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Systems of agricultural
production
- global changes of climate
Chojnicki J., Dmuchowski W., Lenart S., Sosulski T.

Warsaw University of Life Sciences, 02-776 Warszawa, 159/37
Nowoursynowska Street , Poland, email: jozef_chojnicki@sggw.pl

Global Landscapes Forum
Warsaw, 16-17 November 2013
Annual GHG emissions from agriculture are expected to
increase in the coming decades due to escalating
demands for food and shifts in diet.
However, improved management practices and emerging
technologies may permit a reduction in emissions per
unit of food (or of protein) produced.
Agricultural practices that potentially mitigate
GHGs:
•
•
•
•
•
•
•

cropland management;
grazing land management/pasture improvement;
management of agricultural organic soils;
restoration of degraded lands;
livestock management;
manure/bio-solid management;
bio-energy production.
Influence of crop production
on climate change
Main processes:
 Strengthening of warming – emission of N2O (GHG)
N2O is generated by the microbial transformation of
nitrogen in soils and manures and is often enhanced
when available nitrogen exceeds plant requirements,
especially under wet conditions
 Reduction of warming – carbon sequestration in soil
Emission of N2O in Poland in 2011
(KOBIZE, 2013)

Sources

Gg

%

Total

87.9

100

Energy production

6.8

8.7

Industrial processes

3.5

4.0

Sewage

3.6

4.1

Agriculture

73.6

83.7
Properties of greenhouse gases
Gas

Life duration
in air / years

Strengthening of
warming

CO2

50-200

1

CH4

12

43

N2O

115

250

CFC-11

45

15 000

CFC-12

102

19 000

HCFC-22

12

13 000
Concentration of GHGs in the troposphere
Gas

Before 1750

Now

part in
warming

(Start of industrial
revolution)

CO2

280 ppmv

378 ppmv

1.46

CH4

0.70 ppmv

1.78 ppmv

0.48

N2O

0.27 ppmv

0.32 ppmv

0.18

O3

0.025 ppmv

0.034 ppmv

0.35

CFC, HCFC,
HFC

0 pptv

3-544 pptv

0.34
Productivity and environmental impact of
different farming systems
High-input
farming system

Productivity

Precision
agriculture
Integrated
system
Low-input farming
system

Organic system

Favourable impact on environment
Agricultural land on certified organic and
integrated farms in Poland in 2011
Farms

Agricultural land
in thousand ha

%

Total

15442.4

100

organic

605.5

3.9

integrated

10.7

0.1
Emission of N2O (kg ha-1) in different crop
production systems within 1996-2005
(Stalenga & Kawalec 2007)

Source of emission

ORG

CON

INT

N synthetic fertilizer

-

1.78

0.89

Organic fertilizer

0.32

-

0.40

N-fixing crop

0.20

-

0.14

total

0.52

1.78

1.43

ORG – organic; CON – conventional; INT - integrated
Nitrogen balance in different farming
systems in kg N/ha (Jończyk et al. 2007)
Farming system

Input

Output

Balance

Organic

95

85

11

Integrated

147

112

36

Conventional

167

119

49

Wheat
monoculture

192

121

71
Nitrogen losses from soil in various fertilization
systems of rye monoculture (calculated using the
balance method)
0

Mineral-organic
system

Organic
system

50%

Mineral
system

57%

20
kg·ha-1

40

35%

60
80

NPK

NPK + manure

Manure

Sosulski 2005, Department of
Agricultural Chemistry, SGGW
Effect of mineral, mineral-organic and organic
fertilization on N2O emissions from soil under rye
monoculture (monthly average)
16
(g N-N 2 O·ha -1 ·day -1 )

12

NPK

8

NPK+manure
manure

4

0

August

September

October
unpublished data, Sosulski T.,
Department of Agricultural Chemistry,
SGGW
Conclusions
• Crop production has significant influence on GHG emission
(N2O) in Poland (87% total emission) and is correlated with
the usage of mineral N fertilizers
• The level of nitrogen release depends on the applied
agricultural system:
ecological < inegrated < conventional < conventional –
monoculture
• Manure fertilization increases N2O emission more
significantly than mineral fertilization
• The level of organic carbon sequestration in soil depends
on the system of agriculture production: ecological >
inegrated > conventional > conventional – monoculture
• Ecological farming is most favourable in mitigation of
climate changes; however, its influence is insignificant due
to the small area covered by such farming
• Technologies applied in integrated and precision
agriculture will potentially have the largest influence on
mitigation of climate change

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Systems of agricultural production 
- global changes of climate


  • 1. Systems of agricultural production - global changes of climate Chojnicki J., Dmuchowski W., Lenart S., Sosulski T. Warsaw University of Life Sciences, 02-776 Warszawa, 159/37 Nowoursynowska Street , Poland, email: jozef_chojnicki@sggw.pl Global Landscapes Forum Warsaw, 16-17 November 2013
  • 2. Annual GHG emissions from agriculture are expected to increase in the coming decades due to escalating demands for food and shifts in diet. However, improved management practices and emerging technologies may permit a reduction in emissions per unit of food (or of protein) produced.
  • 3. Agricultural practices that potentially mitigate GHGs: • • • • • • • cropland management; grazing land management/pasture improvement; management of agricultural organic soils; restoration of degraded lands; livestock management; manure/bio-solid management; bio-energy production.
  • 4. Influence of crop production on climate change Main processes:  Strengthening of warming – emission of N2O (GHG) N2O is generated by the microbial transformation of nitrogen in soils and manures and is often enhanced when available nitrogen exceeds plant requirements, especially under wet conditions  Reduction of warming – carbon sequestration in soil
  • 5. Emission of N2O in Poland in 2011 (KOBIZE, 2013) Sources Gg % Total 87.9 100 Energy production 6.8 8.7 Industrial processes 3.5 4.0 Sewage 3.6 4.1 Agriculture 73.6 83.7
  • 6. Properties of greenhouse gases Gas Life duration in air / years Strengthening of warming CO2 50-200 1 CH4 12 43 N2O 115 250 CFC-11 45 15 000 CFC-12 102 19 000 HCFC-22 12 13 000
  • 7. Concentration of GHGs in the troposphere Gas Before 1750 Now part in warming (Start of industrial revolution) CO2 280 ppmv 378 ppmv 1.46 CH4 0.70 ppmv 1.78 ppmv 0.48 N2O 0.27 ppmv 0.32 ppmv 0.18 O3 0.025 ppmv 0.034 ppmv 0.35 CFC, HCFC, HFC 0 pptv 3-544 pptv 0.34
  • 8. Productivity and environmental impact of different farming systems High-input farming system Productivity Precision agriculture Integrated system Low-input farming system Organic system Favourable impact on environment
  • 9. Agricultural land on certified organic and integrated farms in Poland in 2011 Farms Agricultural land in thousand ha % Total 15442.4 100 organic 605.5 3.9 integrated 10.7 0.1
  • 10. Emission of N2O (kg ha-1) in different crop production systems within 1996-2005 (Stalenga & Kawalec 2007) Source of emission ORG CON INT N synthetic fertilizer - 1.78 0.89 Organic fertilizer 0.32 - 0.40 N-fixing crop 0.20 - 0.14 total 0.52 1.78 1.43 ORG – organic; CON – conventional; INT - integrated
  • 11. Nitrogen balance in different farming systems in kg N/ha (Jończyk et al. 2007) Farming system Input Output Balance Organic 95 85 11 Integrated 147 112 36 Conventional 167 119 49 Wheat monoculture 192 121 71
  • 12. Nitrogen losses from soil in various fertilization systems of rye monoculture (calculated using the balance method) 0 Mineral-organic system Organic system 50% Mineral system 57% 20 kg·ha-1 40 35% 60 80 NPK NPK + manure Manure Sosulski 2005, Department of Agricultural Chemistry, SGGW
  • 13. Effect of mineral, mineral-organic and organic fertilization on N2O emissions from soil under rye monoculture (monthly average) 16 (g N-N 2 O·ha -1 ·day -1 ) 12 NPK 8 NPK+manure manure 4 0 August September October unpublished data, Sosulski T., Department of Agricultural Chemistry, SGGW
  • 14. Conclusions • Crop production has significant influence on GHG emission (N2O) in Poland (87% total emission) and is correlated with the usage of mineral N fertilizers • The level of nitrogen release depends on the applied agricultural system: ecological < inegrated < conventional < conventional – monoculture • Manure fertilization increases N2O emission more significantly than mineral fertilization
  • 15. • The level of organic carbon sequestration in soil depends on the system of agriculture production: ecological > inegrated > conventional > conventional – monoculture • Ecological farming is most favourable in mitigation of climate changes; however, its influence is insignificant due to the small area covered by such farming • Technologies applied in integrated and precision agriculture will potentially have the largest influence on mitigation of climate change

Editor's Notes

  1. W rolnictwie industrialnym (konwencjonalnym intensywnym) cele ekonomiczno-produkcyjne zdecydowanie dominują nad celami środowiskowymi. W rolnictwie ekologicznym najważniejsze są cele środowiskowe, a więc priorytety gospodarowania stawiane są w tym systemie w odwrotnej kolejności niż w rolnictwie intensywnym. Rolnictwo integrowane równoważy wszystkie cele. W skali regionu i gospodarstwa produkcja rolnicza powinna być tak zorganizowana, aby racjonalnie uwzględnić cele ekonomiczno-produkcyjne, środowiskowe i społeczne. Na zamieszczonym wykresie zajmuje więc centralną przestrzeń pomiędzy rolnictwem industrialnym i ekologicznym. Pozostałe systemy rolnictwa realizują te główne cele w różnym stopniu, trudnym do jednoznacznego określenia.
  2. Doświadczenie założono w 1994 r. w Stacji Doświadczalnej IUNG w Osinach (woj. lubelskie), w którym ocenia sie różne systemy gospodarowania (ekologiczny, integrowany i konwencjonalny prowadzony w dwóch wersjach – uproszczone zmianowanie i monokultura pszenicy ozimej). Doświadczenie założono na glebie płowej o składzie granulometrycznym piasku gliniastego mocnego przechodzącego w glinę lekką. Na powierzchni pola dominuje kompleks 4 -żytni bardzo dobry z pewnymi powierzchniami kompleksu pszennego dobrego. Pole doświadczalne o powierzchni około 20 ha jest podzielone na części, z których każda reprezentuje inny system gospodarowania. W każdym systemie stosuje sie inny płodozmian i całokształt agrotechniki dostosowany do jego specyfiki: SYSTEM EKOLOGICZNY - obejmuje 5-polowy płodozmian: ziemniak – pszenica jara z wsiewką koniczyny czerwonej z domieszka białej i z trawami, która użytkuje sie dwa lata – pszenica ozima + międzyplon ścierniskowy (mieszanka krzyżowych ze strączkowymi). 1. Nawożenie organiczne: kompost - 30 t/ha pod ziemniaki oraz biomasa międzyplonu ścierniskowego. 2. Nawożenie mineralne , w związku ze spadkiem zasobności gleby stosuje się nawozy mineralne dopuszczone do stosowania w rolnictwie ekologicznym: potasowe w dawce około 50 kg K2O/ha oraz fosforowe w dawce około 40 kg/ha P2O5. 3. Środki ochrony roślin – Novodor do zwalczania stonki ziemniaczanej oraz w ostatnich latach preparaty miedziowe do zwalczania zarazy ziemniaczanej. 4. Odchwaszczanie zasiewów - zabiegi mechaniczne oraz dodatkowo w ziemniaku ręczne pielenie przed ostatnim obredlaniem. SYSTEM INTEGROWANY prowadzony jest w 4-polowym płodozmianie: ziemniak – pszenica j. + międzyplon ścierniskowy z gorczycy białej – strączkowe (łubin wąskolistny) – pszenica ozima + międzyplon z gorczycy białej. 1. Nawożenie organiczne: kompost - 30 t/ha pod ziemniaki i biomasa międzyplonów ścierniskowych oraz słoma łubinu. 2. Nawożenie mineralne – dawki fosforu i potasu określane są według pobrania składnika z plonem średnio w rotacji zmianowania. Dawki azotu koryguje sie na podstawie zawartości azotu mineralnego w glebie wczesną wiosną oraz stanu odżywienia pszenicy azotem (test SPAD). 3. Chemiczne środki ochrony roślin są stosowane w sytuacji przekroczenia przez agrofagi progów szkodliwości, w przypadku chwastów jako uzupełnienie pielęgnacji mechanicznej. SYSTEM KONWENCJONALNY - uproszczone zmianowanie: rzepak ozimy – pszenica ozima –pszenica jara. 1. Nawożenie organiczne – przyorywana słoma rzepaku i pszenicy ozimej. 2. Nawożenie mineralne, według zaleceń IUNG dla intensywnych technologii produkcji. 3. Chemiczne środki ochrony roślin – w dawkach niezbędnych dla skutecznego ograniczenia agrofagów i wylegania. Monokultura pszenicy ozimej. 1. Nawożenie organiczne – słoma przyorywana co 2 lata 2. Nawożenie mineralne, według zaleceń IUNG dla intensywnych technologii produkcji. 3. Chemiczne środki ochrony roślin – w dawkach niezbędnych do skutecznego ograniczenia agrofagów i wylegania. Stosuje sie dodatkowo specjalistyczne zaprawy przeciwko Gaeumannomyces graminis.