Next Article in Journal
Impact of Extreme Wind and Freshwater Runoff on the Salinity Patterns of a Mesotidal Coastal Lagoon
Next Article in Special Issue
Prediction of Beach Sand Particle Size Based on Artificial Intelligence Technology Using Low-Altitude Drone Images
Previous Article in Journal
Assessing Nutrient Limitation in Yeongsan River Estuary Using Bioassay Experiments
Previous Article in Special Issue
A Methodological Proposal for the Management of Submerged Cultural Heritage: Study Cases from Cartagena de Indias, Colombia
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Comparison between the Employment of a Multibeam Echosounder on an Unmanned Surface Vehicle and Traditional Photogrammetry as Techniques for Documentation and Monitoring of Shallow-Water Cultural Heritage Sites: A Case Study in the Bay of Algeciras

by
Soledad Solana Rubio
1,
Alberto Salas Romero
1,
Felipe Cerezo Andreo
1,
Raúl González Gallero
1,
Juan Rengel
2,
Luis Rioja
2,
Joaquín Callejo
3 and
Manuel Bethencourt
4,*
1
Department of History, Geography and Philosophy, International Campus of Excellence of the Sea (CEI·MAR), University of Cadiz, 11003 Cadiz, Spain
2
Spanish Hydrographic Office, 11007 Cadiz, Spain
3
Institute of Marine Research, International Campus of Excellence of the Sea (CEI·MAR), University of Cadiz, 11003 Cadiz, Spain
4
Department of Materials Science, Metallurgical Engineering and Inorganic Chemistry, International Campus of Excellence of the Sea (CEI·MAR), University of Cadiz, 11003 Cadiz, Spain
*
Author to whom correspondence should be addressed.
J. Mar. Sci. Eng. 2023, 11(7), 1339; https://doi.org/10.3390/jmse11071339
Submission received: 31 May 2023 / Revised: 26 June 2023 / Accepted: 28 June 2023 / Published: 30 June 2023

Abstract

:
Over the last few years, due to various climatic, anthropogenic, and environmental factors, a large amount of submerged heritage has been unearthed and exposed to deterioration processes in the Bay of Algeciras. These impacts can be more severe in shallow waters, where the cultural heritage is more vulnerable to natural and human-induced impacts. This makes it urgent to document cultural heritage at risk of disappearing using different techniques whose efficiencies in the archaeological record need to be determined and compared. For this purpose, we have documented a shipwreck in the Bay of Algeciras using two techniques: photogrammetry and a multibeam echosounder. The photogrammetric method consists of obtaining a 3D model from numerous photographs taken of an object or a site. The processing software creates three-dimensional points from two-dimensional points found in the photographs that are equivalent to each other. Multibeam echosounders are capable of providing side scan imagery information in addition to generating contour maps and 3D perspectives of the surveyed area and can be installed in an unmanned surface vehicle. As a result, we have obtained two 3D visualisations of the shipwreck, i.e., digital copies, that are being used both for the analysis of its naval architecture and for its dissemination. Through the comparison of the two techniques, we have concluded that while a multibeam echosounder provides a detailed digital terrain model of the seabed, photogrammetry performed by divers gives the highest resolution data on objects and structures. In conclusion, our results demonstrate the benefits of this combined approach for accurately documenting and monitoring shipwrecks in shallow waters, providing valuable information for conservation and management efforts.

1. Introduction

The Bay of Algeciras coastline, with more than 40 km in length, has material evidence of exceptional Underwater Cultural Heritage (UCH) as wrecks, ports, anchorages, etc. This UCH comes from the historical relationships, maintained over millennia, of the societies established in the area surrounding the Strait of Gibraltar with and by the sea. The conservation of the UCH is crucial as an intangible asset that brings responses from our past and has an outstanding universal value from a historical, aesthetic, ethnological or anthropological point of view. In addition, the sustainable exploitation of UCH will increase the relevance of cultural tourism within maritime tourism. Moreover, UCH plays a key role in sustainable development as an important economic engine, which has been recognized by the European Union (EU), the United Nations Educational, Scientific and Cultural Organization (UNESCO) or the International Council on Monuments and Sites (ICOMOS). In this sense, among the strategic objectives of the major economic programs, tourism, leisure, and other cultural activities have been identified as one of the major priorities and opportunities for Spain and Europe.
The formation process, preservation and future perspectives of conservation of the UCH located in coastal areas under the influence of the littoral process cannot be properly undertaken without considering and monitoring the particularities of the surrounding environment. The specific and particular physical–chemical conditions of the underwater environment have allowed, in several cases, the remains to reach a certain degree of stability, permitting each site to be unique [1,2]. Although a deeper theoretical–methodological development is still unclosed, the great dynamism to which these types of deposits are subjected is better understood. This step forward represents a remarkable conceptual advance over the usual and outdated notion of wrecks as “time capsules”, frozen spatially and chronologically. The complex processes operating in an underwater archaeological site and conditioning its state result from the permanent interaction of many agents acting on it [2,3,4,5], mainly the intensity and direction of the currents and waves, as well as sedimentary and geochemical processes.
With the increasing number of shipwrecks and other submerged structures uncovered recently in the Bay of Algeciras [6], Figure 1, it becomes necessary to develop alternative methods of storage, conservation and stabilization of these archaeological sites. Rule Number 1 of the Annex to the 2001 UNESCO Convention on the Protection of Underwater Cultural Heritage [7] states that “The protection of Underwater Cultural Heritage through in situ preservation shall be considered as the first option”.
In the last years, several projects [8,9,10,11] have shown the close relationship between the degree of conservation of the UCH and the marine environmental conditions and concluded that the environmental or anthropic parameters that affect underwater archaeological sites demand immediate actions based on their knowledge and adequate monitoring to prevent the irreversible destruction of the remains and to ensure their long-term stability. In this sense, physical variables are considered a key factor for the in situ preservation of UCH [12] due to their direct impact on the integrity of fragile materials and the de-contextualization of objects and their ability to modulate or control other factors such as sedimentary dynamics, geochemical conditions and biological activity [13]. However, the analysis of the impact of these parameters on the UCH has been performed without evaluating their changes in the long term. This fact is especially relevant in the context of global warming due to Climate Change (CC). The problem of CC and its influence on the conservation of the world’s natural and cultural heritage was pointed out by UNESCO [7], highlighting the need for future research, the development of a legal framework, and interrelationships with other international organizations, such as the Intergovernmental Panel on Climate Change (IPCC). Because of the CC, changes in the wind and low-pressure systems can increase the frequency and intensity of extreme events such as a storm in the next century [14]. The projected rise in global mean sea level ranges from 0.43 to 0.82 m for the best-case (RCP2.6) and worst-case (RCP8.5) at the end of this century. The sea surface temperature is also expected to increase from 0.05 to 0.5 °C decade-1 [15]. These changes are not homogeneous in time and space; therefore, their impact on UCH will not be homogenous either. In the study area, the Bay of Algeciras, the sea level is expected to increase by 0.6 m at the end of the century, and the frequency of flooding events will increase up to 500 times for the RCP8.5 scenario [16]. The yearly mean sea surface temperature is projected to increase by almost 3 °C by 2100 along the Alboran Sea coast, particularly in summer [17].
In this context: (i) the high density of cultural heritage assets on the coast of the Bay of Algeciras; (ii) its social and economic relevance; (iii) the threatening impact of climatic factors contributing to its deterioration; and (iv) the necessity of long-term preservation; the option of in situ protection and monitoring for the required initial environmental characterization can have an unaffordable cost in some cases. Therefore, it is also necessary to develop new tools and methodologies that help identify and prioritize those sites where the in situ protection program or other actions (prospecting, excavation and archaeological documentation) should be implemented to mitigate the loss of archaeological information. The design, development and deployment of autonomous ocean platforms for the observation, exploration and monitoring of marine and oceanic environments have grown exponentially with the lowering of production costs and technological developments brought about by the digital revolution. With the advent of the digital revolution, which has generalized the use of electronic circuits and TTL technology, unmanned vehicles with different degrees of autonomy, marine as Unmanned Surface Vehicles (USV) or underwater as Autonomous Underwater Vehicles (AUV), as well as Remotely Operated Vehicles (ROV), and more recently aerial as Unmanned Aerial Systems (UAS), have begun to revolutionize the exploration of the marine environment and coasts, generally offering observation platforms at a lower cost, free of risks for operators, and capable of obtaining more information in less time [18,19]. Remote sensing tools operating from unmanned vehicles and satellites are contributing to the integration of terrestrial and marine datasets for the assessment of geohazards in coastal and marine areas, with special reference to tsunamis and storms, coastal and marine landslides and sea-level rise-related hazards [20]. In the specific case of USVs, they have been extensively used in archaeological and archaeometric missions, including studies of coastal evolution in shallow waters in areas of high historical interest [21,22,23,24].
These new platforms and the observations they make are essential for documenting the state, variability and changing conditions of the oceans under climate change and other anthropogenic pressures, as well as the effect of such changes on ecosystems or the cultural heritage that remains there. This knowledge is crucial for understanding, predicting and ultimately mitigating and adapting to present and future adverse impacts. These impacts can be more severe in shallow water, where cultural heritage sites are most vulnerable to natural and human-induced impacts, making it critical to document and monitor them over time. Multibeam Echosounders (MBES) and photogrammetry are two techniques commonly used for mapping and documenting underwater sites [25,26]. While MBES provides a detailed digital terrain model of the seabed and can be installed in a USV, photogrammetry performed by divers can provide the highest resolution data on objects and structures. Integrating these techniques can provide a more comprehensive and accurate representation of the site. In this study, we present a case study of the integration of MBES and photogrammetry for the documentation and monitoring of cultural heritage sites in the shallow waters of the Bay of Algeciras. The results demonstrate the benefits of using this combined approach for accurately documenting and monitoring cultural heritage sites in shallow waters, providing valuable information for conservation and management efforts.
Therefore, this paper focuses on comparative experimental fieldwork at two submerged sites. The shite of Puente Mayorga IV contains the remains of a probable gunboat used during the sieges of Gibraltar at the end of the 18th century. Its original construction system and the scarce knowledge of this type of small craft make it very interesting for archaeological and naval history research. For these reasons of originality and exceptionality, we decided to undertake an excavation to obtain detailed planimetry in order to study its naval construction. During this process, priority was given to non-intrusive techniques in the documentation, such as digital methods or real measurements in situ. The contemporary shipwreck is located very close to the Puente Mayorga IV shipwreck. This structure, from the end of the 20th century, is at a very shallow depth, and we have used it, especially as a control element for satellite or aerial measurements in the framework of experimentation with different techniques for recording the UCH of the area.

2. Materials and Methods

2.1. Unmanned Vehicles and Sensors

Data were collected by using two unmanned vehicles from the University of Cadiz Peripheral Drone Service (www.dron.uca.es, accessed on 1 April 2023), Figure 2: a DJI Matrice 300 RTK UAS and a Maritime Robotics Otter Pro USV. The Matrice 300 UAS incorporated a Zenmuse P1 sensor for precision photogrammetry in flight, with a horizontal accuracy of 3 cm and a vertical accuracy of 5 cm, a global mechanical shutter with a shutter speed of 1/2000 s, and a 4.4 μm pixel size. The data were post-processed using the commercial software Pix4D Postflight Terra, a suite for UAS mapping. Several studies have used active remotely sensed imagery collected by UAS to visually detect and record shipwrecks in shallow water, and more recently, results based on hyperspectral technology and LiDAR bathymetry have been published [27,28,29]. Data obtained with UAS on the contemporary shipwreck have been used to calibrate other measurements obtained by Google Earth, bathymetric probes and divers.
Regarding the Otter Pro USV, it was the vehicle in charge of autonomously carrying out the bathymetric work. This USV is a small catamaran with a footprint of 200 × 108 × 81.5 cm and a weight of 63 kg, adequate for bathymetric surveys in sheltered waters (such as shallow-water coasts, harbour areas, lakes, canals, rivers and ponds). The USV is controlled by Maritime Robotics’ Vehicle Control Station (VCS), a graphical user interface with several control modes, such as course and speed control, heading control, or waypoint control.
The integration between the onboard control systems and the MBES allows autonomous bathymetric work to be carried out. The hydrographic work was conducted with a Norbit iWBMSe MBES coupled to an Applanix Position and Orientation System for Marine Vessels (POS MV). Some technical specifications of the MBES are a swath coverage between 5 and 210°, a range resolution of less than 10 mm, a number of beams between 256 and 512, an operating frequency selectable at 200, 400 or 700 KHz, a resolution (across × along) of 0.9° × 1.9° at 400 KHz and 0.5° × 1.0° at 700 KHz, a heading accuracy of 0.08° (Real Time Kinematic, RTK), pitch/roll accuracy of 0.03° and heave accuracy of 2 cm or 2%. For post-processing correction of the bathymetric data, velocity profiles were obtained with an AML Base2 sound profiler, launched automatically from a winch on board the USV. Finally, the Applanix POS MV provides accurate navigation and attitude data to correct the effects of USV motion during survey operations, combining the IMU (Inertial Measurement Unit) and GNSS (Global Navigation Satellite System) sensor data into an integrated navigation system. The appropriate topographic measurements guaranteed the quality of the positioning data in conjunction with the DGPS RTK positioning system and NTRIP (Network Transport of RTCM via Internet Protocol) corrections from the Andalusian Positioning Network and the movement sensor.
Two calibrations were performed before data acquisition: (1) the calibration of the Applanix positioning system and inertial system, performing the “turns of 8” for adjustment in the offset of the equipment and adjustments in the heading of the boat; and (2) the calibration of the Norbit sounder, following the standards set by the International Hydrographic Organization (IHO) for Special Order areas [30] and performing the relevant calibration lines to adjust the pitch, yaw and roll of the sounder. Following this standard, the maximum allowable vertical uncertainty in vertical measurements was calculated with the following formula: “a” (the portion of the uncertainty that does not vary with the depth, 0.25 m Special Order) and “b” (coefficient that represents that portion of the uncertainty that varies with the depth, 0.0075 Special Order), together with the depth “d”, the parameters that have to be introduced in the formula of the Total Vertical Uncertainty (TVU):
T V U m a x   ( d ) = a 2 + ( b   x   d ) 2
A project of lines was prepared to cover the archaeological remains to be studied and to guarantee a good overlap between the lines to achieve a good data resolution, which in our case was 100%. We used a working speed of 2 knots, which we recommend for working in shallow waters. The data were recorded at a frequency of 700 kHz with a beam aperture of 90°. The registration time was 45 min.
There are numerous studies in the literature on the use of MBES for imaging submerged shipwrecks from conventionally manned vessels [31,32,33,34,35]. However, we do not know of any study in which this combination of technologies, MBES plus USV and photogrammetry, has been used in the dimensional study of a shipwreck.

2.2. Google Earth

As a first approach, we used Google Earth (GE) for the acquisition of dimensions and shape information for the contemporary shipwreck. Other authors have already proposed the use of GE as a tool to identify abandoned ships and shipwrecks [36]. GE is a geographic information system that displays a virtual three-dimensional globe that allows the visualization of multiple cartographies, based on satellite images, aerial photography and GIS data. Among other tools available through the desktop application, GE includes a distance measurement tool.

2.3. Bathymetric Data Collection and Post-Processing

The USV has two computers. The first one is used to control the vessel’s movement and speed according to the preplanned lines and orders received by radio. The second one is used for running the MBES and to record the position, attitude, sound velocity at the transducer, time and depth. This computer also records the Sound Velocity Profiles (SVP) when they are obtained.
MBES are the best tool for depth calculation, together with mapping the seabed, because they obtain the complete seafloor insonification with a good resolution. The latter mainly depends on the distance from the MBES transducer to the bottom and the frequency of the sound rays; the higher the frequency, the better. In our case study, that distance was under 3 m, and the frequency was 700 KHz, the highest of our equipment. We achieved good results in spite of the physical limitation of the sound propagation, which prevented us from obtaining more detail on the smallest elements of the wreck.
The MBES principle of operation is based on a transmission pulse directed towards the seafloor. This pulse is narrow along the heading direction of the vessel and wide across the course. After the reflection of the sound by the seabed, the receiving beams are electronically generated. The two-way travel time between transmission and reception is computed by seabed detection algorithms. With the application of ray tracing correction due to the refraction of the sound rays, it is possible to determine (a) the depth and (b) the transversal distance from the USV nadir to the small insonified area by each beam.
The transmitted beam is wide across the USV course and narrow along it, only 1°; on the other hand, the beams electronically formed during the reception phase are wide along the course, near 180°, and narrow across it, only 0.5°. The intersections of the unique transmitted beam in the seabed with the X electronically reception beams are the small areas (footprints) where X soundings are measured. In our case, X was 512 in order to reach the best resolution possible of the wreck.
Since depths are measured from a floating USV with six possible degrees of freedom (three translations and three rotations), for accurate computation of depth measurement and its associated positioning, precise measurements of latitude, longitude, heave, roll, pitch and heading are also recorded by the Applanix IMU, as described in Section 2.1.
To gather complete information about the seabed by MBES, a planned survey with transect lines is needed. It consisted of some parallel lines to the wreck’s keel and another set of lines across, centered in the position of the wreck. Its length was longer than the keel, about 50 m, and the separation among them was only 3 m, to ensure that the overlap was 100% and to prevent any gap or area without data due to the true track of the USV.
Data processing was performed with two software packages for comparison: the HySweep module of the Hypack software (version 2020) and the NaviModel Producer software from EIVA (product no: NM.PRO). Once the data were acquired, a bathymetric surface was generated with the real minimum height, although a CUBE (Combined Uncertainty and Bathymetric Estimator) surface was previously generated with the confidence criteria, and a filter was applied to clean up the very erroneous data above the 95% confidence level. The rest of the data was cleaned manually.

2.4. Photogrammetry and Post-Processing

Photogrammetry is a recording technique that has been used in underwater archaeology since the 1970s [37], although the first experiments were made as early as the 1960s [38,39], because it makes it possible to obtain a 3D model of any object by taking photographs from different angles. As long as visibility conditions allow, it is a method by which a virtual visualisation of any site can be obtained, requiring less dive time than traditional archaeological drawing and sparing the subjective aspects of the archaeological process [38].
Photogrammetry uses a variety of algorithms and techniques to perform image processing and three-dimensional reconstruction. Some of the algorithms used include:
  • Feature matching is used to correlate key points between different images using algorithms like SIFT (Scale-Invariant Feature Transform) or SURF (Speeded-Up Robust Features). These algorithms find key points in the images and compare them to establish correspondences [40,41].
  • Triangulation is used to calculate the three-dimensional position of a point from the images. One of the most common algorithms is the Delaunay Triangulation method, which uses corresponding spots in multiple images to calculate the 3D position of the points of interest [42].
  • Bundle adjustment is an algorithm used to adjust the camera parameters and improve the accuracy of the 3D model. Bundle adjustment methods, such as the least squares method, estimate the camera parameters and 3D points that minimize the discrepancies between the observed 2D projections and the estimated 2D projections in the 3D model [43].
  • Image fusion is used to combine multiple overlapping images into a single panoramic or mosaic image. These algorithms perform image alignment and correction to achieve smooth and seamless transitions between the images [44].
  • Outlier point filtering is used to improve the accuracy and quality of the 3D model by identifying and removing points that do not fit well with the model or have a high discrepancy compared to other points [45].
A GNSS device was used to take various control points on the site. This operation was carried out by three divers and a 4-metre pole attached to the top of the GS receiver or GNSS antenna. This end of the pole, which was out of the water and on the surface, was operated by one diver, while another diver placed the lower part of the pole, submerged, at the exact point on the shipwreck whose coordinates were to be recorded. The third diver, on the boat, recorded each point with the GNSS pad.
For the photogrammetric documentation of Puente Mayorga IV, a total of 1650 photographs were taken over the shipwreck, covering an area of 54.4 m2 in a “grid” pattern (Figure 3). This means that zenith photographs were taken over the site at an altitude of 1.1 m, making 18 lines longitudinal to the axis of the shipwreck, and then a second coverage was performed, with 39 lines transversal to the previous ones [39]. The overlap between the photographs was at least 60%, leaving a distance between the longitudinal lines of approximately 65 cm. The spacing of the transverse lines varied widely, ranging from 20 to 60 cm, and several lines at different altitudes overlapped to document all the details of the shipwreck’s frames. The camera used was a GoPro Hero 7 Silver with a resolution of 3648 × 2736 pixels and a focal length of 3 mm. In addition, thirteen control points were marked on the shipwreck, the coordinates of which were recorded with a Leica GS18 GNSS in the ETRS89/UTM zone 30N coordinate system to fix the 3D model in its correct spatial relationship [39].
The dive time required to take the photographs was one hour and twenty-nine minutes. If we take into account the time for setting the scales, the North arrow, the control measurements, the setting of the control points, and the taking of their coordinates, one hour more must be added. At this point, it should be noted that the results obtained with photogrammetry, which provides a good visualisation of the shipwreck in which many details of its naval architecture can be observed, are because the site was excavated and cleaned before the photographs were taken.
In other words, without prior excavation, photogrammetry only outlines the shipwreck and displays those details that are not buried. Therefore, if we want to compare results between detailed photogrammetries such as the one of Puente Mayorga IV, the excavation time (21 days) must be taken into account.
For the subsequent processing of the photogrammetry, the Agisoft Metashape Pro software version 1.8.3 from Agisoft was used.

3. Results

3.1. Aerial Measurement

The selected coastline was examined with GE at an eye altitude of about 150 m. The range of dates for which suitable imagery was available was between 31 December 1985 and 24 September 2022, for a total of 30 different dates. Of these, the shipwreck was only visible on six dates: 12 September 2012, 4 October 2012, 27 May 2015, 6 May 2020, 18 June 2020 and 2 March 2022, as shown in Figure 4.
Finally, we chose the image on the day of 27 May 2015, as the control image, as it was the sharpest. In the latter, it was possible to take the first measurements, one on the longitudinal axis of the length (line 4) and four on the transverse axis along the beam (lines 1 to 3) (Figure 5a). These locations were maintained for the rest of the measurements. Measurements were taken in duplicate, rotating the image 180° in GE, Table 1. However, none of the images show the remains of the historic shipwreck.
Once the contemporary shipwreck was located, the area was surveyed by a UAS flight at a 50-metre altitude (Figure 5b). The image obtained is sharper and allows more precise measurements to be taken in the Pix4D software (Table 1).
Finally, a third measurement was carried out by divers using a tape measure (Table 1). These measurements can then be compared with those obtained with the bathymetric sounder.
Although, in general, the data obtained by either technique correlates well, the measurements obtained by Google Earth are the most inaccurate due to the low resolution of the images. The measurements obtained by UAS and divers are very similar, with differences in the worst case of 3 cm. However, while the measurements obtained by UAS are zenithal, divers can measure other dimensions of the shipwreck, such as the thickness of the frames. These are, in any case, averages that will help us compare the results obtained on the historical shipwreck using photogrammetry, bathymetry and the use of divers.

3.2. Bathymetric Survey

Once the bathymetric survey data were acquired, they were post-processed with different bathymetric software (Figure 6). A series of filters and reductions were applied to these raw data to obtain quality-corrected data. We worked with two types of files. On the one hand, S7K files are formed by the bathymetry data obtained from the multibeam sounder and the navigation data obtained from the Applanix inertial system, which works with RTK corrections. When loading the S7K files, we will automatically obtain velocity, heading, roll, pitch, heave, swell, RTK tide, position and the bathymetry data itself, as well as sound speed data from the SV gauge for the sounding head. On the other hand, the SVP files corresponding to the sound velocity profiles contain the depth and sound velocity data at each depth.
After a profile analysis, five lines were detected with a lack of RTK correction, probably due to a loss of receiving corrections from the reference station, although the system has maintained the differential correction. In this bathymetric survey, a large overlap was used so that by removing these five lines, there is no significant loss of data.
After processing the bathymetric data, a set of high-quality data with which we carried out a Digital Terrain Model (DTM) was obtained with a 3 cm resolution, and we were ready for the measurement of the structural elements that can be distinguished from the shipwreck as well as for the comparison with another DTM obtained from a different source of data, in our case properly treated photographic images, as already indicated. DTMs using bathymetric data are hereafter referred to as Digital Bathymetric Models (DBM) to distinguish them from Digital Elevation Models (DEM), a term usually reserved for terrestrial elevation data [46]. Finally, the data density of the blocks was very good, meeting the IHO standards for a Special Order survey due to the overlap that was made during the acquisition. At this point, the phase of editing and manipulation of the obtained data is shown (Figure 7), which allows a 3D graphic representation to be made and the final product to be achieved.
To get an idea of the goodness of the measurements made on the DBM, the same four measurements were taken on the contemporary shipwreck, following the lines that were used in the estimations made in Google Earth, with UAS or by divers, showing differences of a few centimeters with the measurements acquired by UAS or divers (Figure 8). The measures in the DBM are shown in Table 2.
In the case of the Puente Mayorga IV shipwreck, five measurement lines were chosen, longitudinal and transversal to the shipwreck (Figure 9a). Having carried out two post-processings of the data, we obtained two DBMs that we are going to compare with each other and with the DEM acquired from photogrammetry. We have made this comparison with CARIS HIPS/GIS software, which has allowed us to generate five graphs in which we have represented the DBM in blue (EIVA) and red (HySweep) and the DEM of the photogrammetry in green. The small differences between the two DBMs are mainly due to the perception of the operator, since the raw data of origin are the same, as are the corrections applied by the tide, movement of the USV, and variation of the speed of sound in the water column. Therefore, we have only made measurements of the five predetermined distances in the shipwreck in one of the two DBMs. Additionally, we have also made distance estimations in the point cloud processed with CARIS, and finally, we have taken the same measurements in the DEM of the photogrammetry, yielding small differences without a fixed pattern being appreciated between them, although the DEM always gives the lowest measurements and the point cloud the highest, and those of the DBM between the two, which show the coherence of both data sources and all their processes. Table 3 shows the measurements taken in the different models and bathymetric point clouds. In the case of line 5, the profile shows a higher error in Z than in X–Y, but only on the starboard side (Figure 9b).

3.3. Photogrammetric Processing

In addition to positioning metric scales before the photographs were taken, which allowed the model to be scaled in the subsequent processing, significant parts of the shipwreck in a good state of preservation were measured. This made it possible to obtain a highly detailed record of the naval architecture and to check the possible margin of error of the photogrammetry. This last task was achieved by using a level drawing frame with a laser pointer to obtain the X, Y and Z coordinates of each recording point. Measurements were taken with tape measures, a carpenter’s ruler, a calliper, a pencil and polyester paper boards. These measures can be spared if the GPS positioning of the control points is accurate. In our case, the thirteen recorded points were enough to correct the scale and distortion of the 3D model [39], although we still took measurements to check the reliability of the two methods [47].
After calibration of the lens [48], their alignment was set to high quality, with the limit of Tie Points at 10,000 and Key Points at 40,000. As a result, 1646 photographs were aligned, generating 954,164 points in a time of 3 h, 7 min and 5 s, obtaining a first point cloud in which the shipwreck could already be visualised. After optimising the alignment (1 min and 7 s), the points that were not part of the shipwreck were cleaned, thus reducing the weight of the model and the processing time in the following steps. We then input the coordinates we had taken with the GNSS at the 13 control points, as well as the markers for scaling the model, using the photographs on which the control points and the metric scales were shown. For the dense cloud building, also in high quality, 6 h and 57 min were needed, obtaining 172,719,340 points. After a second cleaning, in which the points that were not part of the shipwreck were removed, the 3D Model was processed. After 4 h and 5 min, the model was complete, with 28,633,665 faces and 14,355,693 vertices, allowing a mesh visualisation of the shipwreck. The final step, which took 32 min and 15 s, was to generate the texture, that is, to apply the colour and texture information from the photographs to the model. The final resolution of the model is 0.48 mm/pix. After orienting the model in zenith projection, the orthomosaic and the DEM were generated. For the first one, Mosaic was selected as the Blending mode to keep the information of each photograph. The resolution set was 1 mm/pix and after 33 min and 56 s, an orthoimage of 15,979 × 4450 pixels was obtained. The DEM had a resolution of 0.961 mm/pix, a density of 1.08 points/mm2, and a size of 17,253 × 16,867, with a processing time of 3 min and 9 s. The total processing time was 15 h, 19 min and 32 s on a computer with a CPU Intel (R) Core (TM) i9-10920X 3.50 GHz, 64 GB of RAM, and a graphic card NVIDIA Quadro RTX 400, with the platform Windows 10 x64.
Taking control points with GNSS was very useful to check the metric validity of the model. In this case, we have taken 13 control points distributed regularly over the shipwreck in an ETRS 89 UTM30 coordinate system (Figure 10a). Once the coordinates of the points were entered into the 3D model, a series of metric errors were detected by the photogrammetric processing software. The measurements in X, Y and Z accumulate a residual squared metric error of 16.86 cm for the entire model (Table 4). This is due to the deformation that the software applied to adapt the model to the coordinates entered. However, this error is reduced as we reduce the number of control points, and we were able to verify that five or six control points are enough to have a corrected model.
On the other hand, direct measurements were taken at the underwater site of Puente Mayorga IV to compare the data that could be provided by photogrammetry, the GNSS system, and the actual measurement in the field (Figure 10b). These dimensions, expressed in Control Line 1 and Control Line 2, show us that the model, despite accumulating a metric error of more than 10 cm, is consistent in its internal measurements since the discrepancies between measurements are 3 or 4 cm, attributable to a human or technical error of the equipment used.
These data show that the control measurements made in the central area of the shipwreck on its axial and transverse axes present a good fit between the three measurement methods (Table 5). The same is true for the control points located in the central zone of the shipwreck, where the RMSE value is lower.
The most problematic areas of the photogrammetric model are the margins or ends of the model, which are where the control points CP3N, CP8 and CP9 are located. These points have the highest RMSE value, which is due to the optical distortion produced by the type of lens used to generate the model. With “flatter” lenses, the results will be metrically more reliable in their entirety.

4. Discussion

Studying a submerged archaeological site without its alteration should be considered a fundamental premise. In order to keep archaeological sites intact while obtaining as much information as possible, remote sensors play a fundamental role. There are different types of sensors: passive sensors use the electromagnetic spectrum, such as photogrammetry, while active sensors transmit and receive sound (e.g., multibeam sounders). Both have strengths and weaknesses; therefore, depending on the shipwreck to be studied, environmental conditions, resources and time, one or the other can be used, or even both.
In this contribution, we have studied two wrecks, one historical and one contemporary. The contemporary shipwreck is on the bottom and has no documentary value, but it was used to validate the techniques. The Puente Mayorga IV shipwreck was completely buried. One side of the wooden hull of the ship, together with dozens of projectiles concreted in a large mound nest to the starboard bow area, were preserved. The excavation of the wreckage, before the photogrammetry and MBES work, involved three weeks of work with divers. For both techniques, the wreckage must emerge sufficiently from the seabed. These techniques have already been used together with success in [49], where high-resolution sonar and a photogrammetric system were integrated to compare objects on the bottom of a lake as a complete, high-potential, simple and fast monitoring method for inland waters.
Before assessing the feasibility of one technique or another, it is necessary to establish which parameters will be used to compare both techniques: safety for the researchers, degree of autonomy, speed and ease of installation, calibration and design of the data acquisition method, data acquisition and its processing time, economic cost, and finally the quality of the data obtained.
The main limitation of photogrammetry, based on underwater photography, is water turbidity. Thus, in areas such as marshes or river mouths, little or no visibility due to suspended sediment present throughout the water column hinders the realization of photographs. Within open sea areas, water clarity or turbidity will be conditioned by depth, type of bottom, plankton, currents, wind and prevailing waves, proximity to mouths and estuaries, etc. Another major limitation of photogrammetry is working depth. This parameter not only hinders the georeferencing and orientation of the digital model of the shipwreck, but also when depth increases, reduces the time spent by divers, increases their risks, and causes light to be lost and colours to be attenuated or disappear, starting with the lower frequencies. This can be solved by using artificial light or an ROV [50].
For multibeam echo sounder bathymetry, there are two types of uncertainties to take into account: uncertainty in the position of the soundings (positioning uncertainty) and uncertainty in the determination of depth (vertical uncertainty). The regulations established by the IHO determine limit values that help check if the order used is correct. For Special Order surveys, the position of the soundings must be determined with a maximum Total Horizontal Maximum Uncertainty (THU) of 2 m depth at a 95% confidence level. The vertical uncertainty of a sounding is understood as the uncertainty of the reduced depths. Hence, it is necessary to combine all the errors made with depth determination. The formula described in Section 2.4 will be used to calculate, at a 95% confidence level, the maximum allowable TVU. As with the rest of the acoustic sounding systems, multibeam echo sounders can accumulate several errors that can degrade the accuracy of position and depth. Some of the most common are instrumental errors of the sounder itself; GPS errors; errors in the measurement of tides; errors in the measurement of the speed of sound; and errors due to the ship’s inertial movements (pitch, roll and heave).
As aforementioned, the photogrammetry consisted of more than 1600 photographs systematically taken over an hour and a half by divers with an underwater camera. With favourable environmental and meteorological conditions, the acquisition of photographs of the shipwreck followed a pre-designed pattern, obtaining the greatest detail of the shipwreck and its cargo. Subsequently, with the help of specialized software (Futtock), the images were post-processed for 15 h to generate a 3D digital model of the shipwreck, which allowed the study of the naval architecture of the shipwreck and its linkage. The smaller the separation between the photo acquisition lines and the slower the speed to cross these lines, the more time is demanded for data acquisition through photographs, approximately three times longer than a bathymetric work from USV.
On the other hand, the MBES system aboard USV was used to obtain acoustic information on the seafloor. This approach allowed us to measure seafloor depth and represent its cartography, as well as detect georeferenced objects. In this case, the fieldwork was completely autonomous and lasted 45 min, while the post-processing with software took two hours. Additionally, while diving always involves some risk for archaeologists, the risk of an accident is non-existent for technicians working with an MBES installed on a USV since it carries out the work in a programmed manner.
Regarding economic efforts, a distinction must be made between the costs associated with equipment and those related to its operators. The equipment needed to perform the photogrammetry (including a rigid inflatable boat) is much cheaper than the multibeam sounder carried out by an autonomous surface vehicle. In terms of personnel, only two technicians located on land were needed for the USV and the bathymetry, while photogrammetry was carried out by two divers plus the person in charge of the boat, increasing the cost of this item. Post-processing time was also much less in the bathymetric work. Additionally, we valued not only the price of each specific software to analyse data but also the ease of use. Thus, there is a clear advantage for photogrammetry since it does not require acquisition software, and the post-processing is much cheaper and easier to handle than the MBES system. In addition, photogrammetry needs fewer auxiliary data to obtain a good result since it only demands a series of control points whose geographical coordinates are established with GNSS equipment. Nevertheless, MBES forces us to know the position of the sensor and the speed of sound in the water at all times, its movement with the prevailing swell, the height of the tide, the installation parameters of the antennas of the positioning equipment and the transducer of the sounder, as well as the sound velocity profile in the water column.
In terms of environmental and meteorological conditions, both systems have their limitations. As already mentioned, the biggest enemy of photogrammetry is turbidity, which can hamper its use. On the contrary, turbidity practically does not interfere with the effectiveness of MBES. Therefore, this technique can be used as long as the weather conditions are good since waves affect the navigation of the USV and the quality of the obtained data. In any case, in this work, the conditions were excellent for the use of both techniques.
Finally, the quality and comparability of the results can be considered the fundamental points of the study. In principle, the DEM resulting from photogrammetry offers great detail of the smaller elements of the shipwreck and therefore could offer better accuracy in the measurements. With large dimensions, it is preferable to use the model generated by the MBES system. This model is not subject to the distortions of the photogrammetric model, which are produced by the non-integration of the measurements. An example of distortion is the use of a measuring tape to measure the distance between points without any orientation between them. Another is the coordinates of the control points, which are obtained either from a buoy located in the more or less approximate vertical of the point or with a pole of several meters that, supported on them, must emerge from the water with difficulty, in any case, to do it in the same vertical.
For instance, this distortion could be observed on the right-hand side of the transverse profiles of the shipwreck (lines 4 and 5 in Figure 9a) (Figure 11), since models from both techniques presented some distance among them. On the contrary, the longitudinal profiles (lines 1, 2 and 3 in Figure 9a) show that the two models are very close to each other (Figure 12). Profiles 1 and 2 have a good fit between the DEM (in green) and the two DBM (blue and red). In profile 3, a small displacement in X–Y can be observed between the two models, causing the DEM profile not to be carried out on the ceiling stringer but near the keel, giving rise to the appearance of the saw teeth of the floors and clearances (floor spacing). Moreover, as can be observed in profile 5, the two models on the starboard side of the shipwreck have an appreciable difference in Z, something that does not occur on the port side as in profile 2.
Since the MBES system requires the emission of an acoustic wave and its reception in multiple beams, it is very difficult to penetrate the small gaps between the frames or floors. For this reason, the models are almost coincidental on the floors. The photogrammetric DEM is better adjusted for clearances than the DBM. Moreover, since the latter is designed to detect the minimum depth of each beam, it will be affected by shadows generated from behind by obstacles such as frames, excluding when the beam is incident directly on the vertical. This problem could be improved by making more data acquisition lines, i.e., increasing the density of lines by decreasing the separation between them, closing the beams to give higher resolution, and obtaining data in other scanning directions in addition to those in two perpendicular directions.
Either way, even if the number of lines is increased, the physical limitation of acoustic propagation is imposed. Thus, the greater the distance to the shipwreck, the lower the resolution achieved and the fewer details obtained from the wreckage using an MBES system. For greater depths, this problem could be solved or reduced by using an AUV (Autonomous Underwater Vehicle) instead of a USV, which allows one to get very close to the objective shipwreck.
The use of photogrammetry is widespread among archaeologists due to its simplicity and low economic requirements, but this is not the case for MBES. Although it is more complex and expensive, MBES can be used in the study and monitoring of submerged archaeological sites in shallow waters, as it complements photogrammetry and sometimes even replaces it when water turbidity does not allow its use. In the best of cases and whenever possible, both techniques should be combined, as has been demonstrated in this work. Therefore, an effective joint work protocol would be (1) to obtain a DEM with MBES of a wide study area, to know the general geo–morphological dynamics, and to establish a specific documentation priority for sites that are in the process of being unearthed; (2) Once the intervention priorities have been defined, detailed documentation is carried out on some underwater archaeological sites using photogrammetry, as long as the water clarity allows it. (3) Afterwards, the site is covered and the control points of the tumulus are defined, or if it is left uncovered, the control points are archaeological features identified in the fieldwork. (4) Finally, the first MBES documentation of the site and the immediate surroundings is carried out, which will serve as a base model for (5) Monitoring at least once in every warm and cold season in those areas of concentration of shipwrecks with USV.

5. Conclusions

Within the framework of the virtual documentation projects, we have developed a non-intrusive methodology for the documentation of the UCH. In this contribution, we prioritize exploration over recovery and innovation by using geophysical techniques that map the seabed without altering the UCH, identifying what is buried, what is anomalous and at what depth, as well as helping to monitor its degree of preservation. Once it is, our number one concern is to leave the underwater archaeological artefacts in their original location and to document them through interventions in which we establish a proportionate ratio between the impact caused and the scientific information obtained. Our specific action is therefore based on graphic documentation using various techniques (photogrammetry, MBES, video, 360° video, scanning, drawing, etc.). Once processed and studied, these results give rise to virtual models that we use to continue researching the UCH or to communicate it to society.
To date, we have seen how photogrammetry offers greater detail in the documentation of singular elements of the naval architecture of wrecks. In contrast, the use of MBES does not achieve this level of detail. Comparing the two techniques would be complicated and may even be unrealistic in archaeological research given the differences in data acquisition principles (acoustic vs. optical data). However, the complementary use of both techniques is of great interest since MBES with USV covers large areas with a high-resolution level of detail. This aspect is very useful for large-scale monitoring of coastal sites that are at risk of quick burial/covering due to changes produced by climatic change. Data acquisition and post-processing are fast, and sea work is safe and agile as long as wave conditions allow the USV to navigate. Likewise, the use of photogrammetry for the detailed documentation of shipwrecks is necessary if we want to accurately assess aspects of historical interest but, above all, to know millimetric losses and deterioration, which in the medium term affect this heritage. Photogrammetry allows us to know if this or that object has been removed or if the timber has been displaced, and MBES allows us to know if the entire site is being displaced, covered, or eroded. Nevertheless, photogrammetry requires adequate water transparency and longer times of data collection and post-processing, and since it is carried out by divers, risks that could be eliminated by using an ROV are present.
Therefore, the complementary use of both techniques is very productive. In our experience, the joint use of the techniques is useful for monitoring and controlling the deterioration processes of coastal underwater sites in shallow waters in scenarios of anthropic hazards or climate change. Photogrammetry provides the first level of detail necessary to establish control points for site deterioration as well as to obtain archaeological data. Once photogrammetric recording has been carried out, sites can generally be covered with sandbags or re-entered to ensure better preservation. Thereafter, the use of MBES from a USV, which is more economical, safe and effective in covering large areas, is an excellent tool to carry out periodic monitoring of the sites, checking the measures or control elements established in the detailed photogrammetric documentation or the evolution of burial tumulus if the sites have been covered for their protection.
In conclusion, we would like to recall that prioritizing non-intrusive techniques over intrusive ones offers not only the possibility to perform constant monitoring of archaeological sites and to document numerous underwater archaeological sites in a short time and effectively but also helps heritage managers prioritize the order of intervention on different archaeological sites according to the risk they present. Acting quickly and efficiently in the field is essential to protecting a unique heritage that is at risk.

Author Contributions

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

Funding

This research was funded by: (1) Ministry of Science and Innovation, Spain, through the project “Vulnerability of littoral cultural heritage to environmental agents: impact of climate change (VOLICHE)” (PID2020-117812RB-I00/AEI /10.13039/501100011033): (2) European Regional Development Fund (FEDER), EU, Interreg V-A Spain-Portugal program (POCTEP) 2014–2020, through the project “KTTSeaDrones” (0622-KTTSEADRONES-5-E). (3) 2014–2020 ERDF Operational Programme and the Department of Economy, Knowledge, Business and University of the Regional Government of Andalusia, Spain, through the project “Between the Pillars of Hercules, underwater archaeology of a privileged space. The Bay of Algeciras (HERAKLES)”. (FEDER-UCA18-107327).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data is unavailable due to privacy.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Florian, M.L.E. The underwater environment. In Conservation of Marine Archaeological Objects; Pearson, C., Ed.; Butterworths: New York, NY, USA, 1987; pp. 1–20. [Google Scholar]
  2. Bethencourt, M.; Fernández-Montblanc, T.; Izquierdo, A.; González-Duarte, M.M.; Muñoz-Mas, C. Study of the influence of physical, chemical and biological conditions that influence the deterioration and protection of Underwater Cultural Heritage. Sci. Total Environ. 2018, 613–614, 98–114. [Google Scholar] [CrossRef]
  3. Cámara, B.; Alvarez de Buergo, M.; Bethencourt, M.; Fernández-Montblanc, T.; La Russa, M.F.; Ricca, M.; Fort, R. Biodeterioration of marble in an underwater environment. Sci. Total Environ. 2017, 609, 109–122. [Google Scholar] [CrossRef] [PubMed]
  4. Ciarlo, N.C. Methodology for the study of ferrous artefacts corroded in an underwater environment. A case of analysis: The Hoorn site concretions. Zaranda 2006, 2, 87–106. [Google Scholar]
  5. Fernández-Montblanc, T.; Bethencourt, M.; Izquierdo, A. Underwater Cultural heritage risk assessment methodology for wave-induced hazards: The showcase of the Bay of Cádiz. Front. Mar. Sci. 2022, 9, 1–18. [Google Scholar] [CrossRef]
  6. Cerezo Andreo, F.; González-Gallero, R.; Ciarlo, N.; Bettencourt, J.; Pérez-Reverte, C.; Solana Rubio, S.; Fernández-Tudela, E. Primeros resultados de los pecios modernos de la Bahía de Algeciras. Áreas de Puente Mayorga y el Rinconcillo. Proyecto Herakles. In Proceedings of the CIANYS 2021—I Congreso Iberoamericano de Arqueología Náutica y Subacuática, Cádiz, Spain, 21 October 2021. [Google Scholar]
  7. UNESCO. 2007: Climate Change and World Heritage, World Heritage Centre du Patrimoine Mondial, Paris, Rapport n° 22, WHC-06/30.COM/7.1. 55p. Available online: https://whc.unesco.org/en/climatechange/ (accessed on 11 May 2023).
  8. Palma, P. Monitoring of Shipwreck Sites. Int. J. Naut. Archaeol. 2005, 34, 323–331. [Google Scholar] [CrossRef]
  9. Nyström Godfrey, I.; Bergstrand, T.; Petersson, H.; Bohm, C.; Christensson, E.; Gjelstrup Björdal, C.; Gregory, D.; MacLeod, I.; Peacock, E.E.; Richard, V. The RAAR Project—Heritage Management Aspects on Reburial After Ten Years of Work. Conserv. MGMT Arch. Sites 2012, 14, 360–371. [Google Scholar] [CrossRef]
  10. Dix, J.; Cazenave, P.W.; Lambkin, D.O.; Rangecroft, T.; Pater, C.; Oxley, I. Sedimentation-erosion modelling as a tool for underwater cultural heritage management. In MACHU Final Report; Manders, M., Oosting, R., Brouwers, W., Eds.; Educom Publishers: Rotterdam, The Netherlands, 2009; pp. 48–54. [Google Scholar]
  11. Bethencourt, M.; Tomas, F.M.; Izquierdo, A. ARQUEOMONITOR: Contribución de las condiciones físicas, químicas y biológicas en el deterioro y salvaguarda del Patrimonio Cultural Subacuático: Influencia sobre las velocidades de corrosión en la artillería de dos pecios asociados a la Batalla de Trafalgar (1805). In Arquelogía Subacática Española; Nieto Prieto, X., Bethencourt Núñez, M., Eds.; Editorial UCA: Cádiz, Spain, 2014; Volume II, pp. 331–342. [Google Scholar]
  12. Quinn, R.; Smyth, T.A.G. Processes and patterns of flow, erosion, and deposition at shipwreck sites: A computational fluid dynamic simulation. Archaeol. Anthropol. Sci. 2018, 10, 1429–1442. [Google Scholar] [CrossRef]
  13. Ruuskanen, A.T.; Kraufvelin, P.; Alvic, R.; Díaz, E.R.; Honkonen, J.; Kanerva, J.; Karell, K.; Kekäläinen, P.; Lappalainen, J.; Mikkola, R.; et al. Benthic conditions around a historic shipwreck: Vrouw Maria (1771) in the northern Baltic proper. Cont. Shelf Res. 2015, 98, 1–12. [Google Scholar] [CrossRef]
  14. Vousdoukas, M.I.; Mentaschi, L.; Voukouvalas, E.; Verlaan, M.; Feyen, L. Extreme sea levels on the rise along Europe’s coasts. Earth’s Future 2017, 5, 304–323. [Google Scholar] [CrossRef]
  15. Alexander, M.A.; Scott, J.D.; Friedland, K.D.; Mills, K.E.; Nye, J.A.; Pershing, A.J. Projected sea surface temperatures over the 21st century: Changes in the mean, variability and extremes for large marine ecosystem regions of Northern Oceans. Elem. Sci. Anthr. 2018, 6, 9. [Google Scholar] [CrossRef] [Green Version]
  16. European Environment Agency. 2019. Available online: https://www.eea.europa.eu/ims/atmospheric-greenhouse-gas-concentrations (accessed on 20 January 2023).
  17. Darmaraki, S.; Somot, S.; Sevault, F.; Nabat, P.; Cabos Narvaez, W.D.; Cavicchia, L.; Djurdjevic, V.; Li, L.; Sannino, G.; Sein, D.V. Future evolution of Marine Heatwaves in the Mediterranean Sea. Clim. Dyn. 2019, 53, 1371–1392. [Google Scholar] [CrossRef] [Green Version]
  18. Wu, G.; Zhao, M.; Cong, Y.; Hu, Z.; Li, G. Algorithm of Berthing and Maneuvering for Catamaran Unmanned Surface Vehicle Based on Ship Maneuverability. J. Mar. Sci. Eng. 2021, 9, 289. [Google Scholar] [CrossRef]
  19. Bethencourt, M. El uso de los vehículos marinos no tripulados en la gestión y la investigación de aguas marinas y continentales. In Conocimiento y Transferencia de Tecnología Sobre Sistemas de Monitorización Aéreos y Acuáticos para el Desarrollo Transfronterizo de Ciencias Marinas y Pesqueras: Proyecto KTTSeaDrones; Ayuntamiento de Isla Cristina: Huelva, Spain, 2022; pp. 28–65. [Google Scholar]
  20. Prampolini, M.; Savini, A.; Foglini, F.; Soldati, M. Seven Good Reasons for Integrating Terrestrial and Marine Spatial Datasets in Changing Environments. Water 2020, 12, 2221. [Google Scholar] [CrossRef]
  21. Aucelli, P.; Cinque, A.; Mattei, G.; Pappone, G. Historical sea level changes and effects on the coasts of Sorrento Peninsula (Gulf of Naples): New constrains from recent geoarchaeological investigations. Palaeogeogr. Palaeoclimatol. Palaeoecol. 2016, 463, 112–125. [Google Scholar] [CrossRef]
  22. Mattei, G.; Troisi, S.; Aucelli, P.P.C.; Pappone, G.; Peluso, F.; Stefanile, M. Multiscale reconstruction of natural and archaeological underwater landscape by optical and acoustic sensors. In Proceedings of the 2018 IEEE International Workshop on Metrology for the Sea; Learning to Measure Sea Health Parameters (MetroSea), Bari, Italy, 8–10 October 2018; pp. 46–49. [Google Scholar]
  23. Aucelli, P.; Cinque, A.; Mattei, G.; Pappone, G.; Stefanile, M. Coastal landscape evolution of Naples (Southern Italy) since the Roman period from archaeological and geomorphological data at Palazzo degli Spiriti site. Quat. Int. 2018, 483, 23–38. [Google Scholar] [CrossRef]
  24. Pappone, G.; Aucelli, P.P.C.; Mattei, G.; Peluso, F.; Stefanile, M.; Carola, A. A Detailed Reconstruction of the Roman Landscape and the Submerged Archaeological Structure at “Castel dell’Ovo islet” (Naples, Southern Italy). Geosciences 2019, 9, 170. [Google Scholar] [CrossRef] [Green Version]
  25. Pierre, D.; Merad, D.; Hijazi, B.; Gaoua, L.; Nawaf, M.M.; Saccone, M.; Chemisky, B.; Seinturier, J.; Sourisseau, J.C.; Gambin, T.; et al. Underwater Photogrammetry and Object Modeling: A Case Study of Xlendi Wreck in Malta. Sensors 2015, 12, 30351–30384. [Google Scholar]
  26. Zhong, H. Underwater cultural heritage and the disputed South China Sea. China Inf. 2020, 34, 361–382. [Google Scholar] [CrossRef]
  27. Guyot, A.; Lennon, M.; Thomas, N.; Gueguen, S.; Petit, T.; Lorho, T.; Cassen, S.; Hubert-Moy, L. Airborne Hyperspectral Imaging for Submerged Archaeological Mapping in Shallow Water Environments. Remote Sens. 2019, 11, 2237. [Google Scholar] [CrossRef] [Green Version]
  28. Shih, P.T.Y.; Chen, Y.H.; Chen, J.C. Historic Shipwreck Study in Dongsha Atoll with Bathymetric LiDAR. Archaeol. Prospect. 2014, 21, 139–146. [Google Scholar] [CrossRef]
  29. Doneus, M.; Miholjek, I.; Mandlburger, G.; Doneus, N.; Verhoeven, G.; Briese, C.; Pregesbauer, M. Airborne laser bathymetry for documentation of submerged archaeological sites in shallow water. ISPRS Int. Arch. Photogramm. Remote Sens. Spat. Inf. Sci. 2015, 40, 99–107. [Google Scholar] [CrossRef] [Green Version]
  30. S-44. IHO Standards for Hydrographic Surveys (Edition 6.1.0, October 2022). Available online: https://iho.int/uploads/user/pubs/standards/s-44/S-44_Edition_6.1.0.pdf/ (accessed on 11 May 2023).
  31. Calder, B.; Forbes, B.; Mallace, D. Marine heritage monitoring with high-resolution survey tools: Scapa flow 2001–2006. In Proceedings of the U.S. Hydro Conference, Norfolk, VA, USA, 14 May 2007. [Google Scholar]
  32. Quinn, R.; Boland, D. The role of time-lapse bathymetric surveys in assessing morphological change at shipwreck sites. J. Archaeol. Sci. 2010, 27, 2838–2946. [Google Scholar] [CrossRef]
  33. Plets, R.; Quinn, R.; Forsythe, W.; Westley, K.; Bell, T.; Benetti, S.; McGrath, F.; Robinson, R. Using multibeam echo-sounder data to identify shipwreck sites: Archaeological assessment of the Joint Irish Bathymetric Survey data. Int. J. Naut. Archaeol. 2011, 40, 87–98. [Google Scholar] [CrossRef]
  34. Westley, K.; Plets, R.; Quinn, R.; McGonigle, C.; Sacchetti, F.; Dale, M.; McNary, R.; Clements, A. Optimising protocols for high-definition imaging of historic shipwrecks using multibeam echosounder. Archaeol. Anthropol. Sci. 2019, 11, 3629–3645. [Google Scholar] [CrossRef]
  35. Majcher, J.; Quinn, R.; Plets, R.; Coughlan, M.; McGonigle, C.; Sacchetti, F.; Westley, K. Spatial and temporal variability in geomorphic change at tidally influenced shipwreck sites: The use of time-lapse multibeam data for the assessment of site formation processes. Geoarchaeology 2021, 36, 429–454. [Google Scholar] [CrossRef]
  36. Payne, M.R.; Turner, A. Remote sensing of boat abandonment using Google Earth. Environ. Sci. Pollut. Res. 2023, 30, 15616–15622. [Google Scholar] [CrossRef]
  37. Drap, P. Underwater Photogrammetry for Archaeology. In Special Applications of Photogrammetry, 1st ed.; da Silva, D.C., Ed.; InTech: Rijeka, Croatia, 2012; pp. 111–136. [Google Scholar]
  38. Mcallister, M. The Problem with ‘Digital Realism’ in Underwater Archaeology: Photogrammetric Digital 3D Visualization and Interpretation. J. Mar. Archaeol. 2021, 22, 253–275. [Google Scholar] [CrossRef]
  39. Yamafune, K.; Torres, R.; Castro, F. Multi-Image Photogrammetry to Record and Reconstruct Underwater Shipwreck Sites. J. Archaeol. Method Theory 2017, 24, 703–725. [Google Scholar] [CrossRef]
  40. Lowe, D. Distinctive Image Features from Scale-Invariant Keypoints. Int. J. Comput. Vis. 2004, 60, 91–110. [Google Scholar] [CrossRef]
  41. Bay, H.; Tuytelaars, T.; Van Gool, L. SURF: Speeded up robust features. In Computer Vision—ECCV 2006. Lecture Notes in Computer Science; Leonardis, A., Bischof, H., Pinz, A., Eds.; Springer: Berlin/Heidelberg, Germany, 2006; Volume 3951, pp. 404–417. [Google Scholar]
  42. Simena, D.; Bañón, J. A review on Delaunay Triangulation with application on computer vision. Int. J. Comput. Sci. Eng. 2014, 3, 9–18. [Google Scholar]
  43. Triggs, B.; Mclauchlan, P.; Hartley, R. Bundle Adjustment—A Modern Synthesis. In Vision Algorithms’99; Triggs, B., Zisserman, A., Szeliski, R., Eds.; Springer: Berlin/Heidelberg, Germany, 2000; pp. 298–372. [Google Scholar]
  44. Amolins, K.; Zhang, Y.; Dare, P. Wavelet based image fusion techniques—An introduction, review and comparison. J. Photogramm. Remote Sens. 2007, 62, 249–263. [Google Scholar] [CrossRef]
  45. Fei, B.; Yang, W.; Chen, W.M.; Li, Z.; Li, Y.; Ma, T.; Hu, X.; Ma, L. Comprehensive Review of Deep Learning-Based 3D Point Cloud Completion Processing and Analysis. IEEE Trans. Intell. Transp. Syst. 2022, 23, 22862–22883. [Google Scholar] [CrossRef]
  46. Lecours, V.; Dolan, M.; Micallef, A.; Lucieer, V. A review of marine geomorphometry, the quantitative study of the seafloor. Hydrol. Earth Syst. Sci. 2016, 20, 3207–3244. [Google Scholar] [CrossRef] [Green Version]
  47. Pollio, J. Underwater Mapping with Photography and SONAR. Photogramm. Eng. 1971, 37, 955–968. [Google Scholar]
  48. Pollio, J. Application of Underwater Photogrammetry; Informal Report 68–52; Naval Oceanographic Office: John C. Stennis Space Center, MS, USA, 1968; p. 46. [Google Scholar]
  49. Pose, S.; Reitmann, S.; Licht, G.J.; Grab, T.; Fieback, T. AI-Prepared Autonomous Freshwater Monitoring and Sea Ground Detection by an Autonomous Surface Vehicle. Remote Sens. 2023, 15, 860. [Google Scholar] [CrossRef]
  50. Price, D.M.; Robert, K.; Callaway, A.; Lo Lacono, C.; Hall, R.A.; Huvenne, V.A.I. Using 3D photogrammetry from ROV video to quantify cold-water coral reef structural complexity and investigate its influence on biodiversity and community assemblage. Coral Reefs 2019, 38, 1007–1021. [Google Scholar] [CrossRef] [Green Version]
Figure 1. Location of the study area: (a) Red square: Strait of Gibraltar; green circle: Bay of Algeciras, Spain. (b) Blue dots are shipwrecks located in the northern part of the Bay. Red dots: two shipwrecks from this paper, located in Puente Mayorga: Puente Mayorga IV and a contemporary shipwreck.
Figure 1. Location of the study area: (a) Red square: Strait of Gibraltar; green circle: Bay of Algeciras, Spain. (b) Blue dots are shipwrecks located in the northern part of the Bay. Red dots: two shipwrecks from this paper, located in Puente Mayorga: Puente Mayorga IV and a contemporary shipwreck.
Jmse 11 01339 g001
Figure 2. (a) DJI Matrice 300 RTK UAS; (b) Maritime Robotics Otter Pro USV.
Figure 2. (a) DJI Matrice 300 RTK UAS; (b) Maritime Robotics Otter Pro USV.
Jmse 11 01339 g002
Figure 3. (a) Location of each of the photographs used in the photogrammetric model of the shipwreck Puente Mayorga IV; (b) Resulting orthoimage.
Figure 3. (a) Location of each of the photographs used in the photogrammetric model of the shipwreck Puente Mayorga IV; (b) Resulting orthoimage.
Jmse 11 01339 g003
Figure 4. Images of the contemporary shipwreck on different dates at an eye altitude of 50 m.
Figure 4. Images of the contemporary shipwreck on different dates at an eye altitude of 50 m.
Jmse 11 01339 g004
Figure 5. Measurements acquired on the image of the contemporary shipwreck, measurements, one on the longitudinal axis of the length (line 4) and four on the transverse axis along the beam (lines 1 to 3), in (a) Google Earth; (b) Orthophoto acquired by UAS.
Figure 5. Measurements acquired on the image of the contemporary shipwreck, measurements, one on the longitudinal axis of the length (line 4) and four on the transverse axis along the beam (lines 1 to 3), in (a) Google Earth; (b) Orthophoto acquired by UAS.
Jmse 11 01339 g005
Figure 6. Some images of the post-processing of the bathymetric data, performed in this case with the Hysweep software, version 2020 (multibeam editor). In 1: Puente Mayorga IV, 2: Contemporary shipwreck.
Figure 6. Some images of the post-processing of the bathymetric data, performed in this case with the Hysweep software, version 2020 (multibeam editor). In 1: Puente Mayorga IV, 2: Contemporary shipwreck.
Jmse 11 01339 g006
Figure 7. A 3D graphic representation. In 1: Puente Mayorga IV, 2: Contemporary shipwreck.
Figure 7. A 3D graphic representation. In 1: Puente Mayorga IV, 2: Contemporary shipwreck.
Jmse 11 01339 g007
Figure 8. (a) Measurements made on the bathymetry in different areas of the contemporary wreck (lines 1 to 4). (b) Detail of the dimensions of line 1 as seen from the stern, from the Stern-port Side (S-P) to the Stern-starboard Side (S-S).
Figure 8. (a) Measurements made on the bathymetry in different areas of the contemporary wreck (lines 1 to 4). (b) Detail of the dimensions of line 1 as seen from the stern, from the Stern-port Side (S-P) to the Stern-starboard Side (S-S).
Jmse 11 01339 g008
Figure 9. (a) Measurements acquired on the image of Puente Mayorga IV in the bathymetric product. (b) Comparative profiles obtained in line 5. DEM in green, DBM’s in blue (EIVA) and red (HySweep).
Figure 9. (a) Measurements acquired on the image of Puente Mayorga IV in the bathymetric product. (b) Comparative profiles obtained in line 5. DEM in green, DBM’s in blue (EIVA) and red (HySweep).
Jmse 11 01339 g009
Figure 10. (a) Location of control lines and points on the shipwreck. (b) The error margin of each control point according to the calculations made by the software.
Figure 10. (a) Location of control lines and points on the shipwreck. (b) The error margin of each control point according to the calculations made by the software.
Jmse 11 01339 g010
Figure 11. Transverse profiles carried out on the Puente Mayorga IV shipwreck, following the numbering presented in Figure 9a: (a) line 4; (b) line 5.
Figure 11. Transverse profiles carried out on the Puente Mayorga IV shipwreck, following the numbering presented in Figure 9a: (a) line 4; (b) line 5.
Jmse 11 01339 g011
Figure 12. Longitudinal profiles carried out on the Puente Mayorga IV shipwreck, following the numbering presented in Figure 9a: (a) line 1, (b) line 2, and (c) line 3.
Figure 12. Longitudinal profiles carried out on the Puente Mayorga IV shipwreck, following the numbering presented in Figure 9a: (a) line 1, (b) line 2, and (c) line 3.
Jmse 11 01339 g012
Table 1. Measurements acquired with various methods on the contemporary shipwreck.
Table 1. Measurements acquired with various methods on the contemporary shipwreck.
MeasurementGoogle Earth 1UAS 1Divers 1
17.197.497.49
27.147.497.49
37.197.497.51
418.8618.9418.97
1 Expressed in meters.
Table 2. Measurements (expressed in meters) acquired based on the results of bathymetry performed with USV on the contemporary shipwreck.
Table 2. Measurements (expressed in meters) acquired based on the results of bathymetry performed with USV on the contemporary shipwreck.
MeasurementUSV
17.36
27.42
37.53
419.03
Table 3. Measurements acquired with the various methods on the contemporary shipwreck.
Table 3. Measurements acquired with the various methods on the contemporary shipwreck.
Puente Mayorga IVDEM 1DBM 1Point Cloud 1
115.0215.0815.11
27.577.517.47
33.423.493.55
40.180.210.21
52.983.003.03
1 Expressed in meters.
Table 4. GNSS coordinates of each control point and RMES error calculated by the photogrammetric processing software. *: Coordinate system used: ETRS89_UTM_30; International identification code of this coordinate system: EPSG: 25830.
Table 4. GNSS coordinates of each control point and RMES error calculated by the photogrammetric processing software. *: Coordinate system used: ETRS89_UTM_30; International identification code of this coordinate system: EPSG: 25830.
Point
Name
XYZ X Error (cm)Y Error (cm)Z Error (cm)Total Error (cm)
CP1285,705.4684,0063,89.146−1.504 4.30−14.46−4.8115.84
CP2285,703.4754,006,389.853−2.238 0000
CP3N285,703.2174,006,389.879−1.963 13.20−17.045.3522.21
CP4285,707.5574,006,385.691−2.018 −4.79−3.12−5.457.90
CP5N285,707.7394,006,383.642−2.434 13.111.02−0.6913.17
CP6285,705.2454,006,386.734−2.39 0.72−2.022.963.68
CP7285,705.4234,006,384.639−2.103 18.501.034.3919.04
CP8285,711.4794,006,381.911−2.17 −17.0711.481.0320.59
CP9285,713.7864,006,379.583−2.071 −31.0720.153.1737.17
CM1285,704.3094,006,387.14−2.218 0.80−2.130.582.35
CM2285,706.4694,006,384.388−2.285 10.871.330.7110.97
CM3285,707.2574,006,385.298−2.092 0.852.32−4.024.72
CM4285,706.1924,006,384.139−2.068 −9.461.42−3.2910.12
* ETRS89_UTM_30 (EPSG: 25830)Total
RMSE
13.539.433.523716.8637
Table 5. Correlation of the control measures used to rectify the model, expressed in Control Line 1 and Control Line 2.
Table 5. Correlation of the control measures used to rectify the model, expressed in Control Line 1 and Control Line 2.
Control Measure LineMetashape ModelDGPS CoordinatesIn Situ Measures
Control Line 1—CM1—CM23.533.53.48
Control Line 2—CM1—CM21.631.571.6
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Solana Rubio, S.; Salas Romero, A.; Cerezo Andreo, F.; González Gallero, R.; Rengel, J.; Rioja, L.; Callejo, J.; Bethencourt, M. Comparison between the Employment of a Multibeam Echosounder on an Unmanned Surface Vehicle and Traditional Photogrammetry as Techniques for Documentation and Monitoring of Shallow-Water Cultural Heritage Sites: A Case Study in the Bay of Algeciras. J. Mar. Sci. Eng. 2023, 11, 1339. https://doi.org/10.3390/jmse11071339

AMA Style

Solana Rubio S, Salas Romero A, Cerezo Andreo F, González Gallero R, Rengel J, Rioja L, Callejo J, Bethencourt M. Comparison between the Employment of a Multibeam Echosounder on an Unmanned Surface Vehicle and Traditional Photogrammetry as Techniques for Documentation and Monitoring of Shallow-Water Cultural Heritage Sites: A Case Study in the Bay of Algeciras. Journal of Marine Science and Engineering. 2023; 11(7):1339. https://doi.org/10.3390/jmse11071339

Chicago/Turabian Style

Solana Rubio, Soledad, Alberto Salas Romero, Felipe Cerezo Andreo, Raúl González Gallero, Juan Rengel, Luis Rioja, Joaquín Callejo, and Manuel Bethencourt. 2023. "Comparison between the Employment of a Multibeam Echosounder on an Unmanned Surface Vehicle and Traditional Photogrammetry as Techniques for Documentation and Monitoring of Shallow-Water Cultural Heritage Sites: A Case Study in the Bay of Algeciras" Journal of Marine Science and Engineering 11, no. 7: 1339. https://doi.org/10.3390/jmse11071339

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