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Assessment of the behaviour of Potentially Toxic Elements (PTEs) in soil from the Sarno River Basin through compositional data analysis Thiombane Matar1*, De Vivo Benedetto1, Josep-Antoni Martín-Fernández2, Albanese Stefano1, Lima Annamaria1 (1) Università degli Studi di Napoli Federico II, Dipartimento di Scienze della Terra, dell’Ambiente e delle Risorse, Complesso Universitario di Monte Sant'Angelo, – Napoli,Italy. This study shows the applicability and importance of compositional data transformation, which relates perfectly relationships and dependencies between elements which can be lost when univariate and classical multivariate analyses are employed on raw or lognormal geochemical data. Due to the fact that geochemical data give relative information ( ratio of components) and mostly are right skewness and present outliers, we should apply a log ratio transformation to tend to a normal distribution of variables and hold the real correlation between relationships between them. Geochemical data Clustering Analysis Factor Analysis Clr biplot Compositional data transformation Factor score maps Correlation and origins of the PTEs Geogenic features Anthropogenic activities
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Features of the study areas
Sarno River Basin (500 Km2) Campagna region (Southern Italy) Mts. Somma-Vesuvius Mt.Lattari Mts. Picentini Pyroclastic and limestones deposits Sarno river High urbanisation and Industrial activities Intensive agriculture the wide extent of local industrial and agricultural activities release PTEs into the basin.
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Sampling procedure and preparation
319 samples in two saisons, specific grid sampling design SAR-SOB: 283 soil samples (density of 1S/ 2 Km2) SAR-SAR: 36 soil samples (1S/ 600m) Sampling procedure follows UE protocole ( Salminen et al., 1998) 1 sample (5 subsamples) in 100 squared meter and 0.5 kg in each corner and the center. Much of this variability can be attributed to the underlying parent material on which a soil has formed each sample is made up of five subsamples from corners and center of a 20 m square and are sampled from the uppermost 15 cm of mineral soil (nominally a depth of 5 – 20 cm allowing for vegetation cover and surface litter.
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Sampling procedure and preparation
Homogenize, drying and sieved samples in < 2mm seize 50g sample sent to Vancouver ACME Laboratory (Canada) Acqua regia extraction , ICP-MS spectrometry 53 inorganic Elements: Ag, Al, As, Au, B, Ba, Be, Bi, Ca, Cd, Ce, Co, Cr, Cs, Cu, Fe, Ga, Ge, Hf, Hg, In, K, La, Li, Mg, Mn, Mo, Na, Nb, Ni, P, Pb, Pd, Pt, Rb, Re, S, Sb, Sc, Se, Sn, Sr, Ta, Te, Th, Ti, Tl, U, V, W, Y, Zn
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Compositional data Analysis
Compositional data are parts of some whole which carry relative information (ratios of components) Usual units of measurement: parts par unit, percentages, ppm, ppb, concentrations.. Sum of the data subject is constant (100%, 1 millions ppm, etc..) spurious correlation may arise when the raw data is used (Karl Pearson, 1897) Lognormal approach was created to resolve this problem ( normalization ) The sample space of compositional data (D-part simplex S) should be moved to real space RD or RD−1 (John Aitchison, 1982, 1986) using log-ratio transformations
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Compositional data Analysis
Log-ratio Transformations Additive log-ratio transformation (John Aitchison, 1986) Centered log-ratio transformation Euclidean geometry in real space is not a proper geometry for compositional data (orthogonality between vectors is taken into account, distances between data-points are considered). The results of the procedure to construct such a new basis are called sequential binary partitions, and the constructed basis vectors are called balances Isometric log-ratio transformation (Egozcue et al, 2003)
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Multivariate Analysis
Hierarchical Clustering Analysis Ordinary Euclidean distance between vectors of clr coefficients are equal to the Aitchison distance of their corresponding compositions. This also holds for the inner product and the norm, i.e. Clustering analysis using clr transformed data enhances groups of elements and the correlation between variables (use of Aitchison distance)
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Multivariate Analysis
Clr biplot Association 1: Ca-Mg Association 2: Na-K-P-B-Rb-Ba Association 3: Zn-Cd-Pb-Hg –Ag-Au Association 4: As-U-Th-Zr-La-Li Association 5: Fe-Ti-Co-V Association 6 : Ni, Cr
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Multivariate Analysis
Clr biplot (Amalgamation) Most of the SAR-SAR samples ( samples along Sarno river) are linked to the Clr-Amag (Cr-Ni) vertex As-U-Th-Zr-La-Li and Fe-Ti-Co-V Associations might be related to the same origin
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Multivariate Analysis and factor score maps
Factor Analysis Raw data Centered log-transformed data It reduces attribute space from a larger number of variables to a smaller number of factors (each factor carries correlation between the variables which may have the save origin). Total variance for Clr transformation (74.99%) greater than that the use of raw data (69.54%)
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Multivariate Analysis and factor score mapping
Factor score maps ArcGIS and GeoDAS (Fractal and multifractal IDW maps) Concentration-area (C-A) fractal plot (spatial association and singularity) This method tries to locate and group pixels on the map sharing concentrations apparently varying according to a spatial law Factor score ranges and thresholds Fractal and multifractal IDW: It is a method that preserves high frequency information, which is lost in any conventional moving average methods such as kriging and ordinary IDW. This method takes into account both spatial association and local singularity. This method tries to locate and group pixels on the map sharing concentrations apparently varying according to a spatial law.
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Multivariate Analysis and factor score maps
Raw data Elevated factor scores near the slopes of Mts. Somma–Vesuvius Clr data Factor score association of elements is related to features which settle to the slope of the Somma.vesuvius volcano and decrease gradually in inner basin. In fact it’s related to the Potassic and ultrapotassic rocks of the Mt.Somma Vesuvius Factor score values decrease gradually from the slope of the Mt.Vesuvius to inner basin Factor 1 element associations is related to the igneous formations and volcanic soils Potassic and ultrapotassic lavas and pyroclastic materials
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Multivariate Analysis and factor score maps
Raw data Elevated factor scores is mapped near Solofra and surrounding Clr data Low factor scores values correspond to the main urban cities Sedimentary materials dominated by silico-clastic deposits Anthropogenic sources (high rates of fossil fuel combustion and vehicle emissions)
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Multivariate Analysis and factor score maps
Raw data Elevated factor scores values correspond to the main Urban cities Clr data Low factor scores values Map geological features (Mts. Lattari mostly) inner the basin Anthropogenic sources (high rates of fossil fuel combustion and vehicle emissions) Limestone and Dolostone of the Mts. Picentini–Taburno and Mts.Lattari
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Multivariate Analysis and factor score maps
Raw data Elevated factor scores values are located near Solofra and surrounding Clr data Highest factor scores values Are found all along the Sarno River and Solofra tributaries Cr-Ni association is related to anthropogenic activities which release these PTEs into the River Solofra Tannery industries are the main industries which use Chromium and Nickel in the Tanning processes. It might be confirmed that these Industries release their waste water into the Sarno river
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Summarize of the main points
Compositional data need a logratio transformation for correlation analysis Logratio transformation enhances better the interrelationships between variables Clr logratio transformation enables to correlate the main geological features and anthropogenic activities which control the elements associations into the basin Factor score maps lay out the origin of PTEs release of wastewater from Solofra tanneries district (Chromium and Nickel) into the Sarno River vehicle emission (Pb, Zn, Cd, Co)
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Assessment of the behaviour of Potentially Toxic Elements (PTEs)
in soil from the Sarno River Basin through compositional data analysis Thank you
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