Material Database:
BCR-484 - Sewage Sludge amended (Terra Rossa) Soil
|
|
Type |
Certified reference material |
Producer |
JRC - Joint Research Centre
|
Status |
Available |
Material |
Powder |
Reference |
BCR-484 |
Catalog (Web) |
https://irmm.jrc.ec.europa.eu/rmcatalogue/detailsrmcatalog ue.do?referenceMaterial=0484%2B%2B%2B%2B%2B%2B%2B%2B |
|
|
Description
|
The sampling of the material (terra rossa soil) was carried out in 1991 in a farm plot amended with sewage sludge from a water treatment centre located in North-East Catalonia, Spain. Samples were taken from an area of about 250 m2 with a small shovel to a depth of about 10 cm and sifted on-site by hand through a 0.5 cm nylon sieve into polyethylene bags. The samples were taken to the Water Treatment Centre and again sieved through a 20 cm diameter nylon sieve with a mesh size of 2 mm into polyethylene bags for transport to the laboratory Analytical Chemistry of the University of Barcelona. The soil was then spread over a polyethylene sheet and air-dried at 30 oc for one week to a final water content of 1.5 %. The air-dried soil was packed into a 100 litre polyethylene container, tighly sealed and dispatched to the Environment Institute of the Joint Research Centre of Ispra (Italy) for homogenisation and bottling. 4 The air-dried ( < 2 mm) soil sample was transferred in total (91 kg) into a mixing drum filled with dry argon and placed on roll-bed capable of handling 100 kg samples. The homogenisation of this soil, with its large spread of particle sizes, from just below 2 mm down to fractions of a micrometer, required particular care. This procedure was, therefore, carried out by mixing in the drum for over 4 weeks. The bottling procedure was performed as follows: to prevent segregation of fine particles, 10 samples were taken from the centre of the drum immediately upon stopping the rotation of the mixing drum, and were placed into 10 pre-cleaned brown glass bottles, each containing a minimum of 70 g of soil. The drum was again rotated for a further two minutes and a further 10 samples were subsampled in the same way into bottles. The subsampling and bottling operation was continued until 1000 bottles of the soil were obtained. One hundred bottles, selected sequentially over the whole bottling procedure were sent to the Macauley Land Use Research Institute for homogeneity and stability testing. keywords: environmental materials , soil/sediment , biosolids , trace elements , heavy metals , fractionation analysis |
Package |
70 g
|
Parameter
|
Analyte | Cadmium | Specification | Acetic acid extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 0.48 ± 0.04 | |
Analyte | Cadmium | Specification | EDTA extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 0.51 ± 0.03 | |
Analyte | Copper | Specification | Acetic acid extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 33.9 ± 1.4 | |
Analyte | Copper | Specification | EDTA extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 88 ± 4 | |
Analyte | Lead | Specification | Acetic acid extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 1.17 ± 0.16 | |
Analyte | Lead | Specification | EDTA extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 47.9 ± 2.6 | |
Analyte | Nickel | Specification | Acetic acid extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 1.69 ± 0.15 | |
Analyte | Nickel | Specification | EDTA extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 1.39 ± 0.11 | |
Analyte | Zinc | Specification | Acetic acid extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 193 ± 7 | |
Analyte | Zinc | Specification | EDTA extractable element content | Parameter | Certified value | Unit | mg/kg | Result | 152 ± 7 | |
|
|