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Hoyer, Mandy; Weber, Arnd (2022): Soil data from the floodplain of River Elbe. PANGAEA, https://doi.pangaea.de/10.1594/PANGAEA.943271 (dataset in review)

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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).
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).
Keyword(s):
floodplain; nutrients; pollution; Soil; trace- and major elements
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: 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):
#NameShort NameUnitPrincipal InvestigatorMethod/DeviceComment
1Event labelEventHoyer, Mandy
2Location of eventLocationHoyer, Mandy
3Latitude of eventLatitudeHoyer, Mandy
4Longitude of eventLongitudeHoyer, Mandy
5UTM Easting, Universal Transverse MercatorUTM eastmHoyer, Mandy
6UTM Northing, Universal Transverse MercatorUTM northmHoyer, Mandy
7Elevation of eventElevationmHoyer, Mandy
8DEPTH, soilDepth soilmHoyer, MandyGeocode
9Depth, soil, minimumDepth soil minmHoyer, Mandy
10Depth, soil, maximumDepth soil maxmHoyer, Mandy
11CommentCommentHoyer, MandyUsed for the analysis in Hoyer (2022)
12River kilometerRiver kmkmHoyer, MandyAtlas, Wasserstrassen- und Schiffahrtsverwaltung des Bunde
13Euclidean DistanceEuclidean DistmHoyer, Mandyr.grow.distance
14Flow distanceFlow distmHoyer, MandyLength 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)
15Flood duration, annual meanFlood durationday/aHoyer, Mandyhydflood::flood3Time period from 1990 to 2016
16Flood duration, annual meanFlood durationday/aHoyer, Mandyhydflood::flood3Time period from 1990 to 2019
17Difference, elevationElevation diffmHoyer, MandyElbe DEM, FLYS3Between 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)
18Size fraction 63-2 mm63-2 mm%Hoyer, MandyDIN ISO 17892-4:2016wt. %
19Size fraction 2.000-1.000 mm, (-1.0)-0.0 phi, very coarse sand2-1 mm%Hoyer, MandyDIN ISO 17892-4:2016wt. %
20Size fraction 1.000-0.630 mm1-0.63 mm%Hoyer, MandyDIN ISO 17892-4:2016wt. %
21Size fraction 0.630-0.200 mm, medium sand630-200 µm mS%Hoyer, MandyDIN ISO 17892-4:2016wt. %
22Size fraction 0.200-0.125 mm200-125 µm%Hoyer, MandyDIN ISO 17892-4:2016wt. %
23Size fraction 0.125-0.063 mm, 3.0-4.0 phi, very fine sand125-63 µm%Hoyer, MandyDIN ISO 17892-4:2016wt. %
24Size fraction 2.000-0.630 mm, coarse sand2000-630 µm gS%Hoyer, MandyCalculatedwt. %
25Size fraction 0.063-0.020 mm, coarse silt63-20 µm gU%Hoyer, MandyDIN ISO 17892-4:2016wt. %
26Size fraction 0.020-0.0063 mm, medium silt20-6.3 µm mU%Hoyer, MandyDIN ISO 17892-4:2016wt. %
27Size fraction 0.0063-0.002 mm, fine silt6.3-2 µm fU%Hoyer, MandyDIN ISO 17892-4:2016wt. %
28Size fraction 0.063-0.002 mm, silt, mud63-2 µm%Hoyer, MandyCalculatedwt. %
29Size fraction < 0.002 mm, clay<2 µm%Hoyer, MandyDIN ISO 17892-4:2016wt. %
30Size fraction < 2.0 mm<2000 µm%Hoyer, MandyCalculatedwt. %
31Size fraction < 0.063 mm, mud, silt+clay<63 µm%Hoyer, MandyCalculatedwt. %
32Residue, dryDry residue%Hoyer, MandyDIN ISO 11465:1996-12; DIN EN 14346:2007-03wt. %
33pH, soilpH soilHoyer, MandyDIN ISO 10390:2005-02; DIN EN 12176:1998-06measured in soil mixed with water at a ratio of 1:5
34pH, soilpH soilHoyer, MandyDIN ISO 10390:2005-02; DIN EN 12176:1998-06measured in soil mixed with a calcium chloride solution at a ratio of 1:5
35Effective cation exchange capacityECECcmol/kgHoyer, MandyDIN EN ISO 11260:2018-11analyzed in the total sample
36Effective sodium ion exchange capacityEff Na ex-capcmol/kgHoyer, MandyDIN EN ISO 11260:2018-11analyzed in the total sample
37Effective potassium exchange capacityEff K ex-capcmol/kgHoyer, MandyDIN EN ISO 11260:2018-11analyzed in the total sample
38Effective magnesium exchange capacityEff Mg ex-capcmol/kgHoyer, MandyDIN EN ISO 11260:2018-11analyzed in the total sample
39Effective calcium exchange capacityEff Ca ex-capcmol/kgHoyer, MandyDIN EN ISO 11260:2018-11analyzed in the total sample
40Potential cation exchange capacityPCECcmol/kgHoyer, MandyDIN ISO 13536:1997-04analyzed in the total sample
41Potential sodium exchange capacityPot Na ex-capcmol/kgHoyer, MandyDIN ISO 13536:1997-04analyzed in the total sample
42Potential potassium exchange capacityPot K ex-capcmol/kgHoyer, MandyDIN ISO 13536:1997-04analyzed in the total sample
43Potential magnesium exchange capacityPot Mg ex-capcmol/kgHoyer, MandyDIN ISO 13536:1997-04analyzed in the total sample
44Potential calcium exchange capacityPot Ca ex-capcmol/kgHoyer, MandyDIN ISO 13536:1997-04analyzed in the total sample
45Carbon, organic, totalTOC%Hoyer, MandyDIN ISO 10694:1996-08/DIN EN 13137: 2001-12/DIN EN 15936:2012-11analyzed in the <2000 µm fraction, wt. %
46Nitrogen, totalTN%Hoyer, MandyDIN EN 16168:2012-11analyzed in the <2000 µm fraction
47Calcium carbonateCaCO3%Hoyer, MandyCalculated from TOCin the total sample
48Phosphorus, totalTPmg/kgHoyer, MandyDIN ISO 22036:2009-06analyzed in the <2000 µm fraction, of dry matter
49Phosphorus, plant-availableP (P2O5) plant avmg/kgHoyer, MandyVDLUFA volume I A 6.2.1.2analyzed in the total sample
50Potassium, plant-availableK (K2O) plant avmg/kgHoyer, MandyVDLUFA volume I A 6.2.1.2analyzed in the total sample
51Magnesium, plant-availableMg pant avmg/kgHoyer, MandyVDLUFA volume I A 6.2.1.2analyzed in the total sample
52nitrogen, as plant-available ammoniumNH4-N plant avmg/kgHoyer, MandyVDLUFA volume I A 6.2.1.2analyzed in the total sample
53nitrogen, as plant-available nitrateNO3-N plant avmg/kgHoyer, MandyVDLUFA volume I A 6.2.1.2analyzed in the total sample
54Nitrogen, mineral-boundN mineralmg/kgHoyer, MandyVDLUFA volume I A 6.2.1.2analyzed in the total sample
55Iron, dithionite-solvableFeD solmg/kgHoyer, MandyDIN EN ISO 12782-2:2012-09analyzed in the total sample, of dry matter
56Iron, oxalate-solvableFeOx solmg/kgHoyer, MandyDIN 19684-6:1997-12analyzed in the total sample, of dry matter
57Moisture indexMoisture indexHoyer, MandyCalculatedmoisture index (Fe), (fe.oxalat)/(fe.dithionit)
58manganese, soluble in dithioniteMnD solmg/kgHoyer, MandyDIN EN ISO 12782-2:2012-09analyzed in the total sample, of dry matter
59manganese, soluble in oxalateMnOx solmg/kgHoyer, MandyDIN 19684-6:1997-12analyzed in the total sample, of dry matter
60Moisture indexMoisture indexHoyer, MandyDIN 19684-6:1997-12moisture index (Mn), (mn.oxalat)/(mn.dithionit)
61ArsenicAsmg/kgHoyer, MandyDIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01analyzed in the <63 µm fraction, of dry matter
62LeadPbmg/kgHoyer, MandyDIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01analyzed in the <63 µm fraction, of dry matter
63CadmiumCdmg/kgHoyer, MandyDIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01analyzed in the <63 µm fraction, of dry matter
64ChromiumCrmg/kgHoyer, MandyDIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01analyzed in the <63 µm fraction, of dry matter
65CopperCumg/kgHoyer, MandyDIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01analyzed in the <63 µm fraction, of dry matter
66NickelNimg/kgHoyer, MandyDIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01analyzed in the <63 µm fraction, of dry matter
67MercuryHgmg/kgHoyer, MandyDIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01analyzed in the <63 µm fraction, of dry matter
68ZincZnmg/kgHoyer, MandyDIN EN ISO 17294-2-E29:2017-01 and prior digestion according to DIN EN 16174:2012-11/DIN EN 13657:2003-01analyzed in the <63 µm fraction, of dry matter
69ArsenicAsmg/kgHoyer, MandyConverted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractionsin the <2000 µm fraction, of dry matter
70LeadPbmg/kgHoyer, MandyConverted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractionsin the <2000 µm fraction, of dry matter
71CadmiumCdmg/kgHoyer, MandyConverted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractionsin the <2000 µm fraction, of dry matter
72ZincZnmg/kgHoyer, MandyConverted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractionsin the <2000 µm fraction, of dry matter
73MercuryHgmg/kgHoyer, MandyConverted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractionsin the <2000 µm fraction, of dry matter
74ChromiumCrmg/kgHoyer, MandyConverted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractionsin the <2000 µm fraction, of dry matter
75NickelNimg/kgHoyer, MandyConverted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractionsin the <2000 µm fraction, of dry matter
76CopperCumg/kgHoyer, MandyConverted from the analytical results in the <63 µm fraction to the <2000 µm fraction using the grain size fractionsin the <2000 µm fraction, of dry matter
77NaphthaleneNaphthmg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
78AcenaphthyleneAcenaphthylenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
79AcenaphtheneAcenaphthenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
80FluoreneFluorenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
81PhenanthrenePhenanthrenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
82AnthraceneAnthracenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
83FluorantheneFluoranthenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
84PyrenePyrenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
85Benz(a)anthraceneBenz(a)anthracenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
86ChryseneChrysenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
87Benzo(a)anthracenereneBenzo(a)anthracenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
88Dibenzo(a,h)anthraceneDibenzo(a,h)anthracenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
89Benzo(b)fluorantheneBenzo(b)fluoranthenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
90Benzo(k)fluorantheneBenzo(k)fluoranthenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
91Indeno(1,2,3-cd)pyreneIndeno(1,2,3-cd)pyrenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
92Benzo(ghi)peryleneBenzo(ghi)perylenemg/kgHoyer, MandyDIN ISO 18287: 2006-05analyzed in the <2000 µm fraction, of dry matter
93Polychlorinated biphenyl 28PCB_28mg/kgHoyer, MandyDIN EN ISO 10382:2003-05/DIN EN 15308:2016-12analyzed in the <2000 µm fraction, of dry matter
94Polychlorinated biphenyl 52PCB_52µg/kgHoyer, MandyDIN EN ISO 10382:2003-05/DIN EN 15308:2016-12analyzed in the <2000 µm fraction, of dry matter
95Polychlorinated biphenyl 101PCB_101µg/kgHoyer, MandyDIN EN ISO 10382:2003-05/DIN EN 15308:2016-12analyzed in the <2000 µm fraction, of dry matter
96Polychlorinated biphenyl 118PCB_118µg/kgHoyer, MandyDIN EN ISO 10382:2003-05/DIN EN 15308:2016-12analyzed in the <2000 µm fraction, of dry matter
97Polychlorinated biphenyl 138PCB_138µg/kgHoyer, MandyDIN EN ISO 10382:2003-05/DIN EN 15308:2016-12analyzed in the <2000 µm fraction, of dry matter
98Polychlorinated biphenyl 153PCB_153µg/kgHoyer, MandyDIN EN ISO 10382:2003-05/DIN EN 15308:2016-12analyzed in the <2000 µm fraction, of dry matter
99Polychlorinated biphenyl 180PCB_180µg/kgHoyer, MandyDIN EN ISO 10382:2003-05/DIN EN 15308:2016-12analyzed in the <2000 µm fraction, of dry matter
100Polychlorinated biphenyl sum (pcb_28 + pcb_52 + pcb_101 + pcb_138 + pcb_153 + pcb_180)sum PCBmg/kgHoyer, MandyCalculatedanalyzed in the <2000 µm fraction, of dry matter
101alpha-Hexachlorocyclohexanea-HCHµg/kgHoyer, MandyDIN EN ISO 10382:2003-05in the <2000 µm fraction, of dry matter
102beta-Hexachlorocyclohexaneb-HCHµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
103gamma-Hexachlorocyclohexaneg-HCHµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
104ortho,para-Dichlorodiphenyldichloroethaneop-DDDµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
105para,para-Dichlorodiphenyldichloroethanepp-DDDµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
106ortho,para-Dichlorodiphenyldichloroethyleneop-DDEµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
107para,para-Dichlorodiphenyldichloroethylenepp-DDEµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
108ortho,para-Dichlorodiphenyltrichloroethaneop-DDTµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
109para,para-Dichlorodiphenyltrichloroethanepp-DDTµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
1101,2,3-Trichlorobenzene1,2,3-Trichlorobenzeneµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
1111,3,5-Trichlorobenzene1,3,5-Trichlorobenzeneµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
1121,2,4-Trichlorobenzene1,2,4-Trichlorobenzeneµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
1131,2,3,4-Tetrachlorobenzene1,2,3,4-Tetrachlorobenzeneµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
1141,2,3,5-Tetrachlorobenzene1,2,3,5-Tetrachlorobenzeneµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
1151,2,4,5-Tetrachlorobenzene1,2,4,5-Tetrachlorobenzeneµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
116PentachlorobenzenePeCBµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
117HexachlorobenzeneHCBµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
118HexachlorbutadieneHCBUµg/kgHoyer, MandyDIN EN ISO 10382:2003-05analyzed in the <2000 µm fraction, of dry matter
119NaphthaleneNaphthmg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
120AcenaphthyleneAcenaphthylenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
121AcenaphtheneAcenaphthenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
122FluoreneFluorenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
123PhenanthrenePhenanthrenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
124AnthraceneAnthracenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
125FluorantheneFluoranthenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
126PyrenePyrenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
127Benz(a)anthraceneBenz(a)anthracenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
128ChryseneChrysenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
129Benzo(a)anthracenereneBenzo(a)anthracenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
130Dibenzo(a,h)anthraceneDibenzo(a,h)anthracenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
131Benzo(b)fluorantheneBenzo(b)fluoranthenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
132Benzo(k)fluorantheneBenzo(k)fluoranthenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
133Indeno(1,2,3-cd)pyreneIndeno(1,2,3-cd)pyrenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
134Benzo(ghi)peryleneBenzo(ghi)perylenemg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
135Polychlorinated biphenyl 28PCB_28mg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
136Polychlorinated biphenyl 52PCB_52µg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
137Polychlorinated biphenyl 101PCB_101µg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
138Polychlorinated biphenyl 118PCB_118µg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
139Polychlorinated biphenyl 138PCB_138µg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
140Polychlorinated biphenyl 153PCB_153µg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
141Polychlorinated biphenyl 180PCB_180µg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
142alpha-Hexachlorocyclohexanea-HCHµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
143beta-Hexachlorocyclohexaneb-HCHµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
144gamma-Hexachlorocyclohexaneg-HCHµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
145ortho,para-Dichlorodiphenyldichloroethaneop-DDDµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
146para,para-Dichlorodiphenyldichloroethanepp-DDDµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
147ortho,para-Dichlorodiphenyldichloroethyleneop-DDEµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
148para,para-Dichlorodiphenyldichloroethylenepp-DDEµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
149ortho,para-Dichlorodiphenyltrichloroethaneop-DDTµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
150para,para-Dichlorodiphenyltrichloroethanepp-DDTµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
1511,2,3-Trichlorobenzene1,2,3-Trichlorobenzeneµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
1521,3,5-Trichlorobenzene1,3,5-Trichlorobenzeneµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
1531,2,4-Trichlorobenzene1,2,4-Trichlorobenzeneµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
1541,2,3,4-Tetrachlorobenzene1,2,3,4-Tetrachlorobenzeneµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
1551,2,3,5-Tetrachlorobenzene1,2,3,5-Tetrachlorobenzeneµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
1561,2,4,5-Tetrachlorobenzene1,2,4,5-Tetrachlorobenzeneµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
157PentachlorobenzenePeCBµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
158HexachlorobenzeneHCBµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
159HexachlorbutadieneHCBUµg/kgHoyer, MandyConverted from the <2000 µm fraction to the <63 µm fraction using the grain size fractionsin the <63 µm fraction, of dry matter
160Inorganic contamination indexInorg con IHoyer, MandyMultiple linear regression of the concentrations of toxic metals and arsenic, followed by a normalization stepmetals and arsenic
161Organic contamination indexOrg con IHoyer, MandyMultiple linear regression of the concentrations of all analyzed organic pollutants, followed by a normalization step
162Organic contamination indexOrg con IHoyer, MandyMultiple linear regression of the concentrations of all analyzed organic pollutants in the <63 ¬µm fraction, followed by a normalization stepbased on the concentrations in the <63 µm fraction
163Contamination indexCon IHoyer, MandyCalculatedmean of inorganic contamination index and organic contamination index <63 µm
Status:
Curation Level: Enhanced curation (CurationLevelC)
Size:
26835 data points

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