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
PLUVISOST.CTM2010-17365 www.sostenipra.cat.
LCA
Demonstration: from 2v
(vegetables to vegetables)
environmental assessment
Tolousse, June 2013
Roberto Quirós, Gara Villalba, Pere Muñoz, Xavier Font, Xavier Gabarrell, Joan Rieradevall
PLUVISOST.CTM2010-17365 www.sostenipra.cat.
1.Introduction
2.Methodology
3.Results
4.Conclusions
Index
Tolousse, June 2013
Landfill
Transport
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.
LCA: SYSTEM BOUNDARIES
HC
IC
MF
Collection Production Transport Application
Tolousse, June 2013
Experimental emissions
of: NH3, CH4, N2O and
VOC´s
NH3: Ammonia
CH4: Methane
N2O: Nitrous oxide
VOC’s: Volatile organic compounds
PLUVISOST.CTM2010-17365 www.sostenipra.cat.
RESULTS
Quality
parameter
Units Industrial
compost
Home
compost
Mineral
fertilizer
Yield tonnes · m-2 4.5 6.8 8.6
Diameter cm 13 16.5 15.9
Dry weight kg 1.13 1.37 1.34
Highest values
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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
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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
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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