Phosphorus Availability in Lolium perenne L. in Acidic and Limed Soils

Soil liming may increase phosphorus (P) availability, but this increase may also be achieved with generous P applications. However, it is not well known which practice has longer-term effects. Thus, in a pot experiment, an acidic soil (pH 4.57), limed to pH 6.5, was added with P and sown with Lolium perenne L. We conducted three cuttings (on Days 40, 80, and 120) in order to evaluate P dynamics in each of the treatments. As expected, biomass increased significantly with liming. We also found that plant P concentration increased in the liming treatment, but not in the P-added treatment, although the difference was reduced on Day 120. This shows that in severely acidic soils, liming should be preferred over P addition, although the beneficial effects may not last for a very long time, since in this experiment, they only lasted for 4 months. Similar conclusions were drawn from soil P extraction results.     

有机无机磷肥配施对蔬菜地土壤磷素淋失的影响

利用土柱淋溶模拟实验研究化肥、有机肥以及有机无机P肥配施对蔬菜地土壤P素淋失的影响,结果表明,有机肥可明显提高土壤的有机P含量,促进土壤P素的淋失;在施P量相同的情况下,有机P肥所占的比例越大,淋出液总P、溶解总P、溶解有机P的浓度和累积淋失量就越高.在评价蔬菜地土壤P对水环境影响时,应把有机P作为评价指标.     

Effect of Long-Term Fertilizer Management and Crop Rotations on Accumulation and Downward Movement of Phosphorus in Semi-Arid Subtropical Irrigated Soils

Crop species and their varieties vary in phosphorus (P) requirements for optimum production and response to P application. As crop recovery of added P often ranges from 10 to 40%, the rest accumulates in soil and may create potential for P leaching, depending upon the soil characteristics, duration of P applications, and cropping systems. Accumulation and distribution of Olsen P (plant-available labile P), total inorganic P, and total organic P were investigated in soil profiles of three field experiments differing in rate (9–44 kg P ha^–1), frequency (applied once or twice annually), and duration (4–34 years) of fertilizer P applications, crop rotations, soil characteristics, and irrigation pattern (upland irrigated and flooded-rice crop) in a subtropical region. Profile samples were collected from soil depths of 0–15, 15–30, 30–60, 60–90, 90–120, and 120–150 cm of different treatments in these experiments and analyzed for different forms of P and soil characteristics. The results revealed that (i) annual applications of fertilizer P either to one crop (alternative-applied P) or to both crops (cumulative) led to the accumulation of residual fertilizer P in the form of Olsen P, varying from 44 to 148 kg P ha^–1, and the magnitude of accumulation was proportional to applied fertilizer P rate, frequency, and duration; (ii) majority of residual fertilizer P accumulated as inorganic P (74–89%) followed by organic P (11–26%) and Olsen P (9–19%), illustrating that the inorganic P pool is a major sink for fertilizer P; (iii) application of fertilizer nitrogen (N) and potassium (K) alone or in combination with fertilizer P did not affect residual fertilizer P accumulation in soil profile; (iv) incorporation of farmyard manure enhanced the P enrichment of soil profile; (v) irrigation pattern, soil pH (7.1–7.7), and calcium carbonate (CaCO₃) (trace–0.33%) did not influence P movement to deeper soil layers; silt, clay, and soil organic C (SOC) showed strong relationships with Olsen P (r = 0.827, 0.938, and 0.464, P < 0.01) and enhanced the retention of labile P in the plow layer; and (vi) only 6–29% total residual P moved beyond 30 cm deep in fine-textured soils under 22-year rice (Oryza sativa L.)–wheat (Triticum aestivum L.) and 34-year maize (Zea maize L.)–wheat rotations, whereas 41, 27, 20, 9, and 3% were located in soil layers 0–30, 30–60, 60–90, 90–120, and 120–150 cm deep, respectively, in coarse-textured soil profile under 4-year peanut (Arachis hypogaea L.)–sunflower (Helianthus annuus L.) field. These findings confirmed that interplay between the fertilizer P management (alternative vis-à-vis cumulative P application and optimal vis-à-vis excessive rates of fertilizer P in different crop rotations), amount of labile P accumulated in soil profile, and soil characteristics (silt, clay, and SOC) largely controlled the downward movement and resultant potential for P leaching in subtropical irrigated soils.     

酸性硫酸盐土壤上几种磷矿粉对水稻生长的影响

在酸性硫酸盐土壤未垦和已垦地上进行的磷矿粉田间试验结果表明，未垦地上直接施用磷矿粉对水稻有显著的增产作用，主要表现在促进水稻株高、分蘖数、穗数的增加上．但在已垦地上磷矿粉对水稻的增产作用不甚明显．施肥后对相关的土壤肥力状况变化也进行了报道．     

Assessing the Feasibility of Olsen P and P Sorption Parameters in Acidic Soils

Plant-available phosphorus (P) and P adsorption capacities are important for crop growth in acidic soils. Olsen P test, which is based on extraction with bicarbonate for predicting the amount of soil P available to plants, was used in this work. Soil P-adsorption capacities were determined by Langmuir line equation. The purpose of this work was to examine the suitability of Olsen P for predicting phytoavailable P and P sorption parameters in acid soil. To this end, we (i) assessed the phytoavailable P by successively pot-cropping rice and (ii) P adsorption characteristics of soil and their relation with Olsen P. Plant-available P, estimated by Olsen P in tested soil, was correlated to labile P. Qm (phosphorus sorption maximum) was negatively correlated with K (P sorption strength). P buffering capacity of soils was P3 (the highest P rate) >P2 (the second highest P rate) >P1 (the lowest P rate) >P0 (no P adding) after 75 day’s rice growth, which indicated P replenishment capacity was different among P treatments. This also suggested that P of plant uptake may decrease soil buffering capacity, especially for soils that contained relatively lower amounts of P. Qm and K were not significantly correlated to Olsen P. Degree of P saturation and Olsen P shared the similar trend with the change of P application rates and sampling dates. We concluded P status in soil can be characterized by degree of P saturation and Olsen P in tested soil. They were able to explain P status from both agronomic and environmental aspects.

Abbreviations: Qm, P sorption maximum; K, P sorption strength; P3, highest P rate in soil; P2, second highest P rate in soil; P1, lowest P rate in soil; P0, P adding in soil.     

滴灌下酸性物质对石灰性土壤磷有效性及作物吸收的影响

大田滴灌条件下研究了少量多次施用硫酸和磷酸对石灰性土壤pH、磷有效性以及改善作物磷营养的效果。结果表明,施用磷酸和硫酸降低局部土壤pH,且随施用次数的增加,酸化效果趋于加强,在第5次施用酸化剂时下降到最大。水平方向上,滴灌带附近pH降低最大,随距离增加酸化效果减弱,pH最大降幅0.26个单位。垂直方向上,0~10 cm酸化最为强烈,pH最大降幅0.29个单位。pH降低提高了土壤磷的有效性,0~20 cm土层深度酸化剂处理有效磷含量均显著高于对照(P0.05),且硫酸与磷酸酸化效果接近。相同养分用量投入和管理水平下,酸化剂处理棉花吸磷量增加17.6%~23.4%,皮棉产量提高9.9%~11.4%。滴灌条件下施用酸化剂提高石灰性土壤养分有效性是一种可行的提高养分资源利用效率的方法。     

Co-application of Red Gypsum and Sewage Sludge on Acidic Tropical Soils

The agroenvironmental impact of co-utilization of red gypsum and sewage sludge was investigated. Both laboratory and greenhouse studies were conducted. The treatments were soil + sewage sludge (5% w/w) + red gypsum (0, 2.5, 5, 10, 20, and 40%, w/w). Corn was grown in the greenhouse, and the highest rate of red gypsum application was excluded. The residual calcite in red gypsum was able to increase the pH of the red gypsum–sewage sludge acidic soil system. Hence, gypsum reduced the zinc (Zn) concentrations in the soil solution released by sewage sludge. Phosphorus (P) and potassium (K) were insufficient for corn growth. At the rate of 2.5% red gypsum and 5% sewage sludge application, no dry-matter reduction was observed compared to the control. The uptake of Zn, copper (Cu), and iron (Fe) by the corn plants decreased. Therefore, co-utilization of red gypsum and sewage sludge is a better option than using these by-products separately.     

Phosphorus Fractions in Sodic Soils of the Great Ethiopian Rift Valley Soils as Affected by Reclamation

Soil phosphorus (P) availability is commonly assumed to limit productivity in tropical soils, yet there is relatively little information on the chemical forms of soil P in such ecosystems. The study was conducted to determine the size P pools via application of gypsum. We used a sequential fractionation to assess P fractions. The average total P concentration was 519 mg kg?1. Soil organic P was relatively low (74 mg kg?1). The ratio of organic carbon to organic P was generally greater than 298, suggesting the potential for immobilization. Calcium-associated P was the dominant inorganic P pool, whereas Al+Fe-P was the second dominant. Readily available P was very low (1.3 mg kg?1). Gypsum at different level was used as a reclamation material for sodic soils, and application of gypsum significantly affected the different P fractions. Organic P forms were significantly lower for higher levels of gypsum application.     

Liming Effects on Extractable Boron in Six Acidic Soils

A laboratory incubation study was conducted to study the influence of liming on extractable boron (B) in acidic soil. Six soils, three each from the Inceptisols and Alfisols, were incubated for 30 days with combinations of lime and B. The soils were acutely deficient in plant-available B (0.09–0.21 mg kg^?1). Only <50 percent of applied B was recovered from the soils in available form. Such recovery was lower in Alfisols than that in Inceptisols due to adsorption of a greater amount of added B with iron (Fe^?) and aluminium (Al^?) oxides in the former soil group. Required dose of lime showed an increase in availability of native soil B, particularly in Inceptisols (26 percent), and a net decrease in recovery of added B (32.5 percent) as compared to no lime control (41.6 percent). The results thus suggest that liming to acidic soils increases extractable B.     

玉米-大豆轮作中耕作方式和磷肥施用对土壤磷组分冬季变化特征的影响

Determining how agricultural management practices affect soil phosphorus(P) over the winter may further our understanding of the soil P cycle under specific environmental conditions in eastern Canada. This study assessed changes over winter for soil P fractions and other selected chemical properties as affected by tillage and P fertilization. In 1992, a long-term corn(Zea mays L.) and soybean(Glycine max L.) rotational experiment was established in the province of Quebec, Canada. Soil samples(0–15 cm) were collected in fall 2001 and 2007 after a soybean harvest, and in the following spring 2002 and 2008 before corn seeding, in main plots under moldboard plow and no-till managements and selected subplots fertilized with 0, 17.5, or 35 kg P ha-1and 160 kg N ha-1. Soil samples were analyzed for P fractions and other chemical properties to assess changes over winter for 2001–2002 and 2007–2008. Changes over winter of all soil P fractions were significant for the two periods, indicating the occurrence of soil P transformation and movement over winter. The Mehlich-3-extractable Fe, Al, Ca, and Mg decreased during the two studied periods. Tillage had no significant effect on all soil P fractions. The resin-extractable P in 2001–2002 and Na HCO3-extractable inorganic P and Na OH-extractable organic P during the two winters were significantly increased under P fertilization. This study demonstrated that P in cultivated soils changed during winter as a result of changes in labile P fractions possibly due to the solubilization of residual fertilizer P combined with environmental factors.     

Distribution of Inorganic and Organic Phosphorus Fractions in Two Phosphorus-Deficient Soils as Affected by Crop Species and Nitrogen Applications

It is desirable to know the distribution of phosphorus (P) fractions in soil so that plants may use P efficiently. Here we report the dynamics of inorganic and organic P in P-deficient black and rice soil cropped by soybean, white lupin, and maize supplied with nitrogen (N) inputs by N fixation and urea fertilizer. Inorganic P fractions of the three cropped soils could be ranked as O-P (organic phosphorus) > Al-P (aluminum phosphorus) > Fe-P (iron phosphorus) > Ca₁₀-P (calcium-10 phosphorus) > Ca₈-P (calcium-8 phosphorus) > Ca₂-P (calcium-2 phosphorus), irrespective of soil type. The potential of various inorganic P fractions to plant nutrition differed between soybean and white lupin. The percentage of total P present as inorganic P was affected by crop, soil type, and N source. In black soil, the change of organic P fraction induced by N fixation was larger than by urea application. The moderately labile organic P (MLOP) concentration was not affected significantly by soil type and crop species, and it was probably the main P source to the inorganic P fraction because the correlation between the two pools was high (r = 0.945; P < 0.05). Crop species differed in their uptake of inorganic and organic P from soil. Though P fraction concentrations varied between black soil and rice soil, their response to crop species and N source was similar. The amounts of P removed from soil were affected by N source. The right choice of crop species and the application a suitable N source may increase crop yield and P uptake by plant in P-deficient soils.     

Phosphorus Response of Oryza sativa,O. glaberrima,and Hybrid Rice Cultivars on an Ultisol

Phosphorus (P) deficiency is a major constraint to upland rice production on Ultisols in the humid zone of West Africa. Integrated use of P-efficient cultivars and P nutrition is needed for enhanced sustainable productivity on these soils. This article reports on the P responsiveness of interspecific rice hybrids (crosses from Oryza sativa and O. glaberrima) along with O. sativa and O. glaberrima cultivars grown on an acidic Ultisol, low in available P. The cultivars differed in yield and P-uptake response to fresh and residual P. Two interspecific cultivars gave a linear response to P and produced the greatest grain yield under direct and residual P. The O. glaberrima cultivar CG 14 did not respond to the applied P, whereas the O. sativa cultivar was moderate in its performance. Our results show that the interspecific rice cultivars have the potential to adapt and perform well on acidic upland soils.     

Soil Phosphorus Tests for Flooded Rice Grown in Contrasting Soils and Cropping History

Soil phosphorus (P) tests for flooded rice (Oryza sativa L.) generally present uncertainties for estimating P availability. Bray 1, 1% citric acid, Mehlich 3, Olsen extractants (dry samples), and Bray 1 extractant after 3 days (BI3) and 7 days (BI7) of anaerobic incubations were evaluated to estimate P availability for rice in 43 Uruguayan soils. Field trials were conduced at each site (0, 13, 26, and 39 kg P applied ha^?1). Relative yield and absolute and relative yield increases were determined. Extracted P was variable for the different tests. For silty soils, P availability was better estimated by citric acid, Mehlich 3, and Bray 1, with similar soil P critical concentrations (6?8 mg P kg^?1). The BI3 and BI7 tests showed greater soil P critical concentration but poorer correlations with yield indexes. This study contributes to the scientific basis of P fertilization for flooded rice, promoting more effective fertilizer use and minimizing environmental P losses.     

Phosphorus Availability in Low-P and Acidic Soils as Affected by Liming and P Addition

Acidic soils typically suffer from high phosphorus (P) retention, a problem that can be dealt with using greater P fertilization, soil liming, or both. The aim of this work was to examine which of these practices bears the more beneficial result for Lolium perenne L. growth. In a pot experiment, five acidic soils were treated as follows: L0P0 (unamended control), L1P0 (liming only), L0P1 (P addition only), and L1P1 (both liming and P addition). We found that P amendment alone was sufficient to increase plant P levels when the initial soil P concentrations were low. Liming without P addition increased plant P satisfactorily only in the high-P soil. We conclude that P addition alone is a better practice than liming alone for improved plant growth conditions in acidic, low-P soils, unless there is relatively high P content in soil, in which case liming alone may be sufficient to increase P availability.     

Role of Phenolics and Organic Acids in Phosphorus Mobilization in Calcareous and Acidic Soils

Abstract

Phenolic acids (caffeic, CAF; protocatechuic, PCA; p-coumaric, COU; and vanillic, VAN), catechol (CAT), poly-galacturonic acid (PGA), and citric acid (CIT) were compared for their effectiveness in phosphorus (P) mobilization in three soils differing in chemical properties. The addition of organic ligands at 100 μmol g^{? 1} soil increased the concentrations of resin P (P_r), water-extractable P (P_w), and bicarbonate-extractable inorganic P (P_bi), thus improving the phosphorus availability. The magnitude of P mobilization in the calcareous soil can be expressed in the following order: CAF > CAT > PCA = CIT > VAN > COU > PGA, which was consistent with the number of phenolic hydroxyl groups they contained and the position of carboxyl on the benzoic ring. In the two acid soils tested, the order of P mobilization was CIT > CAT > PCA > CAF after 24 h incubation, and CIT > PCA > CAF > CAT after a 14 d incubation. The mobilized P originated partly from the organic P fractions, which could be extracted by 0.5 M NaHCO₃. In addition, P_r decreased and P_w increased during incubation. The exceptions were that the CAF treatment increased P_r and the CIT treatment did not affect P_w. Calcium extraction from the soils after a 1 d or 14 d incubation could not fully account for the P mobilization. The results suggest that the inorganic P dissolution by the organic ligands was not the only mechanism of P mobilization in the calcareous soil, while in acid soils the chelation of metal cations by organic ligands is likely an important factor in P mobilization.     

Root Exudates of Rice Cultivars Affect Rhizospheric Phosphorus Dynamics in Soils with Different Phosphorus Statuses

Exudation of organic acids by the roots of three rice cultivars grown in three soils of different phosphorus (P) statuses, and their impacts on the rhizospheric P dynamics and P uptake by the rice plants, were investigated. Quantum root exudates from all the rice cultivars were significantly greater at 21 days after transplantation than at panicle initiation or flowering stages. Malic acid was the most predominant organic acid present in the rice root exudates (10.3 to 89.5 μmol plant^?1 d^?1), followed by tartaric, citric, and acetic acids. Greater exudation of organic acids from rice grown in P-deficient soil by all the rice cultivars suggested response of rice plant to P stress. Results indicate that the release of organic acids in the root exudates of rice plants can extract P from strongly adsorbed soil P fraction, thereby increasing native soil P utilization efficiency and ensuring adequate P nutrition for the growing rice plants.     

沙化对高寒草甸土壤磷素组分的影响

[目的] 土壤磷素组分决定着土壤演变过程中磷素的迁移和可用性。探讨高寒草甸不同退化程度下土壤磷组分的空间分布特征,为沙化草甸植被恢复提供科学参考。[方法] 以青藏高原若尔盖沙化高寒草甸土壤为研究对象,采用修正后的Hedley磷素分级方法,探究未沙化、轻度、中度和重度沙化程度下高寒草甸土壤磷组分变化。[结果] ①随着沙化程度的加剧,土壤有机碳、全氮、全磷、速效磷及含水量显著降低（p<0.05）;pH值显著升高（p<0.05）。②土壤树脂态磷（Resin-Pi）、碳酸氢钠磷（NaHCO₃-P）、氢氧化钠磷（NaOH-P）、稀盐酸无机磷（D.HCl-Pi）和浓盐酸磷（C.HCl-P）含量随沙化程度的加剧均出现显著（p<0.05）下降,其中在中度和重度沙化下有机磷组分含量较无机磷下降更为明显。③相关性分析显示,在高寒草甸沙化过程中土壤磷素组分的转化主要发生在D.HCl-Pi,NaHCO₃-P与氢氧化钠有机磷（NaOH-Po）组分之间;而HCl-P,NaOH-P和Resin-Pi是植物生长重要的磷源。[结论] 沙化对土壤碳氮、水分、pH值和磷素组分有显著影响,沙化导致土壤碳氮、水分及pH值和磷素组分发生不同程度的变异,且多发生于沙化中后期;在高寒草甸沙化土壤中HCl-P,NaOH-P和Resin-Pi是植物生长重要的磷源。     

提取剂和土水比对旱耕地土壤无机和有机磷的提取效应

比较了O lsen(0.5 mol L-1NaHCO3)和B ray-1(0.03 mol L-1NH4F-0.025 mol L-1HC l)提取剂土水比1∶4和1∶20(W/V),对我国5种类型旱耕地土壤(pHKC l3.3~7.4)无机磷(Pi)和有机磷(Po)及外加正磷酸盐态无机磷的提取效应。结果表明,以O lsen提取剂土水比1∶20对土壤Pi和Po的提取效果最佳,其测定结果是评价土壤磷素供应能力(有效磷)和活性有机磷含量较为适宜的指标。测定的土壤大多数(占60%)磷素供应能力较差(O lsen-Pi为4.2~14.0mg kg-1),应适当加强其磷素的投入。测定的土壤活性有机磷(O lsen-PO)含量为1.4~37.9 mg kg-1,占土壤全磷的0.2%~15.8%,大多数(75%)土壤占1%~6%。采用O lsen提取剂时土壤外加Pi的固定率随土水比减小而增高,当土水比1∶4提取时,酸性和强酸性(pHKC l3.3~5.5)土壤对外加Pi的固定率达40%~86%,据此推测实际田间条件下土壤对外加Pi的固定率更大。表明酸性和强酸性旱耕地土壤对外加Pi具有强烈的固定作用。     

Impact of Poultry Manure Application on Phosphorus Desorption in Some Calcareous Soils

Laboratory experiments were conducted to study the kinetics of phosphorus (P) desorption in different calcareous soils of Hamadan Province of Iran. Soils were fertilized with poultry manure at 50 ton ha^–1 and incubated at 25 ± 1 °C at 15% moisture for 6 months. The release rate of P was studied by successive extraction with 0.5 M sodium bicarbonate (NaHCO₃) over a period of 1–1752 h. Also, available P was determined. The results showed that available P in fertilized and unfertilized soils ranged from 13.3 to 55.1 and 10.0 to 50.1 mg kg^–1, respectively. Phosphorus desorption from the fertilized and unfertilized soils began with a fast initial reaction, followed by a slow secondary reaction. The amount of P released after 1752 h in fertilized and unfertilized soils ranged from 319.2 to 623.9 and 309 to 586.7 mg kg^–1, respectively. The amount of P released was significantly correlated with available P. The kinetics of cumulative P release were evaluated using the five kinetic equations. Phosphorus desorption kinetics were best described by the parabolic diffusion law, first order, and power function equations. Rate constants of these equations different in fertilized and unfertilized soils.     

Effect of Lime and Flooding on Phosphorus Availability and Rice Growth on Two Acidic Lowland Soils

Abstract

Loss of soil‐water saturation may impair growth of rainfed lowland rice by restricting nutrient uptake, including the uptake of added phosphorus (P). For acidic soils, reappearance of soluble aluminum (Al) following loss of soil‐water saturation may also restrict P uptake. The aim of this study was to determine whether liming, flooding, and P additions could ameliorate the effects of loss of soil‐water saturation on P uptake and growth of rice. In the first pot experiment, two acid lowland soils from Cambodia [Kandic Plinthaqult (black clay soil) and Plinthustalf (sandy soil)] were treated with P (45 mg P kg^?1 soil) either before or after flooding for 4 weeks to investigate the effect of flooding on effectiveness of P fertilizer for rice growth. After 4 weeks, soils were air dried and crushed and then wet to field capacity and upland rice was grown in them for an additional 6 weeks. Addition of P fertilizer before rather than after flooding depressed the growth of the subsequently planted upland rice. During flooding, there was an increase in both acetate‐extractable Fe and the phosphate sorption capacity of soils, and a close relationship between them (r²=0.96–0.98). When P was added before flooding, Olsen and Bray 1‐extractable P, shoot dry matter, and shoot P concentrations were depressed, indicating that flooding decreased availability of fertilizer P. A second pot experiment was conducted with three levels of lime as CaCO₃ [to establish pH (CaCl₂) in the oxidized soils at 4, 5, and 6] and four levels of P (0, 13, 26, and 52 mg P kg^?1 soil) added to the same two acid lowland rice soils under flooded and nonflooded conditions. Under continuously flooded conditions, pH increased to over 5.6 regardless of lime treatment, and there was no response of rice dry matter to liming after 6 weeks' growth, but the addition of P increased rice dry matter substantially in both soils. In nonflooded soils, when P was not applied, shoot dry matter was depressed by up to one‐half of that in plants grown under continuously flooded conditions. Under the nonflooded conditions, rice dry matter and leaf P increased with the addition of P, but less so than in flooded soils. Leaf P concentrations and shoot dry matter responded strongly to the addition of lime. The increase in shoot dry matter of rice with lime and P application in nonflooded soil was associated with a significant decline in soluble Al in the soil and an increase in plant P uptake. The current experiments show that the loss of soil‐water saturation may be associated with the inhibition of P absorption by excess soluble Al. By contrast, flooding decreased exchangeable Al to levels below the threshold for toxicity in rice. In addition, the decreased P availability with loss of soil‐water saturation may have been associated with a greater phosphate sorption capacity of the soils during flooding and after reoxidation due to occlusion of P within ferric oxyhydroxides formed.