赤红壤蔗区11年连续增量施磷下磷素演变及其 对甘蔗产量与磷流失的影响

【目的】 系统分析连续11年增量施磷下赤红壤蔗地土壤全磷、Olsen-P以及地表径流磷流失量的变化特征和土壤磷素变化与磷盈亏、蔗茎产量的响应关系,为土壤磷素科学管理提供参考。【方法】 依托长期肥力及地表径流定位监测试验（2008年—）,选取不施肥（CK）、推荐施肥（OPT）和增量施磷（OPT+P）3个处理,测定土壤全磷、Olsen-P含量及地表径流磷流失量,分析土壤磷素变化与磷累积盈亏量的关系,采用Mitscherlich模型拟合蔗茎产量对Olsen-P的响应曲线,计算土壤Olsen-P农学阈值,并推算施肥处理土壤Olsen-P含量从第11年降至环境阈值所需的时间。【结果】 CK处理逐年降低土壤全磷含量,年降速率为0.0251 g·kg ^-1·a ^-1。施肥土壤全磷和Olsen-P含量随种植年限波动增加,土壤全磷和Olsen-P增速率OPT+P处理高于OPT处理。不施肥土壤表观磷盈亏10.2 kg·hm ^-2·a ^-1,施肥处理土壤表观磷盈余41.3—69.2 kg·hm ^-2·a ^-1,占施磷量的31.9%—35.6%,以OPT+P处理显著高于OPT处理67.5%。施肥下赤红壤蔗区土壤全磷和Olsen-P变化量均与土壤累积磷盈亏量呈显著正相关关系（P＜0.01）,土壤每累积盈余100 kg P·hm ^-2,OPT处理和OPT+P处理土壤全磷上升0.06 g·kg ^-1和0.09 g·kg ^-1,Olsen-P 含量上升11.0 mg·kg ^-1和9.1 mg·kg ^-1。土壤每累积亏缺100 kg P·hm ^-2,CK处理土壤全磷下降0.32 g·kg ^-1。Mitscherlich模型较好地拟合蔗茎产量与赤红壤Olsen-P含量的响应关系（P＜0.01）。其计算出的土壤Olsen-P 农学阈值为12.1 mg·kg ^-1。施肥显著提高地表径流磷流失量,且OPT+P处理也显著高于OPT处理。地表径流磷流失量与土壤Olsen-P含量显著正相关。基于土壤磷素变化与累积磷盈亏的关系推算得出第11年OPT和OPT+P处理Olsen-P水平降至环境阈值的时间分别需要12年和16年。 【结论】 在南方赤红壤区,施肥尤其增量施磷在提高土壤磷素累积的同时增加了地表径流磷流失风险。在本试验磷的基础养分条件下,按OPT处理施磷,并从甘蔗种植的第2—3年实行隔年施磷可维持土壤磷素处于农学阈值与环境阈值之间。     

长期施肥下黄土旱塬黑垆土磷平衡及农学阈值

为研究长期施肥条件下土壤磷平衡和土壤有效磷对磷盈亏的响应,明确土壤有效磷(Olsen-P)的农学阈值及合理磷肥施用量,依托甘肃平凉肥料长期定位试验(始于1979),分析了黄土旱塬黑垆土36 a土壤磷盈亏动态、累积磷盈亏与有效磷的响应关系以及土壤磷残余,通过Mitscherlich方程模拟作物相对产量对土壤有效磷的响应关系,计算黄土旱塬黑垆土小麦和玉米的土壤有效磷农学阈值。结果表明:不施肥(CK)和单施氮肥(N)处理土壤磷始终亏缺,N处理每亏缺磷100 kg·hm~(-2),有效磷含量下降1.05 mg·kg~(-1);施磷处理土壤磷当季盈余4.3～207.9 kg·hm~(-2),累积盈余154.9～7 483.6 kg·hm~(-2),其中有机、无机配施(MNP)处理磷盈余最大;土壤累积磷盈余与土壤有效磷增量呈线性正相关,土壤中每盈余100 kg·hm~(-2)磷,秸秆还田配施化肥(SNP,磷肥隔年施)、氮磷配施(NP)、有机肥(M)和有机、无机配施(MNP)处理土壤有效磷分别增加7.55、2.47、0.28 mg·kg~(-1)和0.46 mg·kg~(-1);黄土旱塬黑垆土农田有效磷的小麦和玉米农学阈值分别为22.05 mg·kg~(-1)和13.96 mg·kg~(-1),MNP处理土壤有效磷含量已高于作物农学阈值,NP和SNP处理土壤有效磷含量达到小麦农学阈值分别需要21 a和24 a,达到玉米农学阈值分别需要2 a和8 a,M处理土壤有效磷含量已高于玉米农学阈值,还需要3 a可达到小麦农学阈值。当磷投入量每年平均达22.9 kg·hm~(-2)时,土壤磷呈持平状态;当磷用量达33 kg·hm~(-2)时,不仅作物产量较高,而且磷肥当季利用率也较高;当磷用量增加到233 kg·hm~(-2)时,作物产量对增加磷投入无响应,土壤磷残余超过90%,大量磷素累积在土壤中,增加了土壤磷素的流失风险。黄土旱塬小麦玉米一年一熟轮作黑垆土农田土壤有效磷农学阈值为13.96 mg·kg~(-1)(玉米)和22.05 mg·kg~(-1)(小麦),秸秆还田可促进旱地农田耕层土壤有效磷含量的增加。     

施肥与覆膜对棕壤Olsen-P剖面分布及动态变化的影响

利用沈阳农业大学长期定位试验站裸地和覆膜的不同施肥处理（不施肥、单施氮肥、有机肥、有机无机肥配施）及其附近不同土地利用方式，探讨了不同施肥处理和覆膜对整个生长季的棕壤Olsen-P剖面（0—100 cm）分布及动态变化的影响。结果表明，耕地棕壤各施肥处理土壤剖面Olsen-P含量均表现为0—20 cm和60—100 cm大于20—60 cm；而自然草地、自然林地棕壤Olsen-P含量则随深度加深（0—100 cm）而逐渐增多。施用有机肥或有机无机肥配施处理的Olsen-P含量在60 cm土层以上均远大于不施肥或单施氮肥处理；覆膜后不施肥、有机肥、有机无机肥配施处理土壤0—40 cm土层的Olsen-P含量略有降低（0—20 cm土层有机肥处理除外），但差异未达到显著水平。说明施有机肥或有机无机肥配施，是补充土壤Olsen-P的有效措施；但施肥时应深施以补充表层以下土壤Olsen-P含量。覆膜未对本研究的棕壤Olsen-P含量产生显著的负面影响。     

种植年限对设施菜田土壤剖面磷素累积特征的影响

以山东寿光集约化设施菜田为研究对象,分析了不同种植年限设施菜田土壤磷素投入和土壤磷素累积的差异,比较不同种植年限土壤剖面中无机磷、有机磷、Olsen-P和CaCl2-P含量的变化特征。结果表明：磷素过量积累是设施菜田的显著特征,主要由于有机肥以粪肥投入为主,复合肥中P素比例偏高,收获作物带走量仅占磷素投入的7.2%;随着种植年限增加,P素累积现象明显,过量的磷素盈余导致了土壤剖面中不同形态磷含量的上升,其中以无机磷尤其明显;用来表征土壤有效磷指标的Olsen-P与CaCl2-P有显著的相关性,研究区域中当土壤（Olsen-P）达到80.7mg·kg-1时,土壤CaCl2-P开始显著升高,增大了设施菜田磷素淋溶风险。     

Interactions between phosphorus availability and microbes in a wheat–maize double cropping system: A reduced fertilization scheme

Mechanisms controlling phosphorus (P) availability and the roles of microorganisms in the efficient utilization of soil P in the wheat–maize double cropping system are poorly understood.  In the present study, we conducted a pot experiment for four consecutive wheat–maize seasons (2016–2018) using calcareous soils with high (30.36 mg kg^–1) and low (9.78 mg kg^–1) initial Olsen-P content to evaluate the effects of conventional P fertilizer application to both wheat and maize (Pwm) along with a reduced P fertilizer application only to wheat (Pw).  The microbial community structure along with soil P availability parameters and crop yield were determined.  The results showed that the Pw treatment reduces the annual P input by 33.3% without affecting the total yield for at least two consecutive years as compared with the Pwm treatment in the high Olsen-P soil.  Soil water-soluble P concentrations in the Pw treatment were similar to those in the Pwm treatment at the 12-leaf collar stage when maize requires the most P.  Furthermore, the soil P content significantly affected soil microbial communities, especially fungal communities.  Meanwhile, the relative abundances of Proteobacteria and alkaline phosphatase (ALP) activity of Pw were significantly higher (by 11.4 and 13.3%) than those of Pwm in soil with high Olsen-P.  The microfloral contribution to yield was greater than that of soil P content in soil with high Olsen-P.  Relative abundances of Bacillus and Rhizobium were enriched in the Pw treatment compared with the Pwm treatment.  Bacillus showed a significant positive correlation with acid phosphatase (ACP) activity, and Rhizobium displayed significant positive correlations with ACP and ALP in soil with high Olsen-P, which may enhance P availability.  Our findings suggested that the application of P fertilization only to wheat is practical in high P soils to ensure optimal production in the wheat and maize double cropping system and that the soil P availability and microbial community may collaborate to maintain optimal yield in a wheat–maize double cropping system.     

基因组学在作物抗逆性研究中的新进展

自然环境中各种生物和非生物胁迫是影响作物产量的巨大威胁。随着现代分子生物学的发展,从分子水平研究作物抵御逆境的机理已成为生态农业研究的一个重要任务,分子遗传学与生态学的整合诞生了生态基因组学即用基因组学的技术和手段研究生态学领域的问题。基因组学按其研究内容分为功能基因组学、结构基因组学和比较基因组学,本文从这3方面分别阐述了作物抵抗生物胁迫和非生物胁迫的生态基因组学研究进展,总结了基因组学在植物抗逆性研究中的一些新技术和新手段,特别是基于近几年发展起来的二代深度测序所带来的一系列高通量的检测方法与结果。①功能基因组学包含转录组学、表观遗传学、蛋白组学、相互作用组学、代谢组学和表型组学,本文侧重从植物抗逆的功能基因表达水平上的研究展开,重点探讨了转录组学和表观遗传学在植物抗逆研究的新进展,介绍了一些转录组学和表观遗传学研究技术,如基因芯片技术、RNA测序技术、SAGE、cDNA-AFLP、SSH、亚硫酸盐法、ChIP-Chip、ChIP-seq等;例举了一些转录因子基因家族在植物抗逆反应中的作用,总结其作用共性,结果表明不少抗逆基因受到胁迫后基因转录激活上有一定相关性,大多受激素信号转导途径所调控,很多抗逆途径最终都涉及到ABA信号传导通路并与衰老相关;植物的抗逆性受多个信号通路调控,对同一逆境响应常常需要不同的转录因子共同参与,而同一转录因子也有可能参与2个以上的不同抗逆反应;表观遗传学则指在不改变基因序列前提下,对DNA甲基化修饰、组蛋白翻译后修饰及小RNA介导的信号传导等,有证据表明其存在遗传印记作用。②结构基因组学主要利用QTL定位和DNA测序技术,确定植物基因组的遗传图谱和物理图谱,二代深度测序平台的建立使许多植物的全基因组测序成为可能。迄今为止,已有超过40种植物完成全基因组测序,越来越多的植物全基因组计划正在实施中或预计实施。③比较基因组学是基于功能基因组学和结构基因组学进而比较不同物种或不同群体间的基因组差异和相关性的研究,可分析逆境响应相关基因在进化过程中及在地理位置分布中的作用和意义,也同时为QTL定位及功能基因组学研究提供丰富信息。此外,还简要介绍并列举了一些网络共享作物抗逆的生物信息资源数据库。虽然基因组学在如何正确处理海量数据等问题上还存在瓶颈,但它提供的大量作物抗逆方面的基因组信息已为植物抗逆研究提供了众多线索与依据,为今后改良作物抗逆性的遗传育种工作带来了新启示。     

福建菜田氮磷积累状况及其淋失潜力研究

本文通过采集460个福建菜田代表性耕层土样,采用土壤测试和土柱渗漏水模拟试验的方法研究菜田土壤硝态氮和Olsen P含量状况和淋失临界指标及其淋失潜力。结果表明,耕层土壤硝态氮含量为47.455.5 mg/kg,Olsen-P含量则为61.743.2 mg/kg, 其中瓜果类蔬菜种植地土壤硝态氮和Olsen-P含量明显高于叶菜类和根茎类蔬菜种植地。 应用双速率转折点建模法,得到氮、 磷淋失临界指标X0分别为土壤硝态氮76.3 mg/kg和Olsen-P 42.8 mg/kg。 淋失临界值相当于或略高于满足蔬菜营养的农学指标。当土壤硝态氮或Olsen-P含量低于X0时,随着其含量增加,渗漏水硝态氮或总磷浓度以线性方式缓慢增加,反之,则以非线性形式急剧增大。土壤硝态氮和Olsen-P含量高于其X0的土样数分别占17.9%和81.3%, 表明这些样点具有较高的氮、 磷淋失潜力,是氮、 磷污染控制的关键地块。 瓜果类菜田土壤硝态氮和Olsen-P含量高于其X0的土样数分别占到32.3%和96.3%,淋失潜力明显高于叶菜类和根茎类菜田,是氮、 磷污染控制的优先区域。     

An evaluation of the Olsen test as a measure of plant-available phosphorus in grassland soils derived from basalt parent material

Abstract. Anecdotal and circumstantial evidence have suggested that the Olsen test underestimates plant-available phosphorus (P) in basaltic soils in Northern Ireland. Therefore, the ability of this test to predict plant-available P in basaltic (and non-basaltic) soils was investigated by regressing Olsen-P data against herbage P indices calculated from plant tissue test data using the diagnosis and recommendation integrated system. The average Olsen-P concentration for a range of fields situated on basaltic soils was considerably lower than the average Olsen-P concentration for a range of fields situated on non-basaltic soils, and yet mean sward P status, as given by the herbage P indices, was similar for both groups of fields. Herbage P indices were also much better correlated with Olsen-P measurements in non-basaltic soils than in basaltic soils. Furthermore, at low Olsen-P values (≶9mgPL⁻¹) some swards on basaltic soils were genuinely deficient in P, while others were sufficient or even in surplus for this nutrient. The results confirm that Olsen-P is inadequate as a predictor of plant-available P in basaltic soils. It is concluded that an alternative soil test is needed to provide a reliable assessment of plant-available P in basaltic soils, to prevent overuse of fertilizer and manure P and to minimize the amounts of P entering local watercourses.     

Response of soil Olsen-P to P budget under different long-term fertilization treatments in a fluvo-aquic soil

The concentration of soil Olsen-P is rapidly increasing in many parts of China, where P budget(P input minus P output) is the main factor influencing soil Olsen-P. Understanding the relationship between soil Olsen-P and P budget is useful in estimating soil Olsen-P content and conducting P management strategies. To address this, a long-term experiment(1991–2011) was performed on a fluvo-aquic soil in Beijing, China, where seven fertilization treatments were used to study the response of soil Olsen-P to P budget. The results showed that the relationship between the decrease in soil Olsen-P and P deficit could be simulated by a simple linear model. In treatments without P fertilization(CK, N, and NK), soil Olsen-P decreased by 2.4, 1.9, and 1.4 mg kg~(–1) for every 100 kg ha~(–1) of P deficit, respectively. Under conditions of P addition, the relationship between the increase in soil Olsen-P and P surplus could be divided into two stages. When P surplus was lower than the range of 729–884 kg ha~(–1), soil Olsen-P fluctuated over the course of the experimental period with chemical fertilizers(NP and NPK), and increased by 5.0 and 2.0 mg kg~(–1), respectively, when treated with chemical fertilizers combined with manure(NPKM and 1.5 NPKM) for every 100 kg ha~(–1) of P surplus. When P surplus was higher than the range of 729–884 kg ha~(–1), soil Olsen-P increased by 49.0 and 37.0 mg kg~(–1) in NPKM and 1.5 NPKM treatments, respectively, for every 100 kg ha~(–1) P surplus. The relationship between the increase in soil Olsen-P and P surplus could be simulated by two-segment linear models. The cumulative P budget at the turning point was defined as the "storage threshold" of a fluvo-aquic soil in Beijing, and the storage thresholds under NPKM and 1.5 NPKM were 729 and 884 kg ha~(–1)P for more adsorption sites. According to the critical soil P values(CPVs) and the relationship between soil Olsen-P and P budget, the quantity of P fertilizers for winter wheat could be increased and that of summer maize could be decreased based on the results of treatments in chemical fertilization. Additionally, when chemical fertilizers are combined with manures(NPKM and 1.5 NPKM), it could take approximately 9–11 years for soil Olsen-P to decrease to the critical soil P values of crops grown in the absence of P fertilizer.     

长期不施肥条件下几种典型土壤全磷和Olsen-P的变化

研究了11个不同气候条件、不同耕作制度、典型土壤类型长期定位试验不施肥处理土壤全磷和Olsen-P变化及其影响因素。结果表明,在长期不施肥条件下耕作,土壤Olsen-P含量下降比全磷的明显;在试验进行5年左右,土壤全磷含量都有所降低,以后各点表现不尽相同,新疆灰漠土、长沙水稻土和郑州潮土全磷含量随时间延长呈显著直线下降,其它试验点全磷的变化不明显;作物携出磷与土壤全磷下降之间,无论绝对含量或相对含量都不成比例。土壤Olsen磷下降率比全磷高几倍。Olsen-P下降趋势与起始土壤Olsen磷含量有关:起始土壤Olsen-P磷大于20 mg/kg时,25年内一直呈现明显下降趋势,降低40.5 mg/kg,特别是前5年下降更快,降低30 mg/kg;起始土壤Olsen-P为10～20 mg/kg时,下降趋势比前者缓慢,15年内一直呈明显下降趋势,下降19 mg/kg, 前5年下降15 mg/kg,15年后几乎不变;起始土壤Olsen-P小于10 mg/kg时,25年内无明显变化。Olsen-P下降量与起始Olsen-P占全磷的比例成显著直线关系。