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Chapter 6: Waste

Management of Animal By-products

Animal by-products are regulated because of the risk

they pose to human and animal health.

Animal by-products (ABPs) are defined as “entire bodies

or parts of animals, products of animal origin or other

products obtained from animals that are not intended for

human consumption”. ABPs can present a risk to human

and animal health and their use or disposal is covered by

EU legislation.

Approximately 500,000 tonnes of raw ABPs is produced

in Ireland each year and is mainly rendered to produce

meat-and-bone-meal (MBM) and tallow. Other ABPs that

do not spring directly from the meat industry, such as

former foodstuffs, are more commonly used as feedstock

for composting (DAFM, 2015).

In 2014, renderers accepted 226,000 tonnes of Category 1

material (high risk) and 250,000 tonnes of Category 3 (low

risk) material. Processing of Category 1 material produced

61,000 tonnes of MBM and 27,000 tonnes of biofuel.

Processing of Category 3 material yielded 70,000 tonnes

of meal for pet food and 33,000 tonnes of tallow used

for animal feed and industrial uses (Federation of Irish

Renderers, 2016).

Hazardous Waste Management

Prevention comes first but Ireland is dependent on

exporting for treatment.

The current National Hazardous Waste Management

Plan (NHWMP) for 2014‑2020 (EPA, 2014b) sets out the

priorities to improve the management of hazardous waste,

including hazardous waste prevention, maximise the

collection of hazardous waste, strive for self-sufficiency

in hazardous waste management and minimise the

environmental, health, social and economic impacts of

hazardous waste generation and management.

There is no commercial hazardous waste landfill in the State,

and there are limited hazardous waste treatment operations

(these are mainly used for oil recovery, healthcare waste

treatment and solvent reclamation), meaning that Ireland

is dependent on export for treatment of many hazardous

waste streams. The NHWMP identifies three strategic needs

if additional hazardous waste is to be treated in Ireland:

(1) expansion of physico-chemical treatment, (2) addressing

the deficit in thermal treatment capacity, and (3) securing

long-term disposal arrangements for hazardous waste streams

not suitable for thermal treatment or recovery. Ireland would

be vulnerable in the event of a crisis such as an infectious

disease outbreak. Figure 6.8 shows the destination of

exported hazardous waste in 2014 (EPA, 2016a). The majority

of waste exports were to the UK, Germany and Belgium.

Figure 6.8

Destination of Exported Hazardous

Waste, 2014 (Source: EPA, NTFSO)

Great Britain

37%

Germany

28%

Belgium

25%

Netherlands

5%

France

3%

Northern Ireland

1%

Denmark

<1%

Northern

Ireland

Great Britain

Germany

Denmark

Belgium

France

Netherlands

The amount of hazardous waste generated, and its treatment

pathways, have remained relatively unchanged in recent

years (Figure 6.9). An example of waste treated on site of

generation is waste solvent incinerated at industrial facilities.

Figure 6.9

Treatment of Hazardous Waste, 2014

(Source: EPA)

Exported

44%

Treated on site of generation

27%

Treated at commercial facilities

29%