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Although the key aim of soil classification systems for engineering purposes is to provide a standardised system for the identification and grouping of soils of similar composition and mechanical properties, there is no common consensus among different soil classification systems. Inconsistencies between different soil classification systems can lead to incorrect foundation and earthworks design and an increase in project time and cost. This paper presents a comparison of two chosen soil classification systems, the Unified Soil Classification System (USCS; ASTM D2487-17-reapproved 2025) and the Australian Soil Classification System (ASCS; AS1726: 2017), by way of extensive laboratory test results, the cone penetration test, and the critical state soil mechanics framework. A distinct difference in fine-grained soil classification has been identified between USCS and ASCS. It has been found that the threshold fines content (i.e. 35%), as adopted in ASCS to differentiate fine-grained soil from coarse-grained soil, is more appropriate compared with the threshold fines content (i.e. 50%) adopted in USCS. Furthermore, categorising soil plasticity into three groups (i.e. low, medium, and high) is assessed to be more practical in engineering practice. This review also highlights the need for a worldwide unified approach in defining organic soils due to their detrimental effect on soil mechanical behaviour.

Soil classification serves as a tool for geotechnical engineers to predict and characterise soil behaviours and to separate different soil types into groups of similar mechanical properties (Kovacevi′c and Juri′c-Ka′cuni′c, 2014; Park and Santamarina, 2017). Soil classification is a tool that requires categorising soils based on mineralogical, physical, or chemical properties. Proper classification and assessment of primary, secondary, and minor components, as well as plasticity of a soil, is very important in evaluating appropriate geotechnical parameters and assessing mechanical behaviours of a soil. However, a review of current international classification systems reveals inconsistencies, particularly where transitional boundaries between soil types do not align with actual performance and are thus unable to compare results or communicate with one another.

There are many soil classification systems available worldwide, such as the Unified Soil Classification System (USCS; ASTM D2487-17:R2025), the British Soil Classification System (BSI, 2020), the European Soil Classification System (ISO, 2017a,b), the German Soil Classification System (DIN, 2023), the Australian Soil Classification System (ASCS; AS 1726: 2017), the Japanese Soil Classification System (Japanese Geotechnical Society, 2009), and the Chinnese Soil Classification System (GB, 2007), Swiss soil classification (SNV, 1959), and so on. The common objective of all these classification systems is to provide the means to describe soils through a recognised grouping system so that the soils within a given category may be expected to exhibit similar engineering behaviour.

The USCS, which is an integral part of the US standard ASTM D2487-17:R25, is probably the most widely used soil classification system worldwide. The USCS categorises coarse-grained soils (more than 50% retained) from fine-grained soils (more than 50% passing), while the German classification system uses a 40% fines (particles less than 0.075 mm in diameter) fraction (DIN 18196:2023). On the contrary, other standards in the UK (BS5930:2015 + A1), France (CPCS, 1967), New Zealand (NZGS, 2005), AASHTO (2021), and Australia (AS, 2017) adopt 35% fines as the threshold fines content to differentiate fine-grained soil from coarse-grained soil.

The above comparison shows that the boundary defining the changes from coarse to fine-grained soil is different for different soil classification systems. USCS considers that the dominant (i.e. >50%) fraction governs classification, while AASHTO adopted threshold fines content (35%) from the geotechnical performance viewpoint of pavements and embankments. A behavioural approach has been adopted in AS1726 with an acknowledgement that there is no precise boundary (i.e. % fines content) defining the change in behaviour between coarse and fine-grained soils. In NZGS (2005), 35% fines content was considered appropriate as a threshold fines content on the basis that most soils with 35% fines are more likely to behave as fine soils rather than coarse soils. This brings an opportunity to use the critical state soil mechanics (CSSM) framework to evaluate threshold fines content and the effect of fines on the mechanical behaviours of coarse-grained soil.

Fine-grained soils consist of differing proportions of clay, silt, sand, and organic matter, typically containing a smaller proportion of coarser material. The initial classification of soils was primarily developed for agricultural applications, categorising soil groups based on the relative abundance of their constituent particles (Casagrande, 1948). Although attempts were made to adapt these systems for geotechnical applications, it became apparent by the mid-twentieth century that the engineering behaviour of fine-grained soils was not adequately correlated with grain size. Casagrande (1948) postulates that plasticity constitutes the most critical characteristic of fine-grained soils and thus should be given priority over grain size when developing a new soil classification system for fine-grained soil.

Understanding soil plasticity helps predict its behaviour under mechanical stress, changes in moisture, and environmental conditions (i.e. seasonal changes). For example, high-plasticity clays are more prone to shrinkage, swelling, and potential instability. This has an impact on the design and performance of earthworks and geostructures such as pavements and footings on expansive soils (Devkota et al., 2025). Hassan et al. (2023) investigated the effect of soil plasticity on the mechanical behaviour of geosynthetics. They concluded that an increase in the plasticity index (PI) of soil significantly reduces the performance of reinforcements due to the reduction in interface friction, lateral constraint, and interlocking effect. Recently, Moreno-Maroto et al. (2021) reviewed fine-grained soil classification systems based on plasticity. They pointed out that the plasticity chart proposed by Casagrande (1948) may lead to potential errors in soil classification interpretation. Kulhawy and Chen (2009) also highlighted the shortcomings of the USCS in identifying and classifying coarse-grained soils.

From a geotechnical perspective, the presence of organic matter in soils poses significant challenges for engineers due to its inherent properties, such as lower specific gravity, higher compressibility, larger creep, and low strength characteristics. Due to these properties, organic soil is often considered as ‘problem soils’. Pusch (1973) highlighted that even a minor percentage of organic content (OC), approximately 3%–4%, can substantially influence the geotechnical properties of soils. Numerous studies have investigated the impact of OC on various soil characteristics, including plasticity (Booth and Dahl, 1986; Malkawi et al., 1999; Varghese et al., 2021), consolidation parameters (Huat et al., 2005; Reddy and Latha, 2014; Santagata et al., 2008; Wong et al., 2009), and compaction and shear strength characteristics (Franklin et al., 1973; Romilus, 2004; Varghese et al., 2021; Wong et al., 2014). It has been recognised that the mechanical behaviour of organic soil is rather complex and poses significant design challenges to the practising engineers (Varghese et al., 2021). However, no clear consensus has been reached between different soil classification systems when classifying organic soils.

From the above discussion, it is clear that different soil classification systems are preliminary based on laboratory determination of particle-size characteristics, liquid limit (LL), PI, and OC. However, the basis of adopting criteria for classifying soils differs between standards. Also, it appears that consideration and analysis of threshold fines content based on the CSSM framework is absent in differentiating coarse- to fine-grained soil. Considering the above disparity of criteria makes it necessary to review different soil classification systems. From the author’s interest and to compare with the most commonly adopted against the recently updated soil classification systems, USCS and ASCS have been chosen to review their strengths and weaknesses. For this, a large number of laboratory as well as field investigation results have been used for analysis, with particular focus on how different percentages of soil fraction, soil plasticity, and OC affect compared soil classification systems.

The geotechnical investigation data analysed in this paper were acquired from the Phase 1 geotechnical investigation campaign for the proposed 17.4 km long mass rapid transit Line 5-South, Dhaka, Bangladesh. As per the physiographic map of Bangladesh, published by the Geological Survey of Bangladesh, the proposed route alignment is underlain by silty clay of Pleistocene Madhupur origin, Holocene sediments to the south, alluvial silt and clay, and marshy clay and peat to the east and west (DMTCL, 2022). Figure 1 shows geotechnical investigation locations along the proposed route.

Figure 1.
A satellite map displays various borehole and cone penetration testing locations marked by labels. The map illustrates the geographic layout within a city, highlighting test sites connected by a central route.Satellite imagery presents a detailed geographic layout indicating multiple locations for boreholes, designated by blue circles, and cone penetration tests, indicated by green and red circles. Labels for each site include identifiers such as B H 0 1, C P T 0 1, and B H 0 2, among others, arranged along a central pathway that flows horizontally across the map. The map provides context for understanding the distribution of these geological testing sites throughout the urban environment. A scale bar indicates distances up to four kilometres, while a north arrow is positioned in the corner for orientation. The sites are interconnected, allowing users to trace a route along which the boreholes and tests are positioned.

Geotechnical investigation location plan

Figure 1.
A satellite map displays various borehole and cone penetration testing locations marked by labels. The map illustrates the geographic layout within a city, highlighting test sites connected by a central route.Satellite imagery presents a detailed geographic layout indicating multiple locations for boreholes, designated by blue circles, and cone penetration tests, indicated by green and red circles. Labels for each site include identifiers such as B H 0 1, C P T 0 1, and B H 0 2, among others, arranged along a central pathway that flows horizontally across the map. The map provides context for understanding the distribution of these geological testing sites throughout the urban environment. A scale bar indicates distances up to four kilometres, while a north arrow is positioned in the corner for orientation. The sites are interconnected, allowing users to trace a route along which the boreholes and tests are positioned.

Geotechnical investigation location plan

Close modal

The geotechnical investigation campaign comprised the drilling and testing of a total of 34 boreholes to test termination depths between depths of 40.78 and 52.94 m and six cone penetrometer tests (CPTs) to test termination depths between 27.52 and 41.78 m. Among others, a total of 131 particle size distribution (PSD), 70 Atterberg limits (AL), and 40 OC tests had been conducted on the selected samples, all of which have been considered for analyses. All the laboratory tests were conducted following relevant ASTM standards.

In the following sections, relevant laboratory and field investigation results have been used to evaluate USCS and ASCS in classifying soils.

Total percentage of fines and clay fraction in the conducted samples has been plotted in Figure 2. Out of 131 samples (where sample number has been assigned as S1–S131), 68 samples had a fine content of more than 90%, that is, classified as clay or silt, whereas 10 samples contained fines less than 10%, that is, sand. In the same figure, two horizontal lines at 35% and 50% fines content were drawn to highlight the threshold fines content that differentiates coarse and fine-grained soils as per ASCS and USCS, respectively. It can be seen that five samples (S04, S31, S42, S67, and S87), shown by filled circles in Figure 2, had a fines content between 35% and 50%. Fine content of another four samples (S11, S13, S47, and S50), as shown by filled diamonds in the same figure, is within 2% of the adopted threshold fine content used in the AS soil classification system. In practice, considering factors such as soil profile above and below the tested sample, geological settings, sample collection method, sub-sampling variation, laboratory measurement inaccuracy, and so on, soils with close to borderline fines content (i.e. 35% for ASCS or 50% for USCS) are generally classified as fine-grained soils to be on the conservative side. Considering this, these nine samples (S04, S11, S13, S31, S42, S47, S50, S67, and S87) have been considered for further scrutiny following USCS and ASCS.

Figure 2.
A scatter plot displaying total fines, silt plus clay content, against sample numbers, featuring red markers for specific samples and threshold lines at thirty five percent and fifty percent for fine grained soil.The image presents a scatter plot illustrating the relationship between total fines, represented as a percentage of silt plus clay content, and sample numbers along the horizontal axis, which ranges from zero to one hundred forty. Points representing samples are plotted as black circles, with several red markers highlighting specific sample numbers, including S eleven, S thirteen, S thirty one, S forty two, S forty seven, S sixty seven, and S eighty seven. Two horizontal threshold lines indicate important values for fine grained soil, a red line at fifty percent and a blue dashed line at thirty five percent. The plot also features annotations, which explain the significance of each threshold concerning the A S T M and A S standards for fine grained soil.

Variation of the fines content of all the tested samples

Figure 2.
A scatter plot displaying total fines, silt plus clay content, against sample numbers, featuring red markers for specific samples and threshold lines at thirty five percent and fifty percent for fine grained soil.The image presents a scatter plot illustrating the relationship between total fines, represented as a percentage of silt plus clay content, and sample numbers along the horizontal axis, which ranges from zero to one hundred forty. Points representing samples are plotted as black circles, with several red markers highlighting specific sample numbers, including S eleven, S thirteen, S thirty one, S forty two, S forty seven, S sixty seven, and S eighty seven. Two horizontal threshold lines indicate important values for fine grained soil, a red line at fifty percent and a blue dashed line at thirty five percent. The plot also features annotations, which explain the significance of each threshold concerning the A S T M and A S standards for fine grained soil.

Variation of the fines content of all the tested samples

Close modal

Table 1 provides a summary of the selected nine samples along with the corresponding soil classification based on USCS and ASCS. Sample collection depths and PSD curves of these samples have been plotted in Figures 3 and 4, respectively. As shown in Figure 3, sample collection depths of the scrutinised samples varied between 3.5 and 36 m. The geological origin of these samples was Alluvium (S67), Madhupur Clay (S4, S11, S13, S31, S42, and S47) and Dupi Tila (S50 and S87). Details about the subsurface geology of Dhaka city are reported elsewhere (Alam, 1988; Brammer, 2012; Monsur, 1995). As per USCS, eight of nine samples examined are classified as silty fine SAND (SM) or silty fine-medium SAND (SM), whereas the remaining one sample is classified as clayey fine to medium SAND. On the contrary, ASCS classifies all the same samples as sandy SILT (ML), with clay. It is well known that the mechanical behaviours (i.e. shear strength, compressibility, liquefaction, settlement potential, etc.) of SILT can be transitional between those of fine sands and clay (Boulanger and Idriss, 2007; Hyde et al., 2006). This is because the collapse potential of a silty sand increases with the increase of silt content (Thevanayagam et al., 2002). Further increase in silt causes further reduction in intergranular contact between the coarse grains. At a certain threshold of silt/fines content, contact friction between silt/fines becomes significant and hence controls mechanical behaviours. Therefore, a unified soil classification could reduce uncertainties in predicting such transitional behaviour. The role of fines in controlling mechanical behaviours has been discussed further in a later section below.

Table 1.

Summary of the scrutinised soil samples for fines content

Sample IDBH no.Sample depth: m% Sand (0.6–0.075 mm)% Silt (0.002–0.075 mm)% Clay (<0.002 mm)% Total fines content (<0.075 mm): %Liquid limit, LL: %Plasticity index, PI: %D10: mmd50: mmUSCSASCS
S4BH0115.00–15.455435104528.410.00.0900.0110Clayey fine-medium SAND (SC)Sandy SILT (ML), with clay
S11BH0310.50–10.956627734NANA0.0850.0070Silty fine SAND (SM)Sandy SILT (ML), with clay
S13BH0325.50–25.95652963546.026.90.0950.0180Silty fine SAND (SM)Sandy SILT (ML), with clay
S31BH0712.00–12.456031940NANA0.0900.0110Silty fine SAND (SM)Sandy SILT (ML), with clay
S42BH0913.50–13.956329837NANA0.0780.0115Silty fine SAND (SM)Sandy SILT (ML), with clay
S47BH1110.50–10.956724933NANA0.0870.0072Silty fine SAND (SM)Sandy SILT (ML), with clay
S50BH1230.00–30.455924933NANA0.1600.0200Silty fine-medium SAND (SM)Sandy SILT (ML), with clay
S67BH213.50–4.5059311041NANA0.0900.0094Silty fine SAND (SM)Sandy SILT (ML), with clay
S87BH2735.00–36.005835742NANA0.0750.014Silty fine SAND (SM)Sandy SILT (ML), with clay
Figure 3.
Scatter plot showing sample depth below ground level against sample number, with annotations for fines content.The scatter plot illustrates the relationship between average sample depth below the ground level, measured in metres on the vertical axis, and sample number on the horizontal axis. The y axis ranges from zero to forty metres, while the x axis spans from zero to one hundred. Each point represents a different sample, labelled with alphanumeric identifiers such as S eleven, S forty two, and S fifty. The samples are distinguished by two categories based on fines content, diamonds indicate samples with fines content between thirty three and thirty five percent, while circles represent samples with fines content between thirty five and fifty percent. A legend at the top left identifies these categories. The arrangement of the data reveals varying depths related to sample numbers.

Specimen collection depths of the scrutinised samples

Figure 3.
Scatter plot showing sample depth below ground level against sample number, with annotations for fines content.The scatter plot illustrates the relationship between average sample depth below the ground level, measured in metres on the vertical axis, and sample number on the horizontal axis. The y axis ranges from zero to forty metres, while the x axis spans from zero to one hundred. Each point represents a different sample, labelled with alphanumeric identifiers such as S eleven, S forty two, and S fifty. The samples are distinguished by two categories based on fines content, diamonds indicate samples with fines content between thirty three and thirty five percent, while circles represent samples with fines content between thirty five and fifty percent. A legend at the top left identifies these categories. The arrangement of the data reveals varying depths related to sample numbers.

Specimen collection depths of the scrutinised samples

Close modal
Figure 4.
A graph displaying particle size distribution, showing different data series for various samples along the axes of particle size in millimetres and percentage finer.The image depicts a graph illustrating particle size distribution. The horizontal axis represents particle size measured in millimetres, ranging from zero point zero zero one to ten. The vertical axis shows the percentage finer, ranging from zero to one hundred percent. Different sample data series are represented by distinct markers, diamonds, triangles, circles, crosses, stars, and filled diamonds, each corresponding to a specific sample with varying size ranges. A legend on the top left indicates the sample identifiers and their respective size ranges. The data is presented as a series of curves, showing how the percentage finer changes with particle size, allowing comparison across the different samples.

Particle size distribution (PSD) of the scrutinised samples

Figure 4.
A graph displaying particle size distribution, showing different data series for various samples along the axes of particle size in millimetres and percentage finer.The image depicts a graph illustrating particle size distribution. The horizontal axis represents particle size measured in millimetres, ranging from zero point zero zero one to ten. The vertical axis shows the percentage finer, ranging from zero to one hundred percent. Different sample data series are represented by distinct markers, diamonds, triangles, circles, crosses, stars, and filled diamonds, each corresponding to a specific sample with varying size ranges. A legend on the top left indicates the sample identifiers and their respective size ranges. The data is presented as a series of curves, showing how the percentage finer changes with particle size, allowing comparison across the different samples.

Particle size distribution (PSD) of the scrutinised samples

Close modal

The CPT is widely used in practice for in situ characterisation of saturated or dry soils (i.e. soil profiling, strength, stiffness, and compressibility) for which interpretation methods are well established (Campanella et al., 1983; Lunne et al., 1997; Mayne, 2007; Robertson, 2009; Varghese et al., 2021; Zhang et al., 2002).

To form test pairs and compare BH and CPT test results, a reasonably close offset between test locations and the same geological formation has been considered. Out of nine scrutinised samples (i.e. S04, S11, S13, S31, S42, S47, S50, S67, and S87) and six available CPT tests, only one CPT test (CPT 2) was found to have met both criteria (offset reasonably close and had the same geological formation). Therefore, CPT 2, with a horizontal offset of about 110 m from BH07 (S31) and BH09 (S42), has been used to further scrutinise soil classification. Figure 5 shows the CPTu profile in terms of CPT parameters (cone resistance (qc), sleeve friction (fs), pore pressure (u), and friction ratio (Rf)). Figure 6 shows the same CPT data, but plotted in terms of normalised CPT parameters (normalised friction ratio (Rfn) and nomalised cone resistance (Qtn)) for the corresponding sample depths. The CPT data were normalised following the expressions proposed by Robertson (2009). An average total unit weight of 16 kN/m3 and piezometric profile (uo) were assumed. The plotted data in Robertson’s (2009) chart suggest that the soils are transitional in behaviour between either more silt mixtures (silt/clay-like) or sand mixtures, but not within or close to the sand zone. The interpreted soil type based on the CPT test result is consistent with ASCS (see Table 2) but deviates from USCS, where all the examined soil is classified as sand.

Figure 5.
A series of four graphs display cone resistance, sleeve friction, pore pressure, and friction ratio against depth, with detailed annotations marking specific values and depths.The image includes four vertical graphs arranged side by side, showing data on cone resistance, sleeve friction, pore pressure, and friction ratio relative to depth in metres. The first and second graphs represent cone resistance in megapascals, labelled as q subscript c one and q subscript c two, while the third graph shows sleeve friction in kilopascals, labelled as f subscript s. The fourth graph details pore pressure in kilopascals, labelled as u, and the last displays friction ratio as a percentage, labelled as R subscript f. Annotations indicate specific values and depths for cone resistance, such as R L equals six point eight metres at various depths. The depth is marked along the left side, with increments in metres descending from zero to forty. Data is plotted with a continuous line across the depth range, and annotations are integrated into the graphs, highlighting important values.

Cone penetration test (CPT) results of CTP02

Figure 5.
A series of four graphs display cone resistance, sleeve friction, pore pressure, and friction ratio against depth, with detailed annotations marking specific values and depths.The image includes four vertical graphs arranged side by side, showing data on cone resistance, sleeve friction, pore pressure, and friction ratio relative to depth in metres. The first and second graphs represent cone resistance in megapascals, labelled as q subscript c one and q subscript c two, while the third graph shows sleeve friction in kilopascals, labelled as f subscript s. The fourth graph details pore pressure in kilopascals, labelled as u, and the last displays friction ratio as a percentage, labelled as R subscript f. Annotations indicate specific values and depths for cone resistance, such as R L equals six point eight metres at various depths. The depth is marked along the left side, with increments in metres descending from zero to forty. Data is plotted with a continuous line across the depth range, and annotations are integrated into the graphs, highlighting important values.

Cone penetration test (CPT) results of CTP02

Close modal
Figure 6.
A graph shows C P T data interpretation with two sets of depth data points and various soil types identified, plotted against normalised cone resistance and friction ratio.The graph depicts Cone Penetration Test, C P T, data interpretation based on Robertson’s two thousand ten methodology. It features a logarithmic scale for both axes, with the horizontal axis labelled, normalised friction ratio R f, ranging from zero point one to ten, and the vertical axis labelled, normalised cone resistance Q n, spanning from one to one thousand. Two data sets are illustrated with distinct markers, a green triangle represents C P T zero two at depths from twelve point seven to thirteen point two metres, while a red circle denotes C P T zero two from twelve point two to twelve point seven metres. Several curved lines demarcate soil categories including dense sand to gravelly sand, clean sands to silty sands, and various silt mixtures. The graph effectively communicates the relationship between cone resistance and friction ratio across different soil types, reflecting soil classification at specified depths.

Interpretation of CTP02 results following the Robertson (2009) method

Figure 6.
A graph shows C P T data interpretation with two sets of depth data points and various soil types identified, plotted against normalised cone resistance and friction ratio.The graph depicts Cone Penetration Test, C P T, data interpretation based on Robertson’s two thousand ten methodology. It features a logarithmic scale for both axes, with the horizontal axis labelled, normalised friction ratio R f, ranging from zero point one to ten, and the vertical axis labelled, normalised cone resistance Q n, spanning from one to one thousand. Two data sets are illustrated with distinct markers, a green triangle represents C P T zero two at depths from twelve point seven to thirteen point two metres, while a red circle denotes C P T zero two from twelve point two to twelve point seven metres. Several curved lines demarcate soil categories including dense sand to gravelly sand, clean sands to silty sands, and various silt mixtures. The graph effectively communicates the relationship between cone resistance and friction ratio across different soil types, reflecting soil classification at specified depths.

Interpretation of CTP02 results following the Robertson (2009) method

Close modal
Table 2.

Summary of compared samples with CPT02

Test IDGround RL: mSample depth (RL): mDepth corresponding to CPT02: m (ground RL at CPT02 = 6.6 m)Offset from CPT02Groundwater table depth: mSoil classification
USCSASCSRobertson (2009) 
From lab resultsFrom CPT data interpretation
BH07 (S31)6.4312.0 to 12.5 (RL −5.6 to −6.1)12.2–12.7110 (NW)3.0Silty fine SAND (SM)Sandy SILT (ML), with claySilty clay to clayey or sandy silt/silty sand
BH09 (S42)7.4013.5 to 14.0 (RL −6.1 to −6.6)12.7–13.2110 (SE)4.5

Numerous studies have confirmed that the presence of fines affects the mechanical behaviour of soil considerably (Baki et al., 2012; Chu and Leong, 2002; Rahman et al., 2008; Thevanayagam, 1998; Yamamuro and Covert, 2001; Zlatovic and Ishihara, 1995). In particular, the location of the steady-state (SS) or critical state (CS) line (or curve) in the e–log(p′) space depends on fines content, where e is the void ratio and p′ is the mean effective stress. Initially, the SS strength at the same void ratio decreases, followed by an increase in shear strength with a further increase in fines content (Pitman et al., 1994; Rahman et al., 2008; Zlatovic and Ishihara, 1995). Similarly, cyclic resistance of a sand-fines matrix reverses in direction beyond a certain fines content (Rahman et al., 2008). Researchers also found that up to a certain percentage of fines (or clay content), the fines (or clay) only occupy the pore space of the host granular material and do not significantly affect the engineering behaviour of the matrix (Kenney, 1977; Kuerbis et al., 1988; Mitchell, 1976; Rahman et al., 2008; Thevanayagam, 1998; Xenaki and Athanasopoulos, 2003). There exists a threshold fines content, fthre, beyond which the fines become the matrix. Therefore, fthre defines the transition of a sand-fine matrix from a ‘fines in a coarse matrix’ to ‘coarse material in a matrix of fines’ as illustrated in Figure 7. In Figure 7(a), fine particles are occupying the pore spaces of coarse particles (i.e. sand grains). When the fines content, fc, increases beyond fthre, fines start to contribute to the force structure as shown in red particles in Figure 7(b). In the past, many researchers inferred or estimated fthre of the sand-fines matrix, which was found to vary between 25% and 50% but generally 30% (Hang et al., 2024; Naeini and Baziar, 2004; Papadopoulou and Tika, 2008; Rahman et al., 2008; Yang et al., 2006). However, based on the ratio of fine and sand particles, Rahman and Lo (2008, 2012) proposed an empirical equation (Equation 1) to calculate fthre, which was verified with nine published datasets.

1
Figure 7.
Diagram illustrating the interaction between coarse particles, fine particles, and voids in two different structures, highlighting their roles in force distribution.The diagram displays two configurations of particle interactions. In section a, coarse particles, represented in grey, interconnect to show contact points while fine particles, shown in blue, participate in the force structure. Void spaces are indicated, and it notes that fines have negligible effects on the force structure. In section b, a similar particle arrangement is presented, but with additional red particles indicating another type of fine particles impacting the arrangement. Arrows are used to direct attention to the role of coarse particles and the position of voids, reinforcing the concept of how different particle sizes affect structural integrity.

Schematic diagram showing particles arrangement of sand with fines (a) fc < fthre; and (b) fc > fthre

Figure 7.
Diagram illustrating the interaction between coarse particles, fine particles, and voids in two different structures, highlighting their roles in force distribution.The diagram displays two configurations of particle interactions. In section a, coarse particles, represented in grey, interconnect to show contact points while fine particles, shown in blue, participate in the force structure. Void spaces are indicated, and it notes that fines have negligible effects on the force structure. In section b, a similar particle arrangement is presented, but with additional red particles indicating another type of fine particles impacting the arrangement. Arrows are used to direct attention to the role of coarse particles and the position of voids, reinforcing the concept of how different particle sizes affect structural integrity.

Schematic diagram showing particles arrangement of sand with fines (a) fc < fthre; and (b) fc > fthre

Close modal

where diameter ratio, χ = D10/d50, d50 is the median size of fine and D10 is the 10% fractile of host sand. No additional input parameters are needed in Equation 1.

For the scrutinised samples, fthre has been calculated using Equation 1 to compare ASCS and USCS in relation to the expected mechanical behaviours of fine-grained soil under the CSSM framework. Calculated fthre are presented in Table 3 along with input parameters, which were obtained from PSD curves. It can be seen from Table 3 that the calculated fthre varied between 29% and 33%. Rahman and Sitharam (2020) pointed out that fthre can vary between ∼2% and ∼7% due to a narrow or ‘flat and wide’ zone on either side of fthre. Regardless, these calculated fthre values are close to the 35% threshold as adopted in ASCS but well below the USCS threshold (i.e. 50%). For the scrutinised samples, mechanical behaviours of a sand-fines matrix with fines (or clay) content greater than 33% are expected to be governed by finer particles. The above findings imply that ASCS aligns better with CSSM-based mechanical behaviour predictions.

Table 3.

Calculated threshold fines content

Sample IDBH No.D10: mmd50: mmThreshold fines content, fthre: % (Equation 1)
S4BH010.0900.011030
S11BH030.0850.007033
S13BH030.0950.018029
S31BH070.0900.011030
S42BH090.0780.011530
S47BH110.0870.007233
S50BH120.1600.020030
S67BH210.0900.009431
S87BH270.0750.014029

Plasticity of a soil can affect its settlement, strength, and volume change behaviour and is widely used to assess physical or engineering behaviour of soils (Firincioglu and Bilsel, 2023). The PI, calculated as the numerical difference between the LL and plastic limit (PL), reflects the range of water content within which the soil exhibits plastic behaviour. These parameters (PI, LL, and PL) are essential for classifying fine-grained soils and estimating their engineering properties, such as internal friction angle, compression index, and low-strain shear modulus (Ramsey and Tho, 2024).

Figure 8 shows plasticity plots of all the tested samples as per ASCS. It is to be noted that the plasticity chart used in USCS differentiates low to high plasticity at an LL of 50% with no medium plasticity. Out of 104 test results examined, about 54% of the tested soil had medium plasticity (i.e. LL between 35% and 50%) when classified in accordance with ASCS (Figure 8). This has a practical engineering consequence. In practice, for shallow foundation design, generally the more reactive the soil, the more rigid the footing needed to ensure acceptable performance, unless the foundation system is isolated from surface soils with the use of piles or other deep foundations. Also, for deep foundation design, the contribution to skin friction of fine-grained soil of different plasticity can vary. Soil plasticity also plays a vital role in determining the workability of soil in construction projects. Plasticity of soil also plays an important role in earthwork design, that is, appropriate selection of machinery, such as excavators, graders, and compactors; soil blending requirements; selection of appropriate stabilisation methods; erosion control requirements; and so on.

Figure 8.
A graph displaying the relationship between Liquid Limit and Plasticity Index, classifying soil types by plasticity levels with distinct markers for low, medium, and high plasticity.The graph presents a scatter plot illustrating the relationship between the liquid limit, w L, on the horizontal axis, ranging from zero to one hundred percent, and the plasticity index, I p, on the vertical axis, ranging from zero to sixty percent. Soil samples are plotted with markers indicating different classifications, diamonds for low plasticity, stars for medium plasticity, and circles for high plasticity. The shaded area in the upper right represents soil types with high plasticity, while dashed boundary lines demarcate ranges for different clay and silt classifications according to A S one seven two six two thousand seventeen. A vertical line at fifty percent of the liquid limit indicates a separation between certain soil properties. The graph includes annotations to aid in interpretation and understanding of the classifications.

Plasticity of all the tested samples

Figure 8.
A graph displaying the relationship between Liquid Limit and Plasticity Index, classifying soil types by plasticity levels with distinct markers for low, medium, and high plasticity.The graph presents a scatter plot illustrating the relationship between the liquid limit, w L, on the horizontal axis, ranging from zero to one hundred percent, and the plasticity index, I p, on the vertical axis, ranging from zero to sixty percent. Soil samples are plotted with markers indicating different classifications, diamonds for low plasticity, stars for medium plasticity, and circles for high plasticity. The shaded area in the upper right represents soil types with high plasticity, while dashed boundary lines demarcate ranges for different clay and silt classifications according to A S one seven two six two thousand seventeen. A vertical line at fifty percent of the liquid limit indicates a separation between certain soil properties. The graph includes annotations to aid in interpretation and understanding of the classifications.

Plasticity of all the tested samples

Close modal

The organic matter could be formed by the decomposition of plants, tree roots/wood, and waste. The presence of organic matter at a high percentage is undesirable in soils, as it can have a significant effect on their geotechnical properties due to its detrimental properties, such as high compressibility, low shear strength, low bulk density, high moisture content, and long-term settlement. These properties can lead to excessive settlement, bearing capacity failure, or instability, especially under loading from structures, roads, or embankments. Therefore, characterising organic soil is essential to ensure safe, reliable, and cost-effective engineering design. Also. it guides decisions around foundation systems, settlement control, and risk management. The details of the scrutinised soil samples for OC are presented in Table 4.

Table 4.

Details of scrutinised soil samples for organic content

Sample IDBH no.Sample depth: m% Sand (0.6–0.075 mm)% Silt (0.002–0.075 mm)% Clay (<0.002 mm)Liquid limit, LL: %Plasticity index, PI: %Organic content: %Soil classification
USCSASCS
S1BH013.5–4.50712959.831.411.4Fat CLAY, CHOrganic clayey SILT (OH)
S18BH049.0–9.5375310NANA2.5Sandy lean CLAY, CLOrganic sandy SILT, with clay
S25BH069.5–10.55742193.556.816.1Organic CLAY, OHOrganic clayey SILT (OH), trace sand
S30BH077.5–8.00802035.714.12.3Lean CLAY, CLOrganic clayey SILT (OI)
S34BH083.5–4.51742556.034.92.6Fat CLAY, CHOrganic clayey SILT (OH)
S46BH115.0–6.012761237.322.62.1Lean CLAY with Sand, CLOrganic clayey SILT (OI), trace sand
S51BH132.0–3.05742131.411.32.0Lean CLAY, CLOrganic clayey SILT (OL), trace sand
S53BH143.5–4.50752573.540.73.3Fat CLAY, CHOrganic clayey SILT (OH)
S58BH166.5–7.51782183.450.66.7Fat CLAY trace Organic compound, CHOrganic clayey SILT (OH)
S61BH196.0–6.5196812NANA15.1Organic SILT with Sand, OHOrganic clayey SILT, with sand
S64BH209.5–10.53762147.625.33.5Lean CLAY trace Organic Compound, CLOrganic clayey SILT (OI), trace sand
S69BH2120.0–21.00742551.128.75.0Fat CLAY, CHOrganic clayey SILT (OH)
S78BH268.0–9.05761957.434.93.9Fat CLAY, CHOrganic clayey SILT (OH), trace sand
S81BH279.5–10.57761741.019.22.1Lean Clay trace SAND, CLOrganic clayey SILT (OI), trace sand
S90BH289.5–10.52702989.033.410.6Organic SILT, OHOrganic clayey SILT (OH)
S91BH2815.5–16.59751638.010.42.6SILT trace Sand, MLOrganic clayey SILT (OL), trace sand
S98BH3014.0–15.04791843.017.32.0Lean CLAY, CLOrganic clayey SILT (OI), trace sand
S106BH333.5–4.51811852.832.52.4Fat CLAY, CHOrganic clayey SILT (OH)
S108BH3311.0–12.06771740.519.43.6Lean CLAY trace Sand, CLOrganic clayey SILT (OI), trace sand
S109BH3317.0–18.01811851.626.94.4Fat CLAY, CHOrganic clayey SILT (OH)
S113BH345.0–6.02722579.648.48.9Organic CLAY, OHOrganic clayey SILT (OH)
S118BH358.0–9.08771558.838.15.5Fat CLAY trace Sand, CHOrganic clayey SILT (OH), trace sand
S120BH363.5–4.51792045.819.03.1Lean CLAY, CLOrganic clayey SILT (OI)
S126BH383.5–4.53772055.030.711.4Fat CLAY trace Organic Compound, CHOrganic clayey SILT (OH), trace sand

Both ASCS and USCS consider organic soils as a subgroup of fine-grained soils. However, USCS for organic soil is based on the ratio of the oven-drying to the pre-oven-drying LL (i.e. classified as organic silt/clay if the ratio is less than 75%), whereas soils with OC more than 2% are termed as organic soil in ASCS.

Table 3 provides a summary of the tested samples for OC, whereas Figure 9 shows the variation of the OC for the tested 33 samples for this geotechnical investigation package. Among 33 samples, 22 samples were tested for LL and PI and plotted in Figure 8 (green circles). Out of 33 samples considered, 4 samples (12%) would have been classified as organic soil based on USCS, whereas 24 samples (73%) would have been classified as organic soil as per ASCS.

Figure 9.
Scatter plot showing organic content percentage against sample numbers, with distinct markers for two thresholds of organic content.A scatter plot presents data on organic content percentage, with the vertical axis labelled, organic content percent, ranging from zero to sixteen percent, and the horizontal axis labelled, sample number, ranging from zero to one hundred forty. Data points represent samples, with black circles indicating organic content below two percent and red circles showing organic content above two percent. A horizontal red line at the two percent mark serves as a threshold for organic soils, according to the standard Australian A S one seven two six two thousand seventeen. An arrow indicates the threshold line, while several annotations highlight the varying organic content percentages across samples, with numerous points clustering near the two percent line.

Variation of organic content of all the tested samples (33 samples)

Figure 9.
Scatter plot showing organic content percentage against sample numbers, with distinct markers for two thresholds of organic content.A scatter plot presents data on organic content percentage, with the vertical axis labelled, organic content percent, ranging from zero to sixteen percent, and the horizontal axis labelled, sample number, ranging from zero to one hundred forty. Data points represent samples, with black circles indicating organic content below two percent and red circles showing organic content above two percent. A horizontal red line at the two percent mark serves as a threshold for organic soils, according to the standard Australian A S one seven two six two thousand seventeen. An arrow indicates the threshold line, while several annotations highlight the varying organic content percentages across samples, with numerous points clustering near the two percent line.

Variation of organic content of all the tested samples (33 samples)

Close modal

The variation of the OC with the LL and water content has been plotted in Figures 10 and 11, respectively. Both figures show an increase in the LL and water content with the increase in the OC. For the higher value of the OC (16.1%), the LL reaches 93.5% but had slightly less (8%) water content than the maximum water content (78%) attained in Figure 11. While a trend line with some error band can be established with the LL against OC data points in Figure 10, no such trendline can be established for water content data points due to scatter in data points mainly beyond about 8% OC (Figure 11). Among others, sampling techniques, storage, and transportation of samples may affect field moisture content determination.

Figure 10.
A scatter plot showing the relationship between organic content percentage and liquid limit percentage in soil. Different symbols indicate varying organic content levels.The image presents a scatter plot with the x axis labelled, organic content percent, and ranging from zero to twenty percent, while the y axis is labelled, liquid limit percent, and spans from twenty to one hundred percent. Data points are represented by black circles for organic content below two percent, red circles for organic content above two percent, and red circles with a distinct symbol indicating organic soil as per A S T M classification. A blue curve illustrates the trend in the data. The plot displays a concentration of points primarily in the lower left quadrant, with a gradual increase in liquid limit as organic content rises. Annotations within the plot provide additional information regarding classifications of organic content.

Variation of organic content against the liquid limit of the available 25 samples

Figure 10.
A scatter plot showing the relationship between organic content percentage and liquid limit percentage in soil. Different symbols indicate varying organic content levels.The image presents a scatter plot with the x axis labelled, organic content percent, and ranging from zero to twenty percent, while the y axis is labelled, liquid limit percent, and spans from twenty to one hundred percent. Data points are represented by black circles for organic content below two percent, red circles for organic content above two percent, and red circles with a distinct symbol indicating organic soil as per A S T M classification. A blue curve illustrates the trend in the data. The plot displays a concentration of points primarily in the lower left quadrant, with a gradual increase in liquid limit as organic content rises. Annotations within the plot provide additional information regarding classifications of organic content.

Variation of organic content against the liquid limit of the available 25 samples

Close modal
Figure 11.
Scatter plot displaying the relationship between organic content percentage and water content percentage with data points in black and red, indicating different classifications.The scatter plot illustrates the correlation between organic content percentage on the horizontal axis and water content percentage on the vertical axis. The x axis ranges from zero to twenty percent for organic content, while the y axis spans from zero to one hundred percent for water content. Data points are classified based on organic content levels, black circles represent organic content less than two percent, whereas red circles indicate organic content greater than two percent. Additionally, larger red circles with a cross denote samples classified as organic soil according to A S T M standards. Legends explain the various classifications of organic content within the plot. The distribution of data points primarily shows varying water content levels related to the differing organic content measured.

Variation of organic content against water content of the available 25 samples

Figure 11.
Scatter plot displaying the relationship between organic content percentage and water content percentage with data points in black and red, indicating different classifications.The scatter plot illustrates the correlation between organic content percentage on the horizontal axis and water content percentage on the vertical axis. The x axis ranges from zero to twenty percent for organic content, while the y axis spans from zero to one hundred percent for water content. Data points are classified based on organic content levels, black circles represent organic content less than two percent, whereas red circles indicate organic content greater than two percent. Additionally, larger red circles with a cross denote samples classified as organic soil according to A S T M standards. Legends explain the various classifications of organic content within the plot. The distribution of data points primarily shows varying water content levels related to the differing organic content measured.

Variation of organic content against water content of the available 25 samples

Close modal

For geotechnical engineering purposes, soils categorised into the same groups or subgroups should possess similar properties and exhibit similar mechanical behaviour. Soil classification reflective of expected mechanical behaviour is vital for assessing subsurface variability and geohazards. Classification systems influence how layer boundaries are drawn, soil units are modelled, and geotechnical zones are defined. Inconsistent classification can obscure critical transitions. For example, a ‘clayey sand’ classified in USCS may be described as sandy silt in ASCS, introducing subjectivity in the assessment of compressibility, strength, and drainage behaviour. Such inconsistencies can affect the selection of design parameters for foundation bearing capacity, settlement estimation, and slope stability. This variability can result in inconsistent interpretations of the same soil across projects or jurisdictions and can compromise safety in design. Similarly, the plasticity of soil plays an important role in earthworks specification. For example, the Transport of NSW Specification Guide to QA Specification for Earthworks (TfNSW, 2020) specifies different PI limits for materials to be used for ‘select fill’ or ‘general fill’ material. Therefore, the volume of materials required to blend with the site own materials can vary significantly depending on the plasticity of site own materials and the intended use. Also, as per Australian Standards – Residential Slabs and Footings (AS, 2011), plasticity of soil is a key for classifying a site based on estimated characteristics of soil movement due to seasonal moisture change, that is, shrinkage during drying or swelling during wetting. The expected characteristic soil movement is related to soil reactivity. Reactive soils, such as high-plasticity clays, can exert significant stress on foundations, leading to cracking, tilting, or other structural problems.

Among others, the engineering behaviour of a soil is also dependent on its OC. As an engineering control measure to manage the settlement of a site with an organic soil layer, surcharging is a commonly adopted technique for infrastructure projects. For this, the surcharge load and duration of the surcharge are related to the expected primary and secondary settlement that is expected over the design life. This highlights the need for identification and classification of organic soil with an unified criteria, which is reflective of its actual mechanical behaviour.

Furthermore, miscommunication may arise between designers and contractors when interpreting classification terms in tender documents or material test reports. Without a standard conversion protocol, differences can lead to rejection of suitable materials, incorrect equipment mobilisation, or contract disputes.

Soil classification provides a common framework to describe and group soils with similar properties and expected mechanical behaviours. This helps practising engineers to provide safe, sustainable, and cost-effective foundation or earthwork design solutions. However, despite their common purpose, there is no universal consensus among existing fine-grain soil classification systems. Generally, differences persists in adopted threshold fines content, descriptive criteria, and behavioural assumptions.

A large laboratory test data set and relevant CPT results have been analysed to review and compare fine-grained soil classifications using USCS (ASTM, 2017) and ASCS (AS, 2017). The influence of three key parameters, that is, threshold fines content, soil plasticity, and OC, on fine-grained soil classification was studied. In addition, the CSSM framework has been used to evaluate threshold fines content, which differentiates fine-grained soil from coarse-grained soil. Based on the analyses, the following conclusions and observations were drawn:

  • A distinct difference in fine-grained soil classification was observed between the two soil classification systems compared. While comparing nine samples classified as silty/clayey SAND as per USCS, all those samples are classified as sandy SILT as per ASCS. This highlights that significantly different mechanical behaviours are expected for the same soil depending on the chosen soil classification system, USCS or ASCS. This could lead to an unsustainable design solution unless the assigned design parameters for the subject soil unit are validated by other means (i.e. CPT, laboratory tests, etc.).

  • The threshold fines content (i.e. 35%), which differentiates fine-grained soil from coarse-grained soil in ASCS, is found to be more appropriate, as supported by CPT data as well as the CSSM framework.

  • For the compared soil classification systems, it has been found that different boundaries, descriptive criteria, and identification methods have been adopted in classifying soil plasticity and organic soils. This could lead to potential safety and serviceability consequences in earthworks, foundation, or pavement design.

  • While soil classification is foundational to geotechnical engineering, the divergence between different soil classification systems may pose significant implications on interpretation, design, and project delivery, particularly when multiple international contractors or consultants are involved and limited laboratory testing is available. As such, execution of a comprehensive laboratory testing programme is beneficial to confirm engineering properties for each identified soil unit rather than relying on typical soil parameters.

  • In the absence of comprehensive laboratory test data, it is recommended that a sensitivity analysis be carried out to evaluate how different soil classification systems affect geotechnical design (i.e. foundation or earthwork design). For example, sensitivity checking of pile length design considering the soil layer as sandy silt (and associated design parameters) instead of silty sand.

Further validation of the presented findings herein will require more comparison between the CPT and BH test pair, additional case histories from different geological formations, and the collection of additional experimental data on fine-grained soils. Nonetheless, it is hoped that the above findings will prove useful to engineering practice and provide an opportunity to develop a universal framework in the future to remove existing inconsistencies in fine-grained soil classifications.

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