Towards a biomass matrix for fuels and chemicals: How PSE can … · Towards a biomass matrix for...
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Towards a biomass matrix for fuels and
chemicals:
How PSE can help bridging the gap for the low
carbon economy?
Roberto de Campos Giordano
Andrew Milli Elias
Felipe Fernando Furlan
Simone de Carvalho Miyoshi Chemical Engineering Graduate Program
Federal University of São Carlos (PPGEQ-UFSCar)
PPGEQ
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Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem
Services (IPBES)
Nature’s Dangerous Decline ‘Unprecedented’ Species Extinction Rates
‘Accelerating’
1,000,000 species threatened with extinction www.ipbes.net/news/Media-Release-Global-Assessment
May, 2019
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SUSTAINABLE ECONOMY
ENERGY MATERIALS
Sustainable economy will rely on a
multiplicity of energy sources, with
biomass playing an important role.
6 Technology Roadmap: Delivering Sustainable Bioenergy. IEA, 2017 https://webstore.iea.org/technology-roadmap-delivering-sustainable-bioenergy
ENERGY
RTS: reference technology scenario (emissions under current Paris pledges)
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“what does the future hold for refining-petchems
integration?”: 1,940,000 Google hits (May, 2019)
Gasoline towards olefins->polyolefins?
MATERIALS
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“what does the future hold for refining-petchems
integration?”: 1,940,000 Google hits (May, 2019)
Gasoline towards olefins->polyolefins?
MATERIALS
Biorefineries: value-added molecules are important
for the economic feasibility of the biofuels production
AND…
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“what does the future hold for refining-petchems
integration?”: 1,940,000 Google hits (May, 2019)
Gasoline towards olefins->polyolefins?
MATERIALS
Biorefineries: value-added molecules are important
for the economic feasibility of the biofuels production
AND…
“HOW MUCH OIL WOULD/SHOULD STAY UNDERGROUND?”
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BIOREFINERIES, similarly to oil refineries,
are defined as multipurpose plants with
backbone processes (for the fuels) and
several derived, branched products
(molecules, building blocks)
MATERIALS
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upload.wikimedia.org/wikipedia/commons/4/40/Stone_arch_bridge%2C_Portaikos_river%2C_Pyli%
2C_Trikala%2C_Greece2.jpg
An important gap still remains
to be bridged: how to make
feasible this transition in the
real economy?
Two challenges:
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upload.wikimedia.org/wikipedia/commons/4/40/Stone_arch_bridge%2C_Portaikos_river%2C_Pyli%
2C_Trikala%2C_Greece2.jpg
An important gap still remains
to be bridged: how to make
feasible this transition in the
real economy?
Two challenges:
“Hardware”: Continuous, persistent R&D
efforts for “better”, “feasible” (advanced?)
(bio)processes.
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upload.wikimedia.org/wikipedia/commons/4/40/Stone_arch_bridge%2C_Portaikos_river%2C_Pyli%
2C_Trikala%2C_Greece2.jpg
An important gap still remains
to be bridged: how to make
feasible this transition in the
real economy?
Two challenges:
“Hardware”: Continuous, persistent R&D
efforts for “better”, “feasible” (advanced?)
(bio)processes.
“Software”: Supplying tools for techno-
economic-environmental evaluation from the
scratch.
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upload.wikimedia.org/wikipedia/commons/4/40/Stone_arch_bridge%2C_Portaikos_river%2C_Pyli%
2C_Trikala%2C_Greece2.jpg
An important gap still remains
to be bridged: how to make
feasible this transition in the
real economy?
Two challenges:
“Hardware”: Continuous, persistent R&D
efforts for “better”, “feasible” (advanced?)
(bio)processes.
“Software”: Supplying tools for techno-
economic-environmental evaluation from the
scratch.
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THE “SOFTWARE”
(that’s us, PSE community…)
Big picture: Building tools for supporting
stakeholders’ decision-making and governmental
policies during the transition to low-C economy
Local problems: improving the performance of
bioprocesses, bioreactors, up/downstream unit
operations, etc (several yet unexplored, or low-
explored process solutions)
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Our approach for “big picture” problems:
Retro-techno-economic-environmental analysis
RTEEA
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Cells’ driving forces:
biological survival, reproduction Cell Factory
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Cells’ driving forces:
biological survival, reproduction
(Bio)process industry driving forces:
economical survival, environmental
sustainability
Cell Factory
Biorefinery
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Cells’ driving forces:
biological survival, reproduction
Our approach
Including “survival” equations into the overall
(bio)process model (together with mass, energy
balances, kinetics, thermodynamics, etc)
(Bio)process industry driving forces:
economical survival, environmental
sustainability
Cell Factory
Biorefinery
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Our approach in practice
1. How to quantify the “economical survival” potential?
Response: Classical economic metrics
NPV (Net Present Value)
IRR (Internal Rate of Return)
MSP (Minimum Selling Price), …
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Our approach in practice
1. How to quantify the “economical survival” potential?
Response: Classical economic metrics
NPV (Net Present Value)
IRR (Internal Rate of Return)
MSP (Minimum Selling Price), …
Quantitively, the “survival” limit is defined, for
instance, by:
𝑁𝑃𝑉 = −𝐼𝑛𝑣𝑒𝑠𝑡𝑚𝑒𝑛𝑡 + 𝑃𝑟𝑜𝑓𝑖𝑡
1 + 𝑟 𝑖= 0
𝑁
𝑖=1
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Our approach in practice
2. How to quantify the “environmental survival”
potential?
Response: LCA metrics
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Our approach in practice
2. How to quantify the “environmental survival”
potential?
Response: LCA metrics
Upstream:
Material Flow Accounting: total amount of matter required to produce a unit of mass of product
Embodied Energy Analysis: total energy requirement per unit of mass of product
Exergy Analysis: second-law efficiency of the system.
Downstream:
Global Warming Potential: expressed in gram of CO2 equivalent
Acidification Potential: expressed in gram of SO2 equivalent
Eutrophication potential: expressed in gram of PO4-3 equivalent
Tropospheric ozone & photosmog formation potential: expressed in gram of ethene equivalent
Stratospheric ozone depletion potential: expressed in gram of CFC-11 equivalent
Ecotoxicity potential: expressed in 1,4-dichlorobenzene equivalent
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Retro-techno-economic-environmental analysis
RTEEA
NPV = 0, GWP = % of fossil ...
Classical TEEA
NPV CI ...
Performance parameters: Yield Selectivity Productivity
RTEEA
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Retro-techno-economic-environmental analysis
RTEEA
1 – Solving TEA + environmental equations in simulation
time
2 – Replacing specification of a key variable for the
“survival equation” (e.g. NPV = 0, …), keeping DF = 0
Obs: Equation-oriented simulators avoid external loops…
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*Soares, R. P.; Secchi, A. R. EMSO: A new environment for
modelling, simulation and optimization. Comput.-Aided Chem. Eng.,
2003, 14, 947
EMSO*
- Open models, easily including sizing and
calculation of capital costs
- Equation-oriented: all equations (including
“survival”) are solved simultaneously, so
RTEEA can run together with the simulation of
the overall process (much easier than the trial-
and-error procedure that a modular simulator
would demand)
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RTEEA results,
an illustration
Succinic Acid Production
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Efe Ç, van der Wielen LAM, Straathof AJJ. Techno-economic analysis of succinic acid production using adsorption from fermentation medium. Biomass & Bioenergy 56:479-792, 2013.
Succinic Acid Production
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Biocatalyst productivity (g/(kg h)) Conversion Suc. Acid final concentration (g/L) Selectivity (gAc. Suc./gEthanol)
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Succinic Acid RTEA: “isoeconomic curves”
Final Suc. Ac. concentration in the bioreactor as a function of selectivity for distinct biocatalyst productivities
Biocatalyst productivity (g/(kgh))
Infeasible region
Furlan FF, Costa CBB, Secchi AR, Woodley JM, Giordano RC. Retro-Techno-Economic Analysis: Using (Bio)Process Systems Engineering Tools to Attain Process Target Values. Industrial & Engineering Chemistry Research 55:9865-9872, 2016.
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Succinic Acid RTEA: “isoeconomic curves”
Final Suc. Ac. concentration in the bioreactor as a function of selectivity for distinct biocatalyst productivities
Infeasible region
NPV ≥ 0
Feasible
Furlan FF, Costa CBB, Secchi AR, Woodley JM, Giordano RC. Retro-Techno-Economic Analysis: Using (Bio)Process Systems Engineering Tools to Attain Process Target Values. Industrial & Engineering Chemistry Research 55:9865-9872, 2016.
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Succinic Acid RTEA: “isoeconomic curves”
Final Suc. Ac. concentration in the bioreactor as a function of selectivity for distinct biocatalyst productivities
It is better trying to increase product final concentration than selectivity
Infeasible region
Furlan FF, Costa CBB, Secchi AR, Woodley JM, Giordano RC. Retro-Techno-Economic Analysis: Using (Bio)Process Systems Engineering Tools to Attain Process Target Values. Industrial & Engineering Chemistry Research 55:9865-9872, 2016.
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Succinic Acid RTEEA: what about
environmental impacts?
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Succinic Acid RTEEA: what about
environmental impacts?
To improve economics: optimize bioreactor operation (bioreactor engineering)
To reduce C intensity: back to the clone for higher selectivity (systems biology)
1G-2G Bioethanol from Sugarcane Biorefinery (EMSO)
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Dimensionless cash flow: burning sugarcane
trash (50%); C6 + C5 fermentation
Infeasible
region
Furlan FF et al. Comp. Chem. Eng. (2012) 43:1-9
Furlan FF et al. Biotechnol. Biofuels, (2013) 6:142.
Dimensionless cash flow: burning sugarcane
trash (50%); only C6 fermentation
Bagasse partition in the biorefinery.
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Análise de Ciclo de Vida (ACV)
Environmental footprint, 1G and 1G-2G bioethanol
Economic allocation, CML – IA methodology
a- Global Warming Potentials 100 years’ horizon, in kg CO2eq/MJ ethanol
b- Abiotic depletion, in kg Sb eq./MJ ethanol
c- Ozone layer depletion, in kg CFC-11 eq./MJ ethanol
d- Human toxicity, in kg 1,4DB eq./MJ ethanol
e- Fresh water aquatic ecotoxicity, in kg 1,4DB eq./MJ ethanol
f- Marine aquatic ecotoxicity, in kg 1,4DB eq./MJ ethanol
g- Terrestrial ecotoxicity, in kg 1,4DB eq./MJ ethanol
h- Photochemical oxidation, in kg C2H4 eq./MJ ethanol
i- Acidification, in kg SO2 eq. /MJ ethanol
j- Eutrophication, in kg PO4-3 eq./MJ ethanol
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
1G 1G-2G
Overview of some points
we’re presently working on
LCA: consistency of databases (uncertainty…)
Improving robustness
Key variables: screening & global sensitivity
analysis
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LCA: consistency of databases for
inventory
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Brazilian sugarcane GWP 100
a SimaPro(9.0): 0.1690 kg CO2eq/kgsugarcane b RenovaCalc : 0.0413 kg CO2eq/kgsugarcane
LCA: consistency of databases for
inventory
a 1 kg Sugarcane {BR}| market for, IPCC 2013 GWP 100a V1 b Seabra, J.E., Macedo, I.C., 2011. Comparative analysis for power generation and ethanol production from sugarcane residual biomass in Brazil.
Energy Policy, 39(1), 421-428. https://doi.org/10.1016/j.enpol.2010.10.019
Cavalett, O., Junqueira, T.L., Dias, M.O., Jesus, C.D., Mantelatto, P.E., Cunha, M.P., Franco, H.C.J.; Cardoso, T.F., Maciel Filho, R., Rossel,
C.E.V., Bonomi, A., 2012. Environmental and economic assessment of sugarcane first generation biorefineries in Brazil. Clean Technol.
Environ. Policy, 14, 399-410. https://doi.org/10.1007/s10098-011-0424-7
Matsuura, M.I., Scachetti, M.T., Chagas, M.F., Seabra, J.E., Moreira, M.M., Bonomi, A.M., Bayma, G., Picoli, J.F., Morandi, M.A.B., Ramos, N.P.,
Cavallet, O., Novaes, R.M.L, 2018. Nota Técnica RenovaCalc: Método e ferramenta para a contabilidade da Intensidade de Carbono de
Biocombustíveis no Programa RenovaBio. RenovaBio.
LCA: consistency of databases for
inventory
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1G 1G-2G
g CO2eq/MJethanol g CO2eq/MJethanol
SimaPro 9.0 database 69.90 64.76
Replacing only sugarcane by
RenovaCalc data 23.72 22.48
Bioethanol GWP 100*
* Energetic allocation, electricity and anhydrous ethanol as co-products.
The 1G and 1G-2G biorefinery: 833 tons of sugarcane per hour.
- 1G base case produces 89.81 L/ton of sugarcane.
- 1G-2G base case produces 120.92 L/ton of sugarcane.
LCA: consistency of databases for
inventory
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SimaPro:
Database extrapolated from 2006 to 2016; Ecoinvent v.2.0 a .
RenovaCalc:
Agriculture data from Ecoinvent v.3.1 b.
a Jungbluth N., Chudacoff M., Dauriat A., Dinkel F., Doka G., Faist Emmenegger M., Gnansounou E., Kljun N., Spielmann M., Stettler C. and
Sutter J. (2007) Life Cycle Inventories of Bioenergy. Final report ecoinvent data v2.0 No. 17. Swiss Centre for Life Cycle Inventories, Dübendorf,
CH.
b WERNET, G., et al. (2016). "The ecoinvent database version 3 (part I): overview and methodology." The International Journal of Life Cycle
Assessment, 21(9): 1218-1230
LCA: consistency of databases for
inventory
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SimaPro
• 20 % mechanical harvesting, 80 % manual
• Average annual sugarcane yield: 68.7 t/ha (Macedo et al. 2004).
• Pesticides: Amount of active ingredient, averages for Brazil from CETESB (1988)
• Fertilizing : Based on diesel consumption of sugarcane machinery Brazil (Macedo 1996)
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Improving robustness: virtual heat exchange networks (including
pinch analysis within process simulations)
An example:
• Fraction of solids (FS) in the hydrolysis reactor a the key variable in the
techno-economic-environmental analysis of the 2G ethanol process;
• Depending on FS, heat exchanger (E602) would be a cooler, a heater or
would not even exist.
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LONGATI, ANDREZA A. ; Lino, Anderson R.A. ; Giordano, Roberto C. ;
Furlan, Felipe F. ; Cruz, Antonio J.G. . Defining research & development
process targets through retro-techno-economic analysis: The sugarcane
biorefinery case. BIORESOURCE TECHNOLOGY, v. 263, p. 1-9, 2018.
b a
Improving robustness: virtual heat exchange networks (including
pinch analysis within process simulations)
Before pinch After pinch
Metamodels: Kriging (enzymatic saccharification of sugar cane bagasse)
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Metamodels: Kriging (enzymatic saccharification of sugar cane bagasse)
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Metamodels: Multilinear lookup tables (ethanol distillation train)
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Metamodels: Multilinear lookup tables (ethanol distillation train)
Selection of key variables: screening & global sensitivity analysis
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Screening methods a
• 1G-2G biorefinery: app. 103 specified variables: experience/heuristics before
systematic search
Variance-based global sensitivity analysis (GSA) a
• Model independency;
• Capacity to capture the influence of the full range of variation of each input factor;
• Appreciation of interaction effects among input factors;
a Saltelli, A., Ratto, M., Andres, T., Campolongo, F., Cariboni, J., Gatelli, D., Saisana, M., Tarantola, S., 2007. Global Sensitivity Analysis. The Primer,
Global Sensitivity Analysis. The Primer. John Wiley & Sons, Ltd, Chichester, UK. https://doi.org/10.1002/9780470725184
b Soares, R.P., Secchi, A.R., 2004. Modifications, simplifications, and efficiency tests for the CAPE-OPEN numerical open interfaces. Comput. Chem.
Eng. 28, 1611–1621. https://doi.org/10.1016/j.compchemeng.2003.12.008
EMSO CAPE-OPEN interface b
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Análise de Sensibilidade Global (ASG)
Variables Metrics
ODP AD HT FWET MAET TET EU AC PO GWP100 NPV
HSMF 0.34 0.08 0.08 0.09 0.08 0.08 0.06 0.07 0.00 0.01 0.01
HEL 0.00 0.00 0.00 0.00 0.00 0.00 0.02 0.02 0.53 0.37 0.72
HC 0.20 0.33 0.32 0.33 0.33 0.33 0.37 0.36 0.28 0.33 0.17
XC 0.03 0.08 0.08 0.08 0.08 0.08 0.09 0.09 0.05 0.06 0.02
XRT 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
PSMF 0.40 0.45 0.46 0.45 0.46 0.45 0.40 0.41 0.07 0.16 0.00
PT 0.00 0.01 0.01 0.01 0.01 0.01 0.01 0.01 0.00 0.00 0.00
PCGC 0.02 0.02 0.01 0.01 0.01 0.01 0.02 0.02 0.04 0.04 0.06
PHXC 0.01 0.03 0.03 0.04 0.03 0.04 0.03 0.03 0.02 0.02 0.00
Sobol first order index, normalized
GSA
HSMF: hydrolysis reactor solid mass fraction
HEL: hydrolysis reactor enzymatic load
HC: hydrolysis conversion (C6)
XC: xylose conversion (C5)
XRT: xylose reaction time
PSMF: pretreatment reactor solid mass fraction
PT: pretreatment reactor temperature
PCGC: pretreatment cellulose to glucose conversion
PHXC: pretreatment hemicellulose to xylose conversion
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feasible
RTEEA - 1G/2G bioethanol
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80 ton cane/ha CI = 19 gC02eq/MJ eth
N residual
Industry (6%) Fertilizers
Machinery
diesel
Distribution
Correctives
Burning straw
1G Ethanol in Brazil: contributions for C footprint
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80 ton cane/ha CI = 19 gC02eq/MJ eth
N residual
Industry (6%) Fertilizers
Machinery
diesel
Distribution
Correctives
Burning straw
1G Ethanol in Brazil: contributions for C footprint
Industry impact is comparatively small, BUT since the
biorefinery is multiproduct, allocation will occur in it,
during the production process
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80 ton cane/ha CI = 19 gC02eq/MJ eth
N residual
Industry (6%) Fertilizers
Machinery
diesel
Distribution
Correctives
Burning straw
1G Ethanol in Brazil: contributions for C footprint
Industry impact is comparatively small, BUT since the
biorefinery is multiproduct, allocation will occur in it,
during the production process
Nowadays: global allocation, for instance, “at the gate”
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80 ton cane/ha CI = 19 gC02eq/MJ eth
N residual
Industry (6%) Fertilizers
Machinery
diesel
Distribution
Correctives
Burning straw
1G Ethanol in Brazil: contributions for C footprint
Industry impact is comparatively small, BUT since the
biorefinery is multiproduct, allocation will occur in it,
during the production process
Nowadays: global allocation, for instance, “at the gate”
QUESTION: aren’t there more sound criteria? We’re
working on them…
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A word of advice: the importance of
re-thinking land use, with
sustainability as a keystone…
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apublica.org/2019/04/coquetel-com-27-agrotoxicos-foi-achado-na-agua-
de-1-em-cada-4-municipios-consulte-o-seu/
“Local” problems:
Complex enzymatic reactions:
Fuzzy consortium of simplified models for saccharification of
biomass
Modeling enzymatic esterification/transesterification…
Microbial cultivations:
Metabolic flux-oriented control of bioreactors
Advanced softsensoring: information from NIR, UV,
capacitance probes (less and less expensive)
Data-driven induction in high cell density cultivations for
recombinant m.o.: constructive neural networks (machine
learning)
…
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Rational, structural changes in chains of
production, from field to industry to
distribution...
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Rational, structural changes in chains of
production, from field to industry to
distribution...
A most urgent task, where
surely PSE has a role
62 May 17th, 2019
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“I don’t want you to be hopeful. I want you to panic. I
want you to feel the fear I feel every day. And then I
want you to act,” Greta Thunberg at Davos, January
2019
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Roberto C. Giordano
Antonio C. L. Horta
Antonio J. G. Cruz
Felipe F. Furlan
Marcelo P. A. Ribeiro
Ruy Sousa Jr
Andrew M. Elias
Andreza A. Longati
Christian O. Martins
Ediane S. Alves
Erich Potrich
Gustavo Batista
Harikishan R. Ellamla
Simone C. Miyoshi
Vitor B. Furlong
Wellington M. Santos
…
Argimiro R. Secchi
Roymel Rodríguez-Carpio…
Rafael P. Soares
Collaborations (more frequent)
Teresa C. Zangirolami
Thiago Mesquita…
Raquel L. C. Giordano
Felipe S. Corradini…