Estimation of reference bulk density from soil particle size distribution and soil organic matter content
Introduction
Crop growth is affected by soil structure and compactness. With respect to crop growth, there is an optimum soil compactness above or below which crop growth and yield are reduced (e.g. Håkansson, 1990). While yield loss due to over-compaction is largely a result of high penetration resistance for roots and poor soil aeration, yield losses due to too loose soil are less well understood but are generally associated with reduced transport of water and nutrients to the roots under unsaturated conditions. The optimum soil compactness depends on internal soil attributes such as soil texture and soil organic matter content, but may be different for different crops and climatic conditions (Håkansson and Lipiec, 2000, Håkansson, 2005, Suzuki et al., 2006, Reichert et al., 2009).
Bulk density (or porosity) is the parameter usually used to describe soil compactness. If soil is compacted, bulk density increases and porosity decreases correspondingly. However, absolute values of bulk density are unsuitable for characterising soil compactness with respect to crop yield when comparing different soils, as optimum and critical limits of bulk density for crop growth strongly depend upon soil type, i.e. different values of bulk density are optimum for different soils, as demonstrated by Reichert et al. (2009). A bulk density that indicates a compact state in one soil may imply a loose state in another (Håkansson, 1990).
Therefore, relative bulk density has been suggested to describe the compactness of soil. The relative bulk density is generally obtained as the ratio of actual field bulk density (i.e. bulk density measured either directly in the field or on undisturbed soil samples collected in the field) to a reference bulk density. As bulk density changes with soil moisture for swelling–shrinking soils, field bulk density should be measured at a defined soil moisture content (e.g. at field capacity) in order to obtain reliable and comparable relative bulk density values. Different authors have used different ways of obtaining the reference bulk density. Pidgeon and Soane, 1977, Carter, 1990, da Silva et al., 1994 obtained reference bulk density from the Proctor test at a given amount of impact energy. Other researchers define the reference bulk density as the bulk density obtained by uniaxial compression at 200 kPa (Håkansson, 1990, Lipiec et al., 1991, da Silva et al., 1997) and 1600 kPa (Suzuki et al., 2006). These tests all result in relatively high bulk densities. However, stresses higher than those used for obtaining the reference bulk density may occur due to agricultural field traffic and consequently field bulk densities higher than the reference bulk density can be observed. Recently, Reichert et al. (2009) compared different methods for obtaining reference bulk density and evaluated the usefulness of the relative bulk density approach.
Håkansson (1990) related crop yield to the degree of compactness, DC (%), which is given as:where ρ is the field bulk density, and ρref is the reference bulk density determined by a drained, uniaxial compression test using wet soil samples loosely filled in an oedometer and loaded with a vertical stress of 200 kPa until drainage ceases. In a series of 100 field experiments with spring barley (Hordeum vulgare L.), Håkansson (1990) found that on all types of mineral soils, the highest crop yield was obtained at the same DC (Eq. (1)), viz. at a DC value of 87. This is further supported by other studies relating crop yield to soil compactness (Lipiec et al., 1991, Riley, 1998, Braunack et al., 2006). The main reason, as shown by Håkansson and Lipiec (2000), is that critical limits of soil aeration as well as of soil mechanical resistance to root growth are similarly related to DC in all soils. However, the optimum value for DC may slightly differ between crops as shown by Håkansson, 2005, Reichert et al., 2009.
Analytical soil compaction models used in agricultural research (e.g. O'Sullivan et al., 1999, van den Akker, 2004, Keller et al., 2007) incorporate calculation of (changes in) bulk density due to mechanical stresses (i.e. due to loading with agricultural machinery), but do not include effects on crop yield. Models for estimation of the effects of soil compaction on crop yield are purely empirical (e.g. Arvidsson and Håkansson, 1991). One reason for not including crop response in analytical models is that, as mentioned above, absolute values of bulk density are not useful for characterisation of crop growth. A relative bulk density parameter such as DC (Eq. (1)) would facilitate the inclusion of crop response in analytical models.
In order to calculate DC, ρ and ρref have to be known (Eq. (1)). While ρ is readily measured or easily calculated by means of soil compaction models, determination of ρref is labour-intensive. Therefore, it is relevant to investigate relationships between ρref and readily-quantifiable soil characteristics for potential development of prediction equations.
The objective of this paper was to investigate relationships between the reference bulk density as defined by Håkansson (1990) and the particle size distribution and organic matter content based on extensive data from field experiments conducted in Sweden.
Section snippets
Soils
Data on reference bulk density (ρref), particle density, particle size distribution (PSD) and soil organic matter content were collected from 171 experimental sites in different counties of Sweden, from Malmöhus (55°N) in the south to Västerbotten (65°N) in the north (Fig. 1). Data from two Polish soils (Lipiec et al., 1991) and three Finnish soils (Pietola, 1995) were also included in the analysis. The combined data (Table 1) were used to develop relationships between ρref and PSD, including
Effect of soil texture on reference bulk density
The reference bulk density was affected by clay (Fig. 3a) and sand content (Fig. 3b), but only slightly negatively correlated with silt content (Fig. 3c). The curves in Fig. 3a, b and c depict the regression equations:and
The maximum value of ρref is found from Eq. (5) at a clay content of 29.3%. Several authors (e.g. Larson et al., 1980,
Conclusions
We found that the reference bulk density, ρref, can be satisfactorily estimated from the soil particle size distribution and soil organic matter content. We also found that reference bulk density is largely controlled by organic matter content. Correlations were found between reference bulk density and the clay and sand content. The maximum reference bulk density was found at a clay content of 29.3%, which corresponds to a value at which the mechanical behaviour of soil is known to change.
We
Acknowledgments
This work was financed by the Swedish Farmers’ Foundation for Agricultural Research (SLF), which is gratefully acknowledged. The anonymous reviewers of this paper are thanked for their helpful suggestions.
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