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O carbono como moeda de troca – Experiências e mecanismos
para remunerar os agricultores
Telmo J. C. Amado & Charles W. Rice
CONSORTIUM FOR AGRICULTURAL SOILS MITIGATION OF GREENHOUSE GASES
Global Warming Connections
Soil
Organic
Carbon
Microbial
Activity
Nutrient
Cycling
Soil
Structure
Soil
Biodiversity
WaterErosion
&
Availability
Gaseous
Emissions
Plant Growth
Yield
Environmental
Services
Sustainability
Rice, 2016
-200
0
200
400
600
800
1000
1200
1400
1600
Cro
plan
d m
anag
emen
t
Wat
er m
anag
emen
t
Ric
e m
anag
emen
t
Set
asid
e, L
UC
&
agro
fore
stry
Gra
zing
land
man
agem
ent
Res
tore
cul
tivat
ed
orga
nic
soils
Res
tore
deg
rade
d
land
s
Bio
ener
gy (
soils
com
pone
nt)
Liv
esto
ck
Man
ure
man
agem
ent
Mitigation measure
Glo
bal
bio
ph
ysi
cal
mit
igat
ion
po
ten
tial
(M
t C
O2-eq
. y
r-1)
N2O
CH4
CO2
Global mitigation potential in agriculture
Smith et al. (2008)
Glo
bal
bio
ph
ysic
al m
itig
atio
n p
ote
nti
al (
Mt
CO
2se
q.
yr-1
)G
lob
al b
iop
hys
ical
mit
igat
ion
po
ten
tial
(M
t C
O2
seq
. yr
-1)
N2O
CH4
CO2
Carbon trading
• Market based mechanism
• Cap and trade
• More certain about volume of carbon reduction
• Those firms that are good at reducing CO2 will have permits to sell – these become an asset on the balance sheet
CONSORTIUM FOR AGRICULTURAL
SOILS MITIGATION OF GREENHOUSE GASES
10/24/2016 11
What is needed
• Sellers of C credits: Land managers
• Aggregator
• Buyers
• Monitoring/Verification
Putting a price on carbon
Importance of
Verification and commitment
Scarcity
Price expectations
Clean Development Mechanism
Rewarding efficiency and action
Estimates of various Ecosystem Services
Ecosystem services Value
(trillion $US)
Soil formation 17.1
Recreation 3.0
Nutrient cycling 2.3
Water regulation and supply 2.3
Climate regulation (temperature and
precipitation)
1.8
Habitat 1.4
Flood and storm protection 1.1
Food and raw materials production 0.8
Genetic resources 0.8
Atmospheric gas balance 0.7
Pollination 0.4
All other services 1.6
Total value of ecosystem services 33.3 Constanza et al., 1997
Nature
Effect of C price on implementation
Smith et al. (2007)
0
200
400
600
800
1000
1200
1400
Res
tore
cultiv
ated
org
anic
soils
Cro
pla
nd
man
agem
ent
Gra
zing lan
d
man
agem
ent
Res
tore
deg
raded
lands
Ric
e m
anag
emen
t
Liv
esto
ck
Set
asid
e, L
UC
&
agro
fore
stry
Man
ure
man
agem
ent
Measure
Mt
CO
2-e
q.
yr-1
up to 20 USD t CO2-eq.-1
up to 50 USD t CO2-eq.-1
up to 100 USD t CO2-eq.-1
Geo-reference microsites
• Microsites reduces spatial variability
• Simple and inexpensive
• Used to improve models
• Used to adopt new technology
• Soil C changes detected in 3 yr• 0.71 Mg C ha-1 – semiarid• 1.25 Mg C ha-1 – subhumid Ellert et al. (2001)
Sampling location: initial subsequent electromagnetic marker
4 m
7 m
MEETING NORTH AMERICA’S EVOLVING ENERGY NEEDS
ALBERTA AND CLIMATE CHANGE
Second Round Results
• 2008 reduction obligation - approximately 11 million tonnes of GHGs
– Based on emission projections
– Facility improvements addressed approximate 2 million tonnes• 2.75 million tonnes (31% ) of offsets used
– Tillage, renewables plus a broader range of projects including
acid gas, EOR using CO2
•Agricultural sink protocol (reduced/no-till)– Based on decades of science – Reflects years of carbon policy integration
Alberta Carbon Offset• Alberta, Canada legislation to reduce Greenhouse Gas
(GHG) emissions through the regulation of large emitters (industrial facilities that emit more 100,000 tonnesCO2e/yr).
• Agriculture and forestry are the only two industries that can remove carbon from the atmosphere.
• Approved offset protocols
• Beef and pork systems
• Biofuel
• Energy efficiency
• Tillage (reduced or No-till)
• $15 per ton of C
• $6/ha/y
1.2 - Agro Eco System 18
O que precisamos para prover serviçosambientais nos nossos agroecosistemas?
Soil
Organic
Matter
Water
Holding
Capacity
Crop
Yield
Soil
Biodiversity
Root
growth
Nutrient
Reserves
Soil
Structure
Plant
Biomass
Soil
Quality
Lal, Kimble, and Follett 1997Rice, 2016
SojaBlack oat Maiz Radish
oil
Wheat
Nutrient
cycling
Nutrient
cycling
Crop rotation to increase nutrient cycling
Mineral
Fertilization
Carbon sequestration rate (C rate) expressed in equivalent mass (Mg C/ha/y) to a 30 cm depth for Manhattan, KS USAConversion from tilled to no-till
Rotation
Continuous Soybean 0.066
Continuous Sorghum 0.292
Continuous Wheat 0.487
Soybean - Wheat 0.510
Soybean - Sorghum 0.311
29 Fabrizzi & Rice, 2006
-0.10
0.20
0.40
R0 R1 R2
Till No-Till
Loss
Sequestration
(Mg ha-1
year-1
)
0.02
0.19
0.32
R0 R1 R2
0-0.30 m
Wheat/Soybean
Winter cover/soybean
Intensive cover crop/rotation22 years
Fundacep, Nicoloso, 2009
Soil Carbon Stock
CT NT
2006/07
Yield C grain CO2 Flux CO2 flux-C grain
------------ g m-2 ----------------------------
321.3 150,95 -158.05 -7.10
Soybean
Verma et al. (2005) +/- 45 g C m-2
NT soybean neutral balance
Conclusion: Carbon sequestration? Not with soybean
Soybean Ecosystem C Balance
Escobar, 2007 Não publicado
Biophysical GHG Mitigation Potential
Soil C N2O& CH4
Emissions
Upstream
& Process
Net
Impact
---- t CO2e/ha/yr ------
No-till*1.09
(-0.26–2.60)
-0.18
(-0.91–0.72)
0.14
(0.07–0.18) 1.04
Winter cover crops*0.83
(0.37–3.24)
0.25
(0.00–1.05)
0.61
(0.41–0.81)1.69
Diversify Annual Crop
Rotations*
0.58
(-2.50–3.01)
0.07
(-0.04–0.65)0.00 0.65
Rice, 2016
Para termos sequestro de Carbono é preciso
melhorar a qualidade do Sistema plantio direto
So
il C
co
nte
nt
Cultivation
New
Management
New
Technology
Rice, 2016
Novos materiais para cobertura do solo
Citado por Tivet et al.,
Físicos Químicos
Biológicos
Perfil de solo favorável ao enraizamento profundo
Saturação por Cálcio para a Camada de 0,25-0,40m
Saturação por Calcio na Saturação por Bases(%) na Camada de 0,25-0,40m
16 18 20 22 24 26 28 30
Pro
du
ivid
ad
e(M
g.h
a-1
)
10600
10800
11000
11200
11400
11600
Y=0,4332x^2 + 40,2897x + 9876,6361
R2=0,95 p=0,00261,0 Mg.ha-1 Gesso
2,0 Mg.ha-1 Gesso
Testemunha
6,5 Mg.ha-1 Gesso
5,0 Mg.ha-1 Gesso
3,0 Mg.ha-1 Gesso
4,0 Mg.ha-1 Gesso
Figura 8. Relação entre Rendimento e a Saturação por Calcio para a Camada de 0,25-
0,40m para diferentes doses de gesso.Dalla Nora & Amado, Agronomy Journal 2013
Saturação por Alumínio na camada de 0,25-0,40m
Saturação por Alumínio(m%) na Camada de 0,25-0,40m
4 6 8 10 12 14
Pro
du
ivid
ad
e(M
g.h
a-1
)
10600
10800
11000
11200
11400
11600
Y=-12,8854x^2 + 141,1408x + 10941,3492
R2=0,70 p=0,08
1,0 Mg.ha-1 Gesso
2,0 Mg.ha-1 Gesso
Testemunha
6,5 Mg.ha-1 Gesso
5,0 Mg.ha-1 Gesso
3,0 Mg.ha-1 Gesso
4,0 Mg.ha-1 Gesso
Figura 7. Relação entre Rendimento e a Saturação por Alumínio(m%) na Camada de0,25-0,40m para diferentes doses de gesso.
Dalla Nora & Amado, Agronomy Journal 2013
Exclusão da Precipitação
0 t ha 3 t ha 5 t ha
Dalla Nora et al. 20150 3
Hidróxido de Cálcio
Fonte: Rosso et al., 2016Hansel não publicado
T1
53Fertilização Profunda 20 cm
Comprimento de raíz, cm dm-3
0 50 100 150 200 250
Pro
fundid
ade,
cm
0
5
10
15
20
25
FOX + Fertilização Profunda 20 cm
FOX + Fertilização 10 cm
Lanço
Sulcador 10 cm
Disco Ondulado
Tese doutorado Hansel, 2016
Tratamentos
FOX + Fertilização Prof. Lanço Sulcador (10 cm) Disco ondulado
Pro
duti
vid
ade,
kg h
a-1
2000
2500
3000
3500
4000
4500
5000
Sem Restrição de chuva
Com Restrição de chuva
Aa Aa
AaAa
Aa
Bb
BbBb
Casas de restrição de chuvas
*Letras maiúsculas diferem entre tratamentos. Letras minúsculas diferem o regime pluviométrico dentro de cada tratamento.
- 355 kg (8%)
- 807 kg (19,4%) - 1119 kg
(28%)
- 1201 kg (27,9%)
Escarificador +FertilizaçãoProfunda
Sulcador(10 cm)
Lanço Disco Ondulado Hansel, 2016
Não publicado
“Coquetel” of cover crops = different root systems 07 de julho de 2016
Source: Cemattec
Fonte: Cematter
14 de junho de 2016
Fonte: Cemater
Fonte: Cemater
Cover crops +chiselling
Radish Oil
Source: Cematter
Controlled Traffic
Teixeira et al., 2016
Trafego Controlado
Marcos Souiljee + Paulo Pires (Prestador Serv.) + UFSM