我国23个土壤磷素淋失风险评估Ⅱ.淋失临界值与土壤理化性质和磷吸附特性的关系

从13个省（市）采取23个耕地表层土壤,通过室内模拟试验测定其磷素淋失临界值和pH、有机质、＜0.01mm、＜0.002mm、交换性钙镁、活性铁铝、磷等温吸附特性等,以建立土壤磷素淋失临界值与土壤基本理化性质和磷吸附特性之间的关系.结果表明：土壤pH＜6.0时,随土壤pH提高临界值增加,土壤pH与临界值之间呈显著的指数关系;而当土壤pH＞6.0时,随土壤pH提高临界值减小,在pH6.5左右土壤磷素淋失临界值最高.土壤磷素淋失临界值与土壤有机质、活性铁（铝）、交换性钙之间存在显著的相关,而与交换性镁、CEC、＜0.01mm、＜0.002mm、K、Qm的相关性受土壤酸碱度影响.可以通过测定土壤有机质或活性铁的含量,来计算土壤磷素淋失临界值,评价土壤磷素淋失的风险.供试的23个土壤,除了采自湖北潜江的20号水稻土存在比较大的磷素淋失风险,其余土壤发生磷素淋失的风险很小.     

华南赤红壤无机复合肥氮磷淋失特征

采用室内土柱淋溶模拟试验,研究了不同施肥水平下无机复合肥中氮和磷在华南赤红壤中的淋失特征.结果表明: 铵态氮、硝态氮和总氮淋失量均随施肥量增加而提高;肥料中氮的淋失率在36.8%～49.2%之间,总氮淋失量（y）与施肥量（x）之间的回归方程为y=0.3667x+66.483（R²=0.992）;铵态氮和总氮的淋失主要集中在前5次淋洗,硝态氮的淋失持续时间更长.施肥量对可溶性磷淋失量无显著影响,但颗粒磷和总磷淋失量均随施肥量增加呈上升趋势;肥料磷淋失率在0.002%～0.010%之间,总磷淋失量（y）与施肥量（x）之间的回归方程为y=7e^-5x+0.0538（R²=0.931）;磷的淋失动态与氮显著不同,为缓慢的持续累积过程.硝态氮与铵态氮淋失量比值和可溶性磷与颗粒磷淋失量比值均随施肥量增加呈下降趋势.     

减磷配施有机肥对水旱轮作紫色水稻土磷素淋失的消减效应

为探索长江流域稻油轮作系统水稻季减少农田磷素流失的最佳施肥模式和有效耕作措施,降低其对长江水质的威胁。采用渗漏池长期田间原位定点试验并结合室内实验分析,研究了化肥配施猪粪有机肥和水稻秸秆还田对土壤磷素淋溶迁移的影响。结果表明在水稻生长期内土壤淋溶水中磷素浓度随时间延长呈逐渐下降的趋势,前期波动幅度大且下降迅速,到55d之后逐步稳定达到平衡。总可溶性磷(TDP)是渗漏水磷素的主要形态。土壤淋溶水中总磷(TP)和总可溶性磷(TDP)含量均表现为优化施肥+猪粪有机肥(MP)优化施肥+秸秆还田(SP)优化施肥(P)优化施肥量磷减20%+猪粪有机肥(MDP)优化施肥量磷减20%+秸秆还田(SDP)不施磷肥(P0)。土壤总磷(TP)淋失负荷在0.295—0.493 kg/hm2之间。施用有机肥提高了淋溶水中的磷素含量,促进了土壤中磷素的淋失,同时显著提高了土壤中有效磷的含量,猪粪有机肥的促进作用比水稻秸秆大。减少化肥施用量有利于降低土壤磷素淋失。在综合考虑农业生产省本增效和控制农田面源污染的情况下,可以采取减量化肥配施有机肥的施肥模式。     

宁夏黄灌区稻田冬春休闲期硝态氮淋失量

对宁夏黄灌区稻田设置不同有机肥处理：常规施肥（CK）;常规施肥条件下分别施用4500 kg/hm2（T1）与9000 kg/hm2猪粪（T2）,采用树脂芯法测定了稻田冬春休闲期30 cm、60 cm、90 cm处的硝态氮流失量。结果表明,常规施肥条件下,90 cm处硝态氮淋失量最大,分别为T1、T2的1.10与1.13倍;在常规施肥基础上增施猪粪,硝态氮最大淋失量出现在60 cm土层,T1、T2的流失量分别为4.47 kg/hm2与4.21 kg/hm2,分别为该层CK淋失量的1.50与1.42倍。灌区稻田常规施肥基础上增施有机肥,能够减少硝态氮向深层淋失;但60 cm土层处硝态氮淋失量增加,为硝态氮的深层淋失提供了基础,但在灌区水旱轮作模式下,下季旱作灌水量明显减少,加之作物吸收,硝态氮淋失也将明显降低。     

半干旱地区农田生态系统中硝态氮的淋失

在不同深度的渗漏池,连续6年(11季作物)研究了半干旱地区农田生态系统中硝态氮的淋失.结果表明,在半干旱地区,硝态氮的淋失仍可发生.淋失量和降水量有密切关系:降水多,淋失量大,不同降水年际间表现出显著差异.氮肥用量决定着淋失量的大小,而尿素和碳酸氢铵的淋失量却无本质差别.不同深度的土壤有着不同的贮水量,因而也有着不同的淋失量.实行夏季休闲,会增加硝态氮淋失的潜在危险.     

我国23个土壤磷素淋失风险评估Ⅰ.淋失临界值

随着磷肥施用量增加,土壤磷素累积,由此所引起的土壤磷素流失(径流和淋失)越来越成为水体磷素的重要来源。研究从广西灵川、云南建水、贵州六枝、福建漳浦、浙江象山、江苏如皋、山东泰安、河南南阳、陕西延安、海南海口、湖北潜江、湖南长沙、北京海淀等13个省(市)采集23种耕地土壤,土壤风干过2mm筛后,加入0,30,40,60,100,160,200,240,300,400mg P／kg土(KH2PO4溶液),并将土壤湿度调节至约50％的田问持水量,25℃下培养4d后风干,再加水至约50％的田问持水量,同上培养再风干,如此进行干湿交替3次达到平衡后,分别用pH8．50．5mol／LNaHCO3溶液(Olsen-P)、0．01mol／L CaCl2溶液(CaCl2-P)和铁滤纸条(Fe-P)测定土壤含磷量。结果表明,Olsen-P与Fe-P呈极显著的线性关系,随着土壤Olsen-P或Fe-P的增加,CaCl2-P提高,存在一个明显的突变点,即土壤磷酸盐淋失临界值。但不同土壤其临界值差异很大,前者的Olsen-P在29．96～156．78mg／kg之间,相应的CaCl2-P为0．14～3.87mg／kg;而后者的Fe-P为0．69～2．17mg／kg,相应的CaCl2-P为0．30～7．38mg／kg。两种方法所得到的临界值大部分土壤十分接近,但一些土壤相差很大。根据所获得的临界值推断,供试的23个土壤中,采自浙江象山(9号)、江苏如皋(11号)的土壤极有可能已经发生了磷酸盐淋失,来自广西灵川(2号)、云南建水(3号)、河南南阳(15号)、陕西延安(17号和18号)土壤比较容易发生磷淋失,而来自贵州六枝(5号和6号)、浙江象山(10号)、湖北潜江(20号和21号)土壤则不太容易发生磷的淋失。     

宁夏引黄灌区猪粪还田对稻作土壤硝态氮淋失的影响

以宁夏引黄灌区稻田为例,探索猪粪还田条件下稻田土壤硝态氮淋失规律。试验设置3个处理:常规施肥300 kg纯N kg/hm2(CK)、常规施肥条件下施用4500kg/hm2(T1)和9000 kg/hm2(T2)猪粪。利用树脂芯法吸附稻田30cm、60cm和90cm土层的硝态氮流失量。结果表明:在常规施肥的基础上增施猪粪,可以减少稻田生育期内60cm与90cm处土壤硝态氮淋失量,与CK相比,T1、T2在两个土层处淋失量的减少比例分别为4.93%、13.92%与7.48%、13.77%。同一土层不同处理之间差异显著性比较看(P0.05),30cm处T1、T2与CK相比没有达到显著性差异;60cm处,T1与CK未达到显著差异,T2与CK达到显著差异;90cm处,T1、T2与CK相比达到显著差异;60cm和90cm土层处的T2与T1之间均达到显著差异。T1和T2在30cm处的淋失量高于CK,但增加不明显,处理之间以及处理与对照相比差异不显著。稻田生育期内不同土层硝态氮淋失量在13.61—17.77 kg/hm2(纯N)。硝态氮淋失集中在插秧至分蘖期(5月中旬—6月下旬),该阶段的硝态氮淋失量占生育期内总淋失量的61.62%—72.84%;后期淋失量明显减少。处理T1、T2的水稻产量增产率分别为15.86%与12.85%。由此可见,在引黄灌区稻田,一定数量的猪粪还田,不仅能够减少土壤硝态氮向深层淋失,防控地下水污染,还有利于水稻增产。     

有机物料对滨海盐渍土重金属根际效应的影响Ⅱ.土壤内源铁形态分布

研究了排水条件下施用腐熟有机物料、种稻改良滨海盐渍土内源铁形态分布．结果表明,单淹水利于土中无定形氧化铁、络合态铁、有效态铁以及氧化铁活化度升高,并且络合态铁与有效态铁升高程度,低盐土壤显著;晶形氧化铁变化不明显,土中可能存在其它形态铁向晶形氧化铁转化．种稻不施有机物料,根际络合态铁和有效态铁富集;无定形氧化铁和晶形氧化铁亏缺．根际氧化铁活化度稍低于非根际．增施有机物料利于两种盐渍土根际内外铁形态向络合态铁和无定形氧化铁转化;有效态铁和氧化铁活化度提高,低盐土壤根际较明显     

宁夏引黄灌区猪粪还田对麦田土壤硝态氮淋失的影响

以宁夏引黄灌区为例,探索猪粪还田条件下冬小麦田土壤硝态氮淋失规律.试验设置3个处理:常规施化肥225 kg N·hm-2(CK)、常规施肥基础上施用4500 kg·hm-2(T1)和9000 kg·hm-2(T2)猪粪.利用树脂芯法吸附30、60和90 cm土层的硝态氮淋失量.结果表明:在常规施肥基础上增施猪粪,小麦生育期土壤硝态氮(纯N)淋失量为9.33~14.04kg·hm-2,占施N量的4.2%~6.2%.与CK相比,30 cm土层T1、T2的硝态氮淋失量增加2.6%和2.1%;60 cm土层增加1.5%和减少1.3%;90 cm土层减少8.7%和增加4.0%.增施猪粪与对照在30、60和90 cm土层处的硝态氮淋失量均无显著差异,而在深层土壤表现出减少趋势.硝态氮淋失主要发生在返青至灌浆期间,日均淋失量高于全生育期平均水平,该阶段的硝态氮淋失量占生育期内总淋失量的58.7%~75.3%.T1、T2春小麦产量比对照分别增加9.3%和12.5%.     

耕作扰动对喀斯特土壤可溶性有机质及其组分迁移淋失的影响

土壤可溶性有机质(DOM)及其组分淋失特征研究对深入理解干扰作用下土壤碳氮养分损失机制具有重要意义,本研究基于翻耕模拟试验,分析喀斯特石灰土可溶性有机碳(DOC)、可溶性有机氮(DON)、及DOM官能团组分的淋失动态特征及其对不同耕作频率的响应,并探讨其影响因子。结果表明:(1)土壤DOC与DON的淋失量均随翻耕频率的增加而增加,但4个官能团特征参数对翻耕频率响应均不显著;DOC/DON淋失比随翻耕频率的增大而减少,DON占淋溶水可溶性总氮(TDN)比例随翻耕频率增加而增加。(2)DOC和DON月淋失量同时受翻耕处理与季节变化及其交互作用的影响,4个官能团特征参数仅受季节变化的影响;翻耕处理实施后,DOC月淋失量表现为初期大、后期小,各处理间差异性逐渐降低;但DON月淋失量初期小、后期大,各处理间差异性逐渐增大。(3)DOC淋失量与4个官能团特征参数呈显著负相关(P0.05),与Ca~(2+)、NH_4~+-N的淋失量呈显著正相关;DON淋失量与4个官能团参数无显著相关关系,与Mg~(2+)淋失量呈显著正相关关系。以上结果表明耕作扰动会加剧土壤DOM淋失,但淋失组分中稳定性组分没有变化,意味着耕作干扰将导致土壤有机质的持续损失,且由于其淋失组分碳氮比(DOC/DON)随扰动频率增加而降低,DON/TDN比随扰动频率增加而增加,持续的耕作干扰将大大增加水体氮素污染风险。     

Implications of soil organic carbon and the biogeochemistry of iron and aluminum on soil phosphorus distribution in flooded forests of the lower Orinoco River,Venezuela

Relationships among soil phosphorus distribution, soil organic carbon and biogeochemistry of iron and aluminum were studied along a flooded forest gradient of the Mapire river, Venezuela. Soil samples were collected during the dry season in three zones subjected to different flooding intensity: MAX inundated 8 months per year, MED inundated 5 months per year, and MIN inundated 2 months per year. Total labile phosphorus (resin + bicarbonate extractable fractions) was significantly higher in MIN than in MAX. The longer non-flooding period in MIN probably allowed a higher accumulation of microbial biomass in soils of this zone and consequently a greater release of the bicarbonate organic fraction. The moderately labile phosphorus fraction associated with the chemisorbed phosphorus on amorphous and some crystalline aluminum and iron was significantly lower in MAX than in MIN following the same tendency observed for crystalline iron oxides. This result allowed us to hypothesize that the combined effect of a long flood period and a high soil organic carbon content in the MAX, could be appropriate conditions for microbial reduction of stable forms of iron. The ratio of soil organic carbon to total organic phosphorus decreased from MAX to MIN, indicating higher mineralization of organic phosphorus in MIN. Our results suggests two distinct flood-dependent mechanisms operating for phosphorus release along the gradient. In MAX mineralization process appears to be limited, while microbial mineral dissolution appears to be an important source of phosphorus. In MIN supply of phosphorus is associated with the stability of soil organic matter.     

定位施肥对紫色菜园土磷素状况的影响

基于紫色菜园土壤莴笋-白菜轮作3a的12季连续定位施肥试验,研究施肥对土壤磷素状况的影响。结果表明,在紫色土上以化肥为基础增施有机肥(泥炭或菜籽粕)既提高土壤磷含量,又增加无机磷组分中有效磷源和缓效磷源的比例,且不会增加磷素淋失的风险,是所有处理中最优者;增磷、增钾处理虽然提高了土壤磷含量,但未能提高速效磷源与缓效磷源的比例;增氮、增硼及常规施肥降低土壤磷含量和提高无效磷源的比例;无肥处理磷含量最低,无效磷源比例最高。紫色菜园土无机磷约为有机磷的4—6倍,无机磷各组分以钙磷为主,占I-P总量的60.89%—67.92%,显示紫色土风化程度较低。各形态磷素呈Ca10-P>Ca8-P>Fe-P≈Al-P≈OC-P>Ca2-P序列变化,其中Ca2-P和Al-P总共仅占无机磷总量的11.47%—19.43%,表明紫色土中对植物最有效的磷源不足;而Ca10-P和OC-P共占无机磷总量的42.48%—59.55%,意味着紫色土无机磷有一半左右是以作物不可利用的形态存在的。紫色土全磷与无机磷、有机磷、Ca2-P、Ca8-P、Al-P、Fe-P、OC-P及Ca10-P呈显著正相关;无机磷与多种形态磷呈显著正相关(除有机磷、Ca2-P、有效磷外);有机磷与全磷、Ca2-P显著正相关;有效磷与全磷、Ca2-P、Al-P、Fe-P显著正相关;无机磷组分间也都存在显著正相关关系(OC-P与Ca10-P间有极显著正相关,但它们与其它无机磷组分无相关性)。表明在土壤磷的整个循环系统中,不同组分无机磷与有机磷之间处于一个动态平衡中,它们之间存在着相互影响和制约。土壤pH与各形态磷关系密切。对土壤有效磷与无机磷组分间的关系进行系统分析,简单相关分析结果土壤有效磷与Ca2-P、Fe-P呈极显著正相关,与Al-P呈显著正相关,与Ca8-P、OC-P、Ca10-P正相关但不显著;通径分析结果对土壤有效磷直接影响较大的无机磷组分是Al-P、Ca8-P与Ca2-P,其中Ca8-P的直接影响为负效应;逐步回归分析结果与通径分析一致。综合分析得出,Ca2-P、Al-P是最有效的磷源,Fe-P、Ca8-P次之,Ca10-P与OC-P是非有效磷源。莴笋和白菜产量与紫色土壤Ca2-P、Ca8-P、Al-P、Fe-P呈显著正相关,与OC-P、Ca10-P无相关性。紫色土各形态无机磷与两种蔬菜产量的相关系数r大小依次为Ca2-P>Fe-P>AL-P>Ca8-P>Ca10-P>OC-P,这与各形态无机磷与有效磷简单相关分析的结果一致。     

施肥对设施菜地土壤磷累积及淋失潜能的影响

以不同肥力设施菜地土壤为研究对象,通过填装土柱模拟试验,研究不同施肥措施对磷素累积及淋溶的影响.结果表明： 随着淋溶时间的延长,磷素淋溶量增加,但累积淋溶量较少,说明本试验中磷素淋溶损失的风险较小,主要累积在土体内的不同土层中.试验结束时,土壤肥力和施肥处理均显著影响不同土层中全磷和速效磷含量.与低肥力土壤相比,中肥力土壤全磷和速效磷增幅为14.3%和12.2%,高肥力土壤增幅为33.3%和37.7%.有机肥化肥混施处理(M+NPK)土壤全磷含量显著高于单施化肥(NPK)和有机肥(M)处理,增幅分别为5.7%和4.3%;M及M+NPK处理中速效磷含量显著高于NPK处理,增幅分别为13.0%和3.1%.10～20 cm土层全磷和速效磷含量最高,0～10和10～20 cm土层全磷和速效磷含量显著高于20~40 cm土层.
     

川西亚高山三种森林恢复途径对土壤生物有效磷的影响

土壤生物有效磷在提高森林生产力和生物地球化学循环中起着至关重要的作用,研究不同森林恢复途径对土壤生物有效磷的影响对于退化森林的适应性恢复和可持续经营具有重要意义。选取川西亚高山不同恢复途径下形成的3种森林类型,即粗枝云杉人工林（人工种植,PF）、岷江冷杉-红桦天然次生林（自然更新,NF）和粗枝云杉阔叶混交林（人工种植后自然更新,MF）,采用基于生物有效性的土壤磷分级方法测定土壤生物有效磷（CaCl₂-P、Citrate-P、Enzyme-P和HCl-P）,探究不同森林恢复途径对土壤生物有效磷的影响。结果表明：不同森林恢复途径对土壤生物有效磷影响显著（P<0.05）,NF和MF的土壤Citrate-P和Enzyme-P显著高于PF（P<0.05）,而PF的土壤HCl-P显著高于NF（P<0.05）。自然更新是3种森林恢复途径中最能提高土壤生物有效磷的方式。3种森林恢复途径下的土壤生物有效磷组分与速效磷均呈现显著的正相关关系,且NF的土壤速效磷与生物有效磷的相关性更强（CaCl₂-P除外）。显著影响NF土壤生物有效磷的土壤理化性质有全钾、铵态氮含量和pH值,且全钾对NF的土壤生物有效磷变异的解释程度最高（r²=0.63,P=0.001）。土壤pH值、钙和可溶性有机碳含量是显著影响MF土壤生物有效磷的主要土壤理化性质（P<0.05）。对PF的土壤生物有效磷具有显著影响的土壤理化性质是土壤有机碳、铁和可溶性有机碳含量。土壤理化性质对3种恢复途径下森林土壤生物有效磷的解释率均超过了80%,森林恢复途径对土壤生物有效磷的影响与土壤理化性质有关。     

干旱绿洲灌区大白菜施磷效应与磷肥投入阈值

针对磷肥施用量大且利用率不高的问题,通过2011—2013年在甘肃省农业科学院张掖绿洲灌区农业生态环境重点野外台站进行定位试验,研究了不同施磷量对露地大白菜产量、磷肥利用率以及磷素平衡的影响.结果表明:大白菜产量随施磷量的增加先增加后呈下降的趋势.在施磷量为112.52 kg·hm^-2时产量达到最高(5489.1 kg·hm^-2),且显著高于其他处理,与不施磷处理相比,增产13.3%~23.8%,此时磷肥利用率为14.2%.土壤中土壤有效磷(Olsen-P)和可溶性总磷(CaCl-P)呈现较好的正相关性,土壤Olsen-P含量为24.22 mg·kg-12时对应的施磷量为111.1 kg·hm^-2,表明当土壤中Olsen-P含量小于24.22 mg·kg-1时,土壤中的磷素不发生盈余,对环境不造成污染.当施磷量为60.17 kg·hm^-2时,磷输入与输出达到平衡,即此施磷量水平能满足作物的需求.结合研究区的土壤肥力状况,综合产量、磷肥利用率及土壤有效磷含量,干旱绿洲灌区磷肥投入阈值在60.17~112.52 kg·hm^-2时,能保证露地大白菜高产,并且不会造成环境污染.     

Effects of long-term nitrogen deposition on phosphorus leaching dynamics in a mature tropical forest

Elevated anthropogenic nitrogen (N) deposition is suggested to affect ecosystem phosphorus (P) cycling through altered biotic P demand and soil acidification. To date, however, there has been little information on how long-term N deposition regulates P fluxes in tropical forests, where P is often depleted. To address this question, we conducted a long-term N addition experiment in a mature tropical forest in southern China, using the following N treatments: 0, 50, 100, and 150 kg N ha^?1 year^?1. We hypothesized that (i) tropical forest ecosystems have conservative P cycling with low P output, and (ii) long-term N addition decreases total dissolved phosphorus (TDP) leaching losses due to reduced litter decomposition rates and stimulated P sorption deriving from accelerated soil acidification. As hypothesized, we demonstrated a closed P cycling with low leaching outputs in our forest. Under experimental N addition, TDP flux in throughfall was significantly reduced, suggesting that N addition may result in a less internal P recycling. Contrary to our hypothesis, N addition did not decrease TDP leaching, despite reduced litter decomposition and accelerated soil acidification. We find that N addition might have negative impacts on biological P uptake without affecting TDP leaching, and that the amount of TDP leaching from soil could be lower than a minimum concentration for TDP retention. Overall, we conclude that long-term N deposition does not necessarily decrease P effluxes from tropical forest ecosystems with conservative P cycling.     

Relationships among element contents in the medial meniscus

To elucidate compositional changes of elements in the meniscus with aging, the authors investigated the relationships among elements in the medial meniscus by inductively coupled plasma-atomic emission spectrometry. The subjects consisted of 16 men and 7 women, ranging in age from 65 to 93 yr. In the left medial meniscus, extremely significant correlations were found both between calcium and phosphorus contents and between sulfur and magnesium contents, whereas significant correlations were found between calcium and either iron or zinc contents, between phosphorus and either iron or zinc contents, and between iron and zinc contents. On the other hand, in the right medial meniscus, there were only an extremely significant correlation between calcium and phosphorus contents and a significant correlation between sulfur and magnesium contents. The common finding between the left and right medial menisci was an extremely significant correlation between calcium and phosphorus contents and a significant correlation between sulfur and magnesium contents.     

Chemical and biological leaching of enargite

Enargite (Cu 3 AsS 4 ) was leached faster by bacteria in sulfuric acid medium (pH 1.6) with added ferric sulfate than by chemical leaching at the same or higher iron concentration. During chemical leaching with ferric iron, the copper dissolution rate decreased from an initial value of 0.03% per hour to a value of 0.002% per hour. Enargite is oxidized to elemental sulfur and dissolved arsenic (As 3+ and As 5+ ). Less than 10% of sulfur is oxidized to sulfate. The arsenic and copper dissolutions observed in bacterial leaching experiments suggest the existence of a specific bacterial action on the leaching of enargite, demonstrated by the ability of bacteria to oxidize enargite at very low concentration of dissolved iron and by the higher dissolution rate obtained in bacterial leaching compared to chemical ferric leaching.