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Danish University Colleges

Detailed geophysical mapping and 3D geological modelling to support urban planning:

A case study of Ny Rosborg, Denmark

Andersen, Theis Raaschou; Poulsen, Søren Erbs; Medhus, Anna Bondo

Publication date:

2021

Document Version Peer reviewed version Link to publication

Citation for pulished version (APA):

Andersen, T. R., Poulsen, S. E., & Medhus, A. B. (2021). Detailed geophysical mapping and 3D geological modelling to support urban planning: A case study of Ny Rosborg, Denmark. Paper presented at Australasian Exploration Geoscience Conference 2021.

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support urban planning: A case study of Ny Rosborg, Denmark

Theis R. Andersen Søren E. Poulsen Anna B. Medhus VIA University College VIA University College VIA University College

8700 Horsens, DK 8700 Horsens, DK 8700 Horsens, DK

Thra@via.dk Soeb@via.dk Anbm@via.dk

SUMMARY

At present , urbanisation is taking place . A s cities expand , areas previously omitted due to construction risks are now being urbanised. These areas are typically characterised as those with unforeseen soil properties , unknown groundwater conditions and the risk of flooding from the sea or rivers . Thus, to utilise these areas urban planners need detail ed information about the geology, hydrology and future climate impact on the area. W e have investigated how high-density geophysical data in combination with geotechnical data , borehole data and GIS data could be used for develop ing a high-resolution , 3D geological voxel model for Ny Rosborg. I n this model , specific geotechnical values can be assigned to each voxel thus providing a 3D overview of the geotechnical properties of the study area. The 3D geotechnical model enables city planners to identify those areas that are the most sustainable and cost-effective to develop . The 3D model output was combined with a map showing areas prone to flooding enabling the construction of a series of planning maps show ing the most suitable locations for green areas ( such as parks), blue areas ( such as lakes or wetlands) and grey areas ( such as buildings or roads) within the Ny Rosborg area.

Keywords: 3D Geological model, DualEM-421, Geotechnical mapping, Geophysical mapping, Planning

maps. INTRODUCTION

T he U nited N ations estimates that by 2050 more than 6 5 % of the world’s population will live in urban areas ( United Nations, 2019 ) . As cities expand, former industrial areas and wetlands are being urbani s ed due to the social and economic opportunities they present ( Andersen et al., 2020; Burke et al., 201 5 ; de Rienzo et al., 2008; Marache et al., 2009; Woll et al., 2003). T ypically, t hese areas are characterised by unforeseen ground conditions related to soil properties, unknown groundwater conditions and the risk of flooding from the sea , river s or rain. If urban planners are to properly develop and manage these areas , they need reliable and detailed information / data about the geology and hydrology of these areas along with the maps that show the future impact of climate on these areas . However, often urban planners have to rel y on point information, such as drilling s , in combination with overall 2D geological maps ( e.g., soil type maps ) using which they can only portray , overall, the suitable locations for future devolvement . Thus, the lack of apt and adequate data introduces or exacerbates the risk of poor urban planning.

Our project aims to apply high - density geophysic s in conjunction with lithological descriptions from boreholes, geotechnical data, GIS data and flooding maps to create a series

of detail ed and credible planning maps which urban planners can use while plann ing future urbanisation . This has been exemplified with the help of a case study in the Ny Rosborg area near Vejle in Denmark . The data used in this investigation comprise s borehole information, geotechnical data, electromagnetic (DualEM-421) data , electrical resistivity tomography data (ERT) and flooding maps.

STUDY AREA

The Ny Rosborg area is located to the west of the city of Vejle, Denmark (Fig ure 1 and 2 ) and covers 1.5 km 2 . The southern boundary of the Ny Rosborg area is flanked by the Vejle stream, the eastern and northern boundaries have residential development area s on the other side and the western part is bordered by agricultur al land . A landfill is located in the central part of the area . On the whole, t he geolog ical setting in Ny Rosborg is complex ranging from 1 to 10 m of fill ings (with garbage in the central part where the landfill is located) , underlain by up to 10 m of postglacial organic clay and peat interbedded with postglacial marine sand . G lacial sediments are located underneath the fillings and postglacial sediments that comprise interbedded layers of clay till and meltwater sand.

Figure 1. Overview map showing the location of the study site.

DATA

The Ny Rosborg site has been densely mapped with 80,000 m of D ualEM-421 and 12 ERT surveys (Fig ure 2 ) . Its geophysical mapping is supplemented with lithological samples from 60

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Abbreviated title eg: Author1, Author2 and Author3

3rd AEGC: Geosciences for Sustainable World – 18–21 April 2021, Brisbane, Australia 2 boreholes and geotechnical measurements ( in situ vane tests

and Standard Penetration Tests (SPT) ) . The groundwater table is located approximately 1 to 1.5 metr es below the ground surface (mbgs).

Figure 2. Overview map showing the position of the geophysical mapping and boreholes ( Modified from Andersen et al., 2020).

DualEM-421

The DualEM-421 data is collected by using a DualEM-421 ground conductivity meter (DUALEM Inc., Milton, ON, Canada). For details about the configuration of the DualEM- 421 system , data collection, data processing and inversion see Andersen et al., 2020 . The depth of investigation of this survey was between 5 – 8 mbgs . T he horizontal and vertical resolution s we re approximately 1 m and 0.5 m. 5 % of the data were deleted due to noise or couplings from buried conductors, leaving 76,000 measurements for the inversion (Figure 2).

Electrical Resistivity Tomography (ERT)

A total of 12 ERT profiles wer e collected using an ABEM Terrameter LS (Figure 2) . For details about the configuration of the equipment , data collection, data processing and inversion see Andersen et al., 2020 . The depth of investigation was 30 mbgs. The data points removed in the processing range were less than 0.1 % on lines 1 and 6 and 10 to 22 % on line 9.

Boreholes and geotechnical tests

About 60 boreholes were available within the study area for our investigation (Figure 2) . A majority of these were geotechnical boreholes with drill depths in the range of 5 to 10 m bgs and therefore the quality of the borehole information from the site is high . From boreholes B1, B2, B3, B4, B7, B11, B19, R1, R2 and R3 in situ vane shear test results were available and for boreholes R1, R2 and R3, SPT results were available. The vane shear test is used to determine the peak and remoulded undrained shear strength of cohesive soils ( Danish Geotechnical Society – Field Committee 1999 guidelines ) whereas SPT is conducted to evaluate soil’s resistance to penetration. The N-value cannot be directly correlated with any geotechnical parameter , but it can be used to empirically estimate the approximate shear strength properties of soils.

RESULTS

Based on the DualEM-421 and ERT data , lithological descriptions from the boreholes and GIS data , a 3D geological voxel model wa s constructed (Figure 3) . The model spans from 20 mbgs to 25 m eters above ground surface represented by a total of 67,500,000 voxels (voxel dimension of 1 m x 1 m x 1

m).

Figure 3. Cross- section of the 3d geological model . ( See the location in Figure 2.)

The DualEM-421 provides the overall spatial distribution (both horizontal and vertical) of the resistivity within the upper 5 – 8 mbgs thus enabling a very detail ed and valid interpretation at this depth interval (Figure 4).

Figure 4. Interval resistivity map derived from the DualEM-421 mapping. ( The dots represent the lithology found at the same depth interval.)

Below 8 mbgs , the interpretation of the geological model relied on borehole information in combination with the relevant ERT profiles.

E lectrical resistivities were interpreted into geological units based on lithological soil descriptions for the 60 boreholes.

Anthropogenic structures such as roadbeds, sewer fillings and cable beds we re imported into the model based on the GIS data.

A total of eight geological units were interpreted in the geological voxel model. Each voxel wa s interpreted to a specific lithology , and it wa s assumed that the geological units are homogeneous and have the same geotechnical properties throughout the unit.

The Ny Rosborg area has a complex upper geological setting (8 – 10 mbgs) . This is partly due to its complex geological history and partly due to human activities carried out in the area over time . A brupt changes were observed in the lithological and thereby in the geotechnical properties , especially around the landfill . The upper unit comprises fillings whose thickness ranges from 1 m in the north-western and south-eastern parts of the area to more than 20 m in the western part of the landfill . (Figure 3) The fillings inside the landfill were observed to primarily comprise sand interbedded with garbage. Outside the landfill , sandy fillings dominate. The median shear stress Cv of the fillings was measured to be 24 KPa (min: 16 KPa, max 46

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K P a). The fillings are underlain by a series of organic sediments comprising peat and organic clay interbedded with postglacial marine sand. The organic clay layers are could be interpreted from the DualEM-421 data and ERT profiles as having a low resistivity layer with the resistivities ranging from 5 to 25 Ohmm compared to the moderate to high resistivities of the filling and sand layers. The thickness of these units was around 10 m and this thickness was observed throughout much of the area. The median shear stress Cv of the peat and organic clay was found to be 26.5 KPa and 25 K Pa , respectively. Underlying t his section , 20 m of glacial meltwater sand wa s observed . The glacial meltwater sand is clearly distinguished from the organic clay having high resistivities above 80 Ohmm . Based on the SPT findings, it can be said that the sand , in this case , has a compact soil packing with 10 N-blows. Thus, the glacial meltwater sand is the first layer with proper bearing capacities within the Ny Rosborg area.

Planning maps

Based on the 3D geological voxel model and in combination with the flooding maps , we we re able to construct planning map s that show ed the thickness of the units to be unsuitable for direct foundation (Fig ure 5 ) . At Ny Rosborg fillings, the peat and organic clay are characterised by median shear stress values below 30 KPa and high organic content thus making them unsuitable for having a direct foundation as per Eurocode 7 guidelines (Dansk Standard, 2007) . As can be seen in Fi gure 5 , the thickness of the “low bearing capacity soil”, rang es from 6 m in the south-eastern area to 18 m in the western part of the landfill.

Figure 5. M ap showing the thickness of units unsuitable for direct foundation

Fi gure 6 presents the future climate flooding maps of the area.

This map was taken from Scalgo (www.scalgo. com ) , and it identifies areas with the highest risk of flooding . Ny Rosborg ’s northern , north-western and eastern parts are most likely to be flooded.

Figure 6. M ap showing areas prone to flooding (Taken from Scalgo (www.Scalgo.com)).

Combining Fig ure s 5 and 6 form s the basis for subdivid ing the Ny Rosborg area into the most sustainable and economical sections for optimal placement of green, blue and grey areas (Fig ure 7 ) . Green areas (vegetated areas) can be seen cover ing much of the western part of Ny Rosborg. This area is classified based either on the thickness of the “low bearing capacity soil”

above 12 m or on the high risk of being flooded. Blue areas (lakes and wetlands) are located in the north -eastern corner and along the Fløbæk stream. Grey areas (construction areas) dominate the central , eastern and northern parts of Ny Rosborg . They are characterised by less than 12 m thickness of the “low bearing capacity soil” and a low likelihood of being flooded.

Figure 7. M ap showing the optimal location of green, blue and grey areas within the Ny Rosborg site

CONCLUSIONS

This study proposes that a combination of high-density geophysical mappi ng in conjunction with geotechnical measurements , lithological information from borehole and GIS data can provide a solid basis for the preparation of reliable planning maps. In this case (Ny Rosborg site), the data comprise d 76,000 m of electromagnetic (DualEM-421) data, 12 ERT surveys , data from 60 boreholes and relevant GIS data.

The geophysical data were suitable for mapping the upper 5 to 25 m whe re the interpretation is constrained by the available borehole information. Based on th is data , a 3D geological voxel model w as developed in whi c h geotechnical data were added thereby creating a 3D geotechnical model. Th is 3D geotechnical model was combined with flooding maps and used to generate two planning map s with o ne map showing the thickness of the “low bearing capacity soil” and the other map

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Abbreviated title eg: Author1, Author2 and Author3

3rd AEGC: Geosciences for Sustainable World – 18–21 April 2021, Brisbane, Australia 4 showing the most suitable locations for blue, green and grey

areas for future development.

ACKNOWLEDGMENTS

The authors are grateful to the municipality of Vejle and Rambøll A/S for providing the data and for their assistance during the practical and analytical work. Th is project was supported by the EUDP Denmark (64017-05182).

REFERENCES

Andersen, T.R . , Poulsen, S.E., Pagola, M.A., Medhus, A.B., 2020, Geophysical mapping and 3D geological modelling to support urban planning: A case study from Vejle, Denmark . Journal of Applied Geophysics, 180.

Burke, H., Hough, E., Morgan, D.J.R.J.R., Hughes L., Lawrence, D.J.J., 2015 , Approaches to inform redevelopment of brownfield sites: An example from the Leeds area of the

West Yorkshire coalfield, UK. Land Use Policy 47, 321–331.

de Rienzo, F., Oreste, P., Pelizza, S., 2008 , Subsurface geological-geotechnical modelling to sustain underground civil planning. Engineering Geology 96, 187–204.

Marache, A., Dubost, J., Breysse, D., Denis, A., Dominique, S., 2009 , Understanding subsurface geological and geotechnical complexity at various scales in urban soils using a 3D model.

Georisk: Assessment and Management of Risk for Engineered Systems and Geohazards 3, 192–205.

United Nations, 2019, Department of Economic and Social Affairs, Population Division. World Urbanization Prospects:

The 2018 Revision; ST/ESA/SER.A/420; United Nations: New York, NY, USA, 2019.

Woll, B., Mack, J ., Vetter, J.R., Ellerbusch, F., Vetter, J.R., 2003 , Facilitating brownfields transactions using triad and environmental insurance. Remediation Journal 13, 113–130.

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