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Emission intensity of the domestic sector in Europe

Indicator Specification Created 05 Apr 2013 Published 24 Feb 2014 Last modified 05 Mar 2015, 02:56 PM
Contents
 

Assessment versions

Published (reviewed and quality assured)

Justification for indicator selection

In order to restore receiving waters to their former state, both point and diffuse pollution sources need to be further reduced. Reducing pollutant discharges from municipal and industrial WWTPs remains a central element in decoupling pressures on the aquatic environment from human activity (urban development). This is particularly true for nitrogen and phosphorus, which cause the eutrophication of freshwater and marine ecosystems. Results from large inland and marine catchments show that municipal wastewater constitutes about 75% of the point source discharges of both nitrogen and phosphorus. as a result of implementation of the Urban Waste Water Treatment Directive (UWWTD), the majority of wastewater plants in northern and central Europe now apply tertiary treatment. Elsewhere in the EU, particularly in the south-east, the proportion of primary and secondary treatment is higher. While considerable progress has been made in implementing the UWWTD, full compliance is yet to be achieved, especially in the new Member States.

The consequences of economic activities with regard to water quality and quantity have been analysed under the WFD in the River Basin Management Plans. Research on the link between water status (quality and quantity), relevant pressures and their economic driving forces provides an important basis for decision making and the prioritisation of measures with regard to achieving the objectives of the WFD. Moreover, it can help to indicate whether the particular driver is decoupled from its environmental impact. Easily understandable indicators will be necessary to provide signals and measure progress in improving resource efficiency.

The emission of nutrients from wastewater treatment plants provides an indication of potential water pollution. Human activity - the driver - is, in this indicator, represented by population size.

Scientific references:

  • No rationale references available

Indicator definition

This indicator is used to illustrate the emission intensity of the domestic sector (household plus services), expressed as the amount of discharged pollutant from wastewater treatment/or discharged without treatment per inhabitant per year. Furthermore, the indicator shows a decoupling of the emission of nutrients (nitrogen and phosphorus) and population growth across Europe.

The values of change (increase/or decrease) in discharged load between 1990 and 2009 (expressed in percentages, where values in 1990 = 100%) are plotted against the values of change in population growth.

Absolute decoupling occurs when the environmentally relevant variable is stable or decreasing while the driving force is growing. Relative decoupling occurs when the growth rate of the emission is positive, but less than the population growth rate.

Units

Emission intensity is expressed in kilogrammes of pollutant per inhabitant per year. Changes in pollutant emissions from households between 1990 and 2009 are expressed in percent, where the values recorded in 1990 represent 100%. Changes in population between 1990 and 2009 are expressed in percent, where the values recorded in 1990 represent 100%.

Policy context and targets

Context description

In March 2010, the European Commission issued ‘Europe 2020 strategy’ - the European Strategy for smart, sustainable and inclusive growth. It highlights – among other things - the need for a more resource efficient economy. The “Flagship initiative” under the Europe 2020 strategy, called “A resource efficient Europe”, establishes resource efficiency as the guiding principle for EU policies on energy, transport, climate change, industry, commodities, agriculture, fisheries, biodiversity and regional development.   The Roadmap to a Resource Efficient Europe defines medium- and long-term objectives to achieve efficient resource use in the region. Decoupling, in the sense of breaking the link between economic growth and resource use, is a central concept of the strategy for making Europe resource efficient. The 2050 vision and the objectives for 2020 are to be addressed in the sector initiatives that shall contribute to the resource-efficient Europe Flagship Initiative (i.e. the 7th EU Environmental Action Programme or the revision of the Common Agriculture Policy, Water Framework Directive and Groundwater Directive).

Targets

The Urban Waste Water Treatment Directive (UWWTD; 91/271/EEC) aims to protect the environment from the adverse effects of urban wastewater discharges. It prescribes the level of treatment required before discharge and has to be fully implemented in the EU-15 countries by 2005 and in the ten new Member States by 2008 - 2015. The directive requires Member States to provide all agglomerations of more than 2 000 population equivalent with collecting systems, and all wastewaters collected to be provided with appropriate treatment by 2005. Secondary treatment (i.e. biological treatment) must be provided for all agglomerations of more than 2 000 population equivalent that discharge into fresh waters, while more advanced treatment (tertiary treatment) is required for discharges into sensitive areas.

The achievements through the UWWTD have to be seen as an integrated part of objectives under the Water Framework Directive (WFD), which aim at a good ecological and chemical status for all waters by 2015. That means that more stringent emission targets may be set in case it is needed for achieving the good status.

EU wide targets related to the nutrient emission intensity of domestic sectors, or the decoupling of nutrient emission from population growth have not been set.

Related policy documents

  • European Waters – Assessment of Status and Presures
    This report's results present good and robust European overviews of the data reported by the first RBMPs, and of the ecological status and pressures affecting Europe's waters. Europe's waters are affected by several pressures, including water pollution, water scarcity and floods. Major modifications to water bodies also affect morphology and water flow. To maintain and improve the essential functions of our water ecosystems, we need to manage them well.
  • Roadmap to a Resource Efficient Europe
    Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions. Roadmap to a Resource Efficient Europe.  COM(2011) 571  
  • Urban Waste Water Treatment Directive
    Council Directive 91/271/EEC of 21 May 1991 concerning urban waste-water treatment The Urban Waste Water Treatment Directive (UWWTD) aims to protect the environment from the adverse effects of urban wastewater discharges.

Key policy question

Is nutrient emission in water from the domestic sector decoupling from population growth?

Specific policy question

Is the nutrient emission intensity of the domestic sector decreasing?

Methodology

Methodology for indicator calculation

For overall emission load the following formula was used:

Ntotdischarged= Ntot(coll.system)+Ntot(without treatment)+ Ntot(IAS)+Ntot (primary)+ Ntot(secondary)+ Ntot(tertiary)

 

Where  Ntotdischarged  is a total annual nitrogen load discharged from collecting systems or wastewater treatment plants [kg/y]

 

Ntot(coll.system) is a total annual nitrogen load discharged from collecting systems without treatment [kg/y]

 

Ntot (primary) is a total annual nitrogen load discharged from wastewater treatment plants with primary treatment [kg/y]

 

Ntot(secondary) is a total annual nitrogen load discharged from wastewater treatment plants with secondary treatment [kg/y]

 

Ntot(tertiary) is a total annual nitrogen load discharged from wastewater treatment plants with tertiary treatment (N, P removal)  [kg/y]

 

For calculation of the Ntot(coll.system) and Ntot(without treatment) the population equivalent for nitrogen and phosphorus was used. For calculation of the Ntot(IAS), removal efficiencies, corresponding to the primary treatment were applied.

 

Two approaches were used to calculate nutrient discharged loads (Ntotdischarged and Ptotdischarged) of the domestic sector:

  • The "default” approach is based on the percent values of the population connected to different types of waste water treatment (Based on Eurostat Water Statistics), and the default values of nutrient population equivalent and removal efficiency per type of treatment (primary, secondary, and tertiary).

p.e. for Nitrogen= 12 g/d

p.e. for Phosphorus=2,5 g/d


Removal efficiency :

Nitrogen (primary)=0,15

Nitrogen (secondary)=0,35

Nitrogen (tertiary)=0,70

Phosphorus (primary)=0,10

Phosphorus (secondary)=0,20

Phosphorus (tertiary)=0,80

  • A second approach was used to illustrate the actual emissions from urban treatment plants based on data reported voluntarily by 13 Member States (BE, CY, CZ, DE, DK, EE, ES, IT, LT, LU, LV, NO,  SI) under the UWWTD (2011 data request). Complete datasets on the emission load discharged from treatment plants (size ≥2000 p.e) were available for AT, NL, CZ, DE, DK, LT, LU and SI.

For these eight countries, the total discharged load was calculated according to the following formula:

Ntotdischarged= Ntot(WWTPs) + Ntot(coll.system)+Ntot(without treatment)+ Ntot(IAS)

Where Ntot(WWTPs) corresponds to the sum of discharged loads reported under the UWWTD for individual treatment plants normalised by overall entering load in population equivalent (to make adjustment for industrial share in the load entering into urban waste water treatment plants) and finally multiplied by the total population connected to UWWTPs. 

Calculation of Ntot(coll.system), Ntot(without treatment) and  Ntot(IAS) is explained above.

For the remaining five Member States, the gap analysis was done. Where gaps (missing data on discharged load) did not exceed 30% of the total entering load (EE, NO), data gap filling was done, with emission load values calculated (for each type of treatment) from the formulae specified below. The formulae were derived from the 13 Member State emission load datasets (for UWWTPs > 2000 p.e.) .

The formulae used for calculation of the Ntot  and Ptot (primary), Ntot and Ptot (secondary), Ntot  and Ptot (tertiary) express the annual nutrient load discharged as a function of the reported entering load the treatment plant, (L) [p.e].

The units for the emission factors listed below are kg/y per population equivalent entering load and the emissions include the proportions from households, services as well as connected industry.

Ntot(primary)= 0,004*L

Ntot(secondary)=0,0012*L+1,213

Ntot(tertiary)=0,0014*L, for tertiary treatment with N removal

Ntot(tertiary)=0,0009*L+9,43318, for tertiary treatment with P removal

Ntot(tertiary)=0,0008*L , for tertiary treatment with N and P removal

 

A similar approach was applied to the calculation of the total phosphorus discharged load.

Ptot (primary)= 0,00009*L

Ptot(secondary)=0,0002*L+0,1373

Ptot(tertiary)= 0,0001*L+1,1658, for tertiary treatment with N removal

Ptot(tertiary)=0,0001*L, for tertiary treatment with P removal

Ptot(tertiary)=0,00005*L+0,4182, for tertiary treatment with N and P removal

 

Methodology for gap filling

See the alternative approach (above) based on formulae derived from available emission load data in the UWWTD Waterbase .


 

Methodology references

No methodology references available.

Data specifications

EEA data references

External data references

Data sources in latest figures

Uncertainties

Methodology uncertainty

  • The nutrient population equivalent may vary among European states and over the stated time period. This variation is not included in the pollution load generation based on Eurostat data. Nutrient removal efficiency is more likely higher, in some countries, than the default values used for the calculation and may also have developed over the time period for the same treatment types.
  • Use of actual emissions reported under the UWWTD would be more suitable for the indicator (as documented by additional assessment). However, the load data reported under the UWWTD is not available for all Member States, nor for the required temporal coverage (i.e. 1990s - dataset incomplete).
  • Effluent from the UWWTPs may also include different shares of loads attributed to services and industries, which affect emission intensity values. This impact on the indicator could be further reduced if the industrial load proportion for the relevant parameters could be excluded before normalising per inhabitant connected to the UWWTP.

Data sets uncertainty

  • An older version of Eurostat JQ was used for the assessment (population connected to wastewater collection and treatment systems, [env_watq4] version June 26, 2013), as it included data covering the period from 1990s to 2010s. The dataset on population connected to wastewater collection and treatment systems, which is currently available in Eurostat, contains data covering the period from the 2000s. The indicator will be updated once the dataset in Eurostat covers the entire period analysed.
  • Based on comparative analysis between data reported under SoE Emissions ( http://rod.eionet.europa.eu/obligations/632,  http://www.eea.europa.eu/data-and-maps/data/waterbase-emissions-2 ) for seven countries (EE, LT, LV, NL, RO, SE and SI) and emissions reported under the UWWTD, differences were typically 20-25%, however, major inconsistencies for P-emissions were observed for NL and SI.

 

Rationale uncertainty

No uncertainty has been specified

Further work

Short term work

Work specified here requires to be completed within 1 year from now.

Work description

Short-term work: Indicator specification should be amended on the basis of country review. Encourage complete reporting of the emission load data under the UWWTD. Variability of the emission factors across Europe should be investigated . Inconsistencies with SoE emissions data as well as potentials for using this dataflow as a source should be investigated within Eionet.

Resource needs

No resource needs have been specified

Status

Not started

Deadline

2013/12/15 01:00:00 GMT+1

Work description

Long-term work: Decomposing the indicator to illustrate the effect of key factors influencing the emission intensity of domestic sector.

Resource needs

No resource needs have been specified

Status

Not started

Deadline

2014/12/15 00:00:00 GMT+1

Long term work

Work specified here will require more than 1 year (from now) to be completed.

General metadata

Responsibility and ownership

EEA Contact Info

Bo Jacobsen

Ownership

European Environment Agency (EEA)

Identification

Indicator code
WREI 002
Specification
Version id: 1
Primary theme: Water Water

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Frequency of updates

Updates are scheduled every 2 years

Classification

DPSIR: Pressure
Typology: Efficiency indicator (Type C - Are we improving?)

Related content

Data references used

Data used

Latest figures and vizualizations

Relevant policy documents

Geographic coverage

European Environment Agency (EEA)
Kongens Nytorv 6
1050 Copenhagen K
Denmark
Phone: +45 3336 7100