Nutrient recovery from wastewater: opportunities & challenges of EU regulatory context - KNW Waternetwork symposium "Resource recovery, just do it?", 09-11-2017
Presenter: Kimo van Dijk
European Sustainable Phosphorus Platform (ESPP)
www.phosphorusplatform.eu
Sustainable management of nutrients is crucial for agriculture, food, industry, water and the environment. ESPP brings together companies and stakeholders to address the Phosphorus Challenge and its opportunities for the circular economy.
Countries:
Austria AT
Belgium BE
Bulgaria BG
Cyprus CY
Czech Republic CZ
Germany DE
Denmark DK
Estonia EE
Spain ES
Finland FI
France FR
Greece EL
Hungary HU
Ireland IE
Italy IT
Lithuania LT
Luxembourg LU
Latvia LV
Malta MT
Netherlands NL
Poland PL
Portugal PT
Romania RO
Sweden SE
Slovenia SI
Slovakia SK
United Kingdom UK
Switzerland CH
Phosphorus:
Fosfor
Fosfor
Fòsfòr
Фосфор
Fosfor
Фосфор
Fosfor
Fosfor
Фосфор
Фосфор
Fosforas
Fosfors
Fuosfuors
Fosfor
Ffуsfforws
Fosfar
Fosfaras
Fosfaar
Fosforus
Φωσφορος
Ֆոսֆոր
Fosfor
Fosfor
Фосфор
Фосфор
ফসফরাস
فسفر
ફૉસ્ફરસનો
फास्फोरस
Fosfor
Fosfori
Foszfor
Фосфор
Фосфор
Паликандур
Fosfor
Fosfor
Фосфор
Фосфор
Фосфор
Фосфор
Fosfor
فوسفور
Fosfor
Fosforoa
ფოსფორი
[fūsfūr]
זרחן
Fosfru
Lìn
リン
인
ฟอสฟอรัส
Photpho
磷
Posporo
Fosfor
Pūtūtae-whetū
Fosforus
ഫോസ്ഫറസ്
பொஸ்பரசு
Fosofo
Fosforase
Posfori
Fósforo
Phusphuru
Fosforimi
Fosforo
Fosforon
Pesticium
Phosphate challenges in the Netherlands within a European context - projectme...
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Nutrient recovery from wastewater: opportunities & challenges of EU regulatory context - KNW Waternetwork symposium "Resource recovery, just do it?", 09-11-2017
1. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 1
www.phosphorusplatform.eu
Nutrient recovery from wastewater: opportunities &
challenges of EU regulatory context
Kimo van Dijk, European Sustainable Phosphorus Platform (ESPP)
kimovandijk@phosphorusplatform.eu
2. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 2
www.phosphorusplatform.eu
The big picture of phosphorus - P
• Non-replaceable building block of life on earth
• Finite resource essential for global food security
• Major component of a Nutrient Circular Economy
• Critical Raw Material in leading edge industries
• Pollutant causing water quality failure
8. Phosphorus flows in NL for 2011
IMPORT
110.5 ± 4.0
EXPORT
69.0 ± 4.0
SURPLUS
41.6 ± 3.9
Smit et al. 2015. A substance flow analysis of phosphorus in the food production, processing and
consumption system of the Netherlands. DOI 10.1007/s10705-015-9709-2
Gg P per year
9. Average phosphate surplus in Dutch
agriculture 1880-2010
-10
0
10
20
30
40
50
60
70
80
90
1860 1880 1900 1920 1940 1960 1980 2000 2020
Year
Surplus,kgP2O5/ha
-1000
0
1000
2000
3000
4000
5000
6000
7000
8000
9000
Cumulativesurplus,kgP2
O5
/ha
Annual
Cumulative
Target
2015
1 kg P = 2.29 kg P2O5
Ehlert et al., 2011
10. Phosphorus balance & losses in NL in 2011
Import Export Net balance
Fertilizer 7 +7
Feed 67.1 +67.1
Food 32.9 49.2 -16.3
Non-food 3.4 1.3 +2.1
Animals 0.2 +0.2
Manure 16 -16
Waste 2.4 -2.4
TOTAL 110.6 68.9 41.7
Potential losses Gg P/year
Sequestered 23.2
Accumulation soils 11.8
Emissions to water 6.6
TOTAL 41.6
Smit et al. 2015. A substance flow analysis of phosphorus in
the food production, processing and consumption system of
the Netherlands. DOI 10.1007/s10705-015-9709-2
11. Transition towards sustainable P use (5xR)
•remove non-essential P inputs (e.g. detergents)
•match P requirements more closely (precision
agriculture)
•utilise legacy P stores
Realign P inputs
•optimise input management
•minimise runoff and erosion
•strategic retention zones
Reduce P losses
to water
•avoid wastage
•improve utilization efficiency
•adopt integrated production systems
Recycle P
in bioresources
•recover P in societies' wastes
•produce fertilizer substitutes
Recover P in
wastes
•influence dietary choice
•define end-user P requirements
•re-connect crop and animal production systems
Redefine P in
the food chain
Withers, Van Dijk, et al. (2015): Stewardship to tackle global phosphorus inefficiency: the case of Europe
12. Availability of macro & micronutrients
Source: de Haes et al. 2012. Schaarste van micronutriënten in bodem, voedsel en minerale voorraden:
Urgentie en opties voor beleid. Utrecht, Netherlands, Platform Landbouw, Innovatie & Samenleving.
AND Chardon & Oenema, 2013. Verkenning mogelijke schaarste aan micronutriënten in het
voedselsysteem, Wageningen: Alterra Wageningen UR.
A simplistic way of expressing resource scarcity
R/P ratio = reserve / production
13. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 13
www.phosphorusplatform.eu
1991 – today: EU water policies (principal legislation)
- Urban Waste Water Treatment Directive 1991/271
- defines eutrophication “Sensitive Areas” = ‘potentially’ subject to eutrophication
- requires P removal of 80%P and/or down to 2 mgP/l
for all wwtp > 10 000 pe (1 mgP/l wwtp > 100 000 pe)
in these areas and in their upstream catchments
- requires “appropriate” treatment in wwtp < 10 000 pe
- Nitrates Directive 1991/676
- defines nitrate “Vulnerable Zones”
- requires action plans in these zones
- limits application of manure and fertiliser,
obligations for manure storage, etc.
- Water Framework Directive 2000/2000
- all surface and ground waters
must achieve Good Ecological Quality Status
or (Potential) by 2015 / 2021/ 2027
- Groundwater Directive 2006/118
- Phosphorus on monitoring list (2014)
Phosphorus is first cause of EU Water Framework
Directive quality status failure (other than morphology)
55% of UK rivers and 74% of lakes
exceed P level for good ecological status
14. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 14
www.phosphorusplatform.eu
2014 EU Consultative Communication on
Sustainable Use of Phosphorus
“the EU should prioritise reducing the use of mined phosphate
in favour of recycled phosphates”
Increasing knowledge and research
Security of supply
Risk of soil contamination by mineral or recycled fertilisers
P recycling from wastewater, food waste and other biowastes
P in agriculture: balanced fertilisation, manure processing
Policy instruments
Awareness raising and platforms
see www.phosphorusplatform.eu/scope107
15. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 15
www.phosphorusplatform.eu
2014
Phosphate rock added to
EU list of 20 Critical Raw Materials
- List currently under revision
- Addition of P4 proposed
(as well as phosphate rock)
http://europa.eu/rapid/press-release_MEMO-14-377_en.htm
16. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 16
www.phosphorusplatform.eu
2015
EU Circular Economy Package
In responses to public consultation:
30% of respondents identified bio-nutrients
as “materials the EU should target first” (Q5, Q3)
Overall, 54% cited bio-nutrients or phosphorus
(all questions)
Scope Newsletter n°118
http://www.phosphorusplatform.eu/images/scope/
ScopeNewsletter%20118.pdf
17. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 17
www.phosphorusplatform.eu
March 2016 – ongoing EU Fertilisers Regulation
- currently in Council - Parliament decision process
- EU criteria for all fertilisers & soil amendments
- mineral fertilisers, composts, digestates, food industry wastes,
ABPs animal by-products (but CMC11 still a “blank box”) …
- will open EU market for recycled nutrient products
and also for nutrient recycling technologies
- but - sewage biosolids excluded
- many issues remaining
See www.phosphorusplatform.eu/regulatory
http://ec.europa.eu/DocsRoom/documents/15949
18. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 18
www.phosphorusplatform.eu
EU Fertilisers Regulation – key issues outstanding
- ESPP amendment on traceability
- for products containing organic materials
- STRUBIAS (JRC) process
- struvite/phosphate salts (inc. from sewage) – ash-based materials – biochars
- currently not in Regulation – STRUBIAS = draft criteria proposed to add
see www.phosphorusplatform.eu/regulatory - comments to ESPP by end July latest
- should cover ash used directly on fields (e.g. chicken litter ash)
as well ash input to chemical processing (e.g. sewage sludge ash)
- other sewage-recovered products to add ?
- contaminant limits, by-products, low carbon mineral fertilisers, etc,
www.phosphorusplatform.eu/regulatory
19. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 19
www.phosphorusplatform.eu
EU Fertilisers Regulation revision
A “CE” fertiliser can be sold anywhere in Europe … but
other products/materials can be used on fields
if authorised as a “national” fertiliser
under ‘Waste’ spreading authorisation
A material which is recognised as a “CE” fertiliser …
is granted ‘End-of-Waste’ status
20. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 20
www.phosphorusplatform.eu
National policies
Switzerland 2016 obligatory P-recovery from sewage sludge and
animal waste ash (or separate storage pending recovery)
Germany 2017: new sludge ordinance (AbfKlärV underway) will make
P-recovery obligatory for all sewage works > 50 000 p.e.
(see ESPP eNews n°7 http://www.phosphorusplatform.eu/scope-in-print/news/1408-enews7 )
Scope Newsletter n°118
http://www.phosphorusplatform.eu/scope118
21. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 21
www.phosphorusplatform.eu
National policies
Finland government 2017: objective to process 50%
of manure and sewage sludge for nutrient recycling
Sweden EPA proposed objectives:
2002 = 60% of sewage P to agriculture inc. in biosolids
2015 = 40% of sewage P and 10% of manure N
Denmark – waste strategy 2013
2018 = 80% reuse of sewage P to farmland
And 55-60% of household organic waste to biogas production
http://mmm.fi/en/recyclenutrients
22. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 22
www.phosphorusplatform.eu
Standards
CEN (European standards organisation):
- CEN/TC 308, /TS 13714, /TR 13097 – sludge management
- CEN/TC 165 WG40 – wwtp > 50 PT
- CEN/TC 223 & 260 - Soil improvers, fertiliser, etc
2017: CEN/SABE position on standards needs to support P-recovery
online at www.phosphorusplatform.eu/regulatory
2017 CEN/CLC/BT/JWG 11 standards needs for sustainable chemicals
for the circular economy (underway)
ISO (International Standards Organisation)
- ISO 275 sludge recovery, recycling,
treatment and disposal
Etc …
23. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 23
www.phosphorusplatform.eu
Organic contaminants in sewage biosolids
Priority challenge for ESPP:
more than half of EU sewage sludge is today recycled to land
- ESPP workshop on pharmaceuticals in sewage biosolids
Malmö 27/11/16 www.phosphorusplatform.eu/scope123
- EU consultation on pharmaceuticals in the environment
May 2017 http://www.phosphorusplatform.eu/organic-contaminants
- ESPP & Eureau position on need for R&D
into pharmaceuticals in biosolids:
- risks assessment
- fate in treatments
- EU consultation
on microplastics
http://www.eumicroplastics.com/
“Answers to the Sewage Sludge Questionnaire”, EurEau 4.10.2016 www.eureau.org under Positions/Reports
24. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 24
www.phosphorusplatform.eu
Obstacles for nutrient recycling in Dutch Legislation
Heavy metals legislation:
• More strict legislation in the Netherlands than obliged by EU
• For example: it is impossible to apply sewage sludge direcly on the
land, or other heavy metals issues for waste streams such as sugar
beets
Struvite:
• Discussions about the pathogens and medical wastes in struvite, no
clear framework yet, this is in progress, but still not in place
Manure products:
• Products from manure depend on EU legislation (Nitrates directive,
Fertilisers Regulation), once manure always manure situation,
hopefully new development in 2018 with EU guidelines on products
from manure treatment (“End-of-Manure-status”)
25. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 25
www.phosphorusplatform.eu
Obstacles for nutrient recycling in Dutch Legislation
End-of-waste:
• Still definition of waste, end-of-waste, by-products create difficulty
Manure market disturbed:
• Difficulties with the market which is disturbed because of the large
surplus of manure, creating obstecales for other fertiliser products
26. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 26
www.phosphorusplatform.eu
Positive developments in the Netherlands
2015 recovered phosphate catagory in Dutch fertilisers law
6th Action Programme Nitrates creates exception rule for products
that have a positive effect on the soil
Policy programme: Netherlands circular 2050 -> transition agenda’s
Living lab regions with space for experimenting – fertiliser free ‘Achterhoek’
27. 27European Sustainable Phosphorus Platform
Global nutrient recycling example
Dutch recovered struvite sailed back to south America to be used as fertiliser to grow cacao beans for chocolate factory in Amsterdam
(www.treshombresreep.nl)
28. 28European Sustainable Phosphorus Platform
Regional nutrient recycling example
Festival collected urine used for growing barley for the production of beer in Denmark (Pisner made by local brewery Norrebro
Bryghus, Copenhagen)
29. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 29
www.phosphorusplatform.eu
Dutch Success Stories in nutrient recycling
Success stories in the Netherlands www.nutrientplatform.org/succesverhalen
For Europe: www.phosphorusplatform.eu/successstories
30. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 30
www.phosphorusplatform.eu
Wastewater nutrient recycling
31. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 31
www.phosphorusplatform.eu
Manure nutrient recycling
32. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 32
www.phosphorusplatform.eu
Nutrient recovery from wastewater: opportunities &
challenges of EU regulatory context
Kimo van Dijk, European Sustainable Phosphorus Platform (ESPP)
kimovandijk@phosphorusplatform.eu
33. KNW Waternetwerk symposium "Resource recovery, just do it?", Wageningen, 9th
November 2017 - 33
www.phosphorusplatform.eu
ESPP: a coalition for action
• Objectives: sustainable phosphorus use & recycling
- global food security
- circular economy
- environmental protection
- healthy diet and food safety
• Bringing together:
- wide range of industries
- national & regional governments,
- knowledge institutes
- not for profit Platform
- funded by Members
• Actions:
- vision & awareness
- stakeholders & networking
- dissemination
- policy and regulation dialogue
34. 34European Sustainable Phosphorus Platform
Success story:
Waternet Amsterdam West sewage works
• AirPrex struvite precipitation
• Upstream of sludge digesters
• Operational savings:
150 000 € / year
• Improved sludge dewatering:
250 000 € / year
• Increased methane production
• Achievement of 1 mgP/l discharge
35. 35European Sustainable Phosphorus Platform
Success story:
Ecophos P-recycling from sewage sludge ash
• Pilot plant operational Varna, Bulgaria
• Produce DCP (Di Calcium Phosphate) for fertilisers, animal feed
• Full-scale plant under construction Dunkerque, France
capacity: 200 000 t/y DCP from low grade P-rock and ash
• Contract to treat 60 000 t/y ash from Netherlands (SNB – HVC Groep) = 4 000
t/y P
See SCOPE Newsletter 111 and www.ecophos.com
36. 36European Sustainable Phosphorus Platform
Success story:
Timac: struvite as maize starter fertiliser
• Fertiliser industry added-value for recycled nutrients
• NuReSys recovered struvite from potato processing
• Non-burning, enabling “ultra localisation” next to roots
• Micro-granulation
• Ammonium addition for nutrient balance
37. 37European Sustainable Phosphorus Platform
Success story:
Recophos – ICL
• Electrothermal production
of white phosphorus (P4)
from sewage sludge / ashes
• High-value raw material for chemicals:
fire safety, electronics, …
• Recophos FP7 pilot project
• Technology acquired by ICL March 2016
www.icl-group.com
http://www.prnewswire.com/news-releases/icl---next-step-towardssustainable-innovation-571973381.html
38. 38European Sustainable Phosphorus Platform
Success story:
REVAQ sewage treatment Certification
• > 50% Sweden’s sewage goes to REVAQ Certified sewage works
• Sludge digestate quality, monitoring,
information transparency criteria
• 3000 t/year phosphorus recycled to agriculture
http://www.iea-biogas.net/case-studies.html?file=files/daten-redaktion/download/case-studies/REVAQ_CAse_study_A4_1.pdf
39. 39European Sustainable Phosphorus Platform
Success story:
Friesland Campina milk cooperative, NL
• Biogas production and P-recovery from manure
• Bonus/malus in milk purchase prices
• Funding support for farmers’
manure treatment
investments
www.frieslandcampina.com
40. 40European Sustainable Phosphorus Platform
Success story:
ICL fertilisers Amsterdam & Ludwigshaven
• Use of secondary materials
in fertiliser production:
- meat and bone meal ash
- struvite
• Objective: 100% by 2025
• Pilot testing successful
• Industrial installations
(storage, handling) planned
www.icl-group.com
41. 41European Sustainable Phosphorus Platform
Success story:
SARIA UK – Kalfos
• P-fertiliser and soil conditioner
from combustion of animal by-products (MBM)
• Authorised for arable and grazing land
• 12 000 tonnes/year
http://www.kalfos.co.uk/
42. 42European Sustainable Phosphorus Platform
Success story:
NutriTrade Baltic local fish
• Local fisherman incited to catch cyprinids
- restore food web (algal grazing zooplankton)
- remove nutrients from the sea
• Promote new markets for local fish products:
- recipes, chefs, new processing routes & consumer products
• Biogas production from processing by-products
• Cost: c. 66 €/ kgP removed (not inc. sales)
Launched 2015. John Nurminen Foundation / NutriTrade
http://nutritradebaltic.eu/pilots/pilot-fish/
Editor's Notes
OLD
Different sources: Miterra-Europe, CAPRI, FAOSTAT, Eurostat, reports, articles and experts
P flow = physical flow x P content
‘Top down’ data integration VS ‘bottom up’
Assumptions were necessary
In general (take home message):
Large imports
Longterm accumulation
Little recycling (though high recycling of manure, and other flows in some specific countries)
Leaky losses
>>> Low P use efficiencies throughout the food system > high potential for better P management
Explaining the conceptual system: Right side imports (blue), Left side export (orange) and losses (red), upward flows and downward flows
Flows and stocks in Gg = Mkg = kton P, so not in P2O5
Explanation of each import flow, from the bottom to the top
In every sector primary P is use: mineral fertilizer, inorganic feed P additives, food P additives / fertilizer use elsewhere (“virtual P use”), detergents / chemical industry / fire retardants / matches
Mineral fertilizer the largest, animal feed + P additives significant, food and detergents small
Percentage of total import
IAp 18.40815
ICp 61.46693
IFp 11.0219
INF 9.103019
Mineral P rock based inputs
CP = mineral fertilizers = 1448 Gg P
AP = feed additives = 245
FP = food additives = 27
NF = detergents = 110
Explanation of each export flow:
Mainly export via food processing industry, as food items and animal feed materials, mainly between EU countries
Manure export for some countries such as the Netherlands, but intra trade
Percentage of total export
EAp 13.10174
ECp 2.008089
EFp 78.53402
ENf 6.356152
Explanation of each losses:
Largest losses in human consumption as solid (compost) and liquid organic waste (sewage) (52% of total losses, 77 % of total sector input)
Followed by food processing waste flows (residues, by-products, organic wastes) (29% total, 19% input)
Leaky losses in agriculture: leaching (7 % total, 2 % input)
Percentage of total losses
LAp 6.320538
LCp 6.669956
LFp 29.25992
LHc 51.73891
LNf 6.010671
System balance:
Gross import: 2362 ~2400
Gross export: 185 ~200
Net import: 2178 ~2200
Losses: 1135 ~ 1150
Accumulation: 1043 ~ 1050
The surplus is accumulating in (agricultural) soils (brown stock), which has been done for decenia. It is estimated that in the last century this accounts for a cummulative P surpluss of 150,000 ktons P
P use efficiency in the sectors (2005 relative)
Summary
CP: ~60 % of CP input in crop products
AP: ~ 20-30% in animal products, remainder mainly in manure which is cycled back with a high efficiency
FP: ~80% in food, feed or fertilizer products, at least not lost
NF: ~80% in non-food and detergent products
HC: 0% for adult humans, but for the waste industry it is ~23 % on average
Discuss internal flows. ~2500 kt P in harvest crop materials. 1/3 goes directly to the food industry, 2/3 is used as animal feed in animal production. Point at the flows that will be discusses in next slides, to give an overview.
Food flow is domestic food P supply not the dietary intake at the mouth level.
P flows in the EU-27 food system for 2005 in Gg P/year, showing the imports (I) , exports (E), losses of and internal upward/downward flows between sectors (indicated with square blocks), the width of the arrows representing the magnitude of the flow.
Europe is highly dependent on P imports
Increased soil P stocks
P efficiency and recycling is generaly low
High losses occur by (i) landfilling (ii) losses to hydrosystems
In total 1.6 kg/ca/year enters the households as food (1.1 kg), food additives (0.05), detergents (0.2) and pet food (0.3)
Since there is no accumulation in households apart from homecomposting, this amount also leaves the household as
Solid organic waste = biodegradable solid waste
Liquid organic waste = wastewater / sewage
That part of the food that is not eaten is part of the biodegradable solid waste, together with garden waste and other green waste, which could potentially be reused as compost
Reuse of organic waste is shown here as compost use as fraction of total potential organic waste quantity in %
EU average as red bar, 15 %
NL is doing very well with 65%, on the left side
Several eastern EU countries are not reusing any significant amount
Afther consumption the food P turns into excreta, and together with other waste water flows
In most EU countries this sewage flow is collected in a centralized sewarege system to flow to wastewater treatment plants
There it is treated, the P is, for the largest part, precipitated into the sludge, the solid fraction
Here communal sewage sludge destination as % of the total for
Red > application to land: which can include agricultural land, but not per definition
Blue > Incineration: monoincineration, co-incineration in power plants or the cement industry, the ashes are in principle not recycled back to agriculture
Green > Landfilling: which is less and less the case, in favour of incineration
On the right the EU average
40 % applied to land
30 % incinerated
15 % landfilled
The remainder to other destinations
Large differences between countries:
On the left countries with high % application to land, such as luxembourg, Ireland, Hungary
On the right countries with no return to land/agriculture, such as the Netherlands (prohibited since 1995, incineration by law), Romania and Malta
NL in 2011 overschot 27 Mkg P2O5
Various spatial scales: continent, country, region, farm and within fields
In the top layer of agricultural soils and other soils including gardens, parks, roadsides and allotments
2000-2500 kg P/ha accumulated cumulatively in agricultural soils = ~50 years primary fertilizer use
P saturated soils are situated in the central, southern en eastern parts of NL on mainly sandy soils
Linked to high concentration of livestock and manure surplus
Sequestration 56%
Accumulation 28%
Emissions 16%
Moreefficient and effective use of P in the system, sectors and processes
P is an example element to show nutrient scarcity and flows in society.
But micronutrients are also very important for food production and plant, human and animal health.
What about the scarcity of these nutrients?
The simplistic R/P ratio for the different nutrietns is shown here. Zinc has the lowest R/P ratio, with about 30 years. Mo the highest with about 50 years.
90% of P use is in agriculture. But for micronutrients this is in general not more then 10 %, 90 % is used in industries. Substituion and recycleing is possible, but at the moment still gets no attention.
Copper is the best known micro nutrient, which is relatively scarce at the moment, resulting in high prices and theft of coppor from buildings and infrastructure.
Molybdeum is a crucial element for the biological N fixation, so a shortage in Mo will affects also the N cycle.
Both copper and seleen are important for livestock in animal production. In most western countries micronutrients are supplemented to animal feeds.
Recent studies show that there is widespread deficiencies of micronutrients in human diets, also in the EU and USA.
Van de ca. 20 mogelijke micronutriënten voor planten en dieren hebben 6 een potentieel aspect van schaarste, namelijk: borium, kobalt, koper, molybdeen, selenium en zink (B, Co, Cu, Mo, Se en Zn).
Het mondiale gebruik van deze elementen in het voedselsysteem varieert van <1% tot 11% (Se en B) van het totale gebruik.
Binnen het voedselsysteem vindt recycling plaats van micronutriënten via dierlijke mest, gewasresten, compost en slib.
In bodems vindt niet-duurzame ophoping plaats van Cu en Zn via mest, vooral in gebieden met hoge veedichtheid.
Gebruik van micronutriënten in diervoeding is veelal hoger dan gepubliceerde voedernormen; verlaging vereist nader onderzoek en beleid in internationaal verband.
Prijsfluctuaties van seleen en borium zijn groot en wijzen op schaarste; recycling van beide elementen vindt echter nauwelijks plaats.
De verhouding ‘reserves / jaarlijkse productie’ (R/P) van B, Co, Cu, Mo, Se en Zn varieert van 20 tot 84.
De gerapporteerde relatief lage R/P van Zn (20-46) stemt niet overeen met de relatief lage en stabiele prijzen van Zn.
Voor alle micronutriënten gebruikt door de industrie zijn er alternatieven, behalve voor Co.
Door het lage gehalte in mengvoer hebben prijsfluctuaties van micronutriënten een beperkt effect op de voerprijs.