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Scientia Agricola

versión impresa ISSN 0103-9016

Sci. agric. (Piracicaba, Braz.) vol.68 no.1 Piracicaba enero/feb. 2011

http://dx.doi.org/10.1590/S0103-90162011000100015 

SOILS AND PLANT NUTRITION

 

Soybean growth under stable versus peak salinity

 

Crescimento da soja sob salinidade estável ou em forma de pulsos

 

 

Carolina Bustingorri*; Raúl Silvio Lavado

Universidad de Buenos Aires/Facultad de Agronomía - INBA y Cátedra de Fertilidad y Fertilizantes, Av. San Martín 4453, C1417DSE - Buenos Aires, Argentina

 

 


ABSTRACT

The production of soybean (Glycine max L.) has doubled in the last two decades. It is now being grown on both traditional arable lands and on marginal soils, including saline soils, in various parts of the world. Most research on crop tolerance to salinity has been performed using soils with stable levels of salinity. However, there are soils that undergo sudden increases in topsoil salinity for short periods of time. The aim of this study was to compare the effect of stable salinity concentrations with peaks of salinity for their effects on soybean vegetative growth, grain yield, and the accumulation of chlorides. The response of soybean growth was evaluated in pot experiments with the following treatments: Control (non saline soil), soil salinity level of 0.4 S m-1 (0.4S) or 0.8 S m-1 (0.8S), and soil subjected to salinity peaks of 0.4 S m-1 (0.4P) and 0.8 S m-1 (0.8P). The salinity levels were obtained by application of saline irrigation water. Soybean responded differently to stable salinity levels versus peaks of salinity. When salinity was a permanent stress factor, regardless of the salinity level (i.e. 0.4 and 0.8 S m-1), biomass production and differentiation of reproductive organs was greatly affected. For 0.8S treated plants, they never reached the reproductive phase. Conversely, only small differences in growth data were found between 0.4P and Control treatments, although an 80% decrease in yield was associated with the 0.4P treatment. To obtain a reasonable soybean yield, a leaf chloride concentration of 1 mg g-1 of Cl- in dry matter should be considered a maximum threshold.

Key words: NaCl, Glycine Max L., saline irrigation, yield loss, chloride accumulation


RESUMO

A produção de soja (Glycine max L.) duplicou nas últimas duas décadas. Atualmente está sendo cultivada em terras aráveis tanto nos solos tradicionais quanto marginais, incluindo solos salinos, em várias partes do mundo. A maioria das pesquisas sobre a tolerância das culturas à salinidade foi realizada utilizando solos com níveis estáveis de salinidade. No entanto, há solos que são sensíveis ao aumento brusco de salinidade do solo superficial por curtos períodos de tempo. Comparou-se o efeito das concentrações de salinidade estável com picos de salinidade no crescimento vegetativo da soja, na produção de grãos e no acúmulo de cloretos. A resposta do crescimento da soja à salinidade foi avaliada em experimentos em vasos com os seguintes tratamentos: irrigação com água destilada (Controle, C), a irrigação para alcançar a salinidade de 0,4 S m-1 (0,4S) ou 0,8 S m-1 (0,8S) e irrigação com picos para alcançar a salinidade 0,4 S m-1 (0,4P) e 0,8 Sm-1 (0.8P). A soja respondeu diferentemente aos níveis de salinidade estável contra picos de salinidade. Quando a salinidade foi um fator de estresse permanente, independentemente do nível de salinidade (ou seja, 0,4 e 0,8 S m-1), a produção da biomassa e a diferenciação dos órgãos reprodutivos foram muito afetadas, sendo que plantas tratadas (0,8S) nunca chegaram à fase reprodutiva. Pequenas diferenças nos resultados de crescimento foram encontradas entre 0,4P e tratamentos Controle, apesar de uma diminuição de 80% no rendimento estar associada com o tratamento 0,4P. Para obter uma produtividade de soja razoável, a concentração de cloreto de 1 mg g-1 de Cl- na matéria seca de folha deve ser considerada um limite máximo.

Palavras-chave: NaCl, Glycine Max L., água de irrigação, produção de colheita, acumulação de cloreto


 

 

Introduction

Soybean (Glycine max L.), one of the main crops of the world, has doubled its production in the last two decades in parallel with a rising food demand, increasing the pressure on the world's availability of arable land (USDA, 2008). This is the main reason soybean is now being established not only on traditional arable lands, but also on marginal soils. The expansion of soybean has been documented on saline soils in various parts of the world (Essa, 2002; Scanlon et al., 2005) including Argentina (Nosetto et al., 2009).

Soybean is classified as moderately tolerant to salinity, with a threshold of 0.5 S m-1, beyond which growth is markedly reduced (Maas and Hoffman, 1977). Nevertheless, other authors have suggested lower threshold values, around 0.2 S m-1 (Katerji et al., 2000). However, soybean's response to salinity changes along the phenological stages (Khajeh Hosseini et al., 2002; Wang et al., 2002). A limitation of these studies is that they were performed using permanent saline levels. Since soluble salts are extremely mobile in soils, soil salinity varies over time. In some soils, salinity concentrations are low most of the time; but they can undergo sudden increases in the topsoil salinity and return back to its low level after rainfall. This situation is known as salinity peaks, and is often found during the summer season in soils of wet areas and arid areas as well (Dang et al., 2008; Lavado and Taboada, 1988). Another context for the presence of salty peaks is soils suffering an increase in salinity either by irrigation or waterlogging from a saline water source (Chauhan et al., 2008; Gowing et al., 2009; Gupta, 1985).

Sodium (Na) and chloride (Cl) are the major ions in saline soils. Chloride is phytotoxic, however there is great variability in the sensitivity of plants to it, depending on differences in species and genotypes (Brinkman, 1988; Xu et al., 2000). The minimum concentration of soil chloride that has phytotoxic effects on soybeans is still unknown (Dabuxilatu and Ikeda, 2005a; Yang and Blanchar, 1993). The aim of this work was to compare the effect of salinity peaks on soybean growth, grain yield, and the accumulation of Cl- compared to soybean growth under stable salinity levels.

 

Material and Methods

A pot experiment was established following a completely randomized 2 × 2 factorial design with an additional treatment (Control), 12 replicates for each treatment group were setup. Two soil salinity levels (0.4 vs 0.8 S m-1) and two salinity moments (stable vs peaks) were tested, resulting in the following treatments: i) soil irrigated with distilled water during the whole crop cycle as a Control (C); ii) soil irrigated with saline water of electrical conductivity (EC) of 0.4 S m-1 maintained throughout the crop cycle for a medium stable salinity treatment (0.4S); iii) same as (ii) for 0.8 S m-1 (0.8S) ; iv) a medium salinity peak treatment (0.4P), soil irrigated with distilled water for 35 days after sowing , then subjected to 15 days of irrigation saline water of 0.4 S m-1 and after that irrigation with distilled water; v) a high salinity peak (0.8P), same as (iv) for 0.8 S m-1 . Saline water was obtained by addition of NaCl to distilled water with the purpose of reaching the desired EC level. When soybeans reached the flowering stage (R1) salty peaks had already ended. To avoid salt accumulation within the pots, the irrigation volume was allowed to exceed field capacity by 20%, all treatments received the same volume of water (0.8 L per pot). To avoid surpassing the desired soil salinity level for each treatment, soil EC within the pots was monitored periodically.

Pots were installed under a shelter with the intention of controlling rainfall but not light. Three soybean seeds (maturity group IV, cultivar: NA 4613) that were previously inoculated were sown in 8 L plastic pots filled with a soil mixture composed by 300 g kg-1 sand, 200 g kg-1 perlite, and 500 g kg-1 A horizon. The former was a sandy loam soil (180 g kg-1 clay, 170 g kg-1 silt, 630 g kg-1 sand) (Typic Argiudoll). Following standard soil test methods (Sparks et al., 1996) it was determined that the soil (A horizon) contained 12.6 g kg-1 of total carbon (Walkey and Black method), a neutral pH of 7.56, a good content of available P (Kurtz and Bray method), 32.8 mg kg-1, and a low ECS (0.04 S m-1). After 15 days, plants were thinned to one plant per pot. To prevent a nutritional deficit, each pot was supplemented with 2 g of triple superphosphate and 0.125 g of an all micronutrients mix before sowing. At four intervals during the crop cycle, all pots had 1 g of a soluble fertilizer (N: P: K 25-10-10) added.

At bloom (R1-R2); pod (R3-R4) and maturity (R8) stages (50, 70 and 130 days after sowing, respectively), plant and soil mixture samples were collected from four pots of each treatment group. Plant height, number of flowers, number of pods, and number of grains were recorded. Aerial biomass, previously rinsed with distilled water, was divided into green and senescent leaves, shoots, pods, and grains. Roots were washed and harvested. All vegetative samples were dried at 60ºC for 72 h and then weighed. Plant samples were reduced to ashes with Na2CO3 and the remaining residue was ignited and then dissolved with HNO3 and filtered. Both filtrates were analyzed for total chloride content by a volumetric titration (AOAC, 1965). After each harvest, soil samples were analyzed for the presence of specific cations (Ca, Mg, K, Na) and anions (Cl-, SO4, HCO3) and EC was determined in soil saturation extracts. (Sparks et al., 1996).

The results were evaluated using individual analysis of variance (ANOVA) for each sampling date (R1-R2; R3-R4; R8), corresponding to a factorial design. Treatment differences were analyzed by orthogonal contrasts. A regression analysis was used to identify the relationship between measured chloride content and soybean grain yield, and the best-fit linear regression was chosen (Table Curve 2D; AISN Software, 2000).

 

Results

For the Control treatment soil EC was ~0.08 S m-1 throughout the crop cycle. Stable salinity treatments rapidly reached levels of 0.41 S m-1 and 0.76 S m-1 in average for the 0.4S and 0.8S treatments, respectively. These levels were maintained throughout the crop cycle. For treatments 0.4P and 0.8P, salinity was initially low, and then reached EC levels of 0.33 and 0.74 S m-1 in average, respectively, during the salinity peak, and then the EC levels decreased markedly thereafter, reaching similar EC values than those obtained for Control soils. Table 1 presents the soil ionic composition of saturation extracts for each treatment at the first sampling date.

Table 2 shows the probability values for the contrasts analyzed for plant height at each sampling time and Figure 1 shows soybean plant height recorded for the first two sampling dates. The height at R3-R4 did not differ from that measured at R8, and then the alter data is not shown. This figure also shows the time period over which salinity was kept stable versus the intervals of salinity peak treatments. Fifty days after sowing (R1-R2), soybean plants subjected to stable salinity (treatments 0.4S and 0.8S) were found to differ from the Control plants and these differences became larger as the growth cycle progressed. At R8, plants subjected to either stable salinity treatments only reached half their height compared to the Control. On the contrary plants that underwent salinity peak treatments (0.4P and 0.8P) showed differences only 70 days after sowing. Control and 0.4P plants grew at a similar rate (1.2 cm d-1), whereas 0.8P plants did not increase in height.

 

 

Soybean biomass was drastically reduced by salinity. Figure 2 shows the evolution of dry matter production along the crop cycle; for all saline treatments a reduction in biomass was evident in all vegetative components. The results from the ANOVA are presented in table 3. Compared to the Control plants, all saline treated plants showed a 50% reduction in root biomass at all sampling dates. In general, the inhibition of root growth by salinity was less severe than its effect on aerial components (i.e. green and senescent leaves and shoots), although reduced root biomass was particularly evident in plants that underwent stable salinity treatments. Senescence occurred suddenly during stable salinity treatments with > 70% of the leaf biomass drying out before the second sampling date. On plants receiving a high salinity treatment (0.8S), whole portions of the shoot suffered premature onset of senescence. For peak salinity treated plants, senescence became evident at pod stage (R3-R4) with more than 50% of the leaves becoming senescent. For Control plants and plants receiving salinity peak treatments, 4.5 times more aboveground biomass had been generated at R1-R2 than for plants under stable salinity. The differences in leaf- and stem-derived dry matter between Control, 0.4P and 0.8P treatment groups grew larger as the growth cycle progressed. Even after salinity was restored back to normal levels, the damage caused by the salinity peak had a long-lasting effect on soybean plants with little or no recovery observed for the 0.4P and 0.8P treatments. Finally at R8, 0.4P plants produced 25% less aboveground biomass and around 50% less for 0.8P plants compared to the Control treatment.

Plants in the 0.8S treatment never reached the reproductive phase (Table 4). The soybean pod number and its weight for both salinity peaks (0.4P and 0.8P) and stable salinity (0.4S) was reduced (ranging from 30 to 80%, respectively). On the other hand, reduction in yield was more severe; representing between 66 - 86% yield losses compared to the Control. The salinity treatments 0.4S, 0.4P, and 0.8P were not different. Final grain size was not affected by salinity and only some changes between seed weight in favour of the salinity peak treatments compared to Control plants (163 vs. 132 g 1000 seeds-1) were found. However due to a great variability in this parameter no differences were found. Total plant yield was strongly correlated with grain number (Y = 0.135x; R2 = 0.99), but no relation was found between grain size and plant yield.

The chloride content in root samples was low and did not vary among treatments (Tables 5 and 6). The highest overall chloride concentrations were associated with plants receiving stable salinity treatments, with plant leaves and shoots containing greater amounts than the other organs. Stable salinity treatments showed the chloride concentration in leaves to be 2.5 and 3.6 times higher in the 0.4S and 0.8S treatment, respectively, compared to the Control plants. In contrast, the chloride concentrations in the salinity peak treated plants were not different from that levels measured in the Control plants. As leaf chloride concentrations increases, crop yield abruptly decreases (Figure 3). A limit value concentration was determined to be approximately 1 mg g-1 Cl in dry matter. Surpassing this threshold would result in severe yield reductions. There was no relationship between chloride content in grains and grain yield.

 

 

Discussion

Chloride clearly predominates in the soluble soil ionic composition as salinity increases. Salinity stress reduced plant height and total biomass production and yield. Present results are consistent with results from other studies, indicating a low salt tolerance by soybean plants. In agreement with results from Dabuxilatu and Ikeda (2005b), Essa (2002) and Shalhevet et al. (1995), reduced biomass was evident for all vegetative components. Our results are consistent with other studies that also found greater reductions in aerial biomass than in roots (Cordovilla et al., 1995; Essa, 2002), yet our study reports more pronounced effects. Roots seem to be more resistant to soil salinity than aerial biomass which could be linked to its low chloride levels. In this study clear symptoms of the effect of salinity on aerial biomass were leaf senescence and premature leaf abscission. These processes had been hypothesized to be part of a plant strategy to adapt to high soil salinity (Larcher, 2003; Maggio et al., 2007; Tardieu and Davies, 1993).

Salt damage in soybean results from the accumulation of chloride in stems and leaves (Parker et al., 1983; Wang and Shannon, 1999). Other authors found chloride accumulation in leaves increased with salinity. Leaf chloride values obtained in this work were markedly lower than those found for other soybean cultivars, ranging from 0.7 to 4.45 mg g-1 (Essa, 2002; Jeong-Dong et al., 2008), perhaps due to the different chloride extraction method used, in those studies different water extractions were performed whereas in this paper chloride was determined on ashed plant samples. However, despite the low values in chloride concentration, differences between treatments were found, and leaf chloride content can be used to predict yield under salinity better than other variables such as plant height, and biomass production.

When salinity was a permanent stress factor, either for our high or medium EC levels, biomass production markedly decreased and differentiation of reproductive organs was affected. Salt levels of 0.4 S m-1 or higher resulted in little or no grain production. Despite irrigation with distilled water was re-established before the onset of blooming in both salty peak treatments (0.4P and 0.8P) yield production was markedly reduced. Remarkably, when the crop was subjected to medium level (0.4 S m-1) salinity peak neither size nor biomass was greatly affected, yet the magnitude of the reduction in grain yield was significant. This observation represents a dramatic agronomic consequence in the field, where crops may appear healthy, yet yields will be extremely low.

 

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Received May 29, 2009
Accepted August 13, 2010

 

 

* Corresponding author <cbusting@agro.uba.ar>