79 % 72 % 60 % 58 % 58 % 56 % 54 % 51 % 51 % 51 % 58 %21 % 28 %40 %

42 %43 %

44 % 47 % 49 % 49 %49 %

42 %

913 952

13801584

18362139

2347 24572610

28443087

0

500

1000

1500

2000

2500

3000

3500

2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013

kt/a

Landfill Incineration Total

MSW management system: Mass flows

MIXED WASTE

SOURCE SEPARATEDFOOD WASTE

SOURCE SEPARATEDHAZARDOUS WASTE

3 086 kt/a

73 kt/a

INCINERATION PLANT Lvneng

INCINERATION PLANT Qiaosi

INCINERATION PLANT Yuhang

INCINERATION PLANT Xiaosha

PROCESSING FOR PAPER

PROCESSING FOR GLASS

PROCESSING FOR METAL

PROCESSING FOR PLASTIC

204 kt/a

411 kt/a

256 kt/a

416 kt/a

LANDFILL

LANDFILL Liugongduan

HAZARDOUS WASTE LANDFILL

1 432 kt/a

366 kt/a

COAL? Kt/a

HOUSEHOLDS ETC. WASTE

GENERATION

HANGZHOU ENVIRONMENTAL

GROUP

INCINERATION PLANT

6 t/a

WASTE PICKERS

?

RECYCLING CENTER

ANAEROBIC DIGESTION GAS ENGINE

GAS ENGINE

TIANZILING WASTE DISPOSAL CENTER

COAL8.1 kt/a

COAL29 kt/a

MSW management: Money flows

MIXED WASTE

SOURCE SEPARATEDFOOD WASTE

SOURCE SEPARATEDHAZARDOUS WASTE

INCINERATION PLANT

LANDFILL

HAZARDOUS WASTE LANDFILL

LANDFILL

COALCOMPANY

HOUSEHOLDS ETC. WASTE

GENERATION

COLLECTION BY:HANGZHOU

ENVIRONMENTAL GROUP

INCINERATION PLANT

50 CNY/household

RECYCLING CENTERMANUAL

SEPARATION?

GOVERNMENT

TAX

SUPPORT GATE FEE 73-140 CNY/t PRIZE 570 CNY/t

GATE FEE MIXED WASTE 82 CNY/t

MONEY

MATERIAL USER

MONEY

ELECTRICITYGRID

PRIZE 0.65 CNY/kWh

MANAGEMENT:HANGZHOU MSW

DISPOSAL SUPERVISION

CENTER

SUPPORT

GAS ENGINE

ANAEROBIC DIGESTION GAS ENGINE

GAS ENGINE

TIANZILING WASTE DISPOSAL CENTER

GATE FEE FOOD WASTE? ELECTRICITYGRID

PRIZE ?

WASTE PICKERS

MSW management: Organizing

HANGZHOU JINJIANG GREEN ENERGY Co., Ltd

MIXED WASTE

SOURCE SEPARATEDFOOD WASTE

SOURCE SEPARATEDHAZARDOUS WASTE

INCINERATION PLANT Lvneng

INCINERATION PLANT Qiaosi

INCINERATION PLANT Yuhang

INCINERATION PLANT Xiaosha

PROCESSING FOR PAPER

PROCESSING FOR GLASS

PROCESSING FOR METAL

PROCESSING FOR PLASTIC

LANDFILL Tianziling

LANDFILL Liugongduan

HAZARDOUS WASTE LANDFILL

LANDFILL

HOUSEHOLDS ETC. WASTE

GENERATION

COLLECTION BY:HANGZHOU

ENVIRONMENTAL GROUP Co., Ltd

INCINERATION PLANT

WASTE PICKERS

RECYCLING CENTER

ANAEROBIC DIGESTION

MANAGEMENT:HANGZHOU MSW

DISPOSAL SUPERVISION

CENTER

HANGZHOU ENVIRONMENTAL GROUP Co., Ltd- TIANZILING WASTE DISPOSAL CENTER

HANGZHOU GREEN ENERGY ENVIRONMENTAL

PROTECTION POWER Co., Ltd.

HANGZHOU MUNICIPAL

ENVIRONMENTAL PROTECTION

BUREAU

EMISSION CONTROL

HAZARDOUS WASTEMANAGEMENT

Hangzhou Hazardous Solid Waste Management Center

Hangzhou Urban Management Commission

Life cycle assessment Hangzhou city MSW management system

Functional unit is the MSW mass produced in 2013, i.e. 3 100 kt.

Compared scenarios Scenario 0

• Present incineration and landfilling Scenario 1

• SRF production and incineration in existing incineration plants Scenario 2

• SRF production and incineration in new CFB plants

Scenarios 1 and 2 include sub-scenarios with different biodegradable reject treatment

1. Landfilling2. Biodrying and incineration3. Anaerobic digestion, composting of digestate4. Ethanol production, anaerobic digestion of stillage, composting of digestate

Hangzhou city MSW management LCA

MIXED MSW

INCINERATION PLANT Lvneng

INCINERATION

LANDFILL

MECHANICAL TREATMENT

HANGZHOU ENVIRONMENTAL

GROUP

ANAEROBIC DIGESTION

TIANZILING LANDFILL

SOURCE SEPARATED FOOD WASTE

HOUSEHOLDS ETC. WASTE

GENERATION

BIODRYING

METAL RECYCLING

SRF

Reject

ETHANOL PRODUCTION

ANAEORBIC DIGESTION

PILE COMPOSTING

ANAEORBIC DIGESTION

PILE COMPOSTING

Options for biodegradable waste treatment Option 1Option 2Option 3Option 4

Organic reject

Results: Global warming potential (GWP)

1 810 1 798 1 694

1 412 1 4151 620

1 4731 218 1 220

-1 000

-500

0

500

1 000

1 500

2 000

2 500

kt C

O2-

eq./a

Landfill emissions

Organic treatment emissions

RDF plant

Waste incineration

Metal recycling

Landfill gas motor el disp.

Organic treatment landfill gasel disp.Organic treatment gasolinedisp.Organic treatment stillage ADel disp.Organic treatment AD el disp.

Waste incineration el disp.

Total

Old plants SRF

New plants SRF

Results: Eutrophication potential (EP)

-1 500-1 200 -1 000

-1 800-1 500

-2 200 -2 100

-2 900-2 600

-5 000

-4 000

-3 000

-2 000

-1 000

0

1 000

2 000

t SO

2-eq

./aLandfill emissions

Organic treatment emissions

RDF plant

Waste incineration

Metal recycling

Landfill gas motor el disp.

Organic treatment landfill gas eldisp.Organic treatment gasolinedisp.Organic treatment stillage AD eldisp.

Old plants SRF

New plants SRF

Results: Acidification potential (AP)

-1531 31

-69-40

-95 -99

-200-170

-600

-500

-400

-300

-200

-100

0

100

200

300

400

t PO

4--e

q./a

Landfill emissions

Organic treatment emissions

RDF plant

Incineration

Metal recycling

Landfill gas motor el disp.

Organic treatment landfillgas el disp.Organic treatment gasolinedisp.Organic treatment stillageAD el disp.Organic treatment AD eldisp.Waste incineration el disp.

Old plants SRF

New plants SRF

Conclusions Main problem: lack of source separation

• High food waste share High moisture content low LHV – Mechanical separation of recyclables difficult

• Educating citizens is necessary

The environmental performance would be improved a lot if the incineration plants could recover also heat

• Placing near the industry which uses steam

SRF production could improve significantly the environmental performance of Chinese energy recovery of MSW Recovery of the reject from SRF production is important

Steps towards sustainable municipal solid waste management

in São Paulo, BrazilMiia LiikanenJouni HavukainenMika HorttanainenLappeenranta University of TechnologySustainability Science

15

MSW management in São Paulo

• Brazil is the fourth largest MSW producer in the world• São Paulo is the largest city in Brazil• No proper source separation of MSW• Landfilling is predominant treatment method for MSW • 2 sanitary landfills, 3 waste transfer stations and 2

mechanical sorting plants in the city• MSW management is contracted out to two companies,

Ecourbis and Loga• 20-year contracts

• São Paulo plans to develop MSW management system ─ Need to diminish the volume of MSW landfilled─ Separate collection for organic waste in future─ Incineration opposed

16

17

• CTL landfill operated by Ecourbis• 7.5 kt of MSW is landfilled per day

• Essencis landfill operated by Loga

• 8-9 kt of MSW is landfilled per day

LCA of MSW management in São Paulo

• Functional unit: the treatment of domestic MSW generated in the city in 2015, i.e. 3.8 million tonnes

• Impact categories: global warming potential (GWP), acidification potential (AP) and eutrophication potential (EP)

18

MSW generation

Organic wasteComposting

plant

AD plant

Landfill

MBT plant

Mixed MSW

Organic waste

Organic reject

Inert reject

LFG

Home-composting

Nutrient substitution

(N, P, K)

Metal substitution

RDF

CH4

LFG combustion plant

Biogas combustion plant

Waste incineration plant

Electricity substitution

Al & steel

Al & steel

BiowasteN, P, K

N, P, K

Assessed treatment methods for MSW

Results

• Scenario 2.2 (i.e. home-composting + separate collection of organic waste (AD)) had the lowest environmental impact in all impact categories

• MBT and incineration of mixed MSW did not decrease the environmental impacts of MSW management• In AP and EP impact categories, they even increased the emissions notably• However, it should be noticed that MBT and incineration decreases significantly the volume of

MSW landfilled, i.e. they have other environmental benefits

19

LCA of MSW management in São PauloConclusions

• Home-composting and Separate collection of organic waste beneficial from these impact categories point of view

• Electricity substitution is very important factor• Most of the electricity in Brazil produced with Hydropower• LFG collected and utilized for electricity production Electricity generation from incineration not effective for

environmental impact reduction (if average grid mix substituted)

• Waste to energy could be used for other purpose• Cement kiln fuel• Replacing coal

Electricity production in Brazil

Conclusions from different operation environments

• General MSW management situation important• Incineration increase + coal co-incineration in China• No proper source separation in most of the developing countries

• Political decisions important• Almost categorical incineration ban in Brazil• SRF/RDF proposed for emission reduction in Chinese standardization

Scenario selection for the local needs

• Energy infrastructure important• Substituted energy• Possibility to recover heat (integration with process industry)

Scenarios can be re-formulated after first results and conclusions

Selling arguments for a MSW technology or service can be very different Correct system knowledge and sustainability knowledge is valuable

Thank you for attention!Contacts:Mika Horttanainen ([email protected]) Jouni Havukainen ([email protected])Miia Liikanen ([email protected] )Ivan Deviatkin ([email protected])

Lappeenranta University of TechnologySustainability Science