environmental assessment of closing flows and vegetables...

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PLUVISOST.CTM2010-17365 www.sostenipra.cat . LCA Environmental assessment of closing flows and vegetables production: from urban waste and with Roof Top Greenhouse Tolousse, June 2013 Roberto Quirós, Gara Villalba, Pere Muñoz, Xavier Font, Xavier Gabarrell, Joan Rieradevall

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PLUVISOST.CTM2010-17365 www.sostenipra.cat.

MSW generation for 2010 was 252 million tonnes in EU-27 (Eurostat,

2012).

Estimated organic content in MSW of 30-40%

Mineral fertilizers consumption was 18 million tonnes for 2010 (Eurostat,

2012)

Potential quality compost in EU is aprox. 35-40 million tonnes (131,000

tonnes N available).

Compost with good quality can be used as mineral fertilizer substitute.

INTRODUCTION

Tolousse, June 2013

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

RESEARCH OBJETIVE

The aim of this study is to demonstrate that closing the organic

matter cycle from vegetables to vegetables is better than landfilling.

This research assess the environmental and agricultural performance

of three fertilization treatments: industrial compost (IC), home

compost (HC), and mineral fertilizers (MF)

These compost were applied on open field cauliflower crops.

HOME COMPOST (HC) INDUSTRIAL COMPOST (HC) MINERAL FERTILIZER (MF)

Tolousse, June 2013

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

MATERIALS AND METHODS

IC1 IC2 IC3

HC1 HC2 HC3

M1 M2 M3

Experimental Design

Three blocks with three replicates

with about 150 m2 each

Horticultural Crop

Cauliflower

Brassica oleracea L. var.

botrytis

Soil

Typic Xerothent

Tolousse, June 2013

Location

Experimental Field Santa Susana, Barcelona

41°38′27′′N, 2°43′00′′E,

Period

Plantation: October 2011

Harvesting: February 2012

Period of cultivation:

122 days

Weather

Average temperature: 12 °C

Evapotranspiration: 955 mm

Rainfall: 618 mm

(values for the cultivation

period)

Atypical

weather

conditons

Mediterranean

weather

Atypical

weather

conditons

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

COMPOST APPLIED

Properties Units IC1

HC2

References

Moisture %, wb 17 50 30-40a

Organic matter %, db n.a3

75 ≥ 35a

pH (extract 1:5 w:v) - n.a 8.97 6.5-8b

Electrical conductivity mS · cm-1

(extract 1:5 w:v) 2.47 1.72 ≤6b

N-Kjeldhal %, db n.a 1.66 ≥2b

Dinamic respiration index mg O2 · g-1 OM h-1

0.89 0.43 1.0c

Salmonella (presence / absence in 25 g) n.a Absence Absencea

Escherichia coli (CUF / g) n.a <10 <10a

Heavy metals contenta

Spanish legislation

Metals Units IC HC Class A Class B Class C

Zn mg · kg-1

186 194 200 500 1,000

Cu mg · kg-1

51 50 70 300 400

Ni mg · kg-1

19 9 25 90 100

Cr mg · kg-1

13 13 70 250 300

Pb mg · kg-1

35 26 45 150 200

Cd mg · kg-1

0.3 0.2 0.7 2 3

Compost Class A

The compost

applied were

suitable to be

used as mineral

fertilizer

substitute

Compost stable:

DRI < 1 mg O2·g-1 ·OM· h-1

(European Comission for

Biowaste Management

2008)

COMPOST QUALITY

Tolousse, June 2013 aSpanish legislation: Royal Decree 824/2005

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

LCA METHODOLOGY

• Aim: assess the environmental and agricultural

performance of three fertilization treatments: IC,

HC, MF, applied in open field cauliflower

• Goal: compare the yield, quality and

environmental impacts of three fertilization

treatments.

• Functional unit (FU): total tons per hectare of

horticultural crops of cauliflower.

• CML 2001 methodology was used for impact

assessment.

• Seven categories were studied: ADP, AP, EP,

GWP, OLDP, POP and CED.

Tolousse, June 2013

ISO 14044

1

2

3

4

ADP: Abiotic Depletion Potential; AP: Acidification Potential; EP:

Eutrophication Potential; GWP: Global Warming Potential; OLDP: Ozone Layer

Depletion Potential; POP: Photochemical Oxidation and CED: Cumulative

Energy Demand

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

RESULTS

ADP AP EP GWP OLD POP CED ADP AP EP GWP OLD POP CED ADP AP EP GWP OLD POP CED

Cultivation management

Cultivation fertirrigation

Compost transport

Compost process

Collection organic waste

Mineral fertiliser transport

Mineral fertiliser production

INDUSTRIAL COMPOST HOME COMPOST MINERAL FERTILISERStages

• AP and EP: emissions of

the composting process

(NH3)

• Remainder categories: fuel

consumed in waste

collecting and compost

transportation

• ADP, AP, EP, OLP, CED:

secondary pipes (LDPE),

harvesting post-emissions .

• GWP and POP: emissions

of the compost process

(N2O and COV’s)

• All categories: secondary

pipes (LDPE), collection

crates, transport of mineral

fertilizers and nursery

IMPACT CONTRIBUTION PER STAGE

Tolousse, June 2013

MAIN CONTRIBUTORS

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

RESULTS

Total Impacts WITHOUT avoided burdens

Impactos totales CON cargas evitadas

Home compost shows

the best environmental

perfomance with the

lowest impacts in all

categories assessed

except in AP and EP.

a. Abiotic Depletion Potential b. Acidification Potential

c. Eutrophication Potential d. Global Warming Potential

d. Ozone Layer Depletion Potential e. Photochemical Oxidation

0.0E+00

2.0E+00

4.0E+00

6.0E+00

8.0E+00

1.0E+01

IC HC MF

kg S

b e

q

0.0E+00

2.0E+00

4.0E+00

6.0E+00

8.0E+00

1.0E+01

1.2E+01

1.4E+01

IC HC MF

kg S

O2

eq

-4.0E+00

-3.0E+00

-2.0E+00

-1.0E+00

0.0E+00

1.0E+00

2.0E+00

3.0E+00

4.0E+00

IC HC MFkg P

O4 e

q

-4.0E+02

-2.0E+02

0.0E+00

2.0E+02

4.0E+02

6.0E+02

8.0E+02

1.0E+03

1.2E+03

IC HC MF

kg C

O2

eq

0.0E+00

2.0E-05

4.0E-05

6.0E-05

8.0E-05

1.0E-04

1.2E-04

1.4E-04

1.6E-04

IC HC MF

kg C

FC

-11

eq

-5.0E-01

0.0E+00

5.0E-01

1.0E+00

1.5E+00

2.0E+00

2.5E+00

3.0E+00

3.5E+00

IC HC MF

kg C

2H

4eq

Total Impacts WITH avoided burdens

ENVIROMENTAL

IMPACT PER

FERTILIZATION

TREATMENT AND

CATEGORY

IC: Industrial compost

HC: Home compost

MF: Mineral fertilizer

Tolousse, June 2013

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

Results

• Fertilization treatment made with mineral fertilizer showed the higher yield

but Home Compost was the best in some quality parameters such as:

diameter and weight of fruit.

• Fertilization treatment made with Home Compost showed the best

environmental performance in all categories assessed expect in AP and

EP.

• Industrial compost was affected mainly by the collection of the organic

fraction and by the compost transportation from the facility to the crops

area.

• A good quality compost represents a sustainable alternative to treat the

organic waste from MSW, mainly because it can be used as substitute of

mineral fertilizers and it decreases the waste dumped in landfills (EU

Directive 1999/31/EC).

Tolousse, June 2013

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

CONCLUSION

Tolousse, June 2013

Waste

Vegetables Vegetables

Compost

To

2V IS A SUSTAINABLE USE OF ORGANIC MATTER FRACTION FROM HOUSEHOLD

Production and

application of

compost in crops

is a sustainable

way to treat the

organic matter

from MSW.

Good quality

compost can be

used as

substitute of

mineral fertilizer

and also to avoid

the dumping of

organic matter to

landfill.

PLUVISOST.CTM2010-17365 www.sostenipra.cat.

Thank you for your attention

Tolousse, June 2013