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![Page 1: Sabine Houot, Marie-Noel Pons, Marylis Pradel, Marc-Antoine Caillaud, Isabelle Savini, Anaïs Tibi Brussels March 16th, 2015 USE OF FERTILIZING WASTE MATERIALS.](https://reader036.fdocuments.in/reader036/viewer/2022062720/56649f0d5503460f94c22092/html5/thumbnails/1.jpg)
Sabine Houot, Marie-Noel Pons, Marylis Pradel, Marc-Antoine Caillaud, Isabelle Savini, Anaïs Tibi
BrusselsMarch 16th, 2015
USE OF FERTILIZING WASTE MATERIALSIN AGRICULTURE AND FORESTRY
MAIN CONCLUSIONS OF THE SCIENTIFIC EXPERT REPORT
INRA – CNRS - IRSTEA
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.02
• A mission for the French research organizations a national charter since 2011
• Objective: To provide policy makers with an up to date view of the scientific and technological knowledge on any question of economical, environmental or public health importance
• Procedure for the expert report on fertilizing waste materials (“MAFOR”)Official request from French ministries Constitution of a scientific task force (declaration of potential conflicts of interests)
33 scientific experts + 2 documentation specialists + a project teamExamination of the scientific literature (peer-reviewed mostly) by experts
What is known/unknown, controversial, needs for additional research About 3500 references cited in the report
• The request: assessment of the agronomic benefits of MAFOR, their potential impacts on ecosystem contamination, and the overall economic and social consequences of their use.
No recommendations are proposed Out of the scope: potential health impacts, comparison between agricultural
spreading and other ways of recycling or elimination, assessment of treatments efficiency
Collective scientific expertise a scientific synthesis for policy makers
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.03
• Summary of the expert report in french (107p) (soon available in english) https://inra-dam-front-resources-cdn.brainsonic.com/ressources/afile/267560-bfb3b-resource-esco-mafor-synthese.html
• Synopsis (8p) in englishhttps://inra-dam-front-resources-cdn.brainsonic.com/ressources/afile/261380-eeab2-resource-mafor-8-page-synopsis.html
• Full expert report (950p) in Frenchhttp://institut.inra.fr/Missions/Eclairer-les-decisions/Expertises/Toutes-les-actualites/Expertise-Mafor-effluents-boues-et-dechets-organiques#
Full text documents online
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.04
Ressource and use of MAFOR in France
Diversity of MAFOR- Mainly coming from agriculture: 94% of spread amounts are animal manures- 6% remaining = composts and other MAFOR from urban and industrial origin (15
to 80% of the potential already recycled)
121 millions tons (fresh mass, FM) of MAFOR spread every year 17t FM ha-1 agricultural land in average + 148 millions tons of animal manure directly emitted on pasture lands
Fait avec Philcarto * 26/04/2014 08:09:24 * http://philcarto.free.fr
Effectif total
522293 [R13]
488083 [R12]
318019 [R14]
230708 [R06]
159583 [R07]
86541 [R19]
fumier bovin
lisier bovin
effluents avicoles
effluents porcins
effluents ovins et cunicoles
compost d'origine animale
compost DV ou OM
boues STEU / STEI
effluents de l'industrie betteravière
autre Mafor organique
Fait avec Philcarto * 26/04/2014 08:10:43 * http://philcarto.free.fr
Effectif total
706944 [R19]
373213 [R16]
277097 [R07]
152966 [R18]
50239 [R04]
12831 [R10]
fumier bovin
lisier bovin
effluents avicoles
effluents porcins
effluents ovins et cunicoles
compost d'origine animale
compost DV ou OM
boues STEU / STEI
effluents de l'industrie betteravière
autre Mafor organique
Spatial heterogeneity of Mafor spreading in France potential engineering to optimize the spatial redistribution of ressource
Fait avec Philcarto * 20/03/2014 16:18:46 * http://philcarto.free.fr
Effectif total
522293 [R13]
488083 [R12]
318019 [R14]
230708 [R06]
159583 [R07]
86541 [R19]
fumier bovin
lisier bovin
effluents avicoles
effluents porcins
effluents ovins et cunicoles
compost d'origine animale
compost DV ou OM
boues STEU / STEI
effluents de l'industrie betteravière
autre Mafor organique
Fait avec Philcarto * 20/03/2014 16:18:46 * http://philcarto.free.fr
Effectif total
522293 [R13]
488083 [R12]
318019 [R14]
230708 [R06]
159583 [R07]
86541 [R19]
fumier bovin
lisier bovin
effluents avicoles
effluents porcins
effluents ovins et cunicoles
compost d'origine animale
compost DV ou OM
boues STEU / STEI
effluents de l'industrie betteravière
autre Mafor organiqueOther
Urban composts
sludges
Farmyard manure
Cattle manure
Poultry manure
Pig manure
Other manure
Composted manure
Sugarbeet effluents
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POTENTIAL INTEREST FOR CROPS AND ASSOCIATED ENVIRONMETAL IMPACTS
.05
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.06
Interests of MAFOR use in agriculture fertilizer and soil improver To be demonstrated before use of any new substrate
MAFOR
Soil improverOM, pH
FertilizerN, P, K
WasteCo-products
Treatment
Soil properties
SOIL
Pedo-climatic conditionsAgricultural practices
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.07
Relationship between N fertilizer and organic amendment potentials
Composting
Phase separation
Drying Anaerobic digestion
Potential efficiency as organic amendment
N mineral fertilizer equivalent 100% mineral N equivalent
Slurry/Poultry manures
Pig and cattle slurries
Sewage sludges
Raw digestatesfrom anaerobic digestion
Compost MBT
Farmyardmanure
Composts (manures, sludge, digestates,
greenwastes, biowastes)
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.08
Fertilizer values of MAFOR mineral fertilizer substitution
Mineral N fertilizer equivalent:
From Gutser et al., 2005ESCo « Breeding and Nitrogen » 2012
P fertilizer equivalent: • Mineral P fertilizer equivalent >80%
• Exceptions: Ashes and sludges where P has been precipitated• Potentially enough P in Mafor to satisfy all crop needs for P
K fertilizer equivalent: similar to mineral K fertilizer
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MAFOR as organic amendment: potential increase of soil organic matter Physical:
Structure, water ,
compaction
Chemical:CEC, pH
Biological: Activities,
biodiversity
Standardized indicator of efficiency (XPU 44 162) Database available
Prediction of SOM increase
Lashermes et al.,2009
Peltre et al.,2012
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.010
Associated environmental impacts
WATER
AIR
NO3
DOCP
NH3
0-100% NH4
incorporation
EF N2O: 1.425%
EF CH4: <1%Slurries, digestates
N2O CH4
VOC
VOC1-100 g/ha
Emission factors to be improved
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3 juillet 2014
POTENTIAL IMPACTS RELATED TO CONTAMINANTS
.011
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.012
TransferTo ground waters
Three classes of contaminants
Contaminants in MAFOR
05/05/2014
Run off
Leaching
MAFOR
Retention and transformation
Transfer to plants
Transfer to animals
TransferTo surface waters
Biological
Organic
Trace elements
PersistanceMobilityBiodisponibilityTransfer to
waters
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.013
• Main threats:
Plant diseases or zoonosis
Dissemination of antibiotic resistance genes
• Associated with faecal origin: sewage sludge and animal manures
• Potential actions
Biological contaminants
05/05/2014
Treatments hygienization : temperature (composting , thermophilic anaerobic digestion); drying, pH increase
No treatment 100% efficient
Agricultural practices: Delay between spreading and harvest, animal return to grass… Variation among countries (3 to 6 weeks in France; 1 year in Denmark)
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.014
ADEME, Belon 2012
• Limited numbers; more or less (Sn, Tl…) documented; naturally present in the environment
• Nanoparticles: impacts poorly known (Ag, Ti)
• Persistant accumulation in soils. Sludge regulation and TE thresholds no impacts on soils and crops after 15 years. Longer term?
Trace elements
05/05/2014
Pesticides
Mineral fertilizers
Animal manure
Liming materials
Sludges and composts
Atmospheric deposition
Annual contribution of the 6 contamination sources to the total amount of TE reaching soils in France
Similar regulation for all fertilizers
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.015
Treatment:
Decrease of mobility
Total concentration:
• increase after digestion or composting
• Dilution after liming
Initial imputs
Choice of woods before burning decrease of TE concentration in ashes
Animal feeds or prescriptions
Sorting before treatment: Biowaste composting, separate networks for industrial waste waters
Potential actions to decrease TE fluxes or impacts
05/05/2014
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.016
Very large diversity, few contaminants regulated
Major threats: pharmaceuticals, endocrine disruptors
More or less persistant (days to years); metabolites can be toxic
Partial dissipation during treatment; bound residues linked to organic phases
Impacts on crops:
hydrophobic molecules: sorbed on roots but no transfer
other: potential transfer but few data and not observed in real conditions
Impacts on animals: little data; studies with pure molecules
Organic contaminants
05/05/2014
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3 juillet 2014
SYNTHESIS AND RESEARCH NEEDS
.017
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• Difficult to take into account all variation factors• In publications, Mafor are poorly described• Nothing new on acceptability and economical aspects
Origin : treatment
Soil
Climate
Time
What has to be considered to evaluate the use of MAFOR in agriculture
Spreading
Synthesis of scientific publications:
Emissions
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.019
Economic conditions to the substitution of Mafor for mineral fertilizers?
• Price of Mafor compared to mineral fertilizer• Very few studies; price of Mafor can be an obstacle to their use although they
are usually low.• No cost for Mafor with waste status could be incentive in context of price
increase of mineral fertilizers.
• Synthesis of cost/benefits of treatment/use of Mafor transport and spatial redistribution between areas with surplus or deficit of Mafor• Little scientific data on exchange markets of Mafor between producers and
users• Litle data to arbitrate between cost of spreading raw materials (related to
transport) and cost of treatment before spreading (objective to decrease volume and transport costs) to be able to export Mafor from areas with surplus
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.020
Needs to optimize the use of Mafor
• Upstream : typology of agronomical interests: origin X treatment characteristics
and potential interest of Mafor presence and behavior of contaminants during treatments
• Territorial management including all concerned actors Works on acceptability of Mafor Economic record related to the use of Mafor: cost/benefits approaches, studies
on existing market related to Mafor use; potential spatial redistribution of Mafor? Complete environmental evaluations : including treatment upstream
• Plots/ farm : Quality/method and date of spreading Optimisation of cropping system Adapted and parameterized decision tools Behavior of contaminants; delay after spreading: soil resilience; hierarchy of
contaminants Sanitary risk evaluation To be able to predict long term impacts (> 20 years) long term experiments Environmental evaluations : considering benefits and environmental impacts
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.021
Acknowledgments
Thanks to all involved experts, to the team project!
Thank you for your attention!