不同水平硼对棉花体内硼含量及其分布的影响

本试验在盆栽条件下,以灰紫色土为供试土壤,研究不同水平硼(表1)下,棉花(Gossypium hirsutum,品种“鄂沙28”)体内硼含量及其分布规律。结果如下: 1.棉花不同生育期各器官含硼量随土壤有效硼的增加呈直线增加(图1),除铃期根系外,其相关系数均     

中国鱼类硼本底含量调查研究

了解中国鱼类中硼的本底含量,为科学监管违法添加提供科学依据。方法：2013年在渤海、黄海、东海、南海以及内陆地区的捕捞、养殖环节采集鲜活鱼类样品,应用电感耦合等离子体质谱（ICP-MS）法检测样品中的硼含量。结果：共采集鱼类样品560份,硼检出率为100%,硼含量平均值为0.47mg/kg,中位数为0.37mg/kg,最小值和最大值分别为0.03、3.96mg/kg。水域性质、采样地区和生产模式都是影响鱼类中硼含量的重要因素。结论：建议将2.58mg/kg作为鱼类中硼含量的本底值。     

湖南烟区烤烟(Nicotiana tabacum L.)硼含量与土壤有效硼含量的关系

分析湖南烟区烤烟硼含量与土壤有效硼含量的关系,结果表明：（1）湖南烟叶硼含量偏低,平均为（21.72±12.98）mg/kg,变幅为9.22-89.04mg/kg,有88.89%的烟叶样本硼含量落在10.00-40.00mg/kg范围内;（2）湖南植烟土壤有效硼含量较低,平均为（0.25±0.23）mg/kg,变幅较大（0.07-1.28mg/kg）;有93.40%的土壤样本在不同程度上缺硼（≤0.40mg/kg）,另有4.51%的土样有效硼含量充足（〉1.0mg/kg）,满足优质烟叶生长发育正常的土样仅占2.09%;（3）烟叶硼含量与土壤有效硼含量呈极显著正相关（相关系数为0.745）,288个样品的烟叶硼含量（y^）与土壤有效硼含量（x）建立的回归方程为y^=11.47＋41.71x;（4）在土壤有效硼含量分组后,采用方差分析方法研究了烟叶化学成分的组间差异,表明烟碱、氮/碱、糖/碱的组间差异均达到1%的极显著水平,而总氮、总糖含量的组间差异不显著。     

施硼对番木瓜幼龄株硼形态含量及叶片光合作用的影响

探讨根外喷硼与土壤施硼对植株硼形态含量及叶片光合作用的影响。结果表明,两种供硼方式均可增加植株叶片、叶柄及根的硼形态含量及硼总量,其中以叶片水溶态硼、半束缚态硼及硼总量的增加最为显著。植株硼含量增加提高了叶片净光合速率,但硼过量却抑制了叶片光合能力的提升,而硼中毒导致光合能力显著下降。     

土壤水分和供硼状况对不同硼效率油菜苗期生长、水分含量和硼形态的影响

通过土培试验,研究了土壤水分和供硼状况对不同硼效率油菜苗期生长、叶片水分含量和硼形态的影响.结果表明:低水分胁迫条件下,硼高效甘蓝品种和硼低效甘蓝品种在高供硼水平下的单株鲜质量比低供硼水平分别增加了43.1%和31.7%,但品种间没有显著差异;硼高效品种在两种供硼水平下的束缚态水分含量分别比低效品种高11.4%和1.7%,半束缚态硼分配比例分别比低效品种高6.9%和23.8%.正常水分条件下,硼高效甘蓝品种和硼低效甘蓝品种在高供硼水平下的单株鲜质量比低供硼水平分别增加了11.1%和27.4%;硼高效品种在两种供硼水平下的自由态水分含量较硼低效品种多,自由态硼累积量为低效品种的2倍多,这有利于硼在高效植物体内的移动运输.     

不同硼效率甘蓝型油菜品种细胞壁中硼的分配

应用不同硼效率甘蓝型油菜品种 ,研究硼在细胞壁中的分配。硼主要结合在细胞壁中 ,缺硼显著提高硼在细胞壁中的分配比例。根系细胞壁硼含量显著低于叶片 ,但根系细胞壁硼占根系总硼量之比例显著高于叶片。同一品种根系及其细胞壁、老叶细胞壁硼含量受生育期影响较小 ,新叶及其细胞壁、老叶硼含量受生育期影响较大。在正常供硼条件下 ,硼高效品种根系细胞壁和叶片细胞壁硼含量均低于低效品种 ;正常和缺硼条件下 ,硼高效品种细胞壁硼占器官总硼量之比例均低于低效品种。说明硼低效品种需较多的硼构建细胞壁。     

施硼对圆叶决明植株生长、养分含量及固氮能力的影响

设立田间小区试验,探讨在红壤中施用不同浓度的硼肥对圆叶决明(Chamaecrista rotundifolia)植株生长、牧草品质和根瘤固氮能力的影响。结果表明,施用1.5、3.0和4.5kghm-2硼肥(B)处理的植株分枝数、根部重和植株生物产量分别比对照提高15.7%-36.7%、251%-493%和7.2%-34.2%,其中以施B1.5kghm-2的处理较为适宜。施1.5、3.0和4.5kghm-2硼处理的植株全氮、全磷和全钾的含量分别比对照提高8.80%-31.38%、10.37%-31.26%和18.4%-37.9%,粗蛋白、粗脂肪、粗纤维和氨基酸的含量分别提高8.80%-31.38%、15.6%-65.4%、10.5%-33.7%和1.43%-42.60%,其中也以1.5kghm-2的田间施硼量的效应最佳,适当施用硼肥有利于圆叶决明植株对营养物质的吸收与累积。施硼量为4.5kghm-2时,植株的硼含量最高;施B3.0kghm-2处理的植株根瘤重、根瘤数和根瘤固氮酶活性均达到最大值。综合评价的结果表明,1.5kghm-2B是本试验条件下较佳的硼用量。     

施硼与作物增产

我国某些农作物和果树,有时会出现一些特殊的症状,例如：油菜“花而不实”,棉花“蕾而不花”,小麦“不穗”,苹果、柑桔结“石头果”（又称缩果病）,芹菜生“茎裂病”等,严重地损害作物的生长发育,造成低产。这些是什么原因引起的呢？原来,它们都是患了硼——一种微量营养元素——缺乏症,只要施用少量的硼肥（每公顷1500～7500g）,就可以防治,并使作物大幅度增产。有时候,作物虽不出现上述症状,但产量不高,通常叫做“潜在性”缺硼,施用硼肥可使作物增产一成左右。由于施用硼肥用量少,方法简便,增产多,收益大,所以这一措…     

不同土壤水分状况下施硼对油菜硼吸收、利用的影响

1　引　　言我国是油菜生产大国 ,也是一个土壤缺Ｂ面积较大的国家 .由于油菜缺Ｂ问题突出 ,施用Ｂ肥已成为提高油菜产量、改善品质的重要措施[2 ,3 ,11] .但是 ,Ｂ肥的施用不但存在成本高、难度大、效率低的问题 ,而且也存在造成环境污染的可能性[9] .研究表明[8,10 ] ,不同油菜品种对缺Ｂ的反应存在基因型差异 ,因此 ,筛选、培育Ｂ营养高效基因型油菜以适应缺Ｂ土壤环境是解决油菜缺Ｂ问题的最有效途径之一 .植物对土壤中Ｂ的吸收、运输及利用因土壤水分状况而异[4 ,5] .研究不同水分条件下尤其是干旱情况下Ｂ素营养对油菜Ｂ营养效率的影…     

植物缺硼的生理伤害

硼在作物体内能以3种不同的形式与富羟基化合物络合,文章介绍近10年来有关缺硼引起植物细胸避结构改变,膜透性变化,糖运输受阻,相关酶活性变化,有毒物质积累等一系列生理伤害和机制等方面的研究进展。     

Redistribution of boron in leaves reduces boron toxicity

High soil boron (B) concentrations lead to the accumulation of B in leaves, causing the development of necrotic regions in leaf tips and margins, gradually extending back along the leaf. Plants vary considerably in their tolerance to B toxicity, and it was recently discovered that one of the tolerance mechanisms involved extrusion of B from the root. Expression of a gene encoding a root B efflux transporter was shown to be much higher in tolerant cultivars. In our current research we have shown that the same gene is also upregulated in leaves. However, unlike in the root, the increased activity of the B efflux transporter in the leaves cannot reduce the tissue B concentration. Instead, we have shown that in tolerant cultivars, these transporters redistribute B from the intracellular phase where it is toxic, into the apoplast which is much less sensitive to B. These results provide an explanation of why different cultivars with the same leaf B concentrations can show markedly different toxicity symptoms. We have also shown that rain can remove a large proportion of leaf B, leading to significant improvements of growth of both leaves and roots.Key words: Bor genes, boron tolerance, boron toxicity, efflux pumping, leaf necrosis, membrane transportB-toxic soils are widespread throughout agricultural areas of the world where they cause significant and often substantial reductions in crop quality and yield. The mechanism by which B is toxic to plants is not well understood¹ but toxicity symptoms include reduced root growth which affects uptake of water and nutrients, and the development of necrotic patches on leaves which impairs photosynthesis. Tolerance to B toxicity has been recognized in a number of crops, notably in cereals. In most cases, tolerance is achieved by reduced uptake of B into the root, which then leads to reduced uptake into the shoot. Genetic studies established that in barley, a locus associated with reduced tissue B occurred on chromosome 4 and that this locus could be transferred to other barley cultivars with desirable agronomic traits.²Hayes and Reid³ made a careful study of the characteristics of B uptake in a highly tolerant landrace barley cultivar Sahara, and found that although B was highly permeable, the root B concentration in this cultivar could be maintained at only half that in the external medium, whereas in sensitive cultivars, B was the same in both intracellular and extracellular phases. It was concluded that tolerant cultivars must have a membrane active transporter that exports B from the root. A B exporter, AtBor1 had previously been discovered in Arabidopsis where it was involved in B loading into the xylem⁴ but it was later found to be degraded under high B conditions⁵ and therefore would not be useful in B tolerance.However, other Bor1 homologues were subsequently discovered in Arabidopsis and in rice. Based on homology with rice, Reid⁶ cloned genes from barley and from wheat (HvBor2 and Tabor2 respectively) which were shown to be strongly upregulated in roots of tolerant cultivars, and virtually undetectable in sensitive cultivars. Thus, a simple mechanism to explain tolerance was established; efflux of B from the root reduced the intracellular concentration of B in the root cells, thereby reducing toxicity and improving root growth. At the same time, the lower root content meant that less B was transferred to the shoot, resulting in lower shoot toxicity.Yet there remained several unanswered questions regarding B toxicity. Firstly, it was commonly observed that toxicity symptoms were not reliably correlated with leaf B concentration, and that often after rain, toxicity symptoms became less severe. Nable et al.⁷ had investigated the effect of rain on shoot B concentrations and concluded that although rain did reduce the B concentration in leaves, it did not affect growth and yield. Secondly, field trials with cultivars in which the B tolerance traits were expressed, did not show the improvements in growth and yield that could be observed in glasshouse trials.^8,9Our recent work¹⁰ has provided new insights into these phenomena. Sensitive and tolerant cultivars of both wheat and barley were grown in varying levels of B. Then, ignoring the level of B in the growth solution, leaves of the different cultivars that displayed the same degree of leaf necrosis were selected. This revealed that in the tolerant cultivars, necrosis began to appear at leaf B levels that were two-to five-fold higher than in sensitive cultivars. Since no internal tolerance mechanism had been reported, it was hypothesised that in the tolerant cultivars, internal toxicity was reduced by pumping B from the cytoplasm into the cell wall where B is much less toxic. To prove this hypothesis three types of experiment were conducted. Firstly protoplasts were isolated from leaves of tolerant and sensitive cultivars of barley, and it was shown that when incubated in the same concentration of B, the tolerant cultivar was able to reduce the intracellular B concentration to approximately half that of the sensitive cultivar. Secondly, it was reasoned that if more B was accumulated in the apoplast of the tolerant cultivar, then it should be more quickly released by washing of the leaf; this was confirmed. Thirdly, it was shown that the same efflux transporters that were responsible for B export from the root were also highly expressed in leaves of tolerant cultivars of wheat and barley. The combination of these three experiments provided compelling evidence that redistribution of B in the leaf was a significant factor in B tolerance.The elution experiment also highlighted the fact that because B is highly soluble and has high membrane permeability, it can easily be washed from leaves. Obviously in the field B could be removed from leaves by rain, but no positive effect of this on growth had been quantified. In our experiments, we simulated the average rainfall during the early growing season in a high B region of Southern Australia by spraying plants with calibrated amounts of water for 16 d. At high B concentrations, rain reduced leaf B by around 50% while simultaneously improving growth of shoots by up to 90%. Rather surprisingly, the rain treatment, which had no significant effect on root B concentrations, caused a two-fold increase in root growth, presumably by improving the supply of photosynthate from the shoot.This study has enabled an evaluation of the importance of three main factors in determining the severity of B toxicity; two genetically determined processes, efflux pumping of B in roots and leaves, coupled with the variable leaching of B from leaves by rain (Fig. 1). The results also provide an explanation for the poor correlations observed between toxicity and shoot B concentrations in cereals.^7,11Open in a separate windowFigure 1Summary of processes contributing to reduced B toxicity in wheat and barley. The intensity of shading indicates the level of B in different regions of the plant. Boron (B) enters the leaf via the xylem and continues to accumulate as the leaf grows. When plants are grown in high concentrations of B, the older parts of the leaf become necrotic first while the younger basal tissues continue to expand. In tolerant cultivars, B efflux transporters in leaves pump B from the cytoplasm where it is toxic into the cell walls where it can be tolerated at high concentrations. Sensitive cultivars have a very low capacity for B efflux and therefore retain much higher concentrations inside the cell than in tolerant cultivars. rain can remove large amounts of B from leaves, thereby alleviating toxicity. In roots of tolerant cultivars, the same B efflux transporters that occur in leaves are used to pump B from the cells into the external medium. This reduces the toxicity to roots and limits the amount of B entering the xylem and reaching the leaves.     

Relation of solute and sorbed boron to the boron hazard in irrigation water

Summary The current criteria for evaluating the boron (B) hazard of irrigation water for specified crops are based on the concentration of B in the irrigation water without consideration of soil properties or the leaching fraction. Experiments were conducted to determine the influence of B sorption capacity on plant uptake of B at rates of 0.1, 2.5, 5.0 and 10.0 ppm B in the irrigation water with a leaching fraction of 0.5. A relatively B sensitive crop, oats (Avena sativa), was grown on four arid-region soils of varying B sorption capacities. The results show that B in solution rather than sorbed B influenced B toxicity. Contribution from the Department of Soils, Water and Engineering, The University of Arizona, Tucson, Arizona 85721. Arizona Agricultural Experiment Station No. 2508. Research Associates and Associate Professor, respectively. The senior author is currently at the Department of Soils and Irrigation, American University of Beirut Beirut, Lebanon.     

Distribution of boron in the environment

The findings of a study to identify and quantify the orders of magnitude for major reservoirs and flows of boron (B) in the environment are outlined. The orders of magnitude for B reservoirs and flows arising through natural processes, such as the hydrological cycle and volcanism, are compared with those arising from anthropogenic activities, such as coal combustion and the extraction and use of borates for commercial purposes. The major stores and reservoirs for B have been identified, in order of magnitude, as the continental and oceanic crusts (10¹⁸ kg B), the oceans (10¹⁵ kg B), groundwater (10¹¹ kg B), ice (10¹¹ kg B), coal deposits (10¹⁰ kg B), commercial borate deposits (10¹⁰ kg B), biomass (10¹⁰ kg B), and surface waters (10⁸ kg B). The largest flows of B in the environment arise from the movement of B into the atmosphere from oceans, at between 1.3 * 10⁹ kg and 4.5 * 10⁹ kg B per annum. Other hydrological flows are also important. Drainage from soil systems into groundwaters and surface waters accounts for between 4.3 * 10⁸ kg and 1.3 * 10⁹ kg B per annum. B mining and volcanic eruptions represent the next most significant B flows, accounting for approx 4.0 * 10⁸ kg and 3.0 * 10⁸ kg B, respectively.     

A review of boron effects in the environment

Boron (B) is a naturally occurring element that is found in the form of borates in the oceans, sedimentary rocks, coal, shale, and in some soils. Borates are released naturally into the atmosphere and aquatic environment from oceans, geothermal steams, and weathering of clay-rich sedimentary rocks. B is also released to a lesser extent from anthropogenic sources. B concentrations in air range from <0.5 to 80 ng/m³ with an average of 20 ng/m³, and in soils from 10 to 300 mg/kg with an average of 30 mg/kg. Concentrations of B in surface freshwaters are typically < 0.1–0.5 mg/L; much higher concentrations are measured in a few areas, depending on the geochemical nature of the drainage catchment. B accumulates in both aquatic and terrestrial plants, but it does not appear to be biomagnified through the food chain. No observed effect concentrations (NOECs) for aquatic invertebrates tend to be in the range of 6–10 mg B/L with lower values of 1–2 mg/L for community studies. No effect concentrations for fish in natural waters are around 1 mg/L, although lower values have been recorded in reconstituted water. Comparing no effect concentrations with the general ambient environmental levels indicates that the risk to aquatic ecosystems from B is low. In a few B-rich areas, natural levels will be higher; however, there is some indication that organisms may be Actapted to the local conditions. B is an essential micronutrient for higher plants with interspecies differences in the levels required for optimum growth. In general, there is a small concentration range between deficiency and toxicity; however, toxicity owing to excess B is much less common in the environment than B deficiency. Levels of B in aquatic plants growing in areas receiving B-rich runoff from irrigated fields are higher than dietary concentrations, which cause effects on the growth of young birds in the laboratory; however, the bioavailability in the field of such plant-accumulated B is uncertain.     

Nitrogen-induced boron deficiency in lucerne

Summary In a glasshouse experiment with a boron deficient soil the application of nitrogen was found to decrease the boron concentration and boron uptake by lucerne (Medicago sativa). Without added boron, nitrogen applications killed the lucerne, probably by inducing severe boron deficiency. With added boron, the lowest rate of nitrogen application increased lucerne yield but further additions depressed yields. The effect was due to a physiological interaction rather than an effect of the nitrogen on the availability of the boron in the soil.     

Characteristics of root boron nutrition confer high boron efficiency in Brassica napus cultivars

Background and aims

Brassica napus has high boron (B) demand, but significant genotype differences exist with respect to B deficiency. The aim of this research was to elucidate the relationship between the different sensitivities of Brassica napus cultivars to low B stress and the characteristics of B uptake and transport to characterise the regulation of B efficiency in Brassica napus.

Methods

B-efficient and B-inefficient Brassica napus cultivars were used to compare the uptake and transport of B using the stable isotope ¹⁰B tracer and grafting experiments, as well as expression of B transporters by RT-PCR.

Results

B-efficient cultivars have significant advantages with regard to B limitation. The B-efficient cultivar HZ showed less severe B deficiency symptoms and higher dry biomass than the B-inefficient cultivars LW and LB. Both the amount of total B and the ¹⁰B concentration and accumulation in the shoots and roots of B-efficient HZ were higher than those of B-inefficient cultivars. In B-inefficient LW, the amount of total B and the ¹⁰B that was transported into shoots was less than in the other three cultivars and the content and accumulation of total B and ¹⁰B in the roots of B-inefficient LB were the lowest among all of the cultivars. When the roots of B-efficient HZ were used as stocks, the grafted plants showed B-efficient characteristics, such as mild B deficiency symptoms, and higher dry biomass and B accumulation, regardless of whether they originated from B-efficient or B-inefficient cultivars. In contrast, the grafted plants with B-inefficient LW used as stocks were B-inefficient. The expressions of BnBOR1;1c, BnBOR1;2a and BnNIP5;1 were up-regulated in roots under low B stress compared with the normal B condition. However, there was no obvious difference in the expressions of the three genes or of four other BnBOR1s between B-efficient and B-inefficient cultivars in low or normal B environments.

Conclusions

These results indicate that the B efficiency of Brassica napus is controlled primarily by roots, which allow more uptake and accumulation of B in B-efficient cultivars than B-inefficient cultivars in a low B environment. However the molecular mechanism regulating B efficiency in Brassica napus remains to be determined.     

Enhanced boron transport into the ear of wheat as a mechanism for boron efficiency

Genotypic variation in boron (B) efficiency in wheat (Triticum aestivum L.) is expressed as large differences in grain set and pollen fertility under low soil B, but the mechanisms responsible for such differences are unknown. This paper aims to determine whether differences in B transport and retranslocation can explain cultivar differences in B efficiency between B-efficient (Fang 60) and B-inefficient (SW41) wheat cultivars. Plants were grown with adequate ¹¹B (10 μM), until the premeiotic interphase stage in anther development, then transferred into ¹⁰B at 0.1 or 10 μM. After five days, ending at the young microspore stage, plants were returned to adequate ¹¹B. Plants were harvested at 0, 1 and 5 days after transferring into ¹⁰B, and at anthesis when fresh pollen was examined for viability. After 5 days in 0.1 μM B, pollen viability in SW41 was depressed by 47%, but pollen of Fang 60 was not affected. When B supply was low, the proportion of plant B partitioned into the ear of Fang 60 was almost twice as high as that in SW 41, enabling Fang 60 to maintain B concentration in the ear at 6.8 mg kg^?1 dry weight (DW), whereas it dropped to 3.8 mg kg^?1 DW in SW 41. Boron accumulation in the ear, when external supply was restricted, did not come from the ¹¹B previously taken up by the plant. The greater ¹⁰B accumulation in ears of Fang 60 compared to SW 41, with limited external B supply, indicated that B efficiency was associated with xylem transport of B. The greater increase of ¹⁰B:¹¹B ratio in the ear of Fang 60 compared to SW 41, over the 5 days of B interruption further indicated that greater B efficiency was associated with a stronger capability for long distance transport of B from the rooting medium into the ear via the xylem rather with than retranslocation of B from vegetative parts.     

Translocation and effectiveness of foliar-fertilized boron in broccoli plants of varying boron status

The translocation and effectiveness of foliar-fertiilized boron (B) was investigated in broccoli plants supplied via the root system with luxury, sufficient or deficient levels of B. ¹⁰B-enriched boric acid was applied three times to lower leaves, beginning one week prior to inflorescence emergence, and the shoot and floret yields, as well as the ¹⁰B and ¹¹B contents or concentrations of xylem sap, phloem exudate and various plant parts, were determined three weeks after inflorescence emergence. The amount of ¹⁰B translocated in phloem from fed leaves to the remainder of the shoot did not exceed 0.5%, of that supplied, but it was inversely related to plant-B status. The partitioning of translocated ¹⁰B to florets (16–30%) and the degree of enhancement in floret yield (28–75%) was also inversely related to plant-B status. It is concluded that foliar-B fertilization may be more effective for preventing B deficiency than soil-derived B in leaves.Abbreviations ¹⁰B/¹¹B mass isotopes of boron - DM dry matter - FF foliar fertilization - RF root fertilization