ECETOC Publication Highlights Scientific Perspectives on Developmental Neurotoxicity Testing and Future Regulatory Directions
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ECETOC Publication Highlights Scientific Perspectives on Developmental Neurotoxicity Testing and Future Regulatory Directions

Brussels, 1 October 2026 – ECETOC is pleased to announce the publication of a new review article in Archives of Toxicology titled “Scientific Perspectives on In Vivo Developmental Neurotoxicity T...
Welcome to Talia Neal-Walthall
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Welcome to Talia Neal-Walthall

We are pleased to welcome Talia Neal-Walthall to ECETOC as a secondee. Talia joins us to work on topics related to exposure, an area central to much of our current scientific programme. She will be wi...
HSSD Tool

HSSD Tool

This software was developed by a consortium of partners to facilitate the uptake of novel approaches to estimate aquatic threshold concentrations (e.g. the concentration at which 5% of the species are exposed above their EC50, HC5).
The Human Exposure Assessment Tools Database (heatDB)

The Human Exposure Assessment Tools Database (heatDB)

heatdb is a public directory of exposure data sources as well as available tools for exposure
NanoApp

NanoApp

ECETOC’s NanoApp is a tool designed to define the boundaries of sets of similar nanoforms and to generate a justification for the REACH registration.
Targeted Risk Assessment (TRA)

Targeted Risk Assessment (TRA)

The Targeted Risk Assessment (TRA) estimates exposures to workers, consumers and the environment that arise during a series of events.
TRA Task Force – Worker branch

TRA Task Force – Worker branch

Why? The Worker TRA Task Force has been active since 2019, delivering projects that advance the scientific basis of the Worker Targeted Risk Assessment (TRA) tool. Its overarching objective is to e...
Immunotoxicity assessment: Addressing Challenges and Advancing Methodologies [Workshop → Task Force]​

Immunotoxicity assessment: Addressing Challenges and Advancing Methodologies [Workshop → Task Force]​

Why?Regulatory assessment of immunotoxic properties of chemicals is a complex and challenging task​ Limited regulatory guidance exists​ Lack of industry and regulatory knowledge​...
Chronic fish case studies towards an IATA

Chronic fish case studies towards an IATA

Why?Hazard and safety assessments for the pelagic compartment often rely on in vivo studies using a single fish species, raising ethical concerns and uncertainty in terms of extrapolation....
Technical Report
30.09.1994

TR 062 – Ammonia Emissions to Air in Western Europe

TR 062 : Ammonia Emissions to Air in Western Europe | July 1994

Anthropogenic ammonia (NH3) emissions to the atmosphere in western Europe (EEC + EFTA countries) are estimated to be between 2.8 and 5.2 Mt NH3-N/year in the year 1990, with 4.0 Mt NH3-N/year as best estimate. Waste from farm animals (cattle, sheep, goats, pigs, poultry and horses) is the principal source of atmospheric NH3, as shown in Table 1.

Table 1 Origin and Quantity of Ammonia Emissions to Air in Western Europe in 1990

Emission
(Mt NH3-N/y)
Range
(Mt NH3-N/y)
Origin
(% of total)
Animal husbandry
stables and manure1.434
storage1.332
manure spreading0.38
grazing
Subtotal3.074
Fertiliser
production0.020.5
application0.512.5
Leaf emission from crops0.25
Miscellaneous0.38
Total4.02.8-5.2100

The estimate of NH3 emissions from animal husbandry is based on calculated and measured N excretions and losses, adjusted for national conditions when data are available. Fertiliser derived emissions are estimated from consideration of reactions between fertiliser compounds and soil, taking typical national characteristics of soil into account. Crops can both take up and emit NH3 from the leaves; net emission is probably about 1.5 kg NH3-N/ha/year, but can be larger when the weather during ripening is adverse. A variety of other minor sources also contribute to atmospheric NH3: fur animals and other minor groups of farm animals, pets, exhalations from human beings, domestic use of ammonium products, refrigeration, combustion, treatment of waste water and disposal of sludge. Such emissions are included in "miscellaneous emissions".

The emissions can only be crudely estimated, as they vary greatly with circumstances. Thus the estimates for the Netherlands have a range of uncertainty of approximately 30%. The range of uncertainty for other nations with fewer data useful for making emission estimates is probably even larger. The only source where the magnitude of NH3 emission is accurately known is that of the fertiliser industry, as most plants measure the emissions and report them to authorities.

The estimate of NH3 emissions in Western Europe from the animal sector is about 15% higher than the lowest of other recent estimates. This is well within the range of uncertainty of such estimates. The estimate of total emissions is about 20 to 25% higher than other recent estimates as items not covered by most other estimates are included (crops and miscellaneous).

Published estimates indicate that NH3 emissions in Western Europe increased by about 50% between 1950 and 1980. The emissions probably peaked around 1990. There are no EEC regulations for NH3 emissions, but national efforts and regulations are increasingly specifying rapid manure incorporation into soil after spreading; animal feed composition is better adjusted to avoid excessive N intake, and storage conditions for manures are being improved. Furthermore, fertiliser consumption is falling. Such measures should gradually reduce the emissions by about 20 to 30% of the 1990 level.