磷

基本解释 (translations)

phosphorus  ·  phosphori

与磷相关的网络例句 [注：此内容来源于网络，仅供参考]

The results showed that it was invalid to apply Zn fertilizer alone, but biomass production obviously increased while Zn and P fertilizer applying together during maize seedling stage, P and Zn showed positive interaction effects in carbonate Chernozem of seriously lack of P. While applying P and organic fertilizer, the contents of Zn were 19.4～23.3 mg/kg, P/Zn...

结果表明：在严重缺磷的碳酸盐黑钙土上，单独施锌无效，锌磷配施玉米苗期生物学产量增产明显，磷与锌呈正交互作用；施磷和有机肥时，玉米苗期锌含量下降到 19.4～ 2 3.3mg/kg，磷/锌比值大于 140 ，玉米易出现白苗症；施入土壤的锌第 1年固定率最高可达 65%～ 88%，第 2年达 85%～ 95%，第 3年达 88.5%～92 。4 %；磷与锌配施既能提高锌的利用率又能提高磷的利用率

B组; Gimel ,克; Daleth , D节; Kaph ,钾;体育,磷和托,吨In some systems of transliteration the soft pronunciation is represented thus, bh, gh, dh, kh, ph, th; in others it is b, g, d, k, p, and t.

在某些系统的转软的发音是代表因此，波黑，生长激素，卫生署，链接， pH值，次；在另一些是B ，克，天，钾，磷，和T。

A sequential extraction technique to fractionate P and the method proposed by Bremner to separate N in different fractions were used.

本试验利用Sui 和 Thompson (1999)序列萃取法，以不同强弱的萃取剂来划分土壤中的磷，将土壤磷划分为水萃取磷、碳酸氢钠萃取有机磷及无机磷、氢氧化钠萃取有机磷及无机磷、盐酸萃取磷及残余磷；利用 Bremner (1965)的土壤有机态氮划分法将土壤有机态氮划分为水解性全氮、水解性铵态氮、胺基醣态氮、胺基酸态氮及不可辨认的水解性氮。

According to the above study results, especially the steady operation of two-sludge system（2A/O+N 2SBR）, it can be proved that denitrification and excess phosphorus uptake are relatively independent and intersectant biological processes. The overlap is that denitrifying phosphorus removing bacteriawhich possesses the two bacterial metabolisms, could utilize nitrate as an electron acceptor for phosphorus uptake. The two-sludge system can not only combined biological phosphorus removal and denitrification processes to form a process in practical wastwater treatment , but also solved the main difficulties of current single-sludge systems:①the sludge age competition between phosphorus removing bacteria and nitrifier;② the substrate competition between denitrification and dephosphatation.

以上的研究结果，尤其是时间序列的双泥生物反硝化除磷脱氮系统工艺（2A/O+N 2SBR法）的稳定运行，不仅证明了生物脱氮与生物除磷是两个既相对独立又相互交叉的生理过程，其交叉点是同时拥有硝酸盐还原性和超量吸磷这两种生化特性的细菌进行的反硝化吸磷脱氮生化反应，而且双泥系统工艺克服了常规单泥生物脱氮除磷工艺的两大问题（①聚磷菌和硝化菌的SRT相互干扰；②反硝化与生物除磷竞争VFA），同时保证了脱氮和除磷效果，排水指标达到污水综合排水标准（GB8978-1996）的一级标准，具有实际工程使用价值。

The feldspars of topaz-lepidolite granite in Yashan late stage are P-rich albite and Kfeldspar, and the phosphorus goes into feldspar structure in the form of PAlSi〓 substitution. The phosphorus contents of feldspars vary according to their crystal habitus. In general, the feldspars of later generation have the higher average phosphorus content than that of earlier generation, and the albite contains higher phosphorus than the K-feldspar in the same generation. The zircon is highly rich in Hf, U, P and Al. The phosphorus enters the zircon structure mainly by the form of〓P〓〓Si〓, Al〓P〓Si〓 or P〓Al〓Si〓, Zr〓 substitution. The P-rich zircon is the production of the highly evolved magma, and it might be one of the important characteristic minerals of the high-P subtype granite. The manganocolumbite, manganotantalite, wodginite and titanowodginite are the main niobium and tantalum minerals.

雅山晚阶段黄玉锂云母花岗岩的长石矿物是富磷长石，磷以PAlSi〓替换方式进入长石结构中，并且在长石中的分布很不均一，一般是晚结晶的长石比早结晶的长石的磷含量高，同期结晶的钠长石比钾长石的磷含量高；锆石矿物为高度富铪、铀、磷和铝的锆石，磷主要以(Y， HREE， Fe)〓P〓〓〓Si〓〓、Al〓P〓Si〓〓、P〓Al〓Si〓〓Zr〓〓等替换方式进入锆石晶格中，富磷锆石是岩浆高度演化的结果，是高磷花岗岩的特征矿物之一；雅山含有丰富的磷锂铝石，是高磷花岗岩的主要磷酸盐矿物；铌—钽矿物主要有铌锰矿—钽锰矿、锡锰钽矿—钛锰钽矿、细晶石等。

The amount of Ca8-P in soil with CRMP treatments was lower than that of CMP treatments. The changes of the amount of Al-P, O-P, Fe-P and Ca10-P in soil were neglectable during the course of experiment.3. The shoot and root weight of sorghum increased through application of phosphorus, in addition, The increase of sorghum shoot and root weight was greater than that of common monoammonium phosphate due to the slow release of nutrients from CRMP. The accumulative uptake of phosphorus in shoot and root with CRMP treatment was greater than that with CMP treatment in low (75 mg P2O5/kg soil ) and high（150mg P2O5/kg soil）rates, especially on middle stage, and in high phosphorus rate, this advantage was more obvious than that in low phosphorus rate.

磷肥的施入，促进了高粱地上部和根部的生长，而控释肥由于缓慢释放养分，与作物吸收相一致，更能促进高粱的地上部和根部干物质积累；对于高粱地上部及根部的磷素累积，在两种施磷水平下控释处理地上部及根部磷素累积量均大于非控释处理，尤其是在中期，而且高磷水平下优势更加明显，低磷控释处理的磷素累积量能达到高磷非控释的累积量，即减少一半的用量即能达到同样的效果；在氮、钾、钙、镁相同的水平下，控释处理比非控释处理更能促进地上部及根部氮、钾、钙、镁累积量，这种优势在中期表现最明显。4。

According to the above study result, the diversity of microorganisms population in the SUFR system is complex and the bio-community formed in the SUFR system is stable. The close relations between abundance of bacteria and nutrients were found. The correlation between heterotrophic bacteria and COD was 0.949. The correlation between organic phosphate bacteria and TP was 0.815. The correlation between nitrosobacteria and NH3-N was 0.909. The correlation between disnitrifier bacteria and TN was 0.653. These inneglectable great factors effecting on phosphorus-uptake and phosphorus-release of phosphorus accumulating organisms are the influent COD、the concentration of DO、the sludge retention time、the temperature. The diversity of organic phosphate bacteria population in the SUFR reactor was complex and there is no phosphate bacteria taking the absolute superiority in quantity. The near-native pure culture method powerfully complement the traditional pure culture technique and enrich culture technique. The sludgy bioactivity is very good in whole SUFR reactor. By the quality of being biochemistry, the anaerobic phase is higher than anoxic phase and the anoxic phase is higher than aerobic phase of SUFR.

通过以上试验内容研究发现，SUFR 系统中的微型动物种群较多，微生物生态系统稳定；系统中微生物的数量与营养盐的含量密切相关，其中总异养菌与COD的相关系数r 为0.949，有机磷细菌与TP 的相关系数r 为0.815，亚硝化菌与NH4+-N的相关系数r 为0.909，反硝化菌的数量和TN 的相关系数r 为0.653；污水生物除磷工艺中进水COD 的浓度、DO 浓度、泥龄的长短、温度都是影响聚磷菌释磷及吸磷效果的不可忽视的因素；SUFR 系统中的磷细菌呈现种群多样化的趋势，没有占绝对优势数量的磷细菌；微孔滤膜近自然培养法是对传统纯培养技术和富集培养技术的有力补充；整个SUFR 反应器系统中污泥的生物活性很好，就可生化性来讲，厌氧反应器大于缺氧反应器大于好氧反应器；按照动力学方程式求出的细胞生长动力学特征值和SUFR 脱氮除磷系统工艺的实测值结果基本吻合。

The result indicated that in the low phosphorus condition, using sturdy-seeding agent which inoculates fungi of dissolving phosphorus could obviously improve the plant height, increase fresh and dry biomass of the shoots, root vigor, phosphorus content and P uptake of the shoots. In the five treatments, compared to the blank control groups, the plant height of rice seedling increases 16.81%, fresh biomass 21.28%, dry biomass 12.42%, phosphorus content 31.11% and P uptake 44.03% for the shoots, the results were good. Next was P1 and P4 treatments, especially in the P1 treatment, the dry and fresh biomass, phosphorus content and phosphorus uptake of the roots were highest than any other treatment.

结果表明，在低磷条件下，施用接种解磷菌的壮秧剂可以显著提高水稻秧苗的株高、地上部干、鲜生物量、根系活力、地上部磷含量和磷吸收量，在5个处理中，P2处理水稻秧苗的株高比对照提高16.81%，地上部鲜生物量比对照增加21.28%，地上部干生物量比对照增加12.42%，地上部磷含量比对照提高31.11%，地上部磷素吸收量比对照提高44.03%，表现效果较好，其次是P1和P4处理，其中P1处理的根部干、鲜生物量、根部的磷素含量和磷素吸收量均高于其他处理。

The phosphorus forms and BAP vary with horizontal and vertical positions. The total phosphorus, inorganic phosphorus, BAY, and iron-phosphorus contents were high at a depth of 0~20 cm at the first sampling point, and then decreased at 20-40 cm of depth. This shows that the potential release capacity of P at 0-20 cm of depth is higher. The concentrations of total phosphorus and inorganic phosphorus decreased at 0~20 cm of depth and increased at 20~40 cm of depth at the second sampling point, but BAY and Fe-P increased along with the depth consistently. This shows that the deeper layer at the second sampling point had a higher potential release capacity of phosphorus.

不同地点沉积物各磷形态和BAP的垂向变化有较大的差异。1号采样点的总磷、无机磷、铁磷和BAP质量比在沉积0~20 cm处较高，20~40 cm逐渐减小，说明0~20 cm内释磷潜力较大；2号采样点的总磷和无机磷质量比先减小，20~40 cm逐渐增加，而BAP和铁磷质量比随深度增加呈上升趋势，说明2点深层具有较大的释磷潜力。

Inwheat intercropped with soybean not only N situation could be improved butalso P situation could be.2In intercropping,the pH of soybean rhizospherewas decreased by increasing the R-Apase activity,which could decelerate thetransforming and fixing P fertilizer.3In both monoculture and intercroppingsystem,the soil pH of rhizosphere was affected by cropping system at two Plevel which only 0.1-4mm distance from the root surface,but the effect of S-Apase activity in the rhizospher soil by cropping system was less than3mm.In effect,the rhizosphere P was really available nutrient,and applyingP to rhizosphere was effective ways to reduce the P nutrient competition.4Inwheat/soybean intercropping,the peak stage of reduction ability of roots wasthe same as that of the root growth,so that the time compensation appearedin intensity of nutrient absorption.

间套作大豆、小麦、玉米根系Apase的差异又反映出大豆利用土壤磷的潜在能力最大，而玉米最小，可见禾谷类的小麦与大豆间套后不但能改善小麦的氮素营养状况还使磷素营养也得以好转。2）间套大豆根际pH值的下降，导致磷肥施入土壤后形成〓-P的比例显著提高，转化成〓-P等难溶性磷减少，说明间套的大豆能减缓肥料磷在土壤中的转化和固定，减少磷素向无效化方向转化。3）复合群体根际土壤pH值的影响一般只发生在0.1-4mm的根际微区，而土壤磷酸酶的影响供磷与否在距根表3mm以外都无多大差异，说明根际磷才是真正有效磷，根际施磷是解决磷素竞争的有效途径。4）。

与磷相关的网络解释 [注：此内容来源于网络，仅供参考]

phosphoryl monochloride：一氯一氧化磷;一氯化磷酰

一溴二氟氧化磷;一溴二氟化磷酰 phosphoryl bromodifluoride | 一氯一氧化磷;一氯化磷酰 phosphoryl monochloride | 氮氧化磷;磷酰氮 phosphoryl nitride

phosphorite nodule：磷灰岩结核,磷钙岩结核

磷灰岩,磷钙土,磷钙岩,磷块岩 phosphorite | 磷灰岩结核,磷钙岩结核 phosphorite nodule | 磷氢镁石 phosphorr?sslerite

phosphoryl bromodichloride：一溴二氯一氧化磷;一溴二氯化磷酰

三溴一氧化磷;磷酰溴 phosphoryl bromide | 一溴二氯一氧化磷;一溴二氯化磷酰 phosphoryl bromodichloride | 一溴二氟氧化磷;一溴二氟化磷酰 phosphoryl bromodifluoride

phosphoryl amide：磷酰胺;一氧三胺化磷;三胺化磷酰

磷酰胺;一氧三胺化磷;三胺化磷酰 phosphoryl amide | 三溴一氧化磷;磷酰溴 phosphoryl bromide | 一溴二氯一氧化磷;一溴二氯化磷酰 phosphoryl bromodichloride

phosphorus trichloride：三氯化磷

本标准是为工作场所有害因素职业接触限值配套的监测方法,用于监测工作场所空气中无机含磷化合物[包括五氧化二磷(Phosphorus pentoxide)、五硫化二磷(Phosphorus pentasulfide)、黄磷(Yellow phosphorus)、磷化氢(Phosphine)、三氯化磷(Phosphorus trichloride)、三氯硫磷(Pho

phosphorus oxybromide：三溴一氧化磷;磷酰溴;三溴化磷酰

氧胺化磷;磷酰胺;三胺化磷酰 phosphorus oxyamide | 三溴一氧化磷;磷酰溴;三溴化磷酰 phosphorus oxybromide | 一溴二氯氧化磷;一溴二氯化磷酰 phosphorus oxybromodichloride

phosphorus oxyfluoride：三氟一氧化磷;磷酰氟

二溴一氯氧化磷;二溴一氯化磷酰 phosphorus oxydibromochloride | 三氟一氧化磷;磷酰氟 phosphorus oxyfluoride | 三碘一氧化磷;磷酰碘 phosphorus oxyiodide

phosphorus oxyiodide：三碘一氧化磷;磷酰碘

三氟一氧化磷;磷酰氟 phosphorus oxyfluoride | 三碘一氧化磷;磷酰碘 phosphorus oxyiodide | 氮氧化磷;磷酰氮 phosphorus oxynitride

Demeton-S-methyl sulphone：砜吸硫磷(砜吸磷)

Demeton-s-methyl 硫赶式甲基内吸磷(异吸磷、甲基内吸磷、异甲基1059) | Demeton-S-methyl sulphone 砜吸硫磷(砜吸磷) | Dentin hydroxide 毒菌锡

phosphoryl triamide：三胺化磷酰;磷酰胺;一氧三胺化磷

氮氧化磷;磷酰氮 phosphoryl nitride | 三胺化磷酰;磷酰胺;一氧三胺化磷 phosphoryl triamide | 三氯化磷酰;磷酰氯;三氯一氧化磷 phosphoryl trichloride