CN113340691B - Method for extracting phosphorus with different occurrence forms in marine sediment - Google Patents
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Abstract
本发明提供一种提取海洋沉积物中不同赋存形态磷的方法,本发明的提取方法是对海洋沉积物样品进行连续分级浸提,采用不同的提取剂逐级对样品中磷的提取,以获得不同赋存形态的磷。本发明的提取方法能够全面提取海洋沉积物中不同赋存形态的磷,且提取率高,便于对海洋中磷形态的系统性研究。
The present invention provides a method for extracting phosphorus in different forms of occurrence in marine sediments. The extraction method of the present invention is to carry out continuous graded leaching of marine sediment samples, and use different extractants to extract phosphorus in the samples step by step, so as to Obtain phosphorus in different forms. The extraction method of the present invention can comprehensively extract phosphorus in different forms of occurrence in marine sediments, has a high extraction rate, and facilitates systematic research on phosphorus forms in the ocean.
Description
技术领域Technical field
本发明涉及环境技术领域,尤其涉及一种提取海洋沉积物中不同赋存形态磷的方法。The present invention relates to the field of environmental technology, and in particular to a method for extracting phosphorus in different forms present in marine sediments.
背景技术Background technique
磷是海洋浮游生物生长和繁殖的必需成分,是海洋初级生产力和食物链的基础。河流输入是海洋中磷的主要来源,沉积物是水体中磷的重要储库,二者间磷的交换作用显著,然而能参与交换的生物可利用磷量取决于沉积物中磷的赋存形态,在沉积环境的温度、pH值、生物扰动等因素变化时,只有弱吸附态磷、闭蓄态磷、铁/铝吸附态磷、有机磷可从沉积物中向上覆水体扩散,被生物所利用,进而影响海洋水环境中磷的含量。因此,海洋沉积物中磷的赋存形态对定量潜在生物可利用磷上限,获取沉积环境的有关信息,了解海洋中磷的再循环,进行内源污染控制具有重要的意义。Phosphorus is an essential component for the growth and reproduction of marine plankton and is the basis of marine primary productivity and the food chain. River input is the main source of phosphorus in the ocean, and sediments are an important reservoir of phosphorus in the water body. The exchange of phosphorus between the two is significant. However, the amount of bioavailable phosphorus that can participate in the exchange depends on the form of phosphorus in the sediment. When the temperature, pH value, bioturbation and other factors of the sedimentary environment change, only weakly adsorbed phosphorus, occluded phosphorus, iron/aluminum adsorbed phosphorus, and organic phosphorus can diffuse from the sediment to the overlying water body and be absorbed by organisms. utilization, thereby affecting the phosphorus content in the marine water environment. Therefore, the occurrence form of phosphorus in marine sediments is of great significance for quantifying the upper limit of potential biologically available phosphorus, obtaining relevant information about the sedimentary environment, understanding the recycling of phosphorus in the ocean, and controlling endogenous pollution.
现有技术公开了多种分离定量海洋沉积物中磷形态的方法,最理想的是化学试剂提取法,主要有:Rutternberg法、Jensen(1998)法、Kaarina改进的方法。但是,Rutternberg法仅侧重于碎屑磷与自生磷的分离,该方法对其他形态的磷分离不够,例如第二步提取的实际上是铝结合态磷(Al-P)、铁结合态磷(Fe-P)和闭蓄态磷的总和,如果仅认为是Fe-P则过于偏颇;Jensen(1998)基于Rutternberg法进行改进,将沉积物中磷形态进一步细化,将主要的沉积性的磷分成六部分弱吸附态磷(Lsor-P)、铁结合态无机磷(Fe-P)、可提取有机磷(Lea-OP)、自生磷灰石(CAFP)、碎屑磷灰石(FAP)和稳定有机磷(Ref-OP);Kaarina改进的方法分离了对氧化还原环境敏感的铁锰结合态的磷与氧化铝,不可还原的铁氧化物中的磷和有机磷,但未能区分原生碎屑磷和沉积环境中的自生磷。The existing technology discloses a variety of methods for separating and quantifying phosphorus forms in marine sediments. The most ideal is the chemical reagent extraction method, which mainly includes: Rutternberg method, Jensen (1998) method, and Kaarina's improved method. However, the Rutternberg method only focuses on the separation of detrital phosphorus and authigenic phosphorus. This method is not enough to separate other forms of phosphorus. For example, what is extracted in the second step is actually aluminum-bound phosphorus (Al-P), iron-bound phosphorus ( Fe-P) and the sum of occluded phosphorus, if it is only considered to be Fe-P, it would be too biased; Jensen (1998) improved it based on the Rutternberg method and further refined the form of phosphorus in sediments, dividing the main sedimentary phosphorus into Divided into six parts: weakly adsorbed phosphorus (Lsor-P), iron-bound inorganic phosphorus (Fe-P), extractable organic phosphorus (Lea-OP), authigenic apatite (CAFP), and detrital apatite (FAP) and stabilized organophosphorus (Ref-OP); Kaarina’s improved method separated phosphorus and alumina in the iron-manganese bound state that is sensitive to the redox environment, phosphorus and organophosphorus in irreducible iron oxides, but failed to distinguish the native Detrital phosphorus and authigenic phosphorus in sedimentary environments.
由于现有的许多磷形态分级浸取方法未能系统完整的提取和分析沉积物中磷的赋存形态,基于此,本发明综合前人各类分级浸取方法的优点,提出一种提取海洋沉积物中不同赋存形态磷的方法,细化生物可利用磷,进一步完善并着重考虑环境地球化学的研究要求。Since many existing hierarchical leaching methods of phosphorus forms fail to systematically and completely extract and analyze the existing forms of phosphorus in sediments, based on this, the present invention combines the advantages of various previous hierarchical leaching methods and proposes a method for extracting marine phosphorus. Methods for different forms of phosphorus in sediments to refine bioavailable phosphorus, further improve and focus on the research requirements of environmental geochemistry.
发明内容Contents of the invention
有鉴于此,为了解决现有提取方式无法完整提取沉积物中不同赋存形态磷的技术问题,本发明提供了一种提取海洋沉积物中不同赋存形态磷的方法,目的是能系统完整的提取海洋沉积物中不同赋存形态的磷。In view of this, in order to solve the technical problem that existing extraction methods cannot completely extract phosphorus in different forms of occurrence in sediments, the present invention provides a method for extracting phosphorus in different forms of occurrence in marine sediments, with the purpose of being able to systematically and completely Extraction of different forms of phosphorus in marine sediments.
为达到上述目的,本发明采用如下技术方案:In order to achieve the above objects, the present invention adopts the following technical solutions:
一种提取海洋沉积物中不同赋存形态磷的方法,包括以下步骤:A method for extracting phosphorus in different forms of occurrence in marine sediments, including the following steps:
1)利用pH值为8的MgCl2溶液作为提取剂对海洋沉积物样品进行提取,经离心分离后得到残渣a和含有弱吸附态磷的提取液;1) Use MgCl 2 solution with a pH value of 8 as an extractant to extract marine sediment samples, and obtain residue a and an extract containing weakly adsorbed phosphorus after centrifugal separation;
2)利用pH值为7.6的CDB溶液作为提取剂对步骤1)中的残渣a进行提取,离心分离后得到残渣b和上清液,将上清液经过强酸高温消解后,冷却得到透明色固体,并利用水溶解透明色固体,并调节pH值至3.0~3.1后即得到含闭蓄态磷的提取液;2) Use a CDB solution with a pH value of 7.6 as an extractant to extract the residue a in step 1). After centrifugation, obtain the residue b and the supernatant. After digesting the supernatant with strong acid at high temperature, cool it to obtain a transparent solid. , and use water to dissolve the transparent solid, and adjust the pH value to 3.0~3.1 to obtain an extract containing occluded phosphorus;
3)利用NaOH溶液作为提取剂对步骤2)中的残渣b进行提取,离心分离后得到残渣c和含铁/铝吸附态磷的提取液;3) Use NaOH solution as the extractant to extract the residue b in step 2), and obtain the residue c and the extract containing iron/aluminum adsorbed phosphorus after centrifugation;
4)利用NaAC-HAC缓冲液作为提取剂对步骤3)中的残渣c进行提取,离心分离后得到残渣d和上清液,调节上清液的pH值至3.0-3.1,得到含有自生磷灰石及钙结合态磷的提取液;4) Use NaAC-HAC buffer as the extraction agent to extract the residue c in step 3), obtain the residue d and the supernatant after centrifugation, adjust the pH value of the supernatant to 3.0-3.1, and obtain autogenous phosphorus-containing phosphorus. Extracts of stone and calcium-bound phosphorus;
5)利用HCl溶液作为提取剂对步骤4)中的残渣d进行提取,离心分离后得到残渣e和上清液,调节上清液的pH值至3.0-3.1,得到含有碎屑磷灰石的提取液;5) Use HCl solution as the extractant to extract the residue d in step 4), obtain the residue e and the supernatant after centrifugation, adjust the pH value of the supernatant to 3.0-3.1, and obtain detrital apatite-containing Extract;
6)将步骤5)中的残渣e经高温灼烧并冷却后,采用HCl溶液作为提取剂进行提取,经离心分离后得到残渣f和上清液,调节上清液的pH值至3.0-3.1,得到含有机磷的提取液;6) After burning and cooling the residue e in step 5) at high temperature, use HCl solution as the extractant to extract, obtain the residue f and the supernatant after centrifugation, and adjust the pH value of the supernatant to 3.0-3.1 , to obtain an extract containing organophosphorus;
7)将步骤6)中的残渣f进行高温消解并冷却后,采用HCl溶液作为提取剂进行提取,经离心分离后,调节上清液的pH值至3.0~3.1,得到含硅酸盐碎屑态磷的提取液。7) After high-temperature digestion and cooling of the residue f in step 6), use HCl solution as the extraction agent for extraction. After centrifugation, adjust the pH value of the supernatant to 3.0~3.1 to obtain silicate-containing debris. Phosphorus extract.
优选的,步骤1)所述MgCl2溶液的浓度为1mol/L,配制方法为:将203.3gMgCl2·6H2O溶于1L超纯水中,用10%的NH4OH调节pH至8。Preferably, the concentration of the MgCl 2 solution in step 1) is 1 mol/L, and the preparation method is: dissolve 203.3g MgCl 2 ·6H 2 O in 1 L of ultrapure water, and adjust the pH to 8 with 10% NH 4 OH.
优选的,步骤2)所述CDB溶液是利用32.4gC6H5Na3O7·2H2O、42gNaHCO3、2.87gNa2S2O4溶于500mL超纯水中配制而成,当天配置。Preferably, the CDB solution in step 2) is prepared by dissolving 32.4g C 6 H 5 Na 3 O 7 ·2H 2 O, 42g NaHCO 3 , and 2.87g Na 2 S 2 O 4 in 500 mL of ultrapure water, and is prepared on the same day.
优选的,步骤2)高温消解是取部分上清液于100ml消解管中,按体积比为1:2:7的硫酸、高氯酸和硝酸构成的混合溶液作为消解剂,其中硫酸为优级纯,硫酸含量为95%~98%,其密度为1.84g/cm3;硝酸为优级纯,硝酸含量为65%~68%;高氯酸为天津东方化工厂所生产。Preferably, step 2) high-temperature digestion is to take part of the supernatant in a 100ml digestion tube and use a mixed solution of sulfuric acid, perchloric acid and nitric acid in a volume ratio of 1:2:7 as the digestion agent, in which sulfuric acid is superior grade. Pure, with a sulfuric acid content of 95% to 98%, and a density of 1.84g/cm 3 ; nitric acid is superior grade pure, with a nitric acid content of 65% to 68%; perchloric acid is produced by Tianjin Dongfang Chemical Plant.
优选的,步骤3)所述NaOH溶液的浓度为0.1mol/L。Preferably, the concentration of the NaOH solution in step 3) is 0.1 mol/L.
优选的,步骤4)所述NaAC-HAC缓冲液的pH值为4,浓度为1mol/L。Preferably, the pH value of the NaAC-HAC buffer in step 4) is 4, and the concentration is 1 mol/L.
优选的,所述5)、步骤6)和步骤7)采用的HCl溶液浓度均为1mol/L。Preferably, the concentration of HCl solution used in step 5), step 6) and step 7) is 1 mol/L.
优选的,所述步骤6)中高温灼烧的温度为550℃,灼烧时间为4小时。Preferably, the temperature of high-temperature burning in step 6) is 550°C, and the burning time is 4 hours.
优选的,所述步骤7)中消解所加强酸为浓硫酸与高氯酸。Preferably, the acid enhanced for digestion in step 7) is concentrated sulfuric acid and perchloric acid.
优选的,本发明采用抗坏血酸还原磷钼蓝法(GB/T 12763.4-2007)分别测定出第一步磷形态提取液中弱吸附态磷的含量、第二步磷形态提取液中闭蓄态磷的含量、第三步磷形态提取液中铁/铝吸附态磷的含量、第四步磷形态提取液中自生磷灰石及钙结合态磷的含量、第五步磷形态提取液中碎屑磷灰石的含量、第六步磷形态提取液中有机磷的含量、第七步磷形态提取液中硅酸盐碎屑态磷的含量。Preferably, the present invention uses the ascorbic acid reduction phosphomolybdenum blue method (GB/T 12763.4-2007) to respectively measure the content of weakly adsorbed phosphorus in the phosphorus form extraction solution in the first step and the occluded phosphorus in the phosphorus form extraction solution in the second step. content, the content of iron/aluminum adsorbed phosphorus in the phosphorus form extraction solution in the third step, the content of authigenic apatite and calcium-bound phosphorus in the phosphorus form extraction solution in the fourth step, the detrital phosphorus in the phosphorus form extraction solution in the fifth step The content of limestone, the content of organic phosphorus in the phosphorus form extraction solution in the sixth step, and the silicate detrital phosphorus content in the phosphorus form extraction solution in the seventh step.
与现有技术相比,本发明具有以下有益效果:本发明是通过连续分级浸取方法对海洋沉积物中磷形态进行提取和分析,能够从海洋沉积物中充分获得不同赋存形态的磷,准确反映海洋沉积物中磷的存在形式以及生物可利用性。本发明的提取方式所需的海洋沉积物样品量少,且所采用的化学试剂简单、成本低。Compared with the existing technology, the present invention has the following beneficial effects: the present invention extracts and analyzes phosphorus forms in marine sediments through a continuous graded leaching method, and can fully obtain phosphorus in different forms from marine sediments. Accurately reflects the presence and bioavailability of phosphorus in marine sediments. The extraction method of the present invention requires a small amount of marine sediment samples, and the chemical reagents used are simple and low in cost.
附图说明Description of drawings
图1为本发明实施例1-12的采样站位图;Figure 1 is a sampling station location map of Embodiments 1-12 of the present invention;
图2为本发明海洋沉积物中不同赋存形态磷的提取流程图;Figure 2 is a flow chart for extracting phosphorus in different forms of occurrence in marine sediments according to the present invention;
图3为本发明实施例1-12中不同赋存形态磷的分布示意图。Figure 3 is a schematic diagram of the distribution of phosphorus in different forms in Examples 1-12 of the present invention.
具体实施方式Detailed ways
本发明提出一种提取海洋沉积物中不同赋存形态磷的方法,包括如下步骤:The present invention proposes a method for extracting phosphorus in different forms of occurrence in marine sediments, which includes the following steps:
1)将海洋沉积物和1mol/LpH值为8的氯化镁溶液使用涡旋混合器混合均匀,将混合物在室温下震荡提取2h后,以5000r/min的转速离心分离15min后,得到残渣a和第一步磷形态提取液。其中该步骤所得到的第一步磷形态提取液中含有弱吸附态磷(Lsor-P),该步骤的海洋沉积物,通过抓斗式采样器在所研究海域中采集表层约10cm的沉积物样品,在所述1mol/L的氯化镁溶液中滴加质量浓度为10wt%的氨水调节氯化镁溶液的pH值为8。1) Mix the marine sediment and 1 mol/L magnesium chloride solution with a pH value of 8 evenly using a vortex mixer. After shaking and extracting the mixture at room temperature for 2 hours, centrifuge at a speed of 5000 r/min for 15 minutes to obtain residue a and the first One-step phosphorus form extraction solution. The first step of the phosphorus form extraction solution obtained in this step contains weakly adsorbed phosphorus (Lsor-P). The marine sediments in this step are collected from the surface layer of about 10cm in the sea area under study through a grab sampler. For the sample, add dropwise ammonia water with a mass concentration of 10 wt% into the 1 mol/L magnesium chloride solution to adjust the pH value of the magnesium chloride solution to 8.
2)将残渣a与pH值为7.6的CDB溶液混合均匀,震荡提取6h后,以5000r/min的转速离心15min,得到残渣b和上清液;量取5ml上清液于消解管中,按硫酸、高氯酸、硝酸的体积比为1:2:7分别加入,随后进行高温消解,其中硫酸为优级纯,硫酸含量为95%~98%,其密度为1.84g/cm3;硝酸为优级纯,硝酸含量为65%~68%;高氯酸为天津东方化工厂所生产,直至高氯酸、硝酸全部分解,有硫酸回流时结束,冷却后有透明色固体,加水溶解后的液体为第二步磷形态提取液,其中也可以采用加水煮沸溶解的方法。2) Mix the residue a and the CDB solution with a pH value of 7.6 evenly. After shaking and extracting for 6 hours, centrifuge at a speed of 5000r/min for 15 minutes to obtain the residue b and the supernatant. Measure 5 ml of the supernatant into the digestion tube and press Sulfuric acid, perchloric acid, and nitric acid were added at a volume ratio of 1:2:7, followed by high-temperature digestion. The sulfuric acid was of superior purity, with a sulfuric acid content of 95% to 98% and a density of 1.84g/cm 3 ; nitric acid It is superior grade pure, with a nitric acid content of 65% to 68%; perchloric acid is produced by Tianjin Dongfang Chemical Factory. It will be used until the perchloric acid and nitric acid are completely decomposed and sulfuric acid is refluxed. After cooling, a transparent solid will appear. After adding water to dissolve The liquid is the second step phosphorus form extraction liquid, which can also be dissolved by adding water and boiling.
所述CDB溶液是利用32.4gC6H5Na3O7·2H2O、42g NaHCO3、2.87g Na2S2O4溶于500mL超纯水中配制而成。The CDB solution is prepared by dissolving 32.4g C 6 H 5 Na 3 O 7 ·2H 2 O, 42g NaHCO 3 , and 2.87g Na 2 S 2 O 4 in 500 mL ultrapure water.
该步骤中,用0.1mol/L的氢氧化钠溶液或10mol/L氢氧化钠溶液将第二步磷形态提取液的pH调节至3.0-3.1,得到含有闭蓄态磷(Oc-P)的提取液。In this step, use 0.1 mol/L sodium hydroxide solution or 10 mol/L sodium hydroxide solution to adjust the pH of the phosphorus form extraction solution in the second step to 3.0-3.1 to obtain occluded phosphorus (Oc-P). Extract liquid.
3)将残渣b与0.1mol/L的氢氧化钠溶液混合均匀,震荡提取18h后,以5000r/min的转速离心15min,得到残渣c和第三步磷形态提取液。3) Mix residue b with 0.1 mol/L sodium hydroxide solution evenly, shake and extract for 18 hours, and then centrifuge at 5000 r/min for 15 minutes to obtain residue c and the third step phosphorus form extraction solution.
4)将残渣c与1mol/LpH=4的NaAC-HAC缓冲液混合均匀,震荡提取5h后,以5000r/min的转速离心15min,得到残渣d和第四步磷形态提取液;4) Mix the residue c with 1 mol/L NaAC-HAC buffer with pH=4, shake and extract for 5 hours, and then centrifuge at a speed of 5000 r/min for 15 minutes to obtain the residue d and the fourth step phosphorus form extract;
该步骤中,用1mol/L的盐酸将第四步磷形态提取液的pH调节至3.0-3.1,得到含有自生磷灰石及钙结合态磷(Ca-P)的提取液。In this step, 1 mol/L hydrochloric acid is used to adjust the pH of the phosphorus form extraction solution in the fourth step to 3.0-3.1 to obtain an extract solution containing authigenic apatite and calcium-bound phosphorus (Ca-P).
5)将残渣d与1mol/L的盐酸混合均匀,震荡提取16h后,以5000r/min的转速离心15min,得到残渣e和第五步磷形态提取液;5) Mix the residue d with 1 mol/L hydrochloric acid evenly, shake and extract for 16 hours, and then centrifuge at a speed of 5000 r/min for 15 minutes to obtain the residue e and the fifth step phosphorus form extraction solution;
该步骤中,用0.1mol/L的氢氧化钠溶液或10mol/L氢氧化钠溶液将第五步磷形态提取液的pH调节至3.0-3.1,得到含有碎屑磷灰石(De-P)的提取液。In this step, use 0.1 mol/L sodium hydroxide solution or 10 mol/L sodium hydroxide solution to adjust the pH of the phosphorus form extraction solution in the fifth step to 3.0-3.1 to obtain detrital apatite (De-P). of the extract.
6)将残渣e全部转移至坩埚后置于马弗炉中,在550℃下灰化处理4h。将灰化后并冷却的残渣e与1mol/L的盐酸混合均匀,震荡提取15h后,以5000r/min的转速离心15min,得到残渣f和第六步磷形态提取液。6) Transfer all the residue e to the crucible, place it in a muffle furnace, and ashe it at 550°C for 4 hours. Mix the ashed and cooled residue e with 1 mol/L hydrochloric acid evenly. After shaking and extracting for 15 hours, centrifuge at a speed of 5000 r/min for 15 minutes to obtain the residue f and the phosphorus form extract in step 6.
该步骤中,用0.1mol/L的氢氧化钠溶液或10mol/L氢氧化钠溶液将第六步磷形态提取液的pH调节至3.0-3.1,得到含有有机磷(OP)的提取液。In this step, use 0.1 mol/L sodium hydroxide solution or 10 mol/L sodium hydroxide solution to adjust the pH of the phosphorus form extraction solution in the sixth step to 3.0-3.1 to obtain an extract solution containing organophosphorus (OP).
7)将残渣f全量转移至消解管中,加入4ml硫酸含量为95%~98%的优级纯浓硫酸,5滴高氯酸,进行高温消解至残渣全部变白后,继续消解20min;自然冷却后与1mol/LHCl混合均匀,振荡提取8h,以5000r/min的转速离心15min,得到第七步磷形态提取液。7) Transfer the entire amount of the residue f to the digestion tube, add 4 ml of high-grade pure concentrated sulfuric acid with a sulfuric acid content of 95% to 98%, and 5 drops of perchloric acid, and perform high-temperature digestion until all the residue turns white, then continue digestion for 20 minutes; naturally After cooling, mix it evenly with 1mol/LHCl, oscillate and extract for 8 hours, and centrifuge at 5000r/min for 15min to obtain the phosphorus form extraction solution in the seventh step.
该步骤中,用0.1mol/L的氢氧化钠溶液或10mol/L氢氧化钠溶液将第七步磷形态提取液的pH调节至3.0-3.1,得到含有硅酸盐碎屑态磷(SIF-P)的提取液。In this step, use 0.1 mol/L sodium hydroxide solution or 10 mol/L sodium hydroxide solution to adjust the pH of the phosphorus form extraction solution in the seventh step to 3.0-3.1 to obtain silicate crumb state phosphorus (SIF- P) extract.
本发明通过采用上述方法提取海洋沉积物中不同赋存形态的磷,能够系统完整地分析和研究海洋中磷的存在形式以及生物可利用性。By using the above method to extract phosphorus in different forms of occurrence in marine sediments, the present invention can systematically and completely analyze and study the existence forms and bioavailability of phosphorus in the ocean.
本发明采用抗坏血酸还原磷钼蓝法(GB/T 12763.4-2007)分别测定出第一步磷形态提取液中弱吸附态磷(Lsor-P)的含量、第二步磷形态提取液中闭蓄态磷(Oc-P)的含量、第三步磷形态提取液中铁/铝吸附态磷(Fe/Al-P)的含量、第四步磷形态提取液中自生磷灰石及钙结合态磷(Ca-P)的含量、第五步磷形态提取液中碎屑磷灰石(De-P)的含量、第六步磷形态提取液中有机磷(OP)的含量、第七步磷形态提取液中硅酸盐碎屑态磷(SIF-P)的含量。The present invention adopts the ascorbic acid reduction phosphomolybdenum blue method (GB/T 12763.4-2007) to respectively measure the content of weakly adsorbed phosphorus (Lsor-P) in the phosphorus form extraction solution in the first step, and the content of occlusion in the phosphorus form extraction solution in the second step. The content of phosphorus (Oc-P), the content of iron/aluminum adsorbed phosphorus (Fe/Al-P) in the phosphorus form extraction solution in the third step, authigenic apatite and calcium-bound phosphorus in the phosphorus form extraction solution in the fourth step (Ca-P) content, the content of detrital apatite (De-P) in the phosphorus form extraction solution in the fifth step, the organic phosphorus (OP) content in the phosphorus form extraction solution in the sixth step, the phosphorus form in the seventh step The content of silicate fragment phosphorus (SIF-P) in the extract.
利用Excle、Origin、Surfer等数据统计、分析软件及作图软件,进一步分析其相对含量和空间分布。Use Excel, Origin, Surfer and other data statistics, analysis software and drawing software to further analyze its relative content and spatial distribution.
下面结合附图和实施例对本发明作进一步的详细说明。本发明以下实施例所采用的海洋沉积物样本是2019年10月采用抓斗式采样器分别在渤海湾近岸海域的12个站位采集表层厚约10cm的沉积物样品,现场混匀后封存于聚乙烯密封袋中,4℃保存,采样站位如图1所示。The present invention will be further described in detail below in conjunction with the accompanying drawings and examples. The marine sediment samples used in the following examples of the present invention were sediment samples with a surface thickness of about 10 cm that were collected using grab samplers at 12 stations in the coastal waters of Bohai Bay in October 2019, and were mixed on site and sealed. Store in a polyethylene sealed bag at 4°C. The sampling station is as shown in Figure 1.
实施例1Example 1
一种提取海洋沉积物中不同赋存形态磷的方法,参照图2所述,具体步骤如下:A method for extracting different forms of phosphorus in marine sediments is described with reference to Figure 2. The specific steps are as follows:
本发明的发明人于2019年10月,用抓斗式采样器分别在渤海湾近岸海域的12个站位采集表层厚约10cm的沉积物样品,现场混匀后封存于聚乙烯密封袋中,4℃保存。In October 2019, the inventor of the present invention used a grab sampler to collect sediment samples with a surface thickness of about 10cm at 12 stations in the coastal waters of the Bohai Bay. They mixed them on site and sealed them in polyethylene sealing bags. , stored at 4°C.
对上述采集12个沉积物样品分别按照以下步骤进行不同形态磷的提取和测定,具体实施的流程图参见图2所示,详细步骤如下:The 12 sediment samples collected above were extracted and measured in different forms of phosphorus according to the following steps. The specific implementation flow chart is shown in Figure 2. The detailed steps are as follows:
步骤1,向相当于1g干样的1#湿沉积物样品中加入20ml 1mol/L的MgCl2(pH=8),置于涡旋混合器上将沉积物样品与提取剂混合均匀,在25℃下,置于康氏振荡器上以200r/min振荡提取2h,以5000r/min转速离心15min,得到残渣a与上清液,取上清液得到第一步磷形态提取液。测定出第一步磷形态提取液中弱吸附态磷(Lsor-P)的含量。Step 1: Add 20ml of 1mol/L MgCl 2 (pH=8) to the 1# wet sediment sample equivalent to 1g of dry sample, place it on a vortex mixer, mix the sediment sample and the extractant evenly, and mix at 25 ℃, place it on a Conis shaker and oscillate at 200r/min for extraction for 2h, centrifuge at 5000r/min for 15min to obtain residue a and supernatant, and take the supernatant to obtain the first step of phosphorus form extraction solution. The content of weakly adsorbed phosphorus (Lsor-P) in the phosphorus form extraction solution in the first step was measured.
步骤2,在残渣a中加入20ml pH为7.6的C6H5Na3O7·2H2O、NaHCO3与Na2S2O4的混合溶液,混合均匀,在25℃下振荡提取6h,以5000r/min转速离心15min,得到残渣b与上清液,取上清液5ml放入100ml消解管中,加入5ml按硫酸、高氯酸、硝酸的体积比为1:2:7的强酸,随后在消解仪上进行消解,逐渐升高温度,消解至高氯酸、硝酸全部分解,有硫酸回流时结束,冷却后有白色透明的固体,加水溶解后的液体为第二步磷形态提取液,加一滴2,4-二硝基苯,混匀,用0.1mol/L的氢氧化钠溶液或10mol/L氢氧化钠溶液将第二步磷形态提取液的pH调节至3.0-3.1,测定出闭蓄态磷(Oc-P)的含量。Step 2: Add 20 ml of a mixed solution of C 6 H 5 Na 3 O 7 ·2H 2 O, NaHCO 3 and Na 2 S 2 O 4 with a pH of 7.6 to residue a, mix evenly, and shake and extract at 25°C for 6 hours. Centrifuge at 5000r/min for 15min to obtain residue b and supernatant. Take 5ml of the supernatant and put it into a 100ml digestion tube. Add 5ml of strong acid with a volume ratio of sulfuric acid, perchloric acid and nitric acid of 1:2:7. Then the digestion is carried out on the digestion instrument, and the temperature is gradually increased until the perchloric acid and nitric acid are completely decomposed. The digestion ends when sulfuric acid refluxes. After cooling, a white and transparent solid will appear. The liquid after adding water to dissolve it is the second step phosphorus form extraction solution. Add a drop of 2,4-dinitrobenzene, mix well, use 0.1mol/L sodium hydroxide solution or 10mol/L sodium hydroxide solution to adjust the pH of the second step phosphorus form extraction solution to 3.0-3.1, and measure the The content of occluded phosphorus (Oc-P).
步骤3,在残渣b中加入20ml 0.1mol/LNaOH,混合均匀,在25℃下振荡提取18h,以5000r/min转速离心15min,得到残渣c与第三步磷形态提取液。测定出第三步磷形态提取液中铁/铝吸附态磷(Fe/Al-P)的含量。Step 3: Add 20 ml of 0.1 mol/L NaOH to residue b, mix evenly, shake and extract at 25°C for 18 hours, and centrifuge at 5000 r/min for 15 minutes to obtain the extract of residue c and the third step of phosphorus form. The content of iron/aluminum adsorbed phosphorus (Fe/Al-P) in the phosphorus form extraction solution in the third step was measured.
步骤4,在残渣c中加入20ml 1mol/LpH为4的NaAC-HAC缓冲液,混合均匀在25℃下振荡提取5h,以5000r/min转速离心15min,得到残渣d与第四步磷形态提取液,用1mol/L的盐酸将第四步磷形态提取液的pH调节至3.0-3.1,测定出自生磷灰石及钙结合态磷(Ca-P)的含量。Step 4: Add 20ml of 1mol/L NaAC-HAC buffer with a pH of 4 to the residue c, mix evenly, shake and extract at 25°C for 5 hours, and centrifuge at 5000r/min for 15min to obtain the extract of the residue d and the phosphorus form in the fourth step. , use 1 mol/L hydrochloric acid to adjust the pH of the phosphorus form extraction solution in the fourth step to 3.0-3.1, and measure the content of autogenous apatite and calcium-bound phosphorus (Ca-P).
步骤5,在残渣d中加入20ml 1mol/L HCl,用涡旋混合器混合均匀,在25℃下振荡提取16h,以5000r/min转速离心15min,得到残渣e与第五步磷形态提取液,用0.1mol/L的氢氧化钠溶液或10mol/L氢氧化钠溶液将第五步磷形态提取液的pH调节至3.0-3.1。测定出第五步磷形态提取液中碎屑磷灰石(De-P)的含量。Step 5: Add 20ml of 1mol/L HCl to the residue d, mix evenly with a vortex mixer, oscillate and extract at 25°C for 16 hours, and centrifuge at 5000r/min for 15min to obtain the extract of the residue e and the phosphorus form in the fifth step. Use 0.1 mol/L sodium hydroxide solution or 10 mol/L sodium hydroxide solution to adjust the pH of the phosphorus form extraction solution in the fifth step to 3.0-3.1. The content of detrital apatite (De-P) in the phosphorus form extraction solution in the fifth step was measured.
步骤6,将残渣e全部转移至瓷坩埚内,置于马弗炉内,在550℃下灼烧4h,冷却后全部转移回离心管,加入20ml 1mol/L HCl,混合均匀,在25℃下振荡提取15h,以5000r/min转速离心15min,得到残渣f与第六步磷形态提取液,用0.1mol/L的氢氧化钠溶液或10mol/L氢氧化钠溶液将第六步磷形态提取液的pH调节至3.0-3.1。测定出第六步磷形态提取液中有机磷(OP)的含量。Step 6: Transfer all the residue e to a porcelain crucible, place it in a muffle furnace, burn it at 550°C for 4 hours, transfer it all back to the centrifuge tube after cooling, add 20ml 1mol/L HCl, mix evenly, and heat at 25°C Extract with oscillation for 15 hours, and centrifuge at 5000r/min for 15 minutes to obtain the residue f and the sixth step phosphorus form extract. Use 0.1 mol/L sodium hydroxide solution or 10 mol/L sodium hydroxide solution to separate the sixth step phosphorus form extract. Adjust the pH to 3.0-3.1. Determine the content of organophosphorus (OP) in the phosphorus form extraction solution in the sixth step.
步骤7,将残渣f全量转移到消解管中,加入4ml浓硫酸和5滴高氯酸,消解仪消解至全部变白后,继续消解20min;自然冷却后加20ml 1mol/L HCl转移回离心管,振荡提取8h,离心15min,得到第七步磷形态提取液,用0.1mol/L的氢氧化钠溶液或10mol/L氢氧化钠溶液将第七步磷形态提取液的pH调节至3.0-3.1。测定出第七步磷形态提取液中硅酸盐碎屑态磷(SIF-P)的含量。Step 7: Transfer the entire amount of residue f to the digestion tube, add 4 ml of concentrated sulfuric acid and 5 drops of perchloric acid, and digest it until everything turns white. Continue the digestion for 20 minutes. After natural cooling, add 20 ml of 1mol/L HCl and transfer it back to the centrifuge tube. , shake and extract for 8 hours, and centrifuge for 15 minutes to obtain the phosphorus form extract in the seventh step. Use 0.1mol/L sodium hydroxide solution or 10mol/L sodium hydroxide solution to adjust the pH of the phosphorus form extract in the seventh step to 3.0-3.1 . The content of silicate fragment phosphorus (SIF-P) in the phosphorus form extraction solution in the seventh step was measured.
实施例2-12Example 2-12
采用实施例1的方式分别对海洋沉积物样品2#-12#进行处理,并获取不同赋存形态的磷。Marine sediment samples 2#-12# were processed in the same manner as in Example 1, and phosphorus in different forms was obtained.
实施例1-12的测定结果如图3所示。The measurement results of Examples 1-12 are shown in Figure 3.
由图3可以看出,采用本发明的分级提取方法,能够从海洋沉积物样品中获得七种不同赋存形态的磷,同时各种形态的磷含量存在显著的差异。如图3所示,各形态磷含量变化依次为碎屑磷灰石(De-P)>有机磷(OP)>闭蓄态磷(Oc-P)>硅酸盐碎屑态磷(SIF-P)>铁/铝吸附态磷(Fe/Al-P)>自生磷灰石及钙结合态磷(Ca-P)>弱吸附态磷(Lsor-P),同时1-12样品中的碎屑磷灰石(De-P)、有机磷(OP)、闭蓄态磷(Oc-P)、硅酸盐碎屑态磷(SIF-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、弱吸附态磷(Lsor-P)的平均占比分别为:53.95%、15.89%、11.78%、9.01%、5.66%、2.80%、0.91%。It can be seen from Figure 3 that using the hierarchical extraction method of the present invention, seven different forms of phosphorus can be obtained from marine sediment samples. At the same time, there are significant differences in the phosphorus content of various forms. As shown in Figure 3, the changes in the phosphorus content of each form are in the order of detrital apatite (De-P) > organic phosphorus (OP) > occluded phosphorus (Oc-P) > silicate detrital phosphorus (SIF- P)> Iron/aluminum adsorbed phosphorus (Fe/Al-P)> authigenic apatite and calcium-bound phosphorus (Ca-P)> weakly adsorbed phosphorus (Lsor-P), while the crushed phosphorus in samples 1-12 Detrital apatite (De-P), organic phosphorus (OP), occluded phosphorus (Oc-P), silicate detrital phosphorus (SIF-P), iron/aluminum adsorbed phosphorus (Fe/Al- The average proportions of P), authigenic apatite and calcium-bound phosphorus (Ca-P), and weakly adsorbed phosphorus (Lsor-P) are: 53.95%, 15.89%, 11.78%, 9.01%, 5.66%, 2.80 respectively %, 0.91%.
其中样品1#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:0.76%、18.99%、8.22%、2.69%、49.19%、12.30%、7.85%。Among them, the weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus ( The proportions of Ca-P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) are respectively: 0.76%, 18.99%, 8.22%, and 2.69 %, 49.19%, 12.30%, 7.85%.
样品2#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:0.85%、6.25%、3.37%、2.28%、69.09%、10.56%、7.61%。In sample 2#, the above weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 0.85%, 6.25%, 3.37%, and 2.28% respectively. , 69.09%, 10.56%, 7.61%.
样品3#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:1.16%、16.24%、5.87%、5.76%、42.51%、20.75%、7.72%。In sample 3#, the above weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 1.16%, 16.24%, 5.87%, and 5.76% respectively. , 42.51%, 20.75%, 7.72%.
样品4#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:1.04%、16.21%、8.08%、3.28%、45.27%、18.93%、7.19%。In sample 4#, the above weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 1.04%, 16.21%, 8.08%, and 3.28% respectively. , 45.27%, 18.93%, 7.19%.
样品5#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:1.01%、8.95%、7.60%、2.47%、52.86%、16.94%、10.16%。In sample 5#, the above-mentioned weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 1.01%, 8.95%, 7.60%, and 2.47% respectively. , 52.86%, 16.94%, 10.16%.
样品6#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:1.26%、17.06%、3.90%、3.04%、54.34%、13.05%、7.34%。In sample 6#, the above weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 1.26%, 17.06%, 3.90%, and 3.04% respectively. , 54.34%, 13.05%, 7.34%.
样品7#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:0.93%、9.97%、7.26%、3.00%、51.55%、19.87%、7.43%。In sample 7#, the above weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 0.93%, 9.97%, 7.26%, and 3.00% respectively. , 51.55%, 19.87%, 7.43%.
样品8#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:0.52%、9.72%、3.35%、1.75%、68.02%、9.43%、7.21%。In sample 8#, the above-mentioned weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) are respectively: 0.52%, 9.72%, 3.35%, and 1.75% , 68.02%, 9.43%, 7.21%.
样品9#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:0.90%、11.56%、5.84%、1.63%、54.47%、17.28%、8.32%。In sample 9#, the above weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 0.90%, 11.56%, 5.84%, and 1.63% respectively. , 54.47%, 17.28%, 8.32%.
样品10#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:0.95%、7.28%、5.80%、2.53%、54.64%、16.65%、12.14%。In sample 10#, the above weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) are respectively: 0.95%, 7.28%, 5.80%, and 2.53% , 54.64%, 16.65%, 12.14%.
样品11#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:0.76%、10.06%、4.64%、2.42%、49.24%、19.48%、13.39%。In sample 11#, the above weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 0.76%, 10.06%, 4.64%, and 2.42% respectively. , 49.24%, 19.48%, 13.39%.
样品12#中上述弱吸附态磷(Lsor-P)、闭蓄态磷(Oc-P)、铁/铝吸附态磷(Fe/Al-P)、自生磷灰石及钙结合态磷(Ca-P)、碎屑磷灰石(De-P)、有机磷(OP)、硅酸盐碎屑态磷(SIF-P)的占比分别为:0.83%、9.02%、4.01%、2.77%、56.18%、15.48%、11.71%。In sample 12#, the above-mentioned weakly adsorbed phosphorus (Lsor-P), occluded phosphorus (Oc-P), iron/aluminum adsorbed phosphorus (Fe/Al-P), authigenic apatite and calcium-bound phosphorus (Ca -P), detrital apatite (De-P), organic phosphorus (OP), and silicate detrital phosphorus (SIF-P) account for 0.83%, 9.02%, 4.01%, and 2.77% respectively. , 56.18%, 15.48%, 11.71%.
另外,本发明实施例提出的一种提取海洋沉积物中不同赋存形态磷的方法以标准物质(GBW07333)验证。采用改进的海洋沉积物中磷赋存形态的连续分级浸取方法对黄海海洋沉积物标准物质(GBW07333)进行磷形态分析,七步连续分级浸取中各步精密度分别为:第一步:2.7%、第二步:4.5%、第三步:1.9%、第四步:3.2%、第五步:4.1%、第六步:1.6%、第七步:2.7%,实测七步磷形态总和与标准值之间的误差范围为6.3%~10.3%。因此本发明实施例提出的通过连续分级浸取提取海洋沉积物中不同赋存形态的磷的方法可应用于海洋沉积物中磷形态的分离提取。In addition, a method for extracting phosphorus in different forms present in marine sediments proposed in the embodiment of the present invention was verified with a standard material (GBW07333). The improved continuous graded leaching method of phosphorus occurrence forms in marine sediments was used to analyze the phosphorus form of the Yellow Sea marine sediment standard material (GBW07333). The precision of each step in the seven-step continuous graded leaching is as follows: Step 1: 2.7%, second step: 4.5%, third step: 1.9%, fourth step: 3.2%, fifth step: 4.1%, sixth step: 1.6%, seventh step: 2.7%, measured seven-step phosphorus form The error range between the sum and the standard value is 6.3% to 10.3%. Therefore, the method proposed by the embodiment of the present invention to extract phosphorus in different forms in marine sediments through continuous graded leaching can be applied to the separation and extraction of phosphorus forms in marine sediments.
以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员来说,在不脱离本发明原理的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围。The above are only preferred embodiments of the present invention. It should be noted that those skilled in the art can make several improvements and modifications without departing from the principles of the present invention. These improvements and modifications can also be made. should be regarded as the protection scope of the present invention.
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