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best available technologies for manure treatment - Baltic Green Belt

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Best Available Technologies <strong>for</strong> <strong>manure</strong> <strong>treatment</strong> baltic sea 2020<br />

3: INFORMATION GATHERED<br />

3.3: Community plants <strong>for</strong> livestock<br />

<strong>manure</strong> <strong>treatment</strong><br />

Technologies that are not stand-alone <strong>technologies</strong><br />

and/or have clear economies of scale would typically<br />

have an advantage of being implemented via farmer<br />

cooperations or a service provider as off-farm <strong>manure</strong><br />

<strong>treatment</strong> plants.<br />

• Technologies that cannot stand alone would often<br />

be part of rather complex and high-tech solutions<br />

that would be complicated <strong>for</strong> farmers to handle<br />

along with their key production.<br />

• Technologies with a clear economy of scale, i.e.<br />

where <strong>treatment</strong> of a small amount per year is<br />

more costly than <strong>treatment</strong> of a large amount per<br />

year, see <strong>for</strong> instance Birkmose (2006), would<br />

often be too costly <strong>for</strong> farms of average sizes to<br />

invest in and to operate.<br />

Examples of these cases are livestock <strong>manure</strong> <strong>treatment</strong><br />

plants, where pig slurry is converted to purified<br />

water and different commercial/mineral fertilisers, <strong>for</strong><br />

instance nitrification-denitrification plants as seen in<br />

Spain, Holland and Belgium, purification plants as<br />

seen in Holland, or centralised biogas plants as seen<br />

in Denmark.<br />

Further, it is important <strong>for</strong> farms to handle risks<br />

associated with their business, and the larger investments<br />

they make in relation to their turnover, the<br />

more vulnerable are they to changes in the markets,<br />

regulations and other external factors.<br />

Remarks given by participants at the Roundtable<br />

discussion on 29 September generally expressed the<br />

opinion, that the project could promote larger community<br />

livestock <strong>manure</strong> <strong>treatment</strong> plants <strong>for</strong> combined<br />

<strong>technologies</strong>. This would take away the structural<br />

development pressure on pig producers, which would<br />

be a result in itself in relation to the environmental<br />

load of pig production. The rationale behind the<br />

remarks is that the structural development in the<br />

livestock production is <strong>for</strong>ced by the legislative burden<br />

on the producers, which more rationally can be dealt<br />

with by the large production units than the smaller<br />

ones. Furthermore, if the legislative burden en<strong>for</strong>ces<br />

use of specific <strong>technologies</strong>, then the economy of scale<br />

of the technology would <strong>for</strong>ce the smallest producers<br />

to go out of the market. It is also of importance <strong>for</strong><br />

many pig producers to develop their competences on<br />

animal husbandry, and to source out other activities, as<br />

<strong>for</strong> instance livestock <strong>manure</strong> <strong>treatment</strong>. There<strong>for</strong>e, by<br />

encouraging the livestock <strong>manure</strong> <strong>treatment</strong> <strong>technologies</strong><br />

as community plant solutions, would avoid an<br />

extra pressure <strong>for</strong> livestock farms <strong>for</strong> growing bigger in<br />

order to survive. The extra transport of slurry to and<br />

from a community plant would typically be balanced<br />

by advantages of a more rational slurry handling,<br />

increased value of the slurry etc. within a certain radius<br />

from the community plant.<br />

Additionally it should also be kept in mind that<br />

a major challenge with an environmentally sound<br />

disposal of the livestock <strong>manure</strong> is to distribute it at<br />

sufficiently large areas of agricultural land, as visualised<br />

in tables 1 to 4. There<strong>for</strong>e, a major advantage<br />

of community plants are actually, that they in reality<br />

functions as centres <strong>for</strong> regional re-distribution of<br />

livestock <strong>manure</strong>s, meaning that the logistics around<br />

the collection of pig slurry and distribution of treated<br />

<strong>manure</strong> ensures the distribution to <strong>for</strong> instance specialised<br />

plant producers without livestock production<br />

in the region. See also www.biovakka.fi.<br />

However, the off-farm livestock <strong>manure</strong> <strong>treatment</strong><br />

plants are actually moving the livestock <strong>manure</strong> <strong>treatment</strong><br />

from being a regulated issue to a non-regulated<br />

issue, at least in some cases. The IPPC directive does<br />

not, via the Annex 1 list of installations that needs<br />

environmental approvals, comprise off-farm livestock<br />

<strong>manure</strong> <strong>treatment</strong>.<br />

Off-farm livestock <strong>manure</strong> <strong>treatment</strong> plants should<br />

be listed in Annex 1 of the IPPC Directive as installations<br />

that require environmental approval because the<br />

deployed <strong>technologies</strong> have environmental impacts in<br />

general, and on N and P leaching in specific.<br />

3.4: Efficiency of BAT dissemination in<br />

relation to the IPPC Directive<br />

The following sections give a presentation of the<br />

in<strong>for</strong>mation gathered about the IPPC Directive,<br />

how the administration of it is organised, and of the<br />

BREF document.<br />

Additionally, reference is given to the annexes<br />

C and J with lists of people met and memorandum<br />

from roundtable discussion.<br />

27

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