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Print version ISSN 0103-9016
Sci. agric. (Piracicaba, Braz.) vol.67 no.4 Piracicaba Aug. 2010
Related to: Sci. agric. (Piracicaba, Braz.) 2010;67(4): 0
Related to: Sci. agric. (Piracicaba, Braz.) 2010;67(4): 0
SOILS AND PLANT NUTRITION
Intervalo hídrico ótimo e qualidade física do solo em sistemas de manejo nas entrelinhas de citros
Jonez FidalskiI,*; Cássio Antonio TormenaII; Álvaro Pires da SilvaIII
IIAPAR - Área de Solos, C.P. 564 - 87701-970 - Paranavaí, PR - Brasil
IIUEM - Depto. de Agronomia, Av. Colombo, 5790 - 87090-000 - Maringá, PR - Brasil
IIIUSP/ESALQ - Depto. de Ciência do Solo, C.P. 09 - 13418-900 - Piracicaba, SP - Brasil
Machinery-based farming operations used for perennial fruit crops often damage soils, particularly if the soil is wet and prone to compaction. We hypothesized that perennial vegetation growing in the interrows of orange orchards can mitigate the soil physical degradation from machinery traffic. The objective of this study was to investigate the effects of different groundcover management systems on the soil physical quality indicators including the least limiting water range (LLWR). An experiment was started in 1993 in a Typic Paleudult to evaluate three groundcover management systems: Bahia grass (Paspalum notatum) with mowing, perennial peanut (Arachis pintoi), and natural regrowth in which weeds were controlled by herbicide. The experimental design was randomized complete block with three replications. In May 2003, 216 undisturbed soil samples were collected at 0-0.15-m depths under and between wheel tracks in the orchard interrows. The soil bulk density, soil organic carbon content, resistance to penetration, soil water retention curve and soil resistance to penetration curve were determined in order to estimate the LLWR. The higher LLWR under wheel tracks in Bahia grass compared to perennial peanut or natural regrowth suggest that a better soil physical quality was achieved with Bahia grass.
Key words: organic carbon, soil compaction, bulk density, resistance to penetration, available water
Operações motomecanizadas utilizadas no manejo das entrelinhas dos pomares de frutas com freqüência causam a degradação física do solo, especialmente quando realizadas com o solo úmido e suscetível à compactação. A hipótese desse estudo é que a manutenção da vegetação permanente nas entrelinhas do pomar pode mitigar a degradação física do solo causada pelo tráfego de máquinas. O objetivo desse estudo é verificar o efeito de diferentes sistemas de manejo da cobertura permanente das entrelinhas sobre o intervalo hídrico ótimo (IHO) e a qualidade física do solo. Um experimento foi iniciado em 1993 num Argissolo Vermelho distrófico latossólico para avaliar diferentes sistemas de cobertura permanente do solo: gramínea "grama matogrosso" ou "grama batatais" (Paspalum notatum) com roçadas, amendoim forrageiro (Arachis pintoi) e vegetação espontânea manejada com herbicida. Em maio de 2003, foram coletadas 216 amostras de solo não deformadas na camada de 0-0,15 m de profundidade sob as posições de amostragem rodado e entrerrodado das máquinas nas entrelinhas do pomar. A densidade do solo, teor de carbono orgânico, resistência do solo à penetração, curva de retenção de água e curva de resistência do solo à penetração foram determinadas para estimar o IHO. A manutenção da cobertura do solo nas entrelinhas do pomar reduziu a compactação do solo e a utilização da gramínea proporcionou melhor qualidade física do solo no pomar de laranja.
Palavras-chave: carbono orgânico, compactação do solo, densidade do solo, resistência do solo à penetração, água disponível
Perennial vegetation, mulching, cultivation (disking), and herbicides for weed control are used as soil management practices in interrows of orchards. However, any vegetation growing in plant rows and interrows of orchards is a strong competitor for water, nutrients, and yield (Wright et al., 2003; Belding et al., 2004). Previous studies have indicated that mowing the vegetation in the interrow and applying herbicides to the plant row are the best practices for sustainable soil management in orchards (Hogue and Neilsen, 1987; Lipecki and Berbeć, 1997).
In Brazil, orange orchards have up to 15 passes yearly by machinery to carry out cropping practices and the traffic may occur when the soils are wet and prone to compaction. Soil compaction caused by machinery traffic is a major obstacle in orchards because it reduces root growth and fruit yield (Abercrombie and Plessis, 1995). Quantifying soil physical degradation associated with compaction and their impact in the plant growth is a complex task, which may be achieved using the least limiting water range (LLWR) concept. The LLWR is a multifactor index used for describing the soil physical quality to crop production (Lapen et al., 2004; Siegel-Issem et al., 2005; Tormena et al., 2007). As a single index of soil physical quality, LLWR incorporates most of the critical measurable sources of stress that the soil imposes on crop growth. For example, in compacted soils, LLWR is reduced (Silva et al., 1994; Betz et al., 1998; Tormena et al., 1999; Araújo et al., 2004; Cavalieri et al., 2006; Leão et al., 2006).
LLWR has not yet been quantified for soils of orchards, especially under and between wheel tracks in orchards managed with different groundcover systems. We hypothesized that perennial vegetation in the interrows of an orchard can mitigate the soil compaction from machinery traffic increasing the soil physical quality. Thus, the objective of this study was to investigate the effects of different groundcover management systems on the soil physical quality indicators including the LLWR.
Material and Methods
An experiment was established under Cfa climate type (IAPAR, 2000) with a non-uniform rainfall distribution of 1,500 mm year-1 in northwestern Paraná (22º51' to 23º4' S; 52º12' to 52º27' W, altitude of 480 m), Brazil. The experimental area, previously cultivated with Brachiaria humidicola (Rendle) Schweickt, has a slope of 4 cm m-1 perpendicular to the plant rows. The soil under investigation is classified as a Typic Paleudult or Argissolo Vermelho distrófico latossólico, according to Brazilian soil classification. The particle sizes of their main horizons are in Table 1.
The experiment under non-irrigated conditions underwent three treatments using a randomized complete block design with three replications. Each field plot had three plant rows with five orange trees per row and 15 trees by experimental plot (Figure 1). The "Pêra" orange (Citrus sinsensis L. Osb.) was budded on "Rangpur" lime (Citrus limonia Osb.) to establish the orchard in the growing season of 1993; at planting, the trees were spaced 7 × 4 m apart (Figure 1). The three groundcover management systems in interrows of orange plants were: i) Bahia grass (Paspalum notatum Flügge) with mechanical mowing; ii) leguminous - perennial peanut (Arachis pintoi Krap. and Greg.); and iii) natural regrowth with weeding control performed with herbicide glyphosate. Disease treatment, pest control, lime, and mineral fertilization were performed equally in all three treatments (Auler et al., 2008). Visual evaluation at the field has shown a homogeneous soil cover under Bahia grass on the wheel and between wheel tracks while under natural regrowth and leguminous the soil cover was reduced on wheel tracks. Disease and pest control, mowing, liming and harvest have been done using a tractor with mean weight of 3,300 kg.
In May 2003, soil sampling was carried out on two adjacent interrows representative of most of plantation. Soil samples were taken under wheel tracks at 2.5 and 4.2 m distance from the tree trunks, and between wheel tracks at 3.2 and 3.5 m (Figure 1). A total of two hundred and sixteen undisturbed soil samples were collected at depths of 0 to 0.15 m, using cores (5-cm diameter by 5-cm length).
Soil water retention curve was measured at matric potentials (Ψ) of -10, -20, -40, -60, and -80 hPa on a tension table (Romano et al., 2002), and -100, -300, -500, -700, -1,000, -4,000, and -15,000 hPa in pressure plates (Dane and Hopmans, 2002) using eighteen samples for each Ψ (three treatments, three replicates, and two sampling positions) (Silva et al., 1994). Cores have been put on suction tables or pressure plates and after equilibration at selected Ψ, the weight was recorded and the soil resistance to penetration (SR) was determined on each core (Tormena et al., 1999); them, they were oven dried at 105ºC until constant weight to determine the soil water content (θ) and soil bulk density (Db). The Db's values were determined immediately (Grossman and Reinsch, 2002). After determining θ and Db, the soil from each core was homogenized and sieved with a 2 mm mesh screen for determination of the soil organic carbon content (SOC) (Walkley and Black method) and the particle size distribution (hydrometer method).
The soil water retention curve was fitted to the equation proposed by van Genuchten (1980):
θ is the volumetric water content (m3 m-3), Ψ is the matric potential (hPa), θ r is the residual water content (m3 m-3), θ s is the soil water content at saturation, α (hPa-1) is the reciprocal of Ψ, and n and m are constants. The parameter m was assumed to be related as [m = (1 - 1/ n). The θ s, the soil water content at saturation or total pore volume (m3 m-3), was estimated as:
Dp is soil particle density (Mg m-3), which was measured by using the ethyl alcohol method (Embrapa, 1997) in each sample and the mean (2.62 Mg m-3) was used in Eq. 2.
The data for SR (MPa) were regressed against Dp (Mg m-3) and θ (m3 m-3) using following model (Busscher, 1990):
in which c, d, and e are constants.
The significant effects of Db, sampling positions, SOC and treatments (Bahia grass, perennial peanut and natural regrowth), and coefficients significant of equations 1 and 3 were performed for Fidalski and Tormena (2007), according to Tormena and Silva (2002).
The LLWR was determined for each soil sample (Silva et al., 1994). The soil water limits to θ were estimates, from field capacity at Ψ = -80 hPa (θfc) to wilting point at Ψ = -15,000 hPa (θ wp); both were calculated using their water retention curve equation (Eq. 1). An estimate of θ (θ sr) establishing SR critical to root growth equal to 2.2 MPa (Abercrombie and Plessis, 1995) was obtained from the Eq. 3; the estimates of θ for air-filled porosity (θafp) of 0.10 m3 m-3 (Grable and Siemer, 1968) were calculated:
The Available Water Capacity (AWC) was calculated from θ estimates at Ψ = -80 hPa or field capacity (θfc) to wilting point at Ψ = -15,000 hPa (θ wp):
A completely randomized design in scheme split-plot (Gomez and Gomez, 1984) was used to evaluate the experimental data from different treatments and sampling positions (means n = 12). To determine significant differences among the mean values, ANOVA and Tukey tests at 10% were used for comparing data from treatments and sampling positions (SAS Institute, 2001).
Results and Discussion
The Db, θ, SR and SOC data were dispersed to sampling positions and three treatments (Table 2). There was no influence of sampling position on the soil water retention curve (Table 3), indicating that compaction under wheel track has affected mainly the large pores with no capillary action. However, there was an effect of treatments on θ, which was dependent of Db and SOC. The treatments have promoted modification in soil pore size distribution in addition to those effects from SOC and Db, possibly associated with drying-wetting cycles, amount and type of replenished plant roots from groundcover systems. The increase in Db reduced n parameter and established a decrease in θ (Tormena and Silva, 2002). Otherwise, the θ r was positively influenced by SOC (Rawls et al., 2003). Interactions among Db, SOC and the soil water retention curve parameters have established similar differences in the AWC between treatments (Figure 2), which were observed in another study (Tormena et al., 1999).
Effects of groundcover management systems and SOC were found in the soil resistance curve parameters, which were not influenced by sampling position (Table 3). The positive effect of SOC reduced the c coefficient value, and as a result a lower SR, probably due to the lower Db of the soil aggregates. The lower SOC in the soil under natural regrowth produces the higher value of c coefficient, indicating the highest SR in this treatment (Table 2). The higher value of e coefficient at soil under perennial peanut indicates higher increases in SR with Db; in comparison with natural regrowth. This effect is compensated by the higher SOC, which reduces the SR. Despite this SOC was not different between Bahia grass and perennial peanut (Fidalski et al., 2007), the higher value of e coefficient could be related to soil structural effects at microaggregates level due to physicochemical characteristics of SOC under these treatments.
The LLWR limits, i.e., θfc, θwp, θsr and θafp were influenced by groundcover systems (Figure 2). The θfc decreased with increasing Db whereas θwp was constant in all treatments. Higher AWC under perennial peanut was due to the low θ wp, because θfc values were similar in all treatments. The Bahia grass system induced the lowest AWC in the soil, followed by the natural regrowth. Considering AWC, perennial peanut would be the best groundcover management system for orange trees in terms of soil physical quality. For all treatments θfc was the upper limit of the LLWR. Similar results were reported for sandy and sandy-loam soils (Silva et al., 1994; Leão et al., 2006). Lack of aeration was not a problem in this soil since θafp > θfc within Dbrange. Regardless treatment and sampling position, LLWR = AWC for 1.54 < Db <1.62 Mg m-3. For Db> 1.63 Mg m-3, θsr replaced
θ wp as the LLWR lower limit (Figure 2). Bahia grass induced a higher LLWR than perennial peanut or natural regrowth (Figure 3). The Db = 1.70 Mg m-3 indicates a Db threshold level beyond which the treatment modifies the LLWR performance; thereafter, Bahia grass performed better than other treatments. The SR negative effect on LLWR was higher for perennial peanut and natural regrowth than Bahia grass. The lower θsr in Bahia grass indicates the positive effects of this treatment on the soil physical quality, probably due to the large number of fine roots than perennial peanut (Doss et al., 1960; Fischer and Cruz, 1993).
There was an interaction between treatments and sampling positions to LLWR (Table 4). The LLWR did not vary among the treatment between tracks and it was higher than the one under wheel track treatment. The LLWR mean values indicated differences in the soil physical quality under wheel tracks to Bahia grass and natural regrowth. However, in perennial peanut, the LLWR did not vary in relation to the Bahia grass and to the natural regrowth under the wheel track. The use of perennial peanut increased the risk of water deficits, as indicated by the lower LLWR. In this experiment there was a reduction in the photosynthesis rate and stomatal conductance of orange trees under perennial peanut (Fidalski et al., 2006; 2008). The higher drying effect in the perennial peanut may imply on high frequency of SR values above 2.2 MPa which may induce soil strength stress on the root system.
Growing grass in the interrows of groves was recommended by other authors (Hogue and Neilsen, 1987; Lipecki and Berbeć, 1997). Soil under Bahia grass management yield the best physical quality, enhances water relationships, and provided a better physiological condition for sustainable fruit yield (Fidalski et al., 2006). These achievements are different from previous studies, which suggested that trees compete for water under the groundcover vegetation (Glenn and Welker, 1989; Johns, 1994; Wright et al., 2003). This study suggests that Bahia grass may help to minimize the risks of soil compaction by agricultural machinery and thereby may enhance the physical quality of orange orchard soil.
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Received August 19, 2008
Accepted April 06, 2010