Next Article in Journal
Increasing Summer Rainfall and Asymmetrical Diurnal and Seasonal Warming Enhanced Vegetation Greenness in Temperate Deciduous Forests and Grasslands of Northern China
Next Article in Special Issue
OpenSWAP, an Open Architecture, Low Cost Class of Autonomous Surface Vehicles for Geophysical Surveys in the Shallow Water Environment
Previous Article in Journal
Remote Sensing of Volcanic Processes and Risk
Previous Article in Special Issue
Beyond Never-Never Land: Integrating LiDAR and Geophysical Surveys at the Johnston Site, Pinson Mounds State Archaeological Park, Tennessee, USA
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Geophysical and Sedimentological Investigations Integrate Remote-Sensing Data to Depict Geometry of Fluvial Sedimentary Bodies: An Example from Holocene Point-Bar Deposits of the Venetian Plain (Italy)

Department of Geosciences, University of Padova, Via G. Gradenigo 6, IT-35131 Padova, Italy
*
Author to whom correspondence should be addressed.
Remote Sens. 2020, 12(16), 2568; https://doi.org/10.3390/rs12162568
Submission received: 30 June 2020 / Revised: 31 July 2020 / Accepted: 7 August 2020 / Published: 10 August 2020
(This article belongs to the Special Issue Remote Sensing in Applied Geophysics)

Abstract

:
Over the past few millennia, meandering fluvial channels drained coastal landscapes accumulating sedimentary successions that today are permeable pathways. Propagation of pollutants, agricultural exploitation and sand liquefaction are the main processes of environmental interest affecting these sedimentary bodies. The characterization of these bodies is thus of utmost general interest. In this study, we particularly highlight the contribution of noninvasive (remote and ground-based) investigation techniques, and the case study focuses on a late Holocene meander bend of the southern Venetian Plain (Northeast Italy). Electromagnetic induction (EMI) investigations, conducted with great care in terms of sonde stability and positioning, allowed the reconstruction of the electrical conductivity 3D structure of the shallow subsurface, revealing that the paleochannel ranges in depth between 0.8 and 5.4 m, and defines an almost 260 m-wide point bar. The electrical conductivity maps derived from EMI at different depths define an arcuate morphology indicating that bar accretion started from an already sinuous channel. Sedimentary cores ensure local ground-truth and help define the evolution of the channel bend. This paper shows that the combination of well-conceived and carefully performed inverted geophysical surveys, remote sensing and direct investigations provides evidence of the evolution of recent shallow sedimentary structures with unprecedented detail.

1. Introduction

Modern coastal landscapes are widely shaped by meandering fluvial, fluvio-tidal and tidal channels, which over the late Holocene accumulated complex and extensive sedimentary bodies. These bodies today often define subsoil permeable systems [1] that are often exploited as water reserves for agricultural, industrial and civil uses [2], and are extremely sensitive to saltwater intrusion [3,4] as well as to contamination [5,6]. These channelized bodies commonly consist of clean and poorly consolidated sand, which can also be affected by liquefaction processes [7]. The 2012 earthquake that occurred in the northeastern portion of the Po Plain (Italy) was the cause of sand eruptions that occurred along Holocene paleochannels and crevasse splay deposits down to an 8 m depth [8,9].
Aerial photographs and satellite images are excellent tools to identify and map late Holocene coastal channel networks since the former provide aerial data from the 1950s to present [10,11,12,13] and the latter provide multispectral analysis to highlight surficial paleochannel configurations [14,15,16].
Excellent examples of remote-sensing applications for these types of geomorphological studies can be found in the recent literature [17,18,19,20,21]. Despite the advantages, particularly in locating the position of these surficial bodies, and possibly distinguishing between tide- and fluvial-generated meanders [22], remote sensing alone is of course not capable of providing information at depth, thus remaining essentially a qualitative tool for the characterization of 3D geological structures. On the other hand, direct field surveys [23,24] and microrelief analysis [10,23,25] can provide further information either locally at depth or extensively at the surface. Regardless, a 3D reconstruction is still difficult with these means only [26], if not as a result of interpolation of scarce scattered data.
Addressing these issues requires that extensive and high-resolution data are available to map large areas and, at the same time, investigate the subsoil to a certain depth. This calls for geophysical methods (as they are designed to collect data informative about the subsoil, unlike remote sensing sensu strictu) that can also be deployed rapidly with limited or no ground contact so that large areas can be investigated. The most suitable methods for these purposes are those based on electromagnetic processes. In particular, approaches based on electromagnetic induction (EMI) allow for noncontact subsurface investigation, with no intrinsic limitations as posed, for instance, to wave-propagation EM methods such as ground-penetrating radar (GPR) that can be strongly limited in their depth propagation by the ground electrical conductivity.
EMI is a well-established technique that dates back nearly one century [27] and is based on Faraday’s law of electromagnetic induction. The technique is articulated in a variety of specific instrument designs and investigation strategies [28] ranging in investigation depth from very shallow (the first meter or so) to tens of kilometers. For shallow applications [29,30], EMI has had widespread use in hydrological and hydrogeological characterizations [31,32,33], hazardous waste characterization studies [34,35], precision-agriculture application locations [36,37,38], archaeological surveys [39,40], geotechnical investigations [41] and unexploded ordnance (UXO) detection [42]. EMI measurements at small scale are typically conducted in the frequency domain (frequency domain electromagnetics or FDEM), and the results are classically expressed as apparent electrical conductivities (ECa) [43] using the so-called low-induction number approximation [44]. In addition to ECa mapping, the development of multifrequency and multicoil instruments has recently enabled the possibility of inversion of EMI measurements to provide quantitative models of depth-dependent electrical conductivity (EC), as the different acquisition configurations either in terms of coil geometry or frequency allow for multiple independent data to be acquired in sufficient number to warrant inversion. The majority of inversion algorithms use a 1D forward model based on either the linear cumulative sensitivity (CS) forward model proposed by [44] or nonlinear full solution (FS) forward models based on Maxwell’s equations (e.g., [45,46]). As with EMI mapping, applications using inverted EMI data have also been diverse (e.g., [47,48,49,50,51,52]). Applications typically focus on using an inversion based on either the CS or an FS forward model to produce regularized, smoothly varying models of EC with fixed depths or sharply varying models of EC where layer depths are also a parameter. In the most advanced cases, a full 3D model of electrical conductivity can be reconstructed over a relatively large area, similar to what can be obtained at a larger scale by using, e.g., time-domain airborne EMI systems (e.g., [53]). The use of small FDEM measurement systems, with rapid response and easy integration into mobile platforms, is the key factor in the success of EMI techniques for near-surface investigations in these fields, as they allow dense surveying and real-time conductivity mapping over large areas in a cost-effective manner. However, sufficient control on the acquisition geometry is often needed, as the instrument response has a strong dependence also on the elevation above ground and the relative height of the primary and secondary coils [47].
The purpose of this paper is to show how the integrated use of remote sensing, EMI and direct stratigraphic investigations can provide an effective and comprehensive 3D view of the geometry of a fluvial sedimentary body. Results from the present study highlight the importance of an integrated approach to understand subsurface deposits.

2. Materials and Methods

2.1. Geological Setting and Study Area

The Venetian Plain is located at the northeastern end of the Po Plain, the largest Italian alluvial plain, and was generated during Holocene transgression by aggradation of fluvial meandering channels [23,24]. Specifically, the study area is located at the boundary between the Venetian Plain and the Po River Delta, in a zone which is characterized by a dense network of alluvial ridges and sand bodies that are the geomorphological products of the complex interaction between the Adige and Po Rivers during the late Holocene (Figure 1a) [25,54]. These sedimentary bodies currently host a multilayered system of phreatic and confined aquifers that are affected by saltwater contamination [4,55] and intensive water exploitation. The fluvial sedimentation occurred in an aggrading setting related to the marine highstand, and meander belts often correspond to fluvial ridges slightly elevated over the floodplain (i.e., 2 to 5 m above sea level (asl)) [54]. The present surface is a typical lowland landscape, which developed in the last 5000 years by the avulsions of the Adige and Po rivers [25].
The investigated site is located near the village of Anguillara Veneta (Figure 1b), about 1 km north of the current channel of the Adige River, in an area with surface elevations ranging between 0.7 and 2.0 m asl, where traces of abandoned meanders are visible in several aerial images and could be followed for about 7 km, from Stanghella to Anguillara Veneta. These paleohydrographic traces run nearly parallel to the present Adige River, even if they are slightly out of the natural levee deposits connected to the fluvial ridge of Adige. The river activated its present direction since the early Middle Age, while before it used to flow along the meander belt running from Este to Monselice to Chioggia (from west to east) [56]. Near Anguillara Veneta, the present course of the Adige River cuts the so-called fluvial ridge of Rovigo–Saline–Cona, which was formed by the Po River between 4500 and 3500 years BP [25].
The area experienced strong anthropogenic activity since the Roman period, when extensive field systems were settled in the whole Venetian Plain and parts of the Po Delta [25]. A major phase of reclamation started in the 16th century, when the Venetian Republic started the strong management of the river network, leading to the construction of the dense network of dikes, canals and ditches that still characterizes the landscape. During the same period, the Gorzone Canal was also cut, which represents the northern boundary of the study area, to convey the water discharge of the Agno–Guà–Frassine–Santa Caterina river system towards the Adriatic Sea. During the first part of the 20th century, the reclamation was extended to the coastal plain, where large portions of swamps and lagoon landscapes were drained through the excavation of canals and the use of pumping stations. These interventions made it possible to artificially lower the groundwater table below the surface and to cultivate seasonal crops (e.g., corn, wheat, bit and soya bean) and vegetables. In the last decades, several strong leveling interventions were carried out to improve the efficiency of the new draining system, as in the field investigated for this study. Besides the positive results, unfortunately, the reclamation also induced fast land subsidence caused by groundwater withdrawal, compaction of the drained soil and degradation of the organic matter formerly present in the marsh sediments [57]. From the downlift rate of the natural subsidence, ranging around 1 mm/y [58], in the last century the velocity strongly increased up to average values of 2 to 5 mm/y with large sectors up to 10 mm/y [59].
A large number of historical photos and maps are available for the Venetian Plain, along with freely distributed satellite images. Study sites are easily accessible for geophysical investigation and sedimentary cores. For these reasons, this study area represents an ideal site to develop and test the proposed integrated approach.

2.2. Remote Sensing

The study site was selected after the identification of the paleomeanders in the aerial and satellite images. In particular, the first characterization was carried out on some satellite images available from Google Earth, which generally are pansharpened images of true-color composite bands of the Digital Globe company (Westminster, CO, USA) (e.g., Ikonos, QuickBird, WorldView and GeoEye missions). We selected the images with a detailed spatial resolution between 1.0–0.5 m (i.e., images 31/07/2004; 23/06/2007; 06/06/2010; 21/04/2012; 06/08/2013; 16/08/2013; 28/03/2015; 22/06/2017; 18/07/2018) and imported them into the GIS software ArcMap (version 10.7.1) [60] and QGIS 3.10 [61] for image processing and comparison with the images available as basemap reference in ESRI. Moreover, we also considered several zenithal conventional aerial pictures available from the cartographic service of Veneto Region [62], consisting of scanned versions of black/white and color pictures from 1955 to 2008, with scales from 1:33,000 to 1:5000.
To investigate the spectral characteristics of the field surface, we analyzed some images from the satellite Sentinel-2, obtaining the normalized difference vegetation index (NDVI) and the normal difference moisture index (NDMI) [63,64,65]. These indices have a geometric resolution of 10 m and, being sensitive to plant health and hydraulic stress, respectively [66,67], were used to improve the identification of the traces of paleomeanders by linking sedimentology to vegetation health of the area. In particular, we produced the NDVI and NDMI not only from summer scenes, but also from different seasons and years by processing the multispectral bands through the semiautomatic classification plugin (SCP) [68] and raster calculator of QGIS 3.10. In fact, in the study area the cultivated plants change with seasons; in addition to the crops growing during summer, winter cultivations such as wheat, barley and different vegetables can be present.
Satellite, aerial and processed images were visualised in a properly georeferenced 3D space provided by the Move 2018.2TM [69] software.

2.3. Geophysical Investigations

The EMI surveys at the site were collected using a GF Instruments CMD-Explorer probe [70] that is a six-coil system (three coplanar pairs) operating at a single frequency equal to 10 kHz. The probe can be operated in both horizontal coplanar (HMD) and vertical coplanar (VMD) configurations [71], providing six independent measurements that are generally associated with six different apparent depths of investigation (Table 1). To acquire all six configurations for each geographical location it is, however, necessary to reoccupy with some acceptable degree of approximation the same location twice (once for each coil orientation).
The FDEM probe was mounted on a specifically designed wooden carriage and connected to a Trimble 5800 GPS for continuous positioning, collecting data every second [72]. The wooden support was towed by a small tractor (Figure 2a). The acquisition apparatus adopted satisfies two fundamental requirements that proved extremely effective in terms of data quality [73,74]:
(a)
Reoccupation of the same location is warranted by the GPS within the required precision (note that the sonde is a few meters long);
(b)
The setting of the sonde is the same at all locations, with no changes of either the height above ground or the setting of the sonde that is maintained largely horizontal.
In this manner, we collected about 20,000 EMI data points (Figure 2b), each in both HMD and VMD modes, with about one point every 0.5 m along the acquisition lines. The lines have a mutual distance of roughly 10 m (Figure 2b).
EMI data were then inverted to retrieve real soil conductivity values. For this purpose, we used the Interpex IX1D inversion software [75], a 1D routine based on smooth depth inversion according to the so-called Occam’s approach [76]. The very dense spatial sampling allowed for the reconstruction of the subsoil practically in a 3D fashion by the juxtaposition of the 1D inverted profiles. For all locations, the same number of layers (eight) was used for the inversion, thus producing a consistent dataset. The results are presented in terms of 2D horizontal maps at several depths, that were then georeferenced using the Move 2018.2TM [69] software, which also allowed creation of 3D surfaces, by the linear method, and tetravolumes.

2.4. Sedimentary Cores

Six cores were recovered at the study site to analyze sedimentary features of the study deposits and provide ground-truth for geophysical and remote-sensing data (Figure 2c). The core locations were established based on remote-sensing and geophysical data. Cores were collected by using an Eijkelkamp hand auger and a continuous drilling core sampler with rotary technique. Three cores were recovered using an Eijkelkamp hand auger, through a gouge sampler with a length of 1 m and a diameter of 30 mm, which prevented sediment compaction. Depth for these cores spanned from 2.5 to 6 m (Figure 2c). Three additional cores were recovered using a continuous drilling core sampler with rotary technique. These latter cores, which were 10 cm in diameter and reached a depth of 10 m, were located in the upstream, central and downstream part of the study bar (Figure 2c). Cores were kept humid in PVC liners and successively cut longitudinally, sampled for grain-size analysis, photographed at high resolution and preserved for making dry peels with epoxy. Each core was characterized following the basic principles of facies analysis: highlighting sediment grain size, color, oxidation, sedimentary structures and occurrence of bioturbation, plant debris and shell fragments.
The terminology used in this work is graphically summarized in Figure 3. The channel thalweg is defined as the deepest part of the active channel, where the coarsest deposits occur. Riffles and pools are situated at bend inflections and bend apexes, respectively, and correspond to the shallower and the deeper portions of the thalweg, respectively. Sinuosity is calculated as the ratio between the along-channel distance between two adjacent riffles and their linear distance (Figure 3). Straight channels are characterized by sinuosity close to 1, whereas sinuous channels reach values higher than 2.5.

3. Results

3.1. Remote Sensing

The analyzed satellite images and aerial pictures give a consistent idea of the changes in the land use of the area and the visibility of the paleohydrographic traces over the last 60 years. In particular, recent high-resolution true-color composite images allow mapping these features with submetric accuracy. The traces mainly consist of cropmarks with vegetation suffering from hydraulic stress during the growing season, and dead patches in July and August. Significant changes can be observed over very short periods (compare, e.g., Figure 4d,f) during the hot season, while sensitivity is low in spring time (e.g., Figure 4e) and is lost in winter, when the fields are covered by scarce vegetation and are bare and plowed, respectively. By comparing satellite images mostly taken during the growing season (i.e., those that best show the traces) differences in vegetation colors allow the identification of buried morphologies of two distinct reaches, hereafter named Reach A and Reach B, and a crevasse splay. Reach A consists of two major bends, called Bend 1 and Bend 2 (Figure 4b). The NDVI and NDMI images derived from Sentinel-2 summer images (Figure 5c,d) clearly show the differential behavior of the paleomeanders in comparison to the external floodplain and the inner portion surrounded by Reach A; the vegetation growing on more permeable sandy soil is less healthy than the one living on finer sediments. The paleohydrographic traces are much more evidenced by NDVI and NDMI during the summer season and they clearly help in identifying the general pattern of the abandoned channels. However, the rather low resolution of the Sentinel-2 images does not contribute significantly to discriminating in detail the specific morphological and sedimentological features composing the paleohydrographic traces.
Bend 1 is an open bend, with an SSW–NNE bend axis, and is characterized by a sinuosity of about 2.2 and a radius of curvature of ca. 140 m. The scroll-bar pattern is particularly clear from cropmarks, in the northcentral portion of the bend (Figure 4c,d), showing a different signal compared to the residual channel fill (i.e., light cropmark when the others are dark, and vice-versa), testifying the progressive growth of the meander bend. The channel fill displays a width of about 15–20 m and can be better defined where bounded by opposite-trending scroll-bar patterns, like in the upstream side of the bend. The riffle-to-riffle distance on the channel fill is about 260 m.
Bend 2 is a low sinuosity bend (i.e., 1.12), with an NW–SE bend axis, characterized by an estimated radius of curvature and riffle-to-riffle distance of 135 and 230 m, respectively. Bend 2 is sited upstream from Bend 1, and shows a scroll-bar pattern that testifies a progressive expansional growth style (sensu [77]) of the bend.
Reach B forms a bend occurring south of Reach A, but is less visible from satellite images and its sinuosity cannot be defined. The radius of curvature is ca. 350 m and the axis of the bend trends ca. SW–NE, although satellite images do not show a clear bar-scroll pattern and the position of the relevant channel fill. Reach B cuts over Reach A suggesting that it developed after a chute channel that cut off Reach A [78], which was later abandoned. Additionally, along the eastern side of Reach B, (Figure 4d,f) a divergent pattern of minor channels point to a local development of a crevasse splay sourced from the downstream side of the bend. Several straight dark stripes, with a width of about 1 m, located on Reach B, can be interpreted as traces of abandoned ditches that were associated with a drainage system dating back to Renaissance times and dismissed later on (Figure 4d).

3.2. 3D Electrical Conductivity Model from EMI

The inversion of the EMI data produced a 3D volume of electrical conductivity values. The results are shown in Figure 6, where we elected to show the volume sliced horizontally at eight depth levels down to a depth of nearly 8 m below ground, corresponding each to a layer selected in the inversion approach. Note that the inversion was conducted with an Occam approach, but using a limited number of layers compatible with the information contained in the six different acquisition configurations obtainable with the CMD Explorer instrument.
An arcuate sedimentary body having low electrical conductivity (i.e., a resistive body) is clearly visible at a depth between 1 and 6 m below ground. The internal boundary of this arcuate body (see Slice 5 in Figure 6b) is fully visible in the maps, and shows a radius of curvature and a sinuosity of ca. 60 and 2.3, respectively. The external boundary (see Slice 5 in Figure 6b) slightly debouches from the maps, but its radius of curvature and sinuosity can be estimated to be ca. 135 and 2.2, respectively (Figure 6b), as also confirmed by remote-sensing results. Orientation of the outer boundary of this body fits with the orientation of meander Bend 1 of Reach A, as depicted by remote-sensing analyses, and is also consistent with the associated scroll pattern (Figure 4b), suggesting that these low-resistivity deposits represent the point-bar body associated with meander Bend 1 of Reach A. Of course, the main contribution of the EMI data is to provide continuous and extensive depth information that is not available from remote sensing. In the shallower layers (Slices 1–5), the arcuate point-bar body presents low conductivity values with σ < 20 mS/m, and its conductivity is still close to 40 mS/m at about 5–6 m below ground (Slices 6 and 7; Figure 6b). Note that the width of the most resistive part of the bar is clearly shrinking with depth, thus showing the 3D shape of the sand body. At larger depths (Slice 8—below 6.1 m) conductivity increases up to 180 mS/m, delimiting the base of the bar body. It must be noted, however, that the CMD Explorer provides, as a rule of thumb, reliable information only down to 6 m below ground and thus Slice 8 is effectively an extrapolation due to the need to have an infinite semispace at the bottom of the electrical conductivity model, and thus should be considered with care. Although the point-bar body shows a fairly homogeneous electrical resistivity, a subtle increase in resistivity values defines a 20 m narrow, NNE–SSW trending belt in the SE corner of Slices 2 to 6. The location of this belt fits with that of the abandoned channel forming the meander Bend 1 as apparent in satellite images (Figure 4b), and suggests that the higher resistivity values are linked to the coarser material of the deposits filling the abandoned channel. Deposits surrounding the low-resistivity point-bar body show conductivity values spanning from 80 to 250 mS/m, with values close to 100 mS/m down to 3 m below ground, increasing to 250 mS/m below 3 m. Comparison between geophysical data and geomorphic evidences suggest that these electrically conductive sediments represent floodplain deposits in which the Bend 1 meander was cut, thus developing the related point-bar sedimentary body.

3.3. Sedimentology

Core data provide the ground-truth information needed to calibrate/confirm geophysical data with localized information. The cores help define sedimentary features of the electrically resistive point-bar body, related channel-fill deposits and surrounding electrically conductive overbanks. All cores reveal that the deposits were intensely reworked by agricultural activities down to 80 cm below ground. Note that this fact may pose significant limitations to remote-sensing interpretation that is forcibly limited to surface images. Reworked deposits are dark brown and consist of very fine sand with a variable amount of mud. Point-bar deposits were completely cored at sites AV_a–c (Figure 7). Point-bar deposits occur from 0.8 m to a maximum of 5.4 m below ground and mainly consist of sand with a scarce percentage of mud. Cores AV_a–c reveal that bar deposits cover either organic-rich mud (core AV_b) or sandy deposits (cores AV_a and AV_c). Point-bar deposits are floored by a channel lag that consists of massive medium sand with pebble-sized mudclasts (Figure 8a). This basal lag is covered by lower bar deposits, consisting of 1–1.5 m of mud-free, well-sorted fine to medium sand, which is commonly massive or crudely plane-parallel stratified (Figure 8b). Upper bar deposits are ca. 2.5–3 m thick and consist of fine to very fine sand with subordinate mud layers. Sand is plane-parallel to ripple cross-laminated (Figure 8c) and contains mud for ca. 12%, 21% and 20% in the upstream, central and downstream zone, respectively. Mud layers (Figure 8c) range in thickness between 0.5 and 2 cm, and consist of massive or crudely laminated mud with plant debris. Lower bar deposits are ubiquitously mud free. The overall grain size of the bar deposits does not relevantly change along the bar, which appears as an almost monotonous sandy body from its upstream to downstream reach.
The overbank deposits were cored where geophysical investigations reveal the occurrence of electrically conductive sediments. These deposits mainly consist of silt-rich mud with subordinate sandy layers with horizontal bedding. Mud is massive and can be organic-rich (Figure 8d) or slightly oxidized in the lower and upper part of the overbank succession, respectively.

4. Discussion

4.1. Implications for Noninvasive (Remote Sensing and Ground-Based Electromagnetic) Investigations

This study shows how remote sensing and ground-based geophysical data represent an ideal combination of noninvasive techniques that can guide direct investigations and, at the same time, can be integrated to provide a 3D reconstruction of the shallow subsoil once supported by the local direct evidence for verification and calibration.
Our results show that in the study area the use of aerial images is very effective in supporting the rapid recognition of geomorphological and sedimentological features with a resolution approaching 0.5 m. However, the aerial pictures dating back to before the 1980s do not provide useful paleohydrographic evidence, probably because (a) conventional zenithal pictures were originally taken for cadastral purposes and, thus, were shot during the winter season when vegetation cover was limited; and (b) widespread leveling of the fields and use of strong plowing machines was common until that time, thus causing severe erosion of the topsoil, especially in the zones where convex landforms were formerly present, with slight accumulation in the depressions. Thus, in correspondence with natural levees and sand ridges related to scroll-bar sequences, the sandy and silty sediments were exhumed, showing a lighter signal in the soilmarks.
Cropmarks appear to be, in general, the most effective indicators of shallow geomorphological features in the considered environment. This is linked to the much higher permeability of the coarser sediments, leading to greater drainage and, in absence of irrigation, water stress to crops especially during the hot season (July and August). As documented in other areas of the Venetian Plain, e.g., [79], besides the weather condition of the period before the image acquisition, the maximum detail shown by the cropmarks strongly depends on the type of cultivated plants and, in particular, it decreases with the size of the leaves and the plant spacing. The best data are generally found in zones with soya bean or hay meadow crops. Wheat, barley and corn display variable visibility, as the first two are seeded in tight rows and have small leaves, but are harvested before mid July; in contrast, corn has a larger plant size and larger distance between rows, but is harvested in September or October and thus can (usefully) experience water stress. Note that this study was carried out analyzing freely available high-resolution images, reaching a resolution of about 0.5 m. This suggests that the use of specific images, acquired through latest commercial satellite or drone-borne multispectral scanners, could easily support the recognition of features between 0.1 and 0.5 m with superior results.
Geophysical data play a critical role in our analyses. They bridge the gap between surface-extensive information provided by remote sensing (that primarily guided the identification of the study area and the location of the surveys) with the information at depth carried out through traditional drilling and sampling operations. The latter in turn were positioned on the basis of remote sensing and geophysical evidence, thus minimizing the sampling to the locations where this information was needed for verification and calibration. The geophysical data constitute the backbone of the study in that they provide ultimately the 3D information to fully reconstruct the sedimentary structure of the site. This result, however, is not trivial to achieve.
First, great care must be posed in the acquisition phase. This entails not only the choice of the instrument and the strategy developed for covering a large area—in this case a (nonconductive) sledge towed by a tractor at sufficient distance not to induce current in the metal frame of the tractor itself. In addition, care must be paid when setting the instrument to have a good control of the measurement geometry, which is in turn essential to obtaining reliable inversion results. In this case, the stability of the sledge and the positioning care allowed us to obtain, for all data points, an RMS error of less than 10% between measured and simulated apparent conductivity data at the end of the inversion process. Note that carrying the same sonde by hand, particularly on rugged terrain, can easily unbalance the instrument, with measurements thus taken with some coils much closer to the ground than others. This might induce a very large measurement error that is impossible to correct a posteriori, as the true acquisition geometry is then completely unknown.
Second, obvious outliers must be removed from the dataset. These may include negative or extremely high apparent conductivity values (that are physically implausible for the given acquisition geometry), which may be due to local metallic or magnetic features.
Third, an accurate reconstruction of positioning must be made. The availability of reliable colocated data from HMD and VMD is essential to have the six independent pieces of information necessary for depth inversion. This requires both a guided pace in the field to reoccupy roughly the same locations and proper postprocessing to assemble the data that pertain to the same reasonable surrounding of each measurement point, in this case with a radius of 1 m. Noting that the sonde size itself is of a few meters (Figure 2a), this accuracy is perfectly acceptable for the purpose at hand.
Fourth, geophysical inversion is an inherently ill-posed problem. In this case, it means that while the general pattern of the electrical conductivity variation with depth is constrained by the data, the subtler details may not be retrieved uniquely. In other words, at each measurement location, a number of different 1D models, which all, however, maintain certain key patterns, can be equivalent in terms of goodness of fit to the measured data within the data uncertainty range. In particular, for example, if conductivity increases with depth, all inverted profiles will display the same general pattern. However, the transition from lower to higher conductivity may happen continuously, or in steps, and steps may occur at slightly different depths. While this can be viewed as a weakness of geophysical methods (and EMI in this particular case), it is not without remedy. Indeed, geophysics should never be applied without some “ground-truth” coming (as in this case) from drilling investigations (local and not without their uncertainties, but still necessary). Thus, an iterative revision of the inverted vertical profiles was conducted to select, among the plausible electrical conductivity profiles those that also fit reasonably to the direct evidence where this evidence is available. The procedure was simply performed manually, particularly selecting suitable layer interfaces compatible with drilling evidence. This type of procedure should always be applied, and it is in the energy exploration where 3D seismic data are blended, e.g., with well logs coming from deep borings. For the geophysical data used in this study, the “ground-truth” is given by the local comparison between lithology from sedimentary cores (AV_1, AV_a, AV_b and AV_c) and electrical conductivity derived from EMI inversion at the same locations. A plot showing the resulting correlation, also taking into account the variability of electrical conductivity for the same lithology (shown as standard deviation error bars) is shown in Figure 9.

4.2. Implications for Investigation of Meandering River Deposits

Integrated remote-sensing, geophysical and sedimentological approaches provide insights to discuss key features of investigated point-bar deposits, with specific emphasis on their genesis and internal grain-size variability.
The external boundary of this body is consistent with the morphology of a point bar that originated through lateral migration of a meandering channel [80,81,82]. Nevertheless, the curved profile of the inner boundary suggests that the bar accretion started from the inner bank of an arcuate channel that showed a sinuosity of ca. 2.3 (Figure 6b). This evidence contrasts the common assumption that point bars originate from a progressive increase in channel sinuosity of a relatively straight channel, which gradually migrates laterally until reaching a sinuous configuration [83,84,85,86]. The onset of accretion from a sinuous channel allows for storing a reduced volume of bar sediment in comparison with that produced by inception from a straight channel. In the study case, the 3D reconstruction of the bar body from EMI data shows that about 1.8 million m3 of sand are stored in the arcuate point bar body (Figure 10a). If one assumes that the accretion of this bar started from a straight channel, as would be suggested by the application of classical sedimentological models to remote-sensing data, the estimated volume of the bar would have been of ca. 3.1 million m3 of sand (Figure 10b), leading to a remarkable overestimation of the accumulated sand. The onset of point-bar bar accretion from a sinuous channel was probably driven by pre-existing floodplain morphologies, which, at the early stage of channel development, forced water to drain through the paths defined by adjacent depressed areas [87,88]. The establishment of a curved planiform morphology could have been forced by floodplain lithological and morphological heterogeneities [89,90], which are associated with the occurrence of numerous overbank subenvironments, including crevasse-splays, levees, floodplain lakes and floodbasins (cf., [91]). Different deposits and morphologies associated with these subenvironments possibly forced the newly formed watercourse to connect adjacent depressed areas and assume a sinuous geometry.
The location of the sedimentary cores within the point bar provides information concerning both vertical and lateral grain-size variability within this sedimentary body, with a particular focus on the comparison between upstream and downstream bar deposits. Although a fining-upward grain size distribution has been broadly considered to be typical of point-bar deposits [85,91,92], a certain variability of vertical grain-size distribution has also been documented [93,94]. Core data show that muddy layers occur in the upper part of the bar, although mud is visibly subordinate to sand. The grain size of sand varies significantly neither vertically nor downstream, and the bar is, therefore, characterized by widespread weak vertical grain-size trends. Although the lack of a clear vertical fining in the upstream bar zone is consistent with the occurrence of high bed shear stress [95,96], the paucity of muddy deposits in the downstream part of the bar is a peculiar feature, which cannot be ascribed to the overall lack of mud in the system, being that the overbank deposits are entirely made of mud. The open morphology of the bend [97] associated with the study bar could have hindered the formation of a dead zone, which commonly forms in sharp bends [18], preventing the accumulation of mud in the downstream bar zone.
Figure 11 shows a summary of the workflow we used to extract the relevant information from each data source and blend the pieces of information towards the final conceptual 3D distributed model of the studied site.

5. Conclusions

This paper presents a successful integrated approach to analyze the distribution of sedimentary facies of a paleomeander in the Southern Venetian Plain, Northeastern Italy. The approach is based on a combination of remote-sensing (aerial and satellite) data, geophysical investigations (electromagnetic surveys) and direct sedimentary coring.
From the methodological point of view, we show that the combined use of noninvasive techniques such as remote sensing and ground-based geophysical data provides an effective method for the purpose at hand. In particular, remote sensing is quite effective for the identification of sites of interest and features at a metric scale, which is potentially linked to different subsoil structures. In the case considered here, cropmarks are the most useful features observed from the satellite images, due specifically to the water stress induced in crops by the higher permeability of sandy bodies with respect to silty sediments. However, remote sensing can only provide information on the ground surface. On the contrary, geophysical methods are specifically designed to reconstruct the subsurface structure on the basis of contrasts of geophysical parameters. In this case, we used electromagnetic induction (EMI) methods, and particularly an FDEM small-scale multicoil system. Well-designed, acquired, processed, and inverted EMI data allowed us to extend the surface information provided by remote sensing to a maximum depth exceeding 6 m below ground level, allowing the construction of a 3D model of electrical conductivity of the subsoil. Direct investigations via sedimentary core drilling were positioned on the basis of remote sensing and geophysical data, in order to confirm and calibrate the geophysical investigations, which were also partly reinverted on the basis of the new evidence. The overall cycle of investigations thus allowed us to set up a 3D stratigraphic model of the site, consistent with all available data. On the other hand, the sequence of investigation activities was designed in such a manner that the information collected at one step optimized the design of the next step, thus reducing the overall effort required to complete the task.
From the sedimentary point of view, the point bar studied shows an uncommon arcuate morphology, that contrasts the common assumption that point bars originate from a progressive sinuosity increase of a relatively straight channel that migrates laterally until reaching a sinuous configuration. This can be explained by considering the variety of alluvial subenvironments in the floodplain. These floodplain heterogeneities likely controlled water fluxes over the platform, by facilitating water drainage within traces of depressed areas, defining the sinuous shape of the study channel during the very first phases of channel formation. As far as grain size distribution is concerned, although classical facies models highlight overall trends of upward and downstream fining of grain size within point-bar deposits, the grain-size trends of the study bar do not vary significantly either vertically or laterally. The bar is, indeed, characterized by a widespread weak vertical grain-size trend, and it appears as a homogeneous body of medium to fine sand. The lower mud content in the downstream portion was probably a result of the open morphology of the bend that could have prevented the formation of the dead zone, which is commonly directly linked to mud accumulation in the downstream portion of the sharp bends.
This study provides a solid basis for developing more detailed sedimentological investigations, which could be improved including acquisition of data concerning internal stratal architecture of the alluvial deposits. GPR investigations and recovery of undisturbed sedimentary cores would provide further relevant insights to this approach, with relevant follow up in the frame of subsurface exploration or management of surficial aquifers. Detection of the distinctive morphometric and sedimentological features of Late Holocene paleochannels would allow a comparison with those of the rivers draining the area currently, and allow quantification of human impact on riverine dynamics [18].

Author Contributions

Data curation, E.B.; formal analysis, J.B. and G.C.; funding acquisition, M.G.; investigation, E.B., M.G., A.F. and J.B.; methodology, G.C., M.G. and J.B.; project administration, E.B. and M.G.; resources, M.G., J.B. and G.C.; software, G.C.; supervision, M.G.; validation, A.D.; visualization, E.B. and M.G.; writing—original draft, E.B., A.F., G.C. and J.B.; writing—review and editing, M.G., G.C. and A.D. All authors have read and agreed to the published version of the manuscript.

Funding

This work has been supported by project HYDROSEM (Progetti di Eccellenza CARIPARO 2017, Cassa di Risparmio di Padova e Rovigo): “Fluvial and tidal meanders of the Venetian-Po plain: From hydrodynamics to stratigraphy” project (PI. M. Ghinassi).

Acknowledgments

Reviewers and editors will be acknowledged. The authors thank M. Cosma for logistic support during field work and R. Bonato, the land owner of the study area.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Clement, W.P.; Barrash, W. Crosshole radar tomography in a fluvial aquifer near Boise, Idaho. J. Environ. Eng. Geophys. 2006, 11, 171–184. [Google Scholar] [CrossRef] [Green Version]
  2. Galgaro, A.; Finzi, E.; Tosi, L. An experiment on a sand-dune environment in Southern Venetian coast based on GPR, VES and documentary evidence. Ann. Geophys. 2000, 43, 289–295. [Google Scholar] [CrossRef]
  3. Nofal, E.R.; Amer, M.A.; El-Didy, S.M.; Fekry, A.M. Delineation and modeling of seawater intrusion into the Nile Delta Aquifer: A new perspective. Water Sci. 2015, 29, 156–166. [Google Scholar] [CrossRef] [Green Version]
  4. Da Lio, C.; Carol, E.; Kruse, E.; Teatini, P.; Tosi, L. Saltwater contamination in the managed low-lying farmland of the Venice coast, Italy: An assessment of vulnerability. Sci. Total Environ. 2015, 533, 356–369. [Google Scholar] [CrossRef] [PubMed]
  5. Desbarats, A.J.; Koenig, C.E.M.; Pal, T.; Mukherjee, P.K.; Beckie, R.D. Groundwater flow dynamics and arsenic source characterization in an aquifer system of West Bengal, India. Water Resour. Res. 2014, 50, 4974–5002. [Google Scholar] [CrossRef]
  6. Carraro, A.; Fabbri, P.; Giaretta, A.; Peruzzo, L.; Tateo, F.; Tellini, F. Effects of redox conditions on the control of arsenic mobility in shallow alluvial aquifers on the Venetian Plain (Italy). Sci. Total Environ. 2015, 532, 581–594. [Google Scholar] [CrossRef]
  7. Romeo, R.W.; Amoroso, S.; Facciorusso, J.; Lenti, L.; Madiai, C.; Martino, S.; Monaco, P.; Rinaldis, D.; Totani, F. Soil liquefaction during the Emilia, 2012 seismic sequence: Investigation and analysis. Eng. Geol. Soc. Territ. 2015, 5, 1107–1110. [Google Scholar] [CrossRef]
  8. Amorosi, A.; Bruno, L.; Facciorusso, J.; Piccin, A.; Sammartino, I. Stratigraphic control on earthquake-induced liquefaction: A case study from the Central Po Plain (Italy). Sediment. Geol. 2016, 345, 42–53. [Google Scholar] [CrossRef]
  9. Fontana, D.; Lugli, S.; Dori, S.M.; Caputo, R.; Stefani, M. Sedimentology and composition of sands injected during the seismic crisis of May 2012 (Emilia, Italy): Clues for source layer identification and liquefaction regime. Sediment. Geol. 2015, 325, 158–167. [Google Scholar] [CrossRef] [Green Version]
  10. Mozzi, P. Alluvial plain formation during the Late Quaternary between the southern Alpine margin and the Lagoon of Venice (Northern Italy). Geogr. Fis. Din. Quat. 2005, 7, 219–229. [Google Scholar]
  11. Ninfo, A.; Ferrarese, F.; Mozzi, P.; Fontana, A. High resolution dems for the analysis of fluvial and ancient anthropogenic landforms in the alluvial plain of Padua (Italy). Geogr. Fis. Din. Quat. 2011, 34, 95–104. [Google Scholar] [CrossRef]
  12. Castigoni, G.B. Geomorphology of the Po Plain. Earth Surf. Process. Landf. J. Br. Geomorphol. Res. Group 1999, 24, 1115–1120. [Google Scholar]
  13. Mehdi, S.M.; Pant, N.C.; Saini, H.S.; Mujtaba, S.A.I.; Pande, P. Identification of palaeochannel configuration in the Saraswati River basin in parts of Haryana and Rajasthan, India, through digital remote sensing and GIS. Episodes 2016, 39, 29–38. [Google Scholar] [CrossRef]
  14. De Rossetti, D.F. Multiple remote sensing techniques as a tool for reconstructing late Quaternary drainage in the Amazon lowland. Earth Surf. Process. Landf. 2010, 35, 1234–1239. [Google Scholar] [CrossRef]
  15. Wray, R.A.L. Palaeochannels of the Namoi River Floodplain, New South Wales, Australia: The use of multispectral Landsat imagery to highlight a Late Quaternary change in fluvial regime. Aust. Geogr. 2009, 40, 29–49. [Google Scholar] [CrossRef]
  16. Entwistle, N.; Heritage, G.; Milan, D. Recent remote sensing applications for hydro and morphodynamic monitoring and modelling. Earth Surf. Process. Landf. 2018, 43, 2283–2291. [Google Scholar] [CrossRef]
  17. Demarchi, L.; Bizzi, S.; Piégay, H. Regional hydromorphological characterization with continuous and automated remote sensing analysis based on VHR imagery and low-resolution LiDAR data. Earth Surf. Process. Landf. 2017, 42, 531–551. [Google Scholar] [CrossRef]
  18. Piégay, H.; Arnaud, F.; Belletti, B.; Bertrand, M.; Bizzi, S.; Carbonneau, P.; Dufour, S.; Liébault, F.; Ruiz-Villanueva, V.; Slater, L. Remotely sensed rivers in the Anthropocene: State of the art and prospects. Earth Surf. Process. Landf. 2020, 45, 157–188. [Google Scholar] [CrossRef]
  19. Langat, P.K.; Kumar, L.; Koech, R. Monitoring river channel dynamics using remote sensing and GIS techniques. Geomorphology 2019, 325, 92–102. [Google Scholar] [CrossRef]
  20. Righini, M.; Surian, N. Remote Sensing as a Tool for Analysing Channel Dynamics and Geomorphic Effects of Floods. In Flood Monitoring through Remote Sensing; Springer: Cham, Switzerland, 2018; pp. 27–59. [Google Scholar]
  21. Finotello, A.; Lanzoni, S.; Ghinassi, M.; Marani, M.; Rinaldo, A.; D’Alpaos, A. Field migration rates of tidal meanders recapitulate fluvial morphodynamics. Proc. Natl. Acad. Sci. USA 2018, 115, 1463–1468. [Google Scholar] [CrossRef] [Green Version]
  22. Fontana, A.; Mozzi, P.; Bondesan, A. Alluvial megafans in the Venetian-Friulian Plain (north-eastern Italy): Evidence of sedimentary and erosive phases during Late Pleistocene and Holocene. Quat. Int. 2008, 189, 71–90. [Google Scholar] [CrossRef]
  23. Fontana, A.; Mozzi, P.; Bondesan, A. Late Pleistocene evolution of the Venetian-Friulian Plain. Rend. Lincei 2010, 21, 181–196. [Google Scholar] [CrossRef]
  24. Piovan, S.; Mozzi, P.; Stefani, C. Bronze age paleohydrography of the southern Venetian Plain. Geoarchaeology 2010, 25, 6–35. [Google Scholar] [CrossRef]
  25. Brivio, L.; Ghinassi, M.; D’Alpaos, A.; Finotello, A.; Fontana, A.; Roner, M.; Howes, N. Aggradation and lateral migration shaping geometry of a tidal point bar: An example from salt marshes of the Northern Venice Lagoon (Italy). Sediment. Geol. 2016, 343, 141–155. [Google Scholar] [CrossRef]
  26. Parasnis, D.S. Principles of Applied Geophysics, 5th ed.; Chapman & Hall: London, UK, 1997. [Google Scholar]
  27. Telford, W.M.; Geldart, L.P.; Sheriff, R.E. Applied Geophysics; Cambridge University Press: Cambridge, UK, 1990. [Google Scholar]
  28. Everett, M.E.; Meju, M.A. Near-Surface Controlled-Source Electromagnetic Induction: Background and Recent Advances. In Hydrogeophysics; Rubin, Y., Hubbard, S.S., Eds.; Springer: Berlin/Heidelberg, Germany, 2005; Volume 50, pp. 157–184. ISBN 978-1-4020-3101-4. [Google Scholar]
  29. Boaga, J. The use of FDEM in hydrogeophysics: A review. J. Appl. Geophys. 2017, 139, 36–46. [Google Scholar] [CrossRef]
  30. Lesch, S.M.; Strauss, D.J.; Rhoades, J.D. Spatial Prediction of Soil Salinity Using Electromagnetic Induction Techniques: 1. Statistical prediction models: A comparison of multiple linear regression and cokriging Identification and Estimation. Water Resour. Res. 1995, 31, 373–386. [Google Scholar] [CrossRef]
  31. Paine, J.G. Determining salinization extent, identifying salinity sources, and estimating chloride mass using surface, borehole, and airborne electromagnetic induction methods. Water Resour. Res. 2003, 39. [Google Scholar] [CrossRef] [Green Version]
  32. Sambuelli, L.; Leggieri, S.; Calzoni, C.; Porporato, C. Study of riverine deposits using electromagnetic methods at a low induction number. Geophysics 2007, 72, B113–B120. [Google Scholar] [CrossRef] [Green Version]
  33. Greenhouse, J.P.; Slaine, D.D. The use of reconnaissance electromagnetic methods to map contaminant migration: These nine case studies can help determine which geophysical techniques are applicable to a given problem. Groundw. Monit. Remediat. 1983, 3, 47–59. [Google Scholar] [CrossRef]
  34. Martinelli, P.; Duplaá, M.C. Laterally filtered 1D inversions of small-loop, frequency-domain EMI data from a chemical waste site. Geophysics 2008, 73, F143–F149. [Google Scholar] [CrossRef] [Green Version]
  35. Cassiani, G.; Ursino, N.; Deiana, R.; Vignoli, G.; Boaga, J.; Rossi, M.; Perri, M.T.; Blaschek, M.; Duttmann, R.; Meyer, S.; et al. Noninvasive Monitoring of Soil Static Characteristics and Dynamic States: A Case Study Highlighting Vegetation Effects on Agricultural Land. Vadose J. 2012, 11. [Google Scholar] [CrossRef] [Green Version]
  36. Gebbers, R.; Lück, E.; Heil, K. Depth sounding with the EM38-detection of soil layering by inversion of apparent electrical conductivity measurements. In Precision Agricolture’07; Stafford, J.V., Ed.; Wageningen Academic Publisher: Skiathos, Greece, 2007; pp. 95–102. ISBN 978-90-8686-024-1. [Google Scholar]
  37. Yao, R.; Yang, J. Quantitative evaluation of soil salinity and its spatial distribution using electromagnetic induction method. Agric. Water Manag. 2010, 97, 1961–1970. [Google Scholar] [CrossRef]
  38. Osella, A.; De la Vega, M.; Lascano, E. 3D electrical imaging of an archaeological site using electrical and electromagnetic methods. Geophysics 2005, 70, G101–G107. [Google Scholar] [CrossRef]
  39. Thiesson, J.; Dabas, M.; Flageul, S. Detection of resistive features using towed Slingram electromagnetic induction instruments. Archaeol. Prospect. 2009, 16, 103–109. [Google Scholar] [CrossRef]
  40. Perri, M.T.; Boaga, J.; Bersan, S.; Cassiani, G.; Cola, S.; Deiana, R.; Simonini, P.; Patti, S. River embankment characterization: The joint use of geophysical and geotechnical techniques. J. Appl. Geophys. 2014, 110, 5–22. [Google Scholar] [CrossRef]
  41. Huang, H.; SanFilipo, B.; Oren, A.; Won, I.J. Coaxial coil towed EMI sensor array for UXO detection and characterization. J. Appl. Geophys. 2007, 61, 217–226. [Google Scholar] [CrossRef]
  42. Corwin, D.L.; Rhoades, J.D. An Improved Technique for Determining Soil Electrical Conductivity-Depth Relations from Above-ground Electromagnetic Measurements. Soil Sci. Soc. Am. J. 1982, 46, 517–520. [Google Scholar] [CrossRef]
  43. McNeill, J.D. Electromagnetic Terrain Conductivity Measurement at Low Induction Numbers. Tech. Note 1980, 6, 13. [Google Scholar]
  44. Wait, J.R. Geo-Electromagnetism; Academic Press: New York, NY, USA, 1982. [Google Scholar]
  45. Frischknecht, F.C.; Labson, V.F.; Spies, B.R.; Anderson, W.L. Profiling methods using small sources. In Electromagnetic Methods in Applied Geophysics; Nabighian, M.N., Ed.; Society of Exploration Geophysicists: Tulsa, OK, USA, 1991; Volume 2, pp. 105–270. [Google Scholar]
  46. Deidda, G.P.; Fenu, C.; Rodriguez, G. Regularized solution of a nonlinear problem in electromagnetic sounding. Inverse Probl. 2014, 30, 125014. [Google Scholar] [CrossRef] [Green Version]
  47. Von Hebel, C.; Rudolph, S.; Mester, A.; Huisman, J.A.; Kumbhar, P.; Vereecken, H.; van der Kruk, J. Three-dimensional imaging of subsurface structural patterns using quantitative large-scale multiconfiguration electromagnetic induction data. Water Resour. Res. Res. 2014, 50, 2732–2748. [Google Scholar] [CrossRef] [Green Version]
  48. Saey, T.; De Smedt, P.; Delefortrie, S.; Van De Vijver, E.; Van Meirvenne, M. Comparing one- and two-dimensional EMI conductivity inverse modeling procedures for characterizing a two-layered soil. Geoderma 2015, 241–242, 12–23. [Google Scholar] [CrossRef]
  49. Shanahan, P.W.; Binley, A.; Whalley, W.R.; Watts, C.W. The Use of Electromagnetic Induction to Monitor Changes in Soil Moisture Profiles beneath Different Wheat Genotypes. Soil Sci. Soc. Am. J. 2015, 79, 459–466. [Google Scholar] [CrossRef] [Green Version]
  50. Frederiksen, R.R.; Christiansen, A.V.; Christensen, S.; Rasmussen, K.R. A direct comparison of EMI data and borehole data on a 1000 ha data set. Geoderma 2017, 303, 188–195. [Google Scholar] [CrossRef]
  51. Boaga, J.; Ghinassi, M.; D’Alpaos, A.; Deidda, G.P.; Rodriguez, G.; Cassiani, G. Geophysical investigations unravel the vestiges of ancient meandering channels and their dynamics in tidal landscapes. Sci. Rep. 2018, 8, 3303905. [Google Scholar] [CrossRef] [Green Version]
  52. Viezzoli, A.; Christensen, A.V.; Auken, E.; Sørensen, K. Quasi-3D modeling of airborne TEM data by spatially constrained inversion. Geophysics 2008, 73, F105–F113. [Google Scholar] [CrossRef]
  53. Piovan, S.; Mozzi, P.; Zecchin, M. The interplay between adjacent Adige and Po alluvial systems and deltas in the late Holocene (Northern Italy). Géomorphol. Process. Environ. 2012, 18, 427–440. [Google Scholar] [CrossRef] [Green Version]
  54. De Franco, R.; Biella, G.; Tosi, L.; Teatini, P.; Lozej, A.; Chiozzotto, B.; Giada, M.; Rizzetto, F.; Claude, C.; Mayer, A.; et al. Monitoring the saltwater intrusion by time lapse electrical resistivity tomography: The Chioggia test site (Venice Lagoon, Italy). J. Appl. Geophys. 2009, 69, 117–130. [Google Scholar] [CrossRef]
  55. Mozzi, P.; Piovan, S.; Corrò, E. Long-term drivers and impacts of abrupt river changes in managed lowlands of the Adige river and northern PO delta (Northern Italy). Quat. Int. 2018, 538, 80–93. [Google Scholar] [CrossRef]
  56. Teatini, P.; Tosi, L.; Strozzi, T.; Carbognin, L.; Wegmüller, U.; Rizzetto, F. Mapping regional land displacement in the Venice coastland by an integrated monitoring system. Remote Sens. Environ. 2005, 98, 403–413. [Google Scholar] [CrossRef]
  57. Carminati, E.; Martinelli, G.; Severi, P. Influence of glacial cycles and tectonics on natural subsidence in the Po Plain (Northern Italy): Insights from 14C ages. Geochem. Geophys. Geosystems 2003, 4. [Google Scholar] [CrossRef]
  58. Teatini, P.; Tosi, L.; Strozzi, T. Quantitative evidence that compaction of Holocene sediments drives the present land subsidence of the Po Delta, Italy. J. Geophys. Res. Earth Surf. 2011, 116. [Google Scholar] [CrossRef]
  59. ArcGIS. Available online: https://www.esri.com/en-us/arcgis/about-arcgis/overview (accessed on 20 March 2020).
  60. QGIS. Available online: https://www.qgis.org/it/site/ (accessed on 25 March 2020).
  61. Il Geoportale Della Regione del Veneto. Available online: https://idt2.regione.veneto.it/ (accessed on 3 April 2020).
  62. Recanatesi, F.; Giuliani, C.; Ripa, M.N. Monitoring mediterranean oak decline in a peri-urban protected area using the NDVI and sentinel-2 images: The Case Study of Castelporziano state natural reserve. Sustainability 2018, 10, 3308. [Google Scholar] [CrossRef] [Green Version]
  63. Bannari, A.; Morin, D.; Bonn, F.; Huete, A.R. A review of vegetation indices. Remote Sens. Rev. 1995, 13, 95–120. [Google Scholar] [CrossRef]
  64. Piedelobo, L.; Taramelli, A.; Schiavon, E.; Valentini, E.; Molina, J.L.; Xuan, A.N.; González-Aguilera, D. Assessment of green infrastructure in Riparian zones using copernicus programme. Remote Sens. 2019, 11, 2967. [Google Scholar] [CrossRef] [Green Version]
  65. Goodwin, N.R.; Coops, N.C.; Wulder, M.A.; Gillanders, S.; Schroeder, T.A.; Nelson, T. Estimation of insect infestation dynamics using a temporal sequence of Landsat data. Remote Sens. Environ. 2008, 112, 3680–3689. [Google Scholar] [CrossRef]
  66. Mather, P.M.; Koch, M. Computer Processing of Remotely-Sensed Images: An Introduction, 4th ed.; John Wiley & Sons: Hoboken, NJ, USA, 2011; ISBN 9780470742396. [Google Scholar]
  67. Congedo, L. Semi-Automatic Classification Plugin Documentation. Release 2016, 4, 29. [Google Scholar] [CrossRef]
  68. MOVE Suite-Petroleum Experts. Available online: https://www.petex.com/products/move-suite/ (accessed on 11 May 2020).
  69. GF Instruments S.R.O. Available online: www.gfinstruments.cz (accessed on 10 February 2020).
  70. Um, E.S.; Alumbaugh, D.L. On the physics of the marine controlled-source electromagnetic method. Geophysics 2007, 72, WA13–WA26. [Google Scholar] [CrossRef]
  71. Trimble-Transforming the Way the World Works. Available online: www.trimble.com (accessed on 10 February 2020).
  72. Allred, B.; Daniels, J.J.; Ehsani, R.M. Handbook of Agricultural Geophysics; CRC Press: Boca Raton, FL, USA, 2008; ISBN 9780849337284. [Google Scholar]
  73. Delefortrie, S.; De Smedt, P.; Saey, T.; Van De Vijver, E.; Van Meirvenne, M. An efficient calibration procedure for correction of drift in EMI survey data. J. Appl. Geophys. 2014, 110, 115–125. [Google Scholar] [CrossRef]
  74. Interpex Limited-Specialists in PC Based Geophysical Software. Available online: www.interpex.com (accessed on 3 February 2020).
  75. Constable, S.C.; Parker, R.L.; Constable, C.G. Occam’s inversion: A practical algorithm for generating smooth models from electromagnetic sounding data. Geophysics 1987, 52, 289–300. [Google Scholar] [CrossRef]
  76. Ghinassi, M.; Ielpi, A.; Aldinucci, M.; Fustic, M. Downstream-migrating fluvial point bars in the rock record. Sediment. Geol. 2016, 334, 66–96. [Google Scholar] [CrossRef]
  77. Ghinassi, M. Chute channels in the Holocene high-sinuosity river deposits of the Firenze plain, Tuscany, Italy. Sedimentology 2011, 58, 618–642. [Google Scholar] [CrossRef]
  78. Ninfo, A.; Fontana, A.; Mozzi, P.; Ferrarese, F. The Map of Altinum, Ancestor of Venice. Science 2009, 325, 577. [Google Scholar] [CrossRef] [PubMed]
  79. Bhattacharyya, P.; Bhattacharya, J.P.; Khan, S.D. Paleo-channel reconstruction and grain size variability in fluvial deposits, Ferron Sandstone, Notom Delta, Hanksville, Utah. Sediment. Geol. 2015, 325, 17–25. [Google Scholar] [CrossRef]
  80. Ghinassi, M.; Nemec, W.; Aldinucci, M.; Nehyba, S.; Özaksoy, V.; Fidolini, F. Plan-form evolution of ancient meandering rivers reconstructed from longitudinal outcrop sections. Sedimentology 2014, 61, 952–977. [Google Scholar] [CrossRef]
  81. Durkin, P.R.; Hubbard, S.M.; Smith, D.G.; Leckie, D.A. Predicting heterogeneity in meandering fluvial and tidal-fluvial deposits: The point bar to counter point bar transition. In Fluvial Meanders and Their Sedimentary Products in the Rock Record; Ghinassi, M., Colombera, L., Mountney, N.P., Reesink, J.H., Eds.; John Wiley & Sons: Hoboken, NJ, USA, 2018; Volume 48, pp. 231–250. [Google Scholar]
  82. Brice, J.C. Evolution of meander loops. Geol. Soc. Am. Bull. 1974, 85, 581–586. [Google Scholar] [CrossRef]
  83. Lewin, J. Initiation of bed forms and meanders in coarse-grained sediment. Geol. Soc. Am. Bull. 1976, 87, 281–285. [Google Scholar] [CrossRef]
  84. Nanson, G.C.; Page, K. Lateral accretion of fine-grained concave benches on meandering rivers. In Modern and Ancient Fluvial Systems; Collinson, J.D., Lewin, J., Eds.; John Wiley & Sons, Inc.: Hoboken, NJ, USA, 1983; Volume 6, pp. 133–143. ISBN 0632009977. [Google Scholar]
  85. Wu, C.; Bhattacharya, J.P.; Ullah, M.S. Paleohydrology and 3D facies architecture of ancient point bars, Ferron Sandstone, Notom Delta, south-central Utah, USA. J. Sediment. Res. 2015, 85, 399–418. [Google Scholar] [CrossRef]
  86. Jones, H.L.; Hajek, E.A. Characterizing avulsion stratigraphy in ancient alluvial deposits. Sediment. Geol. 2007, 202, 124–137. [Google Scholar] [CrossRef]
  87. Taylor, C.F.H. The role of overbank flow in governing the form of an anabranching river: The Fitzroy River, northwestern Australia. Fluv. Sedimentol. VI Spec. Publ. Int. Assoc. Sedimentol. 1999, 28, 77–91. [Google Scholar] [CrossRef]
  88. Motta, D.; Abad, J.D.; Langendoen, E.J.; García, M.H. The effects of floodplain soil heterogeneity on meander planform shape. Water Resour. Res. 2012, 48, 1–17. [Google Scholar] [CrossRef]
  89. Bogoni, M.; Putti, M.; Lanzoni, S. Modeling meander morphodynamics over self-formed heterogeneous floodplains. Water Resour. Res. 2017, 53, 5137–5157. [Google Scholar] [CrossRef] [Green Version]
  90. Fidolini, F.; Ghinassi, M.; Aldinucci, M.; Billi, P.; Boaga, J.; Deiana, R.; Brivio, L. Fault-sourced alluvial fans and their interaction with axial fluvial drainage: An example from the Plio-Pleistocene Upper Valdarno Basin (Tuscany, Italy). Sediment. Geol. 2013, 289, 19–39. [Google Scholar] [CrossRef]
  91. Nanson, G.C. Point bar and floodplain formation of the meandering Beatton River, northeastern British Columbia, Canada. Sedimentology 1980, 27, 3–29. [Google Scholar] [CrossRef]
  92. Ielpi, A.; Ghinassi, M. Planform architecture, stratigraphic signature and morphodynamics of an exhumed Jurassic meander plain (Scalby Formation, Yorkshire, UK). Sedimentology 2014, 61, 1923–1960. [Google Scholar] [CrossRef]
  93. Swan, A.; Hartley, A.J.; Owen, A.; Howell, J. Reconstruction of a sandy point-bar deposit: Implications for fluvial facies analysis. In Fluvial Meanders and Their Sedimentary Products in the Rock Record; Ghinassi, M., Colombera, L., Mountney, N.P., Reesink, A.J., Betaman, M., Eds.; John Wiley & Sons Ltd.: Hoboken, NJ, USA, 2018; Volume 48, pp. 445–474. [Google Scholar]
  94. Frothingham, K.M.; Rhoads, B.L. Three-dimensional flow structure and channel change in an asymmetrical compound meander loop, Embarras River, Illinois. Earth Surf. Process. Landf. J. Br. Geomorphol. Res. Gr. 2003, 28, 625–644. [Google Scholar] [CrossRef]
  95. Kasvi, E.; Vaaja, M.; Alho, P.; Hyyppä, H.; Hyyppä, J.; Kaartinen, H.; Kukko, A. Morphological changes on meander point bars associated with flow structure at different discharges. Earth Surf. Process. Landf. 2013, 38, 577–590. [Google Scholar] [CrossRef]
  96. Finotello, A.; D’Alpaos, A.; Bogoni, M.; Ghinassi, M.; Lanzoni, S. Remotely-sensed planform morphologies reveal fluvial and tidal nature of meandering channels. Sci. Rep. 2020, 10, 54. [Google Scholar] [CrossRef]
  97. Ferguson, R.I.; Parsons, D.R.; Lane, S.N.; Hardy, R.J. Flow in meander bends with recirculation at the inner bank. Water Resour. Res. 2003, 39. [Google Scholar] [CrossRef] [Green Version]
Figure 1. The study site: (a) location of Anguillara Veneta town in the southern Venetian Plain, at the boundary with the Po Plain sensu strictu; (b) satellite image (2013) of the study area (yellow box) in Anguillara Veneta town, PD (Italy).
Figure 1. The study site: (a) location of Anguillara Veneta town in the southern Venetian Plain, at the boundary with the Po Plain sensu strictu; (b) satellite image (2013) of the study area (yellow box) in Anguillara Veneta town, PD (Italy).
Remotesensing 12 02568 g001
Figure 2. Methodologies. (ab) Geophysical acquisition: (a) the electromagnetic tool on the wooden sledge dragged by a small tractor on the study field and (b) the survey path. (c) Position of the recovered cores. Yellow dots and green triangles indicate the hand auger core and the drilled cores with rotary technique, respectively.
Figure 2. Methodologies. (ab) Geophysical acquisition: (a) the electromagnetic tool on the wooden sledge dragged by a small tractor on the study field and (b) the survey path. (c) Position of the recovered cores. Yellow dots and green triangles indicate the hand auger core and the drilled cores with rotary technique, respectively.
Remotesensing 12 02568 g002
Figure 3. Descriptive terminology for fluvial meanders and related deposits: (a) alluvial plain morphological elements, (b) point-bar deposits and (c) meander-belt morphometry.
Figure 3. Descriptive terminology for fluvial meanders and related deposits: (a) alluvial plain morphological elements, (b) point-bar deposits and (c) meander-belt morphometry.
Remotesensing 12 02568 g003
Figure 4. Remote-sensing results: (a) aerial photogram of the study area enhancing the poorly visible fluvial pattern during winter time; (b) meander belt reconstruction and fluvial morphology identification in the study area—white dashed lines highlight evidence of scroll-bar morphologies; and (cf) satellite images (2016, 2013, 2012) providing information about fluvial morphology on the basis of seasons and soil use.
Figure 4. Remote-sensing results: (a) aerial photogram of the study area enhancing the poorly visible fluvial pattern during winter time; (b) meander belt reconstruction and fluvial morphology identification in the study area—white dashed lines highlight evidence of scroll-bar morphologies; and (cf) satellite images (2016, 2013, 2012) providing information about fluvial morphology on the basis of seasons and soil use.
Remotesensing 12 02568 g004
Figure 5. Processed satellite images: (a) RGB combination on Sentinel-2 image to highlight petrographic differences in the study area; (b) band 8, of Sentinel-2 image of the study area, showing paleochannel morphologies; and (c,d) NDVI and NDMI indexes calculated on Sentinel 2 images (2018), respectively, enhancing different plant health and hydraulic stress.
Figure 5. Processed satellite images: (a) RGB combination on Sentinel-2 image to highlight petrographic differences in the study area; (b) band 8, of Sentinel-2 image of the study area, showing paleochannel morphologies; and (c,d) NDVI and NDMI indexes calculated on Sentinel 2 images (2018), respectively, enhancing different plant health and hydraulic stress.
Remotesensing 12 02568 g005
Figure 6. Geophysical results: (a) 3D view of the eight 2D conductivity maps; (b) the eight 2D maps showing difference in conductivity values and highlighting point-bar, channel-fill and floodplain morphologies.
Figure 6. Geophysical results: (a) 3D view of the eight 2D conductivity maps; (b) the eight 2D maps showing difference in conductivity values and highlighting point-bar, channel-fill and floodplain morphologies.
Remotesensing 12 02568 g006
Figure 7. Sedimentary features of cores for bar and overbank deposits at the study site. Location of cores is shown with the conductivity for Slice 6.
Figure 7. Sedimentary features of cores for bar and overbank deposits at the study site. Location of cores is shown with the conductivity for Slice 6.
Remotesensing 12 02568 g007
Figure 8. Cored deposits: (a) massive medium sand with pebble-sized mudclasts forming the channel lag; (b) fine to medium sands from the lower point bar; (c) fine to very fine sands, with cross lamination and mud layers from the upper point bar; and (d) massive overbank mud with moderate organic content and horizontal bedding.
Figure 8. Cored deposits: (a) massive medium sand with pebble-sized mudclasts forming the channel lag; (b) fine to medium sands from the lower point bar; (c) fine to very fine sands, with cross lamination and mud layers from the upper point bar; and (d) massive overbank mud with moderate organic content and horizontal bedding.
Remotesensing 12 02568 g008
Figure 9. Plot of the interpretation of the EMI inverted conductivity intervals after the correlation with the sedimentary cores AV_1, AV_a, AV_b and AV_c.
Figure 9. Plot of the interpretation of the EMI inverted conductivity intervals after the correlation with the sedimentary cores AV_1, AV_a, AV_b and AV_c.
Remotesensing 12 02568 g009
Figure 10. old9. Volume of the point-bar body (a) reconstructed through the present study and (b) inferred assuming bar growth from a straight channel, as suggested by classical sedimentological models.
Figure 10. old9. Volume of the point-bar body (a) reconstructed through the present study and (b) inferred assuming bar growth from a straight channel, as suggested by classical sedimentological models.
Remotesensing 12 02568 g010
Figure 11. Workflow of the overall methodology adopted in this study.
Figure 11. Workflow of the overall methodology adopted in this study.
Remotesensing 12 02568 g011
Table 1. Technical specifications of the multicoil CMD Explorer FDEM.
Table 1. Technical specifications of the multicoil CMD Explorer FDEM.
Instrument ProbeCoil Interdistance (m)FrequencyNominal Exploration Depth (Horizontal Mode HMD /Vertical Mode VMD)
11.4810 kHz2.2/1.1 m
22.8210 kHz4.2/2.1 m
34.4910 kHz6.7/3.3 m

Share and Cite

MDPI and ACS Style

Cassiani, G.; Bellizia, E.; Fontana, A.; Boaga, J.; D’Alpaos, A.; Ghinassi, M. Geophysical and Sedimentological Investigations Integrate Remote-Sensing Data to Depict Geometry of Fluvial Sedimentary Bodies: An Example from Holocene Point-Bar Deposits of the Venetian Plain (Italy). Remote Sens. 2020, 12, 2568. https://doi.org/10.3390/rs12162568

AMA Style

Cassiani G, Bellizia E, Fontana A, Boaga J, D’Alpaos A, Ghinassi M. Geophysical and Sedimentological Investigations Integrate Remote-Sensing Data to Depict Geometry of Fluvial Sedimentary Bodies: An Example from Holocene Point-Bar Deposits of the Venetian Plain (Italy). Remote Sensing. 2020; 12(16):2568. https://doi.org/10.3390/rs12162568

Chicago/Turabian Style

Cassiani, Giorgio, Elena Bellizia, Alessandro Fontana, Jacopo Boaga, Andrea D’Alpaos, and Massimiliano Ghinassi. 2020. "Geophysical and Sedimentological Investigations Integrate Remote-Sensing Data to Depict Geometry of Fluvial Sedimentary Bodies: An Example from Holocene Point-Bar Deposits of the Venetian Plain (Italy)" Remote Sensing 12, no. 16: 2568. https://doi.org/10.3390/rs12162568

APA Style

Cassiani, G., Bellizia, E., Fontana, A., Boaga, J., D’Alpaos, A., & Ghinassi, M. (2020). Geophysical and Sedimentological Investigations Integrate Remote-Sensing Data to Depict Geometry of Fluvial Sedimentary Bodies: An Example from Holocene Point-Bar Deposits of the Venetian Plain (Italy). Remote Sensing, 12(16), 2568. https://doi.org/10.3390/rs12162568

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop