Hoyer, Mandy; Weber, Arnd (2022): Soil data from the floodplain of River Elbe [dataset]. PANGAEA, https://doi.org/10.1594/PANGAEA.943271
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Abstract:
The goal of the project was to understand the impact of lateral hydraulic connectivity on the pollution patterns in floodplain soils. Floodplain soils were sampled during summer and autumn 2020 on 89 sites along River Elbe following the German Federal Soil Protection and Contaminated Sites Ordinance (12 July 1999) (Bundes-Bodenschutz- und Altlastenverordnung (BBodSchV)). Five subsamples of topsoil (0 – 10 cm) and subsoil (45 – 55 cm) were taken on each 4 m x 4 m plot and combined to one gross sample each.
By sieving the dried samples were separated into 12 grain size fractions (2-63 mm, 1-2 mm, 0.63-1 mm, 0.2-0.63 mm, 0.125-0.2 mm, 0.063-0.125 mm, 0.063-2mm, 0.02-0.063 mm, 0.0063-0.02 mm, 0.002-0.0063 mm, 0.002-0.063 mm, <0.002 mm). Further laboratory analyses were carried out following recent DIN standards. Inorganic pollutants (As, Cd, Cr, Cu, Hg, Ni, Pb and Zn) were analyzed in the soil fraction <63 µm; organic micro-pollutants (polycyclic aromatic hydrocarbons (PAH), polychlorinated biphenyls (PCB) and organochlorine pesticides) in the fraction <2 mm. The analysis of nutrients and additional soil parameters was carried out in the fraction <2 mm and the total sample, respectively. The concentrations of the organic micro-pollutants were converted to the <63 µm fraction to be able to compare samples of different grain size distributions. The concentrations of the inorganic pollutants were converted to the <2 mm fraction for evaluating them according to the limit values defined in the German Federal Soil Protection and Contaminated Sites Ordinance (12 July 1999). Analytic values below the limit of quantification were replaced by the actual limit itself.
A pollutant index for both inorganic trace pollutants and organic disruptors was calculated using multiple linear regression obtained by factor analysis without rotation.
Additional environmental variables (flood duration, Euclidean distance to the river axis, river stationing) were modeled, computed or queried by GIS within the ElBiota project (https://elbiota.bafg.de).
Related to:
Hoyer, Mandy (2022): Räumliche Muster der Schadstoffverteilung in Auenböden der Mittleren Elbe. Hydrologie und Wasserbewirtschaftung, 66(6), 314-320, https://www.hywa-online.de/download/hywa-heft-6-2022/
Project(s):
Coverage:
Median Latitude: 52.417992 * Median Longitude: 12.157958 * South-bound Latitude: 51.618550 * West-bound Longitude: 11.136810 * North-bound Latitude: 53.167040 * East-bound Longitude: 12.947300
Date/Time Start: 2020-05-25T00:00:00 * Date/Time End: 2020-09-09T00:00:00
Minimum DEPTH, soil: 5 m * Maximum DEPTH, soil: 50 m
Event(s):
ElBiota_01_01 * Latitude: 51.626940 * Longitude: 12.944240 * Date/Time: 2020-07-13T00:00:00 * Elevation: 78.4 m * Location: Elsnig * Campaign: ElBiota_2020 * Method/Device: Edelman auger (EDEA) * Comment: hand shovel and Edelman auger
ElBiota_01_02 * Latitude: 51.628640 * Longitude: 12.945180 * Date/Time: 2020-07-13T00:00:00 * Elevation: 78.4 m * Location: Elsnig * Campaign: ElBiota_2020 * Method/Device: Edelman auger (EDEA) * Comment: hand shovel and Edelman auger
ElBiota_01_03 * Latitude: 51.629920 * Longitude: 12.947300 * Date/Time: 2020-07-13T00:00:00 * Elevation: 78.5 m * Location: Elsnig * Campaign: ElBiota_2020 * Method/Device: Edelman auger (EDEA) * Comment: hand shovel and Edelman auger
Parameter(s):
# | Name | Short Name | Unit | Principal Investigator | Method/Device | Comment |
---|---|---|---|---|---|---|
1 | Event label | Event | Hoyer, Mandy | |||
2 | Location of event | Location | Hoyer, Mandy | |||
3 | Latitude of event | Latitude | Hoyer, Mandy | |||
4 | Longitude of event | Longitude | Hoyer, Mandy | |||
5 | UTM Easting, Universal Transverse Mercator | UTM east | m | Hoyer, Mandy | ||
6 | UTM Northing, Universal Transverse Mercator | UTM north | m | Hoyer, Mandy | ||
7 | Elevation of event | Elevation | m | Hoyer, Mandy | ||
8 | DEPTH, soil | Depth soil | m | Hoyer, Mandy | Geocode | |
9 | Depth, soil, minimum | Depth soil min | m | Hoyer, Mandy | ||
10 | Depth, soil, maximum | Depth soil max | m | Hoyer, Mandy | ||
11 | Comment | Comment | Hoyer, Mandy | Used for the analysis in Hoyer (2022) | ||
12 | River kilometer | River km | km | Hoyer, Mandy | Atlas, Wasserstrassen- und Schiffahrtsverwaltung des Bunde | |
13 | Euclidean Distance | Euclidean Dist | m | Hoyer, Mandy | r.grow.distance | |
14 | Flow distance | Flow dist | m | Hoyer, Mandy | Length of a COST-based flow path following the Elbe DEM to the wetted area of the floodplain at mean low-flow discharge (MLQ) (FLYS3) | Flow distance to the floodplain's wetted area at mean low-flow discharge (MLQ). Length of a COST-based flow path (https://grass.osgeo.org/grass78/manuals/r.drain.html) following the Elbe DEM (doi:10.1594/PANGAEA.919293) to the wetted area of the floodplain at mean low-flow discharge (MLQ) (FLYS3: https://www.bafg.de/DE/08_Ref/M2/03_Fliessgewmod/01_FLYS/flys_node.html) |
15 | Flood duration, annual mean | Flood duration | day/a | Hoyer, Mandy | hydflood::flood3 | Time period from 1990 to 2016 |
16 | Flood duration, annual mean | Flood duration | day/a | Hoyer, Mandy | hydflood::flood3 | Time period from 1990 to 2019 |
17 | Elevation, difference | Elevation diff | m | Hoyer, Mandy | Elbe DEM, FLYS3 | Between the Elbe DEM and the water level at mean low-flow discharge (MLQ). Elbe DEM (10.1594/PANGAEA.919293), FLYS3 (https://www.bafg.de/DE/08_Ref/M2/03_Fliessgewmod/01_FLYS/flys_node.html) |
18 | Size fraction 63-2 mm | 63-2 mm | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
19 | Size fraction 2.000-1.000 mm, (-1.0)-0.0 phi, very coarse sand | 2-1 mm | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
20 | Size fraction 1.000-0.630 mm | 1-0.63 mm | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
21 | Size fraction 0.630-0.200 mm, medium sand | 630-200 µm | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
22 | Size fraction 0.200-0.125 mm, fine sand | 200-125 µm | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
23 | Size fraction 0.125-0.063 mm, 3.0-4.0 phi, very fine sand | 125-63 µm | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
24 | Size fraction 2.000-0.630 mm, coarse sand | 2000-630 µm | % | Hoyer, Mandy | Calculated | wt. % |
25 | Size fraction 0.063-0.020 mm, coarse silt | 63-20 µm gU | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
26 | Size fraction 0.020-0.0063 mm, medium silt | 20-6.3 µm mU | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
27 | Size fraction 0.0063-0.002 mm, fine silt | 6.3-2 µm fU | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
28 | Size fraction 0.063-0.002 mm, silt, mud | 63-2 µm | % | Hoyer, Mandy | Calculated | wt. % |
29 | Size fraction < 0.002 mm, clay | <2 µm | % | Hoyer, Mandy | DIN ISO 17892-4:2016 | wt. % |
30 | Size fraction < 2.0 mm | <2000 µm | % | Hoyer, Mandy | Calculated | wt. % |
31 | Size fraction < 0.063 mm, mud, silt+clay | <63 µm | % | Hoyer, Mandy | Calculated | wt. % |
32 | Residue, dry | Dry residue | % | Hoyer, Mandy | DIN ISO 11465:1996-12; DIN EN 14346:2007-03 | wt. % |
33 | pH, soil | pH soil | Hoyer, Mandy | DIN ISO 10390:2005-02; DIN EN 12176:1998-06 | measured in soil mixed with water at a ratio of 1:5 | |
34 | pH, soil | pH soil | Hoyer, Mandy | DIN ISO 10390:2005-02; DIN EN 12176:1998-06 | measured in soil mixed with a calcium chloride solution at a ratio of 1:5 | |
35 | Effective cation exchange capacity | ECEC | cmol/kg | Hoyer, Mandy | DIN EN ISO 11260:2018-11 | analyzed in the total sample |
36 | Effective sodium ion exchange capacity | Eff Na ex-cap | cmol/kg | Hoyer, Mandy | DIN EN ISO 11260:2018-11 | analyzed in the total sample |
37 | Effective potassium exchange capacity | Eff K ex-cap | cmol/kg | Hoyer, Mandy | DIN EN ISO 11260:2018-11 | analyzed in the total sample |
38 | Effective magnesium exchange capacity | Eff Mg ex-cap | cmol/kg | Hoyer, Mandy | DIN EN ISO 11260:2018-11 | analyzed in the total sample |
39 | Effective calcium exchange capacity | Eff Ca ex-cap | cmol/kg | Hoyer, Mandy | DIN EN ISO 11260:2018-11 | analyzed in the total sample |
40 | Potential cation exchange capacity | PCEC | cmol/kg | Hoyer, Mandy | DIN ISO 13536:1997-04 | analyzed in the total sample |
41 | Potential sodium exchange capacity | Pot Na ex-cap | cmol/kg | Hoyer, Mandy | DIN ISO 13536:1997-04 | analyzed in the total sample |
42 | Potential potassium exchange capacity | Pot K ex-cap | cmol/kg | Hoyer, Mandy | DIN ISO 13536:1997-04 | analyzed in the total sample |
43 | Potential magnesium exchange capacity | Pot Mg ex-cap | cmol/kg | Hoyer, Mandy | DIN ISO 13536:1997-04 | analyzed in the total sample |
44 | Potential calcium exchange capacity | Pot Ca ex-cap | cmol/kg | Hoyer, Mandy | DIN ISO 13536:1997-04 | analyzed in the total sample |
45 | Carbon, organic, total | TOC | % | Hoyer, Mandy | DIN ISO 10694:1996-08/DIN EN 13137: 2001-12/DIN EN 15936:2012-11 | analyzed in the <2000 µm fraction, wt. %, Limit of Quantification: <0.1 |
46 | Nitrogen, total | TN | % | Hoyer, Mandy | DIN EN 16168:2012-11 | analyzed in the <2000 µm fraction, Limit of Quantification: <0.02 |
47 | Calcium carbonate | CaCO3 | % | Hoyer, Mandy | Calculated from TOC | in the total sample |
48 | Phosphorus, total | TP | mg/kg | Hoyer, Mandy | DIN ISO 22036:2009-06 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <10 |
49 | Phosphorus, plant-available | P (P2O5) plant av | mg/kg | Hoyer, Mandy | VDLUFA volume I A 6.2.1.2 | analyzed in the total sample |
50 | Potassium, plant-available | K (K2O) plant av | mg/kg | Hoyer, Mandy | VDLUFA volume I A 6.2.1.2 | analyzed in the total sample |
51 | Magnesium, plant-available | Mg pant av | mg/kg | Hoyer, Mandy | VDLUFA volume I A 6.2.1.2 | analyzed in the total sample |
52 | nitrogen, as plant-available ammonium | NH4-N plant av | mg/kg | Hoyer, Mandy | VDLUFA volume I A 6.2.1.2 | analyzed in the total sample |
53 | nitrogen, as plant-available nitrate | NO3-N plant av | mg/kg | Hoyer, Mandy | VDLUFA volume I A 6.2.1.2 | analyzed in the total sample |
54 | Nitrogen, mineral-bound | N mineral | mg/kg | Hoyer, Mandy | VDLUFA volume I A 6.2.1.2 | analyzed in the total sample |
55 | Iron, dithionite-solvable | FeD sol | mg/kg | Hoyer, Mandy | DIN EN ISO 12782-2:2012-09 | analyzed in the total sample, of dry matter |
56 | Iron, oxalate-solvable | FeOx sol | mg/kg | Hoyer, Mandy | DIN 19684-6:1997-12 | analyzed in the total sample, of dry matter |
57 | Moisture index | Moisture index | Hoyer, Mandy | Calculated | moisture index (Fe), (fe.oxalat)/(fe.dithionit) | |
58 | Manganese, soluble in dithionite | MnD sol | mg/kg | Hoyer, Mandy | DIN EN ISO 12782-2:2012-09 | analyzed in the total sample, of dry matter |
59 | Manganese, soluble in oxalate | MnOx sol | mg/kg | Hoyer, Mandy | DIN 19684-6:1997-12 | analyzed in the total sample, of dry matter |
60 | Moisture index | Moisture index | Hoyer, Mandy | DIN 19684-6:1997-12 | moisture index (Mn), (mn.oxalat)/(mn.dithionit) | |
61 | Arsenic | As | mg/kg | Hoyer, Mandy | DIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01 | analyzed in the <63 µm fraction, of dry matter, Limit of Quantification: <1 |
62 | Lead | Pb | mg/kg | Hoyer, Mandy | DIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01 | analyzed in the <63 µm fraction, of dry matter, Limit of Quantification: <5 |
63 | Cadmium | Cd | mg/kg | Hoyer, Mandy | DIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01 | analyzed in the <63 µm fraction, of dry matter, Limit of Quantification: <0.1 |
64 | Chromium | Cr | mg/kg | Hoyer, Mandy | DIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01 | analyzed in the <63 µm fraction, of dry matter, Limit of Quantification: <2 |
65 | Copper | Cu | mg/kg | Hoyer, Mandy | DIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01 | analyzed in the <63 µm fraction, of dry matter, Limit of Quantification: <2 |
66 | Nickel | Ni | mg/kg | Hoyer, Mandy | DIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01 | analyzed in the <63 µm fraction, of dry matter, Limit of Quantification: <2 |
67 | Mercury | Hg | mg/kg | Hoyer, Mandy | DIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01 | analyzed in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
68 | Zinc | Zn | mg/kg | Hoyer, Mandy | DIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01 | analyzed in the <63 µm fraction, of dry matter, Limit of Quantification: <10 |
69 | Arsenic | As | mg/kg | Hoyer, Mandy | Converted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractions | in the <2000 µm fraction, of dry matter, Limit of Quantification: <1 |
70 | Lead | Pb | mg/kg | Hoyer, Mandy | Converted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractions | in the <2000 µm fraction, of dry matter, Limit of Quantification: <5 |
71 | Cadmium | Cd | mg/kg | Hoyer, Mandy | Converted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractions | in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.1 |
72 | Zinc | Zn | mg/kg | Hoyer, Mandy | Converted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractions | in the <2000 µm fraction, of dry matter, Limit of Quantification: <2 |
73 | Mercury | Hg | mg/kg | Hoyer, Mandy | Converted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractions | in the <2000 µm fraction, of dry matter, Limit of Quantification: <2 |
74 | Chromium | Cr | mg/kg | Hoyer, Mandy | Converted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractions | in the <2000 µm fraction, of dry matter, Limit of Quantification: <2 |
75 | Nickel | Ni | mg/kg | Hoyer, Mandy | Converted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractions | in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
76 | Copper | Cu | mg/kg | Hoyer, Mandy | Converted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractions | in the <2000 µm fraction, of dry matter, Limit of Quantification: <10 |
77 | Naphthalene | Naphth | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
78 | Acenaphthylene | Acenaphthylene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
79 | Acenaphthene | Acenaphthene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
80 | Fluorene | Fluorene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
81 | Phenanthrene | Phenanthrene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
82 | Anthracene | Anthracene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
83 | Fluoranthene | Fluoranthene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
84 | Pyrene | Pyrene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
85 | Benz(a)anthracene | Benz(a)anthracene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
86 | Chrysene | Chrysene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
87 | Benzo(a)anthracenerene | Benzo(a)anthracene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
88 | Dibenzo(a,h)anthracene | Dibenzo(a,h)anthracene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
89 | Benzo(b)fluoranthene | Benzo(b)fluoranthene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
90 | Benzo(k)fluoranthene | Benzo(k)fluoranthene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
91 | Indeno(1,2,3-cd)pyrene | Indeno(1,2,3-cd)pyrene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
92 | Benzo(g,h,i)perylene | Benzo(ghi)perylene | mg/kg | Hoyer, Mandy | DIN ISO 18287: 2006-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.01 |
93 | Polychlorinated biphenyl 28 | PCB_28 | mg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05/DIN EN 15308:2016-12 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
94 | Polychlorinated biphenyl 52 | PCB_52 | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05/DIN EN 15308:2016-12 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
95 | Polychlorinated biphenyl 101 | PCB_101 | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05/DIN EN 15308:2016-12 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
96 | Polychlorinated biphenyl 118 | PCB_118 | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05/DIN EN 15308:2016-12 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
97 | Polychlorinated biphenyl 138 | PCB_138 | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05/DIN EN 15308:2016-12 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
98 | Polychlorinated biphenyl 153 | PCB_153 | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05/DIN EN 15308:2016-12 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
99 | Polychlorinated biphenyl 180 | PCB_180 | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05/DIN EN 15308:2016-12 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
100 | Polychlorinated biphenyl sum (pcb_28 + pcb_52 + pcb_101 + pcb_138 + pcb_153 + pcb_180) | sum PCB | mg/kg | Hoyer, Mandy | Calculated | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
101 | alpha-Hexachlorocyclohexane | a-HCH | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
102 | beta-Hexachlorocyclohexane | b-HCH | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
103 | gamma-Hexachlorocyclohexane | g-HCH | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
104 | ortho,para-Dichlorodiphenyldichloroethane | op-DDD | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
105 | para,para-Dichlorodiphenyldichloroethane | pp-DDD | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
106 | ortho,para-Dichlorodiphenyldichloroethylene | op-DDE | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
107 | para,para-Dichlorodiphenyldichloroethylene | pp-DDE | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
108 | ortho,para-Dichlorodiphenyltrichloroethane | op-DDT | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
109 | para,para-Dichlorodiphenyltrichloroethane | pp-DDT | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
110 | 1,2,3-Trichlorobenzene | 1,2,3-Trichlorobenzene | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
111 | 1,3,5-Trichlorobenzene | 1,3,5-Trichlorobenzene | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
112 | 1,2,4-Trichlorobenzene | 1,2,4-Trichlorobenzene | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
113 | 1,2,3,4-Tetrachlorobenzene | 1,2,3,4-Tetrachlorobenzene | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
114 | 1,2,3,5-Tetrachlorobenzene | 1,2,3,5-Tetrachlorobenzene | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
115 | 1,2,4,5-Tetrachlorobenzene | 1,2,4,5-Tetrachlorobenzene | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
116 | Pentachlorobenzene | PeCB | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
117 | Hexachlorobenzene | HCB | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
118 | Hexachlorbutadiene | HCBU | µg/kg | Hoyer, Mandy | DIN EN ISO 10382:2003-05 | analyzed in the <2000 µm fraction, of dry matter, Limit of Quantification: <0.05 |
119 | Naphthalene | Naphth | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
120 | Acenaphthylene | Acenaphthylene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
121 | Acenaphthene | Acenaphthene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
122 | Fluorene | Fluorene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
123 | Phenanthrene | Phenanthrene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
124 | Anthracene | Anthracene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
125 | Fluoranthene | Fluoranthene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
126 | Pyrene | Pyrene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
127 | Benz(a)anthracene | Benz(a)anthracene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
128 | Chrysene | Chrysene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
129 | Benzo(a)anthracenerene | Benzo(a)anthracene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
130 | Dibenzo(a,h)anthracene | Dibenzo(a,h)anthracene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
131 | Benzo(b)fluoranthene | Benzo(b)fluoranthene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
132 | Benzo(k)fluoranthene | Benzo(k)fluoranthene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
133 | Indeno(1,2,3-cd)pyrene | Indeno(1,2,3-cd)pyrene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
134 | Benzo(g,h,i)perylene | Benzo(ghi)perylene | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.01 |
135 | Polychlorinated biphenyl 28 | PCB_28 | mg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
136 | Polychlorinated biphenyl 52 | PCB_52 | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
137 | Polychlorinated biphenyl 101 | PCB_101 | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
138 | Polychlorinated biphenyl 118 | PCB_118 | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
139 | Polychlorinated biphenyl 138 | PCB_138 | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
140 | Polychlorinated biphenyl 153 | PCB_153 | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
141 | Polychlorinated biphenyl 180 | PCB_180 | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
142 | alpha-Hexachlorocyclohexane | a-HCH | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
143 | beta-Hexachlorocyclohexane | b-HCH | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
144 | gamma-Hexachlorocyclohexane | g-HCH | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
145 | ortho,para-Dichlorodiphenyldichloroethane | op-DDD | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
146 | para,para-Dichlorodiphenyldichloroethane | pp-DDD | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
147 | ortho,para-Dichlorodiphenyldichloroethylene | op-DDE | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
148 | para,para-Dichlorodiphenyldichloroethylene | pp-DDE | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
149 | ortho,para-Dichlorodiphenyltrichloroethane | op-DDT | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
150 | para,para-Dichlorodiphenyltrichloroethane | pp-DDT | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
151 | 1,2,3-Trichlorobenzene | 1,2,3-Trichlorobenzene | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
152 | 1,3,5-Trichlorobenzene | 1,3,5-Trichlorobenzene | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
153 | 1,2,4-Trichlorobenzene | 1,2,4-Trichlorobenzene | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
154 | 1,2,3,4-Tetrachlorobenzene | 1,2,3,4-Tetrachlorobenzene | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
155 | 1,2,3,5-Tetrachlorobenzene | 1,2,3,5-Tetrachlorobenzene | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
156 | 1,2,4,5-Tetrachlorobenzene | 1,2,4,5-Tetrachlorobenzene | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
157 | Pentachlorobenzene | PeCB | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
158 | Hexachlorobenzene | HCB | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
159 | Hexachlorbutadiene | HCBU | µg/kg | Hoyer, Mandy | Converted from the <2000 µm fraction to the <63 µm fraction using the grain size fractions | in the <63 µm fraction, of dry matter, Limit of Quantification: <0.05 |
160 | Inorganic contamination index | Inorg con I | Hoyer, Mandy | Multiple linear regression of the concentrations of toxic metals and arsenic; followed by Normalization step | metals and arsenic | |
161 | Organic contamination index | Org con I | Hoyer, Mandy | Multiple linear regression of the concentrations of all analyzed organic pollutants; followed by Normalization step | ||
162 | Organic contamination index | Org con I | Hoyer, Mandy | Multiple linear regression of the concentrations of all analyzed organic pollutants in the <63 ¬µm fraction; followed by Normalization step | based on the concentrations in the <63 µm fraction | |
163 | Contamination index | Con I | Hoyer, Mandy | Calculated | mean of inorganic contamination index and organic contamination index <63 µm |
License:
Creative Commons Attribution-ShareAlike 4.0 International (CC-BY-SA-4.0)
Status:
Curation Level: Enhanced curation (CurationLevelC)
Size:
26835 data points
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