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Each of us releases around 1.5 grammes of phosphorus
per day into sewage, and
sewage also contains phosphorus from food wastes, organic materials, detergents
and industrial sources. Today, around one quarter of the phosphates in
municipal sewage in Europe are already effectively recycled as fertiliser
values to agriculture :
39-45% of phosphates in EU sewage are removed and then 53% of sewage sludges are reused in
agriculture.
National objectives
Both Germany and Sweden have announced national
objectives for phosphorus recovery for recycling from sewage.
Sweden’s action plan centres on recycling P to land through sewage sludge use
in farming, whereas the German Federal Environment Office (UBA) suggests
recovery for recycling in sewage works. Phosphate recovery is now also officially
included in UK Environment Agency strategy.
The
German Federal Environment office announced in March 2003 the objective of
developing phosphorus recovery for recycling from sewage and other wastes. The
press release followed the organisation of a symposium (Berlin, 6-7 Feb. 2003)
which brought together around one hundred German experts, regulators and water
industry operators to discuss P-recovery from sewage and wastes. A paper
presented by UBA at this conference suggests that existing taxes on waste water
could be used to support the technical development of phosphorus recycling, and
that P-recovery and recycling requirements could be instated within the terms
of existing waste and water legislation.
Sweden has also announced the objective of developing phosphorus
recycling, but the Swedish action plan published in 2002 proposes to achieve 60%
P-recycling by 2015 largely by re-use in agricultural by sewage sludge
spreading. The Agency estimates that at present 46% of sewage phosphorus is
already effectively recycled through agricultural sludge application. Sweden
hopes to move back to agricultural sludge spreading by implementing sludge quality
criteria which. The environmental courts in Sweden have already begun to condition
operating authorisations for sewage sludge incineration on the implementation
of phosphate recovery. The cities of Ekilstuna, Falun, Halmstad, Malmö,
Södertälje and Stockhom are already subject to such a requirement, or the issue
is now being addressed.
The European
detergent industry has also fixed as an objective that 25% of detergent
phosphates should come from recycling within a decade.
This places phosphates in a unique position as a potentially sustainable
detergent component.
Phosphorus recycling
The application of the EU Urban Waste Water
Treatment Directive 91/271 means that phosphates in domestic waste water, be
they from detergents, food wastes or from natural bodily emissions (the main
source) are effectively no longer an environmental issue. This Directive
requires that phosphates be removed wherever sewage works situated in
conurbations of more than 10,000 “person equivalent” (that is villages or
groups of villages or more than around 6-7,000 population) discharge into
surface waters which are susceptible or potentially susceptible to
eutrophication. That is, phosphates must be removed from sewage wherever they
are a potential environmental issue. These requirements are effectively
confirmed and reinforced by the recent EU Water Framework Directive.
Where sewage
sludges are spread on agricultural land, phosphates are already effectively
recycled, as fertilisers contributing to crop growth. However, agricultural
re-use of sewage sludge is diminishing throughout Europe, for a variety of
reasons independent from phosphorus contents.
Agricultural
re-use of sewage sludge is diminishing both for logistic, environmental and
social reasons. Around big cities, there is simply not enough farmland
available to spread sludge production. In other cases, spreading is limited by
levels of contaminants in sewage sludge, in particular heavy metals. More
generally, there is a tendency for farmers to refuse sewage sludge, often under
pressure from supermarkets and food processing companies, in response to
varying consumer concerns from hormones to pharmaceutical residues (even though
there may be no rational basis for such perceived risks ).
Where sludges are
no longer used on land, they will increasingly have to be treated by
incineration or other thermal processes. This will mean that phosphates become
a dead weight in the thermal treatment, and then finish their life in sludge
incineration ash, consigned to landfill. Where sewage sludge is disposed of by
use as an energy source in the cement industry, phosphates are not only a dead
weight but even a problem, as they affect the setting properties of the cement.
Biomass production
Phosphorus can
also be recycled from sewage by using it, either directly, or as sewage
sludges, as a fertiliser and support for the growth of plants or biomass, which
can then be used as animal feed, to produce compost, as an energy source, or as
a raw material for industrial processes. Such systems can use sewage, and so
recycle phosphorus and other nutrients, to produce algal or water plant
biomass, wood or other energy crops, etc.
Phosphorus recovery
Phosphate recovery
consists of extracting phosphates from the sewage works in a form which can be
used either industrially (as a raw material in the phosphate industry) or as a
fertiliser (either directly as recovered, or after further processing or mixing
by the fertiliser industry). P-recovery is feasible, for example, by precipitation
of calcium phosphates, struvite (MAP, magnesium ammonium phosphate) or
potassium struvite (potassium ammonium phosphate, K-struvite).
Phosphorus
recycling potentially offers economic returns through the commercial value of
the recovered product, through economies in sludge management and improvements
in sewage works operation.
Cost/benefits of phosphorus-recovery :
| Costs |
Returns
|
Recovery reactor
investment
|
Value
of recovered product (phosphate raw material or fertiliser)
|
Chemical costs for
reactor operation (may be low or zero depending on
reactor design and availability of reagents locally
as wastes)
|
Reductions
in sewage sludge and reductions in sludge incineration ash |
| Possible
modifications to sewage works configuration |
Improved
sludge management (eg. P is an obstacle to use in cement
industry and lower P in sludge increases land
spreading possibilities) |
| Operating costs |
Improved
sewage works operation (nuisance deposit avoidance, improved
biological P removal) |
A number of full
scale or pilot recovery installations are already operational in sewage works
treatment centres in several countries, recovering phosphates as calcium
phosphates (Geestmerambacht, The Netherlands), as struvite (Canada, UK, Italy,
Japan …) or as potassium struvite from veal calf manures (Putten, The
Netherlands).
The industrial use
of recovered phosphates has been successfully tested and is operational at the
Thermphos International plant, Vlissingen, The Netherlands (use as a secondary
raw material of recovered calcium phosphates from Geestmerambacht sewage works
since 1998, and currently testing of the use of sewage sludge incineration
ashes from The Netherlands, Germany).
Fertiliser value
Struvite can be
used directly as a fertiliser, or mixed with other compounds to provide
specific fertiliser properties. Struvite produced by recovering phosphate is in
some circumstances sold with an added marketing value as a “green recycled”
product, as in the UK, Japan and recently Canada.
Market prices for
the sale of such recovered struvite have been reported as:
- 464
€/tonne according to Schu et al., Australia, 2006
- 2,700
yen = 166 €/tonne gross sale price for sewage-recovered struvite reported
in Japan, 2001. The fertiliser,
after mixing with other products to provide a potassium content, is then
sold to the public for 1 – 2,000 yen (3,000 – 6,100 €) per 20kg bag.
- UK£
217 – 865 = 320 – 1290 € UK, 2000
Agronomic studies
of the fertiliser value of struvite are summarised in SCOPE Newsletter n° 43 at www.ceep-phosphates.org and further
recent trials of struvite as a fertiliser are summarised in Scope Newsletters
n°s 69 (wheat), 68 (rye grass), 60 (field tests on potatoes),
50 (oats and rye grass). These suggest that struvite is as good a phosphorus
source as commercial fertilisers, comparable to Triple Super Phosphate and
maybe better than DCP (Di Calcium Phosphate)
Working together
A number of international conferences have
brought together R&D teams and scientists, water and animal waste industry
(water companies, engineering companies) and regulators to exchange information
about the different technical routes, economics and operational feasibility of
phosphorus recovery.
Papers from these different conferences are
available on this website, see under “Conference documents”.
Closing the loop
Phosphate
recycling is essential for the sustainable future of our society as it is
inconceivable to continue to simply throw away a non-renewable resource which
is essential for life. Whilst this is a long term objective, increasing
economic pressure on sewage sludge disposal and on water industry environmental
life-cycle responsibility are likely to bring phosphate recycling into the
short-term future.
The best way to
recycle phosphorus is agricultural re-use of sewage solids, but problems with
logistics (lack of farmland around big cities), contamination with pollutants
and consumer resistance mean that this route is fast disappearing in many
countries. In situations where agricultural re-use is not possible, industrial recycling
of phosphates offers a sustainable solution. Phosphates from sewage (of human,
food waste, detergent or industrial origin, recovered together) or from animal
manures can be industrially recycled into either fertilisers or into industrial
phosphate applications (flame retardants, detergents, electronics …).
Industrial P-recovery
processes already in operation or testing
Japan :
- Kurita Water Industries[i],
Fukuoka City West and Washiro
- Unitika Ltd[ii],
Shimane/Lake Shini, Fukuoka East, Osaka South Ace.
The Netherlands - Geestmerambacht (230,000
pe.)[iii]
The phosphates are recovered as calcium phosphates and re-used as a raw
material by the phosphate industry (Thermphos International in Vlissingen).
Canada and USA – Goldbar, Edmonton, Alberta
(commissioned May 2007),
with further pilot plants being tested in Hampton Roads / Nansemond, Suffolk,
Virginia ; Lulu Island, Richmond, British Columbia ; Penticon, British Columbia
;Durham, Oregon [iv]
UK - Thames Water, Slough sewage works
(250.000 pe.) – struvite recovery[v]
Italy - Treviso sewage works, Italy –
struvite recovery[vi]
The Netherlands – Putten
full scale plant recovering potassium struvite from 700,000 tonnes/year of veal
calf manures
The Netherlands – Peer
recovery of struvite from 15,000 tonnes of pig manure per year[vii]
Belgium – Aalst – DHV P-recovery unit
at Amylum Europe starch factory[viii]
Pilot plants are also currently being developed or tested across the
world :
- Brisbane Water, Australia at Owley Creek
sewage works[ix]
- Mill Creek, Cincinnati, Ohio[x]
- Si-Ellen, Idaho and Werkhoven,
Washington, dairy units[xi]
- City of Kitakyushi, Hiagari sewage works,
Japan[xii]
- Morigasaki sewage works, Tokyo, Japan –
Ebara process[xiii]
- Osaka City central sludge treatment
installation, Japan [xiv]
- Berlin, Germany [xv]
- Italy – Massafra sewage plant, using
REM-NUT ion exchange process[xvi]
- The Netherlands – energy and
P-recovery from 350,000 tonnes per year of poultry litter[xvii]
- Japan National Institute of Livestock and
Grassland Management
2 years operating experience precipitating struvite from piggery wastes[xviii]
North Carolina – pilot struvite recovery
reactor sized for a 1,000 head pig farm[xix]
English translation of Germany UBA documents 2003 under Library on
this website
Sweden: By 2015 at least 60% of phosphorus compounds present in
wastewater will be recovered for use on productive land. At least half of this
amount should be returned to arable land. http://www.miljomal.nu/english/obj15.php
[11] Shu et al., “An
economic evaluation of phosphorus recovery as struvite from digester
supernatant”, Bioresource Technology 97, pages 2211-2216, 2006
[12] Ueno &Fuji,
“Three years experience of operating and selling recovered struvite from
full-scale plant”, Environmental Technology, Vol. 22. pp 1373-1381
[13] Gaterell et al,
“An economic and environmental evaluation of the opportunities for substituting
phosphorus recovered from waste water treatment works in existing UK fertiliser
markets”, Environmental Technology vol. 21 n° 9 pages 1067-1084, 2000.
J. Hammond et al. « Is struvite a valuable phosphate source
for agriculture”, available on this website under “Library”
[i] Personal
communication, Satoru Ishiduka, Kurita Water Industries Ltd, Japan
[ii] T. Taruya,
Japan Sewage Works Association et al., IWA Congress, Paris, 3-7 July 2000
[iii] A. Giesen,
Environmental Technology vol. 20, n°, July 1998
[vi] P. Battistoni
et al., “Auto-nucleation and crystal growth of struvite in a demonstrative
fluidized bed reactor (FBR)”, Environmental Technology, vol. 26, pages 975-982. http://www.environtechnol.co.uk/contents.htm and full report “Treviso P-recovery full report 2003” under Library on this
website
[ix] E. von Münch et al., Wat. Res. Vol. 35 n°1, 2000
[xii] Y. Matsumiya
et al., J. Ciwem n° 14, Aug. 2000
[xvi] “A
phosphate-selective sorbent for the REM NUT process: field experience at Massafra Wastewater Treatment Plant”, D.
Petruzzelli, L. Liberti et al., Reactive and Functional Polymers 60 (2004),
pages 195-202
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