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Lager, Tanja (2004): Experimental data from column and batch samples. PANGAEA, https://doi.org/10.1594/PANGAEA.776653, Supplement to: Lager, T (2004): Predicting the source strength of recycling materials within the scope of a seepage water prognosis by means of standardized laboratory methods. Berichte aus dem Fachbereich Geowissenschaften der Universität Bremen, 239, 141 pp, urn:nbn:de:gbv:46-diss000101449

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Abstract:
The presented thesis was written in the frame of a project called 'seepage water prognosis'. It was funded by the Federal Ministry for Education and Science (BMBF). 41 German institutions among them research institutes of universities, public authorities and engineering companies were financed for three years respectively. The aim was to work out the scientific basis that is needed to carry out a seepage water prognosis (Oberacker und Eberle, 2002). According to the Federal German Soil Protection Act (Federal Bulletin, 1998) a seepage water prognosis is required in order to avoid future soil impacts from the application of recycling products. The participants focused on the development of either methods to determine the source strength of the materials investigated, which is defined as the total mass flow caused by natural leaching or on models to predict the contaminants transport through the underlying soil. Annual meetings of all participants as well as separate meetings of the two subprojects were held.
The department of Geosciences in Bremen participated with two subprojects. The aim of the subproject that resulted in this thesis was the development of easily applicable, valid, and generally accepted laboratory methods for the determination of the source strength. In the scope of the second subproject my colleague Veith Becker developed a computer model for the transport prognosis with the source strength as the main input parameter.
Related to:
Delay, Markus; Lager, Tanja; Schulz, Horst D; Frimmel, Fritz H (2007): Comparison of leaching tests to determine and quantify the release of inorganic contaminants in demolition waste. Waste Management, 27(2), 248-255, https://doi.org/10.1016/j.wasman.2006.01.013
Lager, Tanja; Delay, Markus; Karius, Volker; Hamer, Kay; Frimmel, Fritz H; Schulz, Horst D (2006): Determination and quantification of the release of inorganic contaminants from municipal waste incineration ash. Acta hydrochimica et hydrobiologica, 34(1-2), 73-85, https://doi.org/10.1002/aheh.200500610
Lager, Tanja; Hamer, Kay; Schröter, Jürgen; Schulz, Horst D (2003): Predicting the source strength of different recycling materials – methods and preliminary results. In: Schulz, H D; Hadeler, A (eds.) Geochemical processes in soil and groundwater – Measurement – Modelling – Upscaling (Proceedings GeoProc2002), Wiley-VCH Verlag, ISBN-10: 3-527-27766-8, 450-467
Lager, Tanja; Hamer, Kay; Schulz, Horst D (2005): Mobility of heavy metals in harbour sediments: an environmental aspect for the reuse of contaminated dredged sediments. Environmental Geology, 48(1), 92-100, https://doi.org/10.1007/s00254-005-1269-3
Event(s):
Experiment_02WP0142 * Device: Experiment (EXP)
Comment:
The German Federal Soil Protection Act (Federal Bulletin, 1998) demands a prediction of the transport of pollutants with the seepage water if waste materials are reused. Within the framework of a program funded by the Federal Ministry for Education and Science (BMBF) called 'Seepage Water Prognosis' methods to obtain relevant parameters for the prediction of the transport of pollutants through the unsaturated zone should be employed, compared and, if required, refined. Our investigations on diverse contaminated materials aim at the determination of their source strength and temporary variations. The three materials investigated in this project are (1) sediment dredged from the port of the city of Bremen, (2) municipal waste incineration ash, and (3) demolition waste. The study presented here focuses on inorganic contaminants. Crucial are the pH and Eh conditions as well as the liquid/solid ratio. Four batch tests, the DEV S4 test, the soil saturation extract, ammonium-nitrate extract, the pH-stat test, and column experiments were performed and compared. The acid neutralisation capacity is determined by means of pH-stat tests. Thus the time period until a soil horizon is acidified can be calculated. The oxidation and reduction capacity can be calculated on the basis of the potential electron transfer of redox reactions and thus enable a prediction when a sediment layer will be oxidised or reduced. In this paper we focus on the presentation of the laboratory methods. Preliminary results of the batch experiments are presented. In addition, results of the pore water analysis of the fine fraction of harbour sediments, providing the most realistic estimation of the source strength gained by dialysis and centrifugation, are shown.
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Datasets listed in this Collection

  1. Lager, T (2004): A 1.1.1. Harbour sediments: material description - material parameter. https://doi.org/10.1594/PANGAEA.776604
  2. Lager, T (2004): A 1.1.2. Harbour sediments: material description - bulk concentration. https://doi.org/10.1594/PANGAEA.776605
  3. Lager, T (2004): A 1.2.1. Data of the batch experiments with the fine fraction of harbour sediments - electric conductivity, pH- and Eh value and acid neutralisation capacity. https://doi.org/10.1594/PANGAEA.776606
  4. Lager, T (2004): A 1.2.2. Data of the batch experiments with the fine fraction of harbour sediments - main elements. https://doi.org/10.1594/PANGAEA.776607
  5. Lager, T (2004): A 1.2.3. Data of the batch experiments with the fine fraction of harbour sediments - trace elements. https://doi.org/10.1594/PANGAEA.776608
  6. Lager, T (2004): A 1.3.1. Data of the batch experiments with the sandy fraction of harbour sediments - electric conductivity, pH- and Eh value and acid neutralisation capacity. https://doi.org/10.1594/PANGAEA.776609
  7. Lager, T (2004): A 1.3.2. Data of the batch experiments with the sandy fraction of harbour sediments - main elements. https://doi.org/10.1594/PANGAEA.776610
  8. Lager, T (2004): A 1.3.3. Data of the batch experiments with the sandy fraction of harbour sediments - trace elements. https://doi.org/10.1594/PANGAEA.776611
  9. Lager, T (2004): A 1.4.1. Data of the saturated column experiments with the sandy fraction of harbour sediments - characteristic data of the column. https://doi.org/10.1594/PANGAEA.776612
  10. Lager, T (2004): A 1.4.2.1. Data of the saturated column experiments with the sandy fraction of harbour sediments - outlet - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776613
  11. Lager, T (2004): A 1.4.2.2. Data of the saturated column experiments with the sandy fraction of harbour sediments - main elements. https://doi.org/10.1594/PANGAEA.776614
  12. Lager, T (2004): A 1.4.2.3. Data of the saturated column experiments with the sandy fraction of harbour sediments - outlet - trace elements. https://doi.org/10.1594/PANGAEA.776615
  13. Lager, T (2004): A 1.4.3.1. Data of the saturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 282 days - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776616
  14. Lager, T (2004): A 1.4.3.1. Data of the saturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 90 days - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776617
  15. Lager, T (2004): A 1.4.3.2. Data of the saturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 282 days - main elements. https://doi.org/10.1594/PANGAEA.776619
  16. Lager, T (2004): A 1.4.3.2. Data of the saturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 90 days - main elements. https://doi.org/10.1594/PANGAEA.776618
  17. Lager, T (2004): A 1.4.3.3. Data of the saturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 282 days - trace elements. https://doi.org/10.1594/PANGAEA.776621
  18. Lager, T (2004): A 1.4.3.3. Data of the saturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 90 days - trace elements. https://doi.org/10.1594/PANGAEA.776620
  19. Lager, T (2004): A 1.5.1. Data of the unsaturated column experiments with the sandy fraction of harbour sediments - characteristic data of the column. https://doi.org/10.1594/PANGAEA.776622
  20. Lager, T (2004): A 1.5.2.1. Data of the unsaturated column experiments with the sandy fraction of harbour sediments - outlet - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776623
  21. Lager, T (2004): A 1.5.2.2. Data of the unsaturated column experiments with the sandy fraction of harbour sediments - main elements. https://doi.org/10.1594/PANGAEA.776624
  22. Lager, T (2004): A 1.5.2.3. Data of the unsaturated column experiments with the sandy fraction of harbour sediments - trace elements. https://doi.org/10.1594/PANGAEA.776625
  23. Lager, T (2004): A 1.5.3.1. Data of the unsaturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 24 days - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776626
  24. Lager, T (2004): A 1.5.3.2. Data of the unsaturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 24 days - main elements. https://doi.org/10.1594/PANGAEA.776627
  25. Lager, T (2004): A 1.5.3.3. Data of the unsaturated column experiments with the sandy fraction of harbour sediments - flow-path sampling after 24 days - trace elements. https://doi.org/10.1594/PANGAEA.776628
  26. Lager, T (2004): A 2.1.1. Demolition waste: material description - material parameter. https://doi.org/10.1594/PANGAEA.776629
  27. Lager, T (2004): A 2.1.2. Demolition waste: material description - bulk concentration. https://doi.org/10.1594/PANGAEA.776630
  28. Lager, T (2004): A 2.2.1. Data of the batch experiments with construction waste - electric conductivity, pH- and Eh value and acid neutralisation capacity. https://doi.org/10.1594/PANGAEA.776631
  29. Lager, T (2004): A 2.2.2. Data of the batch experiments with construction waste - main elements. https://doi.org/10.1594/PANGAEA.776632
  30. Lager, T (2004): A 2.2.3. Data of the batch experiments with construction waste - trace elements. https://doi.org/10.1594/PANGAEA.776652
  31. Lager, T (2004): A 2.3.1. Data of the saturated column experiment with demolition waste - characteristic data of the column. https://doi.org/10.1594/PANGAEA.776634
  32. Lager, T (2004): A 2.3.2.1. Data of the saturated column experiment with demolition waste - outlet - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776635
  33. Lager, T (2004): A 2.3.2.2. Data of the saturated column experiment with demolition waste - outlet - main elements. https://doi.org/10.1594/PANGAEA.776636
  34. Lager, T (2004): A 2.3.2.3. Data of the saturated column experiment with demolition waste - outlet - trace elements. https://doi.org/10.1594/PANGAEA.776637
  35. Lager, T (2004): A 3.1.1. Municipal waste incineration ash: material description - material parameter. https://doi.org/10.1594/PANGAEA.776638
  36. Lager, T (2004): A 3.1.2. Municipal waste incineration ash: material description - bulk concentration. https://doi.org/10.1594/PANGAEA.776639
  37. Lager, T (2004): A 3.2.1. Data of the batch experiments with municipal waste incineration ash - electric conductivity, pH- and Eh value and acid neutralisation capacity. https://doi.org/10.1594/PANGAEA.776640
  38. Lager, T (2004): A 3.2.2. Data of the batch experiments with municipal waste incineration ash - main elements. https://doi.org/10.1594/PANGAEA.776641
  39. Lager, T (2012): A 3.2.3. Data of the batch experiments with municipal waste incineration ash - trace elements. https://doi.org/10.1594/PANGAEA.776713
  40. Lager, T (2004): A 3.3.1. Data of the saturated column experiment with municipal waste incineration ash - characteristic data of the column. https://doi.org/10.1594/PANGAEA.776642
  41. Lager, T (2004): A 3.3.2.1. Data of the saturated column experiment with municipal waste incineration ash - outlet - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776643
  42. Lager, T (2004): A 3.3.2.2. Data of the saturated column experiment with municipal waste incineration ash - flow-path sampling after 276 days - main elements. https://doi.org/10.1594/PANGAEA.776649
  43. Lager, T (2004): A 3.3.2.2. Data of the saturated column experiment with municipal waste incineration ash - flow-path sampling after 83 days - main elements. https://doi.org/10.1594/PANGAEA.776648
  44. Lager, T (2004): A 3.3.2.2. Data of the saturated column experiment with municipal waste incineration ash - outlet - main elements. https://doi.org/10.1594/PANGAEA.776644
  45. Lager, T (2004): A 3.3.2.3. Data of the saturated column experiment with municipal waste incineration ash - outlet - trace elements. https://doi.org/10.1594/PANGAEA.776645
  46. Lager, T (2004): A 3.3.3.1. Data of the saturated column experiment with municipal waste incineration ash - flow-path sampling after 276 days - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776646
  47. Lager, T (2004): A 3.3.3.1. Data of the saturated column experiment with municipal waste incineration ash - flow-path sampling after 83 days - liquid/solid ratio, electric conductivity, pH and Eh value, inorganic carbon, dissolved organic carbon and anions. https://doi.org/10.1594/PANGAEA.776647
  48. Lager, T (2004): A 3.3.3.3. Data of the saturated column experiment with municipal waste incineration ash - flow-path sampling after 276 days - trace elements. https://doi.org/10.1594/PANGAEA.776651
  49. Lager, T (2004): A 3.3.3.3. Data of the saturated column experiment with municipal waste incineration ash - flow-path sampling after 83 days - trace elements. https://doi.org/10.1594/PANGAEA.776650