# The role of sedimentation and natural compaction in a prograding delta: insights from the mega Mekong delta, Vietnam

## Abstract

The Vietnamese Mekong Delta was formed by rapid transgression during the second half of the Holocene by deposition of mainly unconsolidated, fine-grained (clayey) sediments undergoing high compaction rates. The natural subsidence can seriously impact the already vulnerable delta plain as its low elevation exposes the delta to global sea level rise, flooding, salinization. Human activities such as groundwater pumping, infrastructural loading, sand mining and dam construction have exacerbated the effects of natural consolidation. Here we present a novel modeling study that has allowed to reproduce the formation and evolution of the Mekong delta over the past 4000 years. Using an adaptive finite-element mesh, the model properly simulates accretion and natural consolidation characterizing the delta evolution. Large soil grain motion and the delayed dissipation of pore-water overpressure are accounted for. We find that natural compaction of Holocene deposits following delta evolution exceeds predicted values of absolute sea level rise. The unprecedented high rates (up to ~20 mm/yr) threaten the lower delta plain with permanent inundation and inevitably reduce the designed service life of flood defense structures along the coast. Total subsidence and sediment delivery to the delta plain will determine its future elevation and vulnerability to relative sea level rise.

## Introduction

The populous Vietnamese Mekong Delta (VMD) hosts a thriving agricultural and industrial economy1. Like many deltas in the world2, its current delta plain has only been formed recently by deposition of sediments during the last several thousand years3. Its low elevation makes the VMD vulnerable to global sea level rise4,5, river flooding6, and salinization7. Moreover, fluvial sediment supply of the Mekong river is diminishing due to upstream dams8,9,10 and decreased activity of tropical cyclones over the Mekong river basin11. Within the delta, sediment delivery to the flood plains is decreasing due to dykes12 and sand mining13,14.

In addition, the delta is subsiding15 and the rates are accelerating due to the strong increase in groundwater extraction during the past decades16. Although human activities, like groundwater extraction and infrastructural loading, can increase land subsidence, sediment compaction in deltas is a natural process inherently related to delta evolution. As deltas evolve and prograde, new sediments are deposited on top of older, earlier deposits. The gravitational load of overlying sediments (overburden) causes the underlying sediments to compact (reduction in sediment volume and increase in bulk density), as a result of pore collapse (mechanical grain reorganization) and fluid expulsion17. Delayed dissipation of excess pore water pressure can result in ongoing compaction long after sedimentation has ceased. This process is especially apparent in fine-grained soils (i.e., peat and clay). The factors that determine the rate of natural compaction, and possibly land subsidence, are sediment type (hydrological and geotechnical properties) and the specific depositional history that has resulted in the present stratigraphy. Secondarily, compaction can be influenced by chemical or biological processes like dissolution, cementation, and decay of organic matter. As such, natural compaction can spatially be variable and characterized by high rates; in the Mississippi delta for example, compaction of Holocene sediments is identified as the main cause for delta subsidence, with multi-decadal rates exceeding 10 mm per year18,19,20. Determining compaction rates in modern transitional environments is difficult and direct observations and monitoring efforts are expensive and time consuming. Calculation of natural compaction is often complicated by the lack of data on sediment properties and incomplete knowledge of the depositional history21.

In VMD, very high compaction rates of Holocene strata between 25 and 41 mm per year are measured at three locations in coastal mangrove areas by surface elevation tables (SET) combined with marker horizons that register accretion at the surface22. Although sediment accretion for these locations exceeds compaction rate, which results in a net elevation gain of the surface, these numbers reveal the potential of the Holocene deltaic sediments to contribute to VMD subsidence through natural consolidation. This holds especially in cases where sediment accretion is reduced by natural causes, dyke development or following cultivation23. With subsidence posing an increasing threat to the VMD, it is essential to quantify the contribution of each specific driver to the delta subsidence to create an action perspective for sustainable delta management16.

In this paper, we aim to address and quantify natural compaction of the Holocene strata in the VMD as a result of the sedimentation history following delta evolution. We present a novel modeling approach that allows us to reproduce the VMD evolution and quantify the corresponding compaction over the past 4000 years. The model represents the most low-lying and vulnerable part of the delta, mainly consisting of fine-grained Holocene material (clays). Due to the extremely high porosity of newly deposited soil, the medium is deformable with large solid grain movements. Therefore, we use a two-dimensional (2D) groundwater flow model coupled to a one-dimensional (1D) compaction module where the assumption of infinitesimal displacements is relaxed to account for large deformations24. This implies the recast of Darcy’s law in term of relative velocity of the soil grains to the fluid velocity. We do not incorporate chemical or biological processes as they represent secondary factors contributing to compaction because of general waterlogged conditions25,26. This approach may serve as a model to investigate natural compaction in other deltas and prograding coastal environments elsewhere in the world.

## Results

The present study focuses on the simulation of the VMD evolution over the past 4000 yrs during which the prodelta moved 200 km in seaward direction along the alignment A-A′ traced in Fig. 1. Large amounts of fine-grained material from the Mekong river mouths entered the sea and were subsequently transported by dominant longshore currents in southwest direction. Accumulation of these sediments resulted in a shoreline migration of about 150 km seaward during the past 3000 yrs at an average progradation rate of 50 m/yr27, creating the Ca Mau peninsula. The Holocene sediments mainly consist of clay and organic clay and accumulated to a total thickness varying between 18 and 25 m on top of the older Pleistocene deposits (Fig. 2). We assess spatio-temporal compaction and deformation of the Holocene sediments following delta progradation for both the prodelta and the lower delta plain. The northern part of section A-A′ demarcates the boundary between the marine dominated deposits of the lower delta plain and the fluvial dominated deposits of the upper delta plain28 (Fig. 1).

The large accumulation of clayey sediments on the subaqueous shoreface (i.e. prodelta) caused the rapid progradation of the delta in the direction of profile A-A′. The prodelta migration of 50 m/yr is simulated by a spatio-temporal evolution of the sedimentation rate properly constrained by available data (see Materials and Methods).

The modelling approach enabled the dynamical simulation of the prograding prodelta employing an adaptive mesh. New grid elements were progressively added at increasing time steps to account for the accumulation of new material, burying the underlying sediments. The mesh initially consisted of 1000 nodes and 998 triangular elements, which increased during the simulation to the final values of 103,799 nodes and 206,372 triangles. The initial thickness of a new-deposited element equaled 0.2 m, whereas a 400 m-discretization was used along the x-axis with a 1:1000x-scaling factor. The mesh elements deformed accordingly to the occurring consolidation process and their thickness decreased as the load of the overlying sediments increased. The deformations were obtained through the computation of the movement of the soil grains, which are represented by the grid nodes in the 1D geomechanical model24.

Prodelta formation was simulated with a sedimentation rate (ω) ranging from 0 to 70 mm/yr with shoreline proximity, accounting for increasing near-coastal sedimentation. This sedimentation evolved over the distance of 50 km in 1000 yrs (Fig. 3a). After 1000 yrs, i.e. at 3000 yrs BP, the prodelta was completely formed. At this stage, the accumulated sediments became elevated above sea level and the depositional environment changed from prodelta to lower delta plain. The simulated thickness of compacting sediments at the coastline reached 18 m (Fig. 3b). This value is in line with the 18–20 m-thick Holocene clays on top of stiffer Pleistocene silty clays to silty sands reported for the Ca Mau peninsula (Fig. 2)28,29. A detailed description of the data used to derive the ω behavior is provided in Materials and Methods section.

Figure 3b shows the post-depositional lowering (PDL) of the delta sediments occurred in the interval between 4000 and 3000 yrs BP. The PDL value at any z-coordinate represents the compaction of the sediment column underlying z from time of deposition to 3000 yrs BP and its integral over z gives the total compaction of the soil column. The highest PDL equal to ~2.3 m is experienced by sediments at the shoreline and approximately in the middle of the column thickness. As the cumulative amount of unconsolidated sediments deposited at the shoreline is 35 m (average sedimentation rate over 1000 yrs is 35 mm/yr), the total compaction taking place during prodelta formation is 17 m, corresponding to an average rate of 17 mm/yr.

After 3000 yrs BP, the prodelta successively advanced along the delta progradation-direction at a constant speed of 50 m/yr until it reached the present 200 km-length. Figure 3c shows the profiles of delta progradation at 3000, 2000, and 1000 yrs BP, and at present. The model outcomes agree with: (i) data from corings that reveal the southward evolution of the delta and approximate locations of the prodelta in the past (Fig. 2); and (ii) high-resolution, offshore seismic profiles of the low-gradient prodelta surrounding the modern VMD with a maximum thickness of ~20 m at the shoreline30,31.

### Lower and upper delta plain evolution

During delta evolution over the past 3000 yrs, the lower delta plain remained about constantly elevated at the sea level or slightly above as it is at present, with wetlands forests and marshes being the main eco-morphological features3. This is the result of a dynamic balance of sediment accumulation and compaction. Accommodation created by ongoing compaction following delayed overpressure dissipation was filled by new, clastic, and organic sediments. As a result, the delta plain sustained its elevation and the total thickness of Holocene sediments remained constant, while becoming more compact. Simulated sedimentation rates are based on available data (see Materials and Methods). The maximum sedimentation rate equals 35 mm/yr just behind the shoreline, corresponding to the location of Dat Mui at the present day coastline (Ca Mau peninsula, see Fig. 2). The sedimentation rate decreases progressively moving inland along the cross-section A-A′ (Fig. 3a) as, with the gradual decrease in overpressure (Fig. 4a), compaction rate decreases and less sediment is needed to fill the accommodation. On the upper delta plain, a constant sedimentation rate of 6 mm/yr suffices to counterbalance the consolidation (Fig. 3a).

At 1000 yrs BP (Fig. 3a, magenta line), the total compaction is equal to 17 m at shoreline location (x = 100 km) and 37 m at the edge of the lower delta plain (x = 0 km), where the total thickness of the deposited material (before consolidation) is 35 m and 55 m, respectively (Fig. 3c). The maximum PDL at 1000 yrs BP amounts up to 8.5 m (x = 0 km, location of the shoreline 3000 yrs BP) (Fig. 3c), meaning that these sediments are now buried 8.5 m below their elevation at time of deposition. This value increases to 9.3 m at present, i.e., at the end of the model simulation.

The overpressure (p) in the present condition (t = 0 yrs BP) is shown in Fig. 4(a). The maximum value (p = 80 kPa) is located at the bottom of the Holocene column at the shoreline (x = 150 km) where sedimentation rate assumes the largest value. Overpressure is lower seaward as there is less overburden and inward as partial dissipation of overpressure has already taken place. At the edge of the lower delta plain (x = 0 km) the remaining overpressure at the bottom of the sediment column amount to p = 53 kPa. Obviously, there is no overpressure at the delta surface. At Ca Mau city (Fig. 4), the simulated maximum overpressure is equal to ~60 kPa and the maximum PDL to ~7.8 m, suggesting that natural compaction is an ongoing process. The modeled overpressure values are within the range of values measured in shallow VMD clays using cone penetration tests (overpressures up to 200 kPa are reported)32,33. Figure 4(b) and (c) show the vertical permeability (kz) and porosity (ϕ) distribution within the domain, respectively. Porosity decreases with depth due to the increase of the intergranular effective stress (σz), see Materials and Methods for the ϕ-σz relationship. An empirical relationship is used to relate permeability to soil deformation (see Materials and Methods) and, in turn, to porosity distribution. The permeability reduction of about two orders of magnitude from the shallowest to the deepest deposits strongly delays overpressure dissipation and, consequently, consolidation dynamics.

### Sensitivity analysis

The model is calibrated using the available datasets of sedimentation rates, geotechnical soil properties and lithology of the Holocene sediments (see Materials and Methods). Although the model results provide a satisfactorily match with observations, we present a sensitivity analysis of the model output to the main input data and parameters to evaluate the variability range of the system dynamics due to different factors. The sensitivity analysis refers to the prodelta formation phase, i.e., the time interval between 4000 and 3000 yrs BP.

The investigated range of model parameter (mp) variability is 20% ($${m}_{p}\pm \mathrm{20 \% }{m}_{p}$$), which is probably a somewhat narrow range due to the large uncertainty associated with the hydraulic permeability and deposition rate. Figure 5(a) shows the changes in total elevation of Holocene deposits due to variations of permeability and sedimentation rate. A smaller vertical permeability implies a slower overpressure dissipation in time, thus lower consolidation rate and higher elevations. A variation in the total elevation of 12–15% is found for kz ± 20%kz. On the other hand, keeping permeability fixed, the sedimentation rate affects the thickness of deposited sediments, causing an approximate 22% difference in elevation from the calibrated value.

The relation between sediment deformation and the geomechanical properties of the soil is also investigated, with the results presented in Fig. 5(b). The geomechanical characteristics are described through the coefficient of compression, Cc, with organic clays having higher compressibility than mineral clays. Cc is kept constant for each lithological unit. A smaller Cc yields lower deformations of the porous matrix, which, in turn, influences the permeability distribution within the soil column. Following the relationship between permeability and vertical deformation εv provided in Materials and Methods, a 50% decrease of vertical deformation results in a 23% higher permeability. As such overpressure dissipation is higher, subsequently larger consolidation rates are computed. This complex behavior is summarized in Fig. 5(b) where the total deformation of the soil column εtot at x = 0 km and t = 3000 yrs BP is plotted against Cc. εtot is computed as εtot = (Ttot − T3000)/Ttot with T3000 the thickness of the Holocene column at t = 3000 yrs BP and Ttot the thickness of the deposited, unconsolidated material between t = 4000 yrs BP and t = 3000 yrs BP. Overpressure drops of about 70 kPa follow the reduction of Cc from 0.7 to 0.2. This implies a 20% variation of εtot, corresponding to 3.6 m-difference in elevation.

### Future delta evolution

In the past, natural compaction of the delta plain was counterbalanced by clastic and organic sedimentation, allowing the delta to maintain its elevation above sea level. However, cultivation23, dyke development on the delta plain12, and reduction of upstream sediment supply have disturbed this natural balance. As a result, Ca Mau peninsula is receiving a decreasing amount of sediments both at the prodelta and on the delta plain. The feedback of this new condition on land subsidence is not straightforward because a dynamic coupling between accretion and overpressure dissipation, and therefore land subsidence, exists. Moreover, the coupling is governed by the intrinsic hydro-geomechanical properties of the accreting and underlying deposits.

To understand this complex mechanism the proposed model has been applied. We simulated two scenarios of delta evolution over the next 100 yrs. The first scenario (scenario A) investigates the situation in which the sediment supply is halved compared to the present values for which compaction and sedimentation are in equilibrium. The model results are provided in Fig. 6. With a 50% reduction of sedimentation rate, we can reasonably assume that the delta is still prograding at halved speed of 25 m/yr. The consequence is a net aggradation at the prodelta up to 6 mm/yr. However, on the delta plain, sedimentation is no longer enough to counterbalance the consolidation of the underlying deposited sediments. At the present shoreline location (Dat Mui) this results in an average subsidence rate of 12 mm/yr, amounting to ~1.2 m by the end of the century (Fig. 6b). Subsidence rates decrease gradually inland to 0.8 mm/yr towards the upper delta plain.

In the worst case (scenario B) sediment deposition is assumed to cease completely (ω = 0 mm/yr). Land subsidence is no longer counterbalanced by sedimentation and, because of the ongoing overpressure dissipation, subsidence is expected along the entire prodelta and delta plain. The results presented in Fig. 6c show a maximum loss of land elevation equal to ~2.0 m at the present shoreline, which means an average subsidence rate of 20 mm/yr. This rate gradually decreases toward the upper delta plain, where the subsidence rate drops to 2.4 mm/yr. Progradation of the VMD completely stops in this scenario and a large part of the lower delta plain will sink below sea level before the end of the century.

## Discussion

The main processes controlling delta progradation are sediment aggradation and natural compaction of Holocene sediments. Here natural compaction involves the volume reduction of the deposited material due to the loading exerted by the overlying, more recent deposits following the consequent overpressure dissipation. Our novel model allowed for the first time to simulate the spatio-temporal formation and evolution of the VMD along a representative 2D vertical section (Fig. 1) by using an adaptive mesh, with changing element shape and number following new sediment deposition and consolidation over time. The modelling application is properly supported by geomorphological and geotechnical information.

We estimate rates of natural compaction of the Holocene sediment sequence at the coastline equal to ~20 mm/yr as a result of thousands of years of VMD delta evolution. These high rates were previously unaccounted for15 and pose a serious threat to the Mekong delta as these rates cannot be mitigated. Moreover, such natural compaction rates directly affect unfounded structures and inevitably reduce the designed service life of coastal defense structures that are currently being build. As a result, if not taken into account, natural compaction seriously threatens Vietnam’s investments in a hard coastal protection system of the VMD coastline. Such measures should be considered carefully, also because the construction of a coastal dyke system decreases sedimentation on the hinterland, accelerating delta plain subsidence further.

Land subsidence in modern deltas is partly related to the decrease of sediment availability2. It is reported that the VMD has experienced a decrease of sediment supply by 12% in the 20th century. Larger reduction are expected in the coming decades. Dam development in the Mekong drainage basin may potentially cause major changes in the amount of sediment transported to the delta34. Major dam construction began in the Mekong basin in 1993; by April 2016, 35 dams had been commissioned for hydropower, irrigation reservoirs, and drinking water supply. A further 226 dams are under construction and even more are planned35. A recent study predicts that the cumulative suspended sediment in the Mekong river decreased to 51% following the construction of the current dams, and that this value goes up to 96% in case all planned dams are constructed9. Changing global climate may also affect the future water and sediment supply to the Mekong Delta36, as a large fraction of the suspended sediment load reaching the delta is associated with rainfall from tropical cyclones. Climate models suggest the locations of cyclone tracts to shift away from the latitude of the Mekong Basin, which may also lead to additional suspended sediment reduction11.

We estimate that a sediment reduction of 50% over the 21st century results in a loss of elevation amounting to ~1.2 m at the present coastline due to ongoing natural compaction of the Holocene sequence. The prediction worsens if sedimentation on the delta surface is completely prevented, leading to an elevation loss of ~2.0 m by the end of the century. More inland, towards the upper delta plain, the elevation loss reduces to ~10 cm and ~20 cm for a sediment reduction of 50% and 100%, respectively. Our estimates suggest that Ca Mau city will subside ~34 cm as a result of natural compaction of Holocene sediments during the next century as flood sedimentation in the city has completely ceases.

Other natural and human-induced drivers and processes may also contribute to subsidence and the future evolution of deltaic regions. Examples of natural subsidence drivers are tectonics, natural compaction of Quaternary units, and glacial isostatic adjustment. In the VMD their contribution to subsidence has been quantified in the order of a few mm/yr over the late-Holocene3,37. Therefore, they have played a secondary role on the recent delta evolution and have been neglected in our analysis. The effect of biological and chemical processes, which may trigger additional subsidence, have been negligible in the past as a result of the general waterlogged conditions and were therefore not included in this study. However, they should be accounted for in future modelling as drained conditions may be established in deltaic-plain sediments for agricultural purposes. Aeration triggers oxidation of the organic matter, which represents a large fraction of the top soils, and consequently enhances the ongoing natural compaction as experienced for example in the Rhine-Meuse (The Netherlands)38,39 and Po (Italy)25 river deltas. Concerning anthropogenic subsidence, groundwater pumping from the deep multi-aquifer system has significantly contributed, in the range of 10 to 25 mm/yr16, to the present land subsidence in the VMD over the last few decades. Oil and gas activities are also on the rise offshore of the VMD with areas undergoing seismic exploration and some initial drilling by the Vietnam National Oil and Gas Group (PetroVietnam) and international partners34. Future hydrocarbon explorations may contribute as well to subsidence of the delta.

Finally, also sea level rise contributes, although secondarily, to the relative loss of land elevation with respect to the sea level. Estimates of absolute sea level rise for the VMD are ~3.5 mm/yr40, which are small compared to the land subsidence the delta may experience in the coming decades. Our study reveals that natural compaction of the Holocene sediments alone can create subsidence rate up to one order of magnitude larger than absolute sea level rise.

As the VMD is only elevated ~1–2 m above sea level, the anticipated subsidence rates seriously threaten the lower delta plain with permanent inundation. Therefore, sediment supply to the delta plain and a proper management of surface water and groundwater resources are key factors for the VMD survival. The model presented here represents a valuable tool for understanding the natural compaction dynamics of the VMD and, more generally, of coastal environments at risk of submersion. It can be used to identify areas vulnerable to high compaction rates and hereby contribute to improve coastal protection plans.

## Materials and Methods

### Site evolution over the Holocene

With an area of 50,000 km2, the Mekong delta, largely situated in the southwest of Vietnam, is the third largest delta plain in the world and it is characterized by the largest areal extent elevated less than 2 m above mean sea level2, i.e. more than 20,000 km2 (Fig. 1). The combination of high sediment supply, wave-sheltered position and relatively shallow sea favored a very rapid growth of the delta over the last 6000 years27. Around ~3000 yrs BP, the delta changed from a tide dominated delta to a wave-tide dominated delta with increased long-shore sediment transport28. On entering the flat delta plain, the Mekong river branched out in eastward direction, forming a river landscape with large channel belts and floodplains. Sand transported by the river was deposited in sequences of wave-formed beach ridges between the different river mouths41. The impressive muddy load of the Mekong river was transported by wave-induced longshore currents towards the south-western part of the delta. The accumulation of fine-grained sediments filled the space between the coarser-grained Pleistocene surface and the present day delta surface. This resulted in the rapid progradation of the so-called Ca Mau peninsula (Fig. 1), and the formation of vast swamp, marsh and mangroves areas14.

### Available data to constrain the sedimentation and consolidation model

The prodelta moved seaward approximately 200 km during the past 4000 years3,27. This results in an average progradation rate of ~50 m/yr for the Ca Mau peninsula. Figure 1 shows a map of the present Vietnamese Mekong delta and its evolution in time. The model simulates the delta formation and progradation along the A-A′ section (Fig. 1) over the 4000 yrs-interval. Note that the 200 km-delta includes 50 km of prodelta.

The information on the sedimentation rates over the delta is available from the literature. In particular, the bay and prodelta sediments are found to accumulate at a rate up to 32–63.7 mm/yr28,42. Sedimentation rates up to 36.8 ± 3.1 mm/yr and 67.8 ± 6.6 mm/yr, respectively, at Dat Mui and the Bassac river mouth, have been quantified using marker horizon measurements at SET sites22. These data allow constraining the model input in term of prodelta sedimentation rates. An average sedimentation rate (ω) of 35 mm/yr over a 1000-yr time interval roughly corresponds to a prodelta progradation of 50 km.

For the lower delta plain we assume a dynamic balance between natural compaction and sedimentation, meaning that accommodation is filled through sedimentation but sedimentation rate does not exceed compaction rate. An average subsidence rate of 30–35 mm/yr is derived from 12 SET stations established at 4 locations in mangrove areas along the coast22. Thus, sedimentation rates of 30–40 mm/yr represent a likely estimate of the amount of sediment required at the coastal front to balance subsidence. Notice that these SET combined with marker horizon data are not representative of most of the the peninsula which is nowadays predominantly agricultural. Therefore, a reduced value is prescribed at the upper delta plain with an average floodplain sedimentation of ~6 mm/yr43. This results in a flat and lowly elevated surface in agreement with the present setting of the VMD lower delta plain. Sedimentation likely decreases gradually away from the coastline towards the upper delta plain. Following this principle and data to constrain on past coastline progradation, a consistent behavior of sedimentation rate, ω(x, t), for the prodelta and the delta plain was determined (Fig. 3a).

Surely, we are aware that the sediment deposition and its spatial variability as provided in Fig. 3a is a semplification of a much more complex process of sediment re-distribution, starting from the sources (the Mekong river and its mouth) to the dispersal work carried out by dominant longshore currents and river floodings in the delta plain. However, an accurate representation of these processes is beyond the scope of our study and it cannot be captured in a 2D modelling framework as the one used in the proposed analysis.

### Hydro-geomechanical data and model set-up

The main input parameters of the model are the hydro-geomechanical properties of the Holocene deposits. These features have been quantified using datasets from the geotechnical measurements summarized in Table 1. Lithological boreholes and geotechnical profiles in Ca Mau revealed the presence of very soft organic clays overlying soft mineral clays in the upper 20 m-depth29,44. Based on the available lithological information (Fig. 2), these two sediment types, which prevail within the Holocene sequence, are accounted for in the model.

The behavior of the vertical oedometric compressibility cb versus the vertical effective intergranular stress σz represents the fundamental constitutive relationship implemented in our modelling approach. This law is obtained by integrating the relation:

$$\frac{-1}{\mathrm{(1}+e({\sigma }_{z}))}de={c}_{b}d{\sigma }_{z}$$
(1)

with e the void ratio and e(σz) = e0 − Cclogσz. The void index e0 is representative of the porosity of the newly deposited sediments on the delta surface. An initial void index e0 = 2.5 has been obtained by geotechnical analyses on shallow organic clay samples collected in Ca Mau44. A corresponding Cc = 1.05 is computed using the relationship $$\frac{{C}_{c}}{1+{e}_{0}}$$ = 0.3 experimentally derived from the geotechnical surveys carried out by NGI32. These values are supported by empirical relationships45,46 and measurements on similar, shallow very-soft clays in Ho Chi Minh city where Cc = 1.01 with e0 = 2.2347. Different values of e0 and Cc are measured for the mineral clays underlying the organic clays. An average value Cc = 0.57 is derived using a liquid-limit relationship45 based on the analyses of 133 soil samples collected at Ca Mau city with e0 = 1.89. Notice that in the proposed model the geomechanical properties depend on the lithotype and vary with the vertical effective stress differently for each sediment type. Moreover, it has been assumed that the properties of each element shift from organic to mineral clay for an effective stress larger than 5 KPa, i.e., when the element is buried at depth approximately larger than 1 m.

Oedometer tests carried out by the NGI at zero-volume change provide a vertical hydraulic conductivity kz,0 = 2.2 10 −9 m/s32. This value is considered representative for the unconsolidated soil at the delta surface. Moreover, the same tests also define the following relationship between kz and the volumetric change εvol of the porous media due to compaction:

$$\frac{\mathrm{log}\,{k}_{z\mathrm{,0}}-\,\mathrm{log}\,{k}_{z}}{{\varepsilon }_{vol}}=4.0$$
(2)

Since εvol is provided by the numerical model as described below, Equation 2 allows reproducing the change of kz during the delta evolution. Finally, an anisotropic hydraulic conductivity with a ratio between the horizontal value kx and kz equal to 2.0 is assumed for shallow clay material48.

### Governing equations

The formation and evolution of the VMD is described with the aid of a numerical model (NATSUB-2D) by coupling a 2D groundwater flow model over a cross-section of the delta and a 1D geomechanical module. The model allows describing the spatio-temporal evolution of the consolidation process within the forming delta system, depending on the overpressure evolution.

The rigorous equations of the 1D flow in an elastic saturated compacting porous medium was originally developed in the late 70 s49,50, where the hypothesis of infinitesimal displacement of the grains is relaxed and large soil deformations are accounted for introducing a geometric non-linearity. In a 2D vertical cross-section, the governing equations of the groundwater flow can be written as24

$$\frac{\partial }{\partial x}(\frac{{k}_{x}}{\gamma }\frac{\partial p}{\partial x})+\frac{\partial }{\partial z}(\frac{{k}_{z}}{\gamma }\frac{\partial p}{\partial z})=({c}_{b}+{\varphi }\beta )Dp-2\beta {k}_{z}\frac{\partial p}{\partial z}-\beta \frac{{k}_{x}}{\gamma }{(\frac{\partial p}{\partial x})}^{2}-\beta \frac{{k}_{z}}{\gamma }{(\frac{\partial p}{\partial z})}^{2}$$
(3)

where kx and kz are the horizontal and vertical hydraulic conductivities, γ is the specific weight of water, cb is the soil oedometric compressibility, ϕ is the soil matrix porosity, β is the volumetric water compressibility, p is the incremental pore pressure with reference to the hydrostatic condition (overpressure), x and z are the horizontal and vertical coordinates. Dp refers to the total or Eulerian derivative, which can be treated as a partial time derivative ∂p/∂t by using a Lagrangian approach24 with a dynamic mesh where the grid nodes follow the grains in their consolidation movements. In this case, the second term of Dp = ∂p/∂t + vg,z p/∂z vanishes and the mesh nodes move accordingly to the vertical grain velocity vg,z51:

$${v}_{g,z}(z,t)=\mathrm{(1}-\alpha {\sigma }_{z}){\int }_{0}^{z}\frac{(\alpha +{\sigma }_{z}\frac{\partial p}{\partial t})}{{\mathrm{(1}-\alpha {\sigma }_{z})}^{2}}dz$$
(4)

In Equation 4, α is the classical compressibility defined as α = z/z with εz the vertical deformaition, and linked to cb by the relationship $${c}_{b}=\frac{pd\alpha \,/\,dp+\alpha }{1+\alpha p}$$. It follows that the compaction u(z, t) (and hence the volumetric change) of the mesh elements can be computed as

$$u(z,t)=-\,{\int }_{0}^{z}\frac{\alpha {\sigma }_{z}}{1-\alpha {\sigma }_{z}}dz$$
(5)

Equation 3 holds under the following expression of the relative Darcy’s law

$$\varphi ({v}_{w,i}-{v}_{g,i})=-{k}_{i}\frac{{\rm{\partial }}\psi }{{\rm{\partial }}i},\,i=x,z$$
(6)

with vg,i and vw,i the (absolute) velocity of solid grains and water along the i direction, respectively, and ψ the hydraulic potential expressed as $$\psi =z+{\int }_{0}^{p}dp/\gamma$$. Notice that for the specific process of interest vg,x is negligible and only vertical compaction is considered. Moreover, it is assumed incompressible solid grains and constant total stress expressed by Terzaghi’s principle in the form σt = σz,0 + σz + p0 + p, with σz,0 and σz the initial and incremental intergranular effective stress, respectively, and p0 the initial reference value for p.

To account for the delta progradation due to sediment accumulation, a sedimentation rate ω(x, t) is admitted and Equation 3 turns into24

$$\frac{\partial }{\partial x}(\frac{{k}_{x}}{\gamma }\frac{\partial p}{\partial x})+\frac{\partial }{\partial z}(\frac{{k}_{z}}{\gamma }\frac{\partial p}{\partial z})=(\frac{{\sigma }_{z}\frac{d\alpha }{d{\sigma }_{z}}+\alpha }{1-\alpha {\sigma }_{z}}+{\varphi }\beta )Dp-\frac{{\sigma }_{z}\frac{d\alpha }{d{\sigma }_{z}}+\alpha }{1-\alpha {\sigma }_{z}}D{\sigma }_{t}$$
(7)

In natural conditions, the variation of the total stress, t, is due to the change of load by new sediment deposition on the delta surface, thus t = ω(x, t) (1 − ϕ0)(γs − γ) with γs the specific weight of the grains and ϕ0 the initial porosity at σz,0. The material properties such as porosity, compressibility, and hydraulic conductivity are functions of the intergranular effective stress to account for their variability with the progressive deformation of the soil matrix. Indeed, cb, kz, and ϕ diminish at increasing values of σz.

The numerical solution of Equations 5 and 7 is implemented in NATSUB-2D by a Finite Element discretization, using a back Euler method for the time integration and a fixed-point iteration scheme to solve the material and geometric non-linearities. A constant time step equal to 1 year has been adopted.

Figure 7 shows the evolution of the computing mesh in time. The increasing number of triangular elements is provided to point out the spatio-temporal evolution of the computing grid following the delta formation and progradation.

## References

1. 1.

Renaud, F. & Kuenzer, C. The Mekong Delta System. Interdisciplinary analyses of a river delta. (Springer Netherlands, 2012).

2. 2.

Syvitski, J. P. M. et al. Sinking deltas due to human activities. Nature Geoscience 2, 681–686, https://doi.org/10.1038/ngeo629 (2009).

3. 3.

Nguyen, V., Ta, T. & Tateishi, M. Late Holocene depositional environments and coastal evolution of the Mekong river delta, southern Vietnam. Journal of Asian Earth Sciences 18, 427–439, https://doi.org/10.1016/S1367-9120(99)00076-0 (2000).

4. 4.

Wassmann, R., Hien, N. X., Hoanh, C. T. & Tuong, T. P. Sea level rise affecting the Vietnamese Mekong Delta: water elevation in the flood season and implications for rice production. Clim. Change 66, 89–107, https://doi.org/10.1023/B:CLIM.0000043144.69736.b7 (2004).

5. 5.

Ericson, J., Vorosmarty, C., Dingman, S., Ward, L. & Meybeck, M. Effective sea-level rise and deltas: causes of change and human dimension implications. Glob. Planet. Change 50, 63–82, https://doi.org/10.1016/j.gloplacha.2005.07.004 (2006).

6. 6.

Kuenzer, C. et al. Flood mapping and flood dynamics of the Mekong delta: ENVISAT-ASAR-WSM based time series analyses. Remote Sens. 5, 687–715, https://doi.org/10.3390/rs5020687 (2013).

7. 7.

Renaud, F. G., Le, T. T. H., Lindener, C., Guong, V. T. & Sebesvari, Z. Resilience and shifts in agro-ecosystems facing increasing sea-level rise and salinity intrusion in Ben Tre Province, Mekong Delta. Climatic Change 133, 69–84, https://doi.org/10.1007/s10584-014-1113-4 (2015).

8. 8.

Milliman, J. D. & Farnsworth, K. River Discharge to the Coastal Ocean: A Global Synthesis. (Cambride University Press, 2011).

9. 9.

Kondolf, G. M., Rubin, Z. K. & Minear, J. T. Dams on the Mekong: cumulative sediment starvation. Water Resources Research 50, 5158–5169, https://doi.org/10.1002/2013WR014651 (2014).

10. 10.

Kummu, M. & Varis, O. Sediment-related impacts due to upstream reservoir trapping, the Lower Mekong River. Geomorphology 85, 275–293, https://doi.org/10.1016/j.geomorph.2006.03.024 (2007).

11. 11.

Darby, S. E. et al. Fluvial sediment supply to a mega-delta reduced by shifting tropical-cyclone activity. Nature 539, 276–279, https://doi.org/10.1038/nature19809 (2016).

12. 12.

Triet, N. V. K. et al. Has dyke development in the Vietnamese Mekong Delta shifted flood hazard downstream? Hydrology and Earth System Sciences Discussions 21, 3991–4010, https://doi.org/10.5194/hess-21-3991-2017 (2017).

13. 13.

Brunier, G., Anthony, E. J., Goichot, M., Provansal, M. & Dussouillez, P. Recent morphological changes in the Mekong and Bassac river channels, Mekong delta: The marked impact of river-bed mining and implications for delta destabilisation. Geomorphology 224, 177–191, https://doi.org/10.1016/j.geomorph.2014.07.009 (2014).

14. 14.

Anthony, E. J. et al. Linking rapid erosion of the Mekong River delta to human activities. Sci. Rep. 5, 14745, https://doi.org/10.1038/srep14745 (2015).

15. 15.

Erban, L. E., Gorelick, S. M. & Zebker, H. A. Groundwater extraction, land subsidence, and sea-level rise in the Mekong Delta, Vietnam. Environmental Research Letters 9, 084010, https://doi.org/10.1088/1748-9326/9/8/084010 (2014).

16. 16.

Minderhoud, P. S. J. et al. Impacts of 25 years of groundwater extraction on subsidence in the Mekong delta, Vietnam. Environmental Research Letters 12, 064006, https://doi.org/10.1088/1748-9326/aa7146 (2017).

17. 17.

Teatini, P., Tosi, L. & Strozzi, T. Quantitative evidence that compaction of Holocene sediments drives the present land subsidence of the Po Delta, Italy. J. Geophys. Res. - Solid Earth 116, B08407, https://doi.org/10.1029/2010JB008122 (2011).

18. 18.

Meckel, T. A., ten Brink, U. S. & Williams, S. J. Current subsidence rates due to compaction of Holocene sediments in southern Louisiana. Geophysical Research Letters 33, 1–5, https://doi.org/10.1029/2006GL026300 (2006).

19. 19.

Törnqvist, T. E. et al. Mississippi Delta subsidence primarily caused by compaction of Holocene strata. Nature Geoscience 1, 173–176, https://doi.org/10.1038/ngeo129 (2008).

20. 20.

Jankowski, K. L., Törnqvist, T. E. & Fernandes, A. M. Vulnerability of Louisiana’s coastal wetlands to present-day rates of relative sea-level rise. Nature Communications 8, 14792, https://doi.org/10.1038/ncomms14792 (2017).

21. 21.

Meckel, T. A., Ten Brink, U. S. & Williams, S. J. Sediment compaction rates and subsidence in deltaic plains: numerical constraints and stratigraphic influences. Basin Research 19, 19–31, https://doi.org/10.1111/j.1365-2117.2006.00310.x (2007).

22. 22.

Lovelock, C. E. et al. The vulnerability of indo-pacific mangrove forests to sea-level rise. Nature 526, 559–563, https://doi.org/10.1038/nature15538 (2015).

23. 23.

Minderhoud, P. et al. The relation between land use and subsidence in the Vietnamese Mekong delta. Science of The Total Environment 634, 715–726, https://doi.org/10.1016/j.scitotenv.2018.03.372 (2018).

24. 24.

Zoccarato, C. & Teatini, P. Numerical simulations of Holocene salt-marsh dynamics under the hypothesis of large soil deformations. Advances in Water Resources 110, 107–119, https://doi.org/10.1016/j.advwatres.2017.10.006 (2017).

25. 25.

Zanello, F., Teatini, P., Putti, M. & Gambolati, G. Long term peatland subsidence: experimental study and modeling scenarios in the Venice coastland. J. Geophys. Res. - Earth Surface 116, F04002, https://doi.org/10.1029/2011JF002010 (2011).

26. 26.

Hooijer, A. et al. Subsidence and carbon loss in drained tropical peatlands. Biogeosciences 9, 1053–1071, https://doi.org/10.5194/bg-9-1053-2012 (2012).

27. 27.

Ta, T. K. O. et al. Sediment facies and Late Holocene progradation of the Mekong River Delta in Bentre Province, southern Vietnam: an example of evolution from a tide-dominated to a tide- and wave-dominated delta. Sedimentary Geology 152, 313–325, https://doi.org/10.1016/S0037-0738(02)00098-2 (2002).

28. 28.

Ta, T. K. O., Nguyen, V. L., Tateishi, M., KobayashiI, I. & Saito, Y. Holocene delta evolution and depositional models of the Mekong delta, southern Vietnam. SEPM, SEPM Special Publication 83, 453–466 (2005).

29. 29.

Giao, P. H., Thoang, T. T., Thuyen, L. X. & Vu, N. H. H. Geotechnical characterization of the subsoil profile underlying the land subsidence monitoring points in Southern Vietnam Delta. 9th Int. Symp. Lowl. Technol. 1, 429–436, https://doi.org/10.1017/CBO9781107415324.004 (2014).

30. 30.

Xue, Z., Liu, J. P., DeMaster, D., Van Nguyen, L. & Ta, T. K. O. Late Holocene Evolution of the Mekong Subaqueous Delta, Southern Vietnam. Mar. Geol. 269, 46–60, https://doi.org/10.1016/j.margeo.2009.12.005 (2010).

31. 31.

Liu, J. P. et al. Stratigraphic formation of the Mekong river delta and its recent shoreline changes. Oceanography 30 (2017). https://doi.org/10.5670/oceanog.2017.316.

32. 32.

Norwegian Geotechnical Institute (NGI). Land subsidence in Ca Mau province, Vietnam. Tech. Rep., 20120075-02-R (2017).

33. 33.

Hoang, T. M., van Lap, N., Oanh, T. T. K. & Jiro, T. The influence of delta formation mechanism on geotechnical property sequence of the late Pleistocene–Holocene sediments in the Mekong River Delta. Heliyon 2, https://doi.org/10.1016/j.heliyon.2016.e00165. (2016).

34. 34.

Allison, M. A., Nittrouer, C. A., Ogston, A. S., Mullarney, J. C. & Nguyen, T. T. Sedimentation and survival of the Mekong Delta: A case study of decreased sediment supply and accelerating rates of relative sea level rise. Oceanography 30, 98–109, https://doi.org/10.5670/oceanog.2017.318 (2017).

35. 35.

WLE–Greater Mekong (Water, Land, and Ecosystems–Greater Mekong). Dams in the Mekong River basin: commissioned, under construction and planned dams in april 2016. Tech. Rep. (2016).

36. 36.

Xue, Z., Liu, J. P. & Ge, Q. Changes in hydrology and sediment delivery of the Mekong River in the last 50 years: connection to damming, monsoon, and ENSO. Earth Surface Processes and Landforms 36, 296–308, https://doi.org/10.1002/esp.2036 (2011).

37. 37.

Hanebuth, T. J. J., Voris, H. K., Yokoyama, Y., Saito, Y. & Okuno, J. Formation and fate of sedimentary depocentres on Southeast Asia’s Sunda shelf over the past sea-level cycle and biogeographic implications. Earth-Sci. Rev. 104, 92–110, https://doi.org/10.1016/j.earscirev.2010.09.006 (2011).

38. 38.

van Asselen, S., Stouthamer, E. & van Asch, T. W. J. Effects of peat compaction on delta evolution: A review on processes, responses, measuring and modeling. Earth-Sci. Rev. 92, 35–51, https://doi.org/10.1016/j.earscirev.2008.11.001 (2009).

39. 39.

Koster, K., Erkens, G. & Zwanenburg, C. A new soil mechanics approach to quantify and predict land subsidence by peat compression. Geophysical Research Letters 43, 10792–10799, https://doi.org/10.1002/2016GL071116 (2016).

40. 40.

Nicholls, R. J. & Cazenave, A. Sea-level rise and its impact on coastal zones. Science 328, 1517–1520, https://doi.org/10.1126/science.1185782 (2010).

41. 41.

Tamura, T. et al. Origin and evolution of interdistributary delta plains; insights from Mekong River delta. Geology 40, 303–306, https://doi.org/10.1130/G32717.1. (2012).

42. 42.

Ta, K. T. O., Nguyen, V. L., Tateishi, M. & Kobayashi, I. Holocene delta evolution and sediment discharge of the Mekong. Quat. Sci. Rev. 21, 1807–1819 (2002).

43. 43.

Hung, N. N. et al. Sedimentation in the floodplains of the Mekong Delta, Vietnam Part II: deposition and erosion. Hydrol. Process. 28, 3145–3160, https://doi.org/10.1002/hyp.9855 (2014).

44. 44.

DWRPIS. Division of water resources planning and research in South Vietnam. Tech. Rep. (2017).

45. 45.

Moayed, R. Z., Kordnaeij, A. & Mola-Abasi, H. Compressibility indices of saturated clays by group method of data handling and genetic algorithms. Neural Comput. Appl. 28, 551–564, https://doi.org/10.1007/s00521-016-2390-9 (2016).

46. 46.

Higashi, T., Ohtsubo, M., Hiyama, H., Kanayama, M. & Akaboshi, K. A consideration on the compression index of Ariake clay (in Japanese). In 83th Congr. Kyushu Branch, Japanese Soc. Irrig. Drain. Reclam. Eng., 215–216 (2002).

47. 47.

Thoang, T. T. & Giao, P. H. Subsurface characterization and prediction of land subsidence for HCM City, Vietnam. Eng. Geol. 199, 107–124, https://doi.org/10.1016/j.enggeo.2015.10.009 (2015).

48. 48.

Clennell, M. B., Dewhurst, D. N., Brown, K. M. & Westbrook, G. K. Permeability anisotropy of consolidated clays. Muds Mudstones Phys. Fluid Flow Prop. 158, 79–96, https://doi.org/10.1144/GSL.SP.1999.158.01.07 (1999).

49. 49.

Gambolati, G. Equation for one-dimensional vertical flow of groundwater. 1. The rigorous theory. Water Resour. Res. 9, 1022–1028 (1973).

50. 50.

Gambolati, G. Equation for one-dimensional vertical flow of groundwater. 2. Validity range of the diffusion equation. Water Resour. Res. 9, 1385–1395 (1973).

51. 51.

Gambolati, G., Giunta, G. & Teatini, P. Numerical modeling of natural land subsidence over sedimentary basins undergoing large compaction. In Gambolati, G. (ed.) CENAS - Coastiline evolution of the Upper Adriatic Sea due to sea level rise and natural and anthropogenic land subsidence, no. 28 in Water Science and Technology Library, 77–102 (Klwer Acedemic Publ., 1998).

52. 52.

Anthony, E. J. Wave influence in the construction, shaping and destruction of river deltas: A review. Marine Geology 361, 53–78, https://doi.org/10.1016/j.margeo.2014.12.004 (2015).

## Acknowledgements

We thank the Division of Water Resources Planning and Investigation for the South (DWRPIS) of Vietnam and Division for Geological Mapping for the South (DGMS) of Vietnam for supplying lithological and geotechnical data. Kjell Karlsrud of the Norwegian Geotechnical Institude (NGI) is thanked for discussions on the subject and sharing geotechnical data from three subsidence monitoring sites in Ca Mau. Simon van Laarhoven (former MSc. student of PM) is thanked for building the digital geotechnical database of this data. CZ and PT are supported by the Flagship Project RITMARE - The Italian Research for the Sea, CNR-MIUR, National Research Program 2011–2013, “Linea SOLVE”. PM is supported by the Urbanizing Deltas of the World (UDW): “Rise and Fall” research project (grant: W 07.69.105) funded by the Dutch scientific organization (NWO-WOTRO), Deltares and the Dutch geological survey (TNO).

## Author information

Authors

### Contributions

C.Z. developed the model and conducted the experiments, P.M. built-up the dataset, P.M. and P.T. conceived the experiments. All authors analyzed the results and prepared the manuscript.

### Corresponding author

Correspondence to Claudia Zoccarato.

## Ethics declarations

### Competing Interests

The authors declare no competing interests.

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Zoccarato, C., Minderhoud, P.S.J. & Teatini, P. The role of sedimentation and natural compaction in a prograding delta: insights from the mega Mekong delta, Vietnam. Sci Rep 8, 11437 (2018). https://doi.org/10.1038/s41598-018-29734-7

• Accepted:

• Published:

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