离子色谱法测定海水中氯离子和硫酸根离子

氯离子和硫酸根离子是海水中重要的无机阴离子,在研究海洋生态变化、海洋循环作用过程与海洋全球气候变化等领域具有重要的指示意义。其测定方法较多,但缺少相应的测试方法。本文对测定海水中Cl^–,SO₄^2–的离子色谱方法进行了优化,选用IonPacAS14碳酸盐选择性离子色谱柱,以3.5mmol/L Na₂CO₃+1 mmol/L NaHCO₃为流动相,可消除海水样品中碳酸盐及其他阴离子的干扰。该方法对Cl^–检出限为0.29mg/L,线性相关系数r²=0.999 2,对SO₄^2–检出限为0.42mg/L,线性相关系数r²=0.997 9。样品的加标回收率在95%～102%,Cl^–和SO₄^2–的相对标准偏差分别为1.92%和4.18%。该方法简便、迅速、灵敏、准确度高,可满足批量海水样品中Cl<...     

海水营养盐自动测定研究--Ⅲ.磷酸盐和硅酸盐的反流动注射分析

采用因子设计和单纯形优化对反流动注射分析测定海水中的PO₄³和SiO₃²进行了条件优化选择.设计的分析线路可以实现PO₄³、SiO₃²连续测定.样品测定速度为30个/h.PO₄³的测定存在明显的盐效应.SiO₃²的测定没有盐效应.彼此之间的干扰可以忽略.对实际样品测定并与规范法对比,二者结果基本一致.     

薄层流动玻炭金膜电极阳极溶出伏安法测定海水中痕量银

本文提出了测定海水中痕量银的新方法.实验结果表明,用玻炭金膜电极与薄层流动示差脉冲溶出法相结合,改善了玻炭电极的重现性,提高了测定银的灵敏度.实验中,控制流速为1.8-2.0毫升/分,电极电位取-0.6伏,银峰电位在0-+0.9伏之间,灵敏度、线性、重现性和干扰实验均获得较好的结果.海水不经预富集,在天然海水中加入纯硝酸至酸度为0.025M,即可进行测定.实验可得到清晰的示差脉冲阳极溶出峰,方法灵敏度为1×10-10M,重复测定六次的标准偏差小于±2%,回收率为85-96%.应用本方法测定了厦门港海水、外海海水等水样,均得到满意的结果.     

离子迁移谱现场观测渤海和北黄海二甲基硫的研究

渤海、黄海是高产二甲基硫（Dimethyl Sulfide, DMS）的大陆架海区。该海区DMS的现场调查研究有助于准确评估海洋DMS释放量及其对全球气候变化的负反馈作用。目前,无论是基于模型还是直接测量法的通量估算均以表层海水或低层大气DMS浓度为基础,因此,先进的检测技术对其通量估算的准确度具有决定性作用。气相色谱法、质谱法、化学发光法以及卫星遥感技术是现在常用的观测技术,而本文则基于苯辅助光电离离子迁移谱技术进一步提出了一种可在海域现场观测海水中DMS的方法。通过结合动态气提-Nafion管在线除水进样系统,消除环境水汽的干扰;在最优条件下,基于DMS两个产物离子峰,可以实现0.10～120 nmol/L之间DMS的定量分析,检测限低至0.065 nmol/L;然后将所建方法应用于2019年秋季渤海、北黄海海水中DMS的现场观测。结果表明,表层海水中DMS的浓度为0.080～0.96 nmol/L（平均值为（0.44±0.34）nmol/L）,其海气通量为0.12～17.75 μmol/（m²·d）（平均值为（ 3.23±4.02）μmol/（m²·d））;通过结合实验室检测结果、环境因子和浮游植物群落结构讨论了海水样品低温储存条件下DMS的变化和影响因素,结果显示,营养盐成分及浮游植物群落结构是影响储存样品中DMS浓度显著增加的主要因素,进一步表明了现场观测方法的建立对海洋DMS释放量的准确评估具有重要意义。     

EGTA滴定法测定海水Ca2+浓度精度评估及其在近海海域实测的必要性

海水Ca²⁺浓度是计算碳酸钙饱和度的重要参数之一,通常由海水钙盐比值计算得出,但该方法在受多种因素影响的近海海域可能不适用。本研究开展了EGTA自动电位滴定法对不同盐度海水Ca²⁺浓度测定精度和准确度的研究,探究“盐效应”对Ca²⁺浓度测定可能存在的影响,并比较了近海养殖区海水实测Ca²⁺浓度与通过钙盐比估算值的差异。研究表明：(1)EGTA自动电位滴定法测定不同盐度海水Ca²⁺浓度精度较高,在各个盐度条件下,5次平行测定的标准偏差为0.001～0.006 mmol/kg,精度均优于0.1%;(2)在盐度20.00～34.62范围内,Ca²⁺的实测值与通过钙盐比值计算所得的相对误差为-0.043%～0.023%,准确度在±0.05%内;(3)不同盐度海水样品Ca²⁺浓度的实测值与理论值基本吻合,电位滴定法测定Ca²⁺浓度不存在“盐效应”问题;(4)受陆源输入过程的影响,近海(烟台牟平养殖区)表层及底层海水Ca     

流动注射Ferene分光光度法测定海水中溶解态铁的方法优化

热液流体中溶解态铁是海水原位测量的重要参数之一。本研究采用Ferene分光光度法,搭建流动注射分析系统,优化进样条件、显色条件,实现了热液流体中溶解态铁的在线测定。结果表明,测定Fe(II)时,Ferene、缓冲液浓度分别为8×10–3、0.4 mol/L,Ferene、样品流速分别为0.8、0.6 m L/min,显色盘管长度为40 cm时,方法的灵敏度、检测限最佳;测定Fe(III)时,Ferene、缓冲液、抗坏血酸浓度分别为1×10–2、0.5、0.01 mol/L,Ferene/抗坏血酸、样品流速均为1.0 m L/min,还原、显色盘管长度均为40 cm时,方法的灵敏度、检测限最佳。最佳实验条件下,Fe(II)、Fe(III)在0.2~10μmol/L和0.5~16μmol/L范围内,工作曲线回归方程分别为A=0.0834 C+0.0564(μmol/L,n=8,R2=0.997)和A=0.0478C+0.0423(μmol/L,n=8,R2=0.997)。Fe(II)、Fe(III)检测限分别为24、39 nmol/L,相对标准偏差分别为0.8%、1.2%(n=10),加标回收率为97.9%~103.0%。共存离子实验表明,流体中的Na+、Mn2+、Cu2+、Cu+不会对测量造成干扰。     

刻蚀不锈钢丝固相微萃取-气相色谱法检测海水中多氯联苯

用氢氟酸刻蚀不锈钢丝制作了固相微萃取(solid-phase microextraction, SPME)纤维,与气相色谱(gas chromatography, GC)联用直接测定了海水水样中的痕量多氯联苯(polychlorinated biphenyls, PCBs),优化了萃取时间、萃取温度、搅拌速率、解吸温度和解吸时间对SPME的萃取效率的影响。本方法的线性范围可达两个数量级,PCB28和PCB52的线性范围是1.0～100.0 ng/L,其他8种PCBs的线性范围是0.5～50.0 ng/L(除PCB198外,r²均在0.99以上),检出限为0.01～0.10 ng/L。单个纤维间及纤维与纤维间的相对标准偏差分别为2.4%～7.2%和4.9%～8.7%。实际海水样品的加标回收率为80.9%～106.0%。微萃取纤维机械强度高、耐海水腐蚀、寿命长、制作成本低,该方法适用于测定海水水样中的痕量PCBs。     

海水中硫丹及衍生物气相色谱快速测定及应用

通过固相微萃取(SPME)技术富集海水中6种硫丹及其衍生物,使用气相色谱-电子捕获检测器(GC-μECD)测定和外标法定量,建立海水中硫丹及其衍生物的快速测定方法。结果表明:硫丹及其衍生物的线性范围为2.5～100.0μg/L,相关系数为0.990～0.998,检出限为0.10～21.30 ng/L。在3个加标条件(5,10和25μg/L)下,人工海水硫丹的加标回收率为85.60%～119.50%,相对标准偏差(n=6)为1.3%～7.8%。实际海水硫丹的加标回收率为90.60%～120.70%,相对标准偏差为1.6%～7.9%。该方法应用于青岛近岸海域海水的测试,在青岛近岸水体中未检出α-硫丹和β-硫丹,检出硫丹衍生物:硫丹醚(N.D.～1.758μg/L),硫丹内酯(1.040～11.260μg/L)和硫丹硫酸酯(1.009～6.091μg/L)。实际应用表明该方法前处理简便易行、灵敏度高,并可满足海水中硫丹及其衍生物的快速检测分析。     

海水中硫丹及其衍生物气相色谱快速测定及应用

通过固相微萃取(SPME)技术富集海水中6种硫丹及其衍生物,使用气相色谱-电子捕获检测器(GC-μECD)测定和外标法定量,建立海水中硫丹及其衍生物的快速测定方法。结果表明:硫丹及其衍生物的线性范围为2.5～100.0μg/L,相关系数为0.990～0.998,检出限为0.10～21.30 ng/L。在3个加标条件(5,10和25μg/L)下,人工海水硫丹的加标回收率为85.60%～119.50%,相对标准偏差(n=6)为1.3%～7.8%。实际海水硫丹的加标回收率为90.60%～120.70%,相对标准偏差为1.6%～7.9%。该方法应用于青岛近岸海域海水的测试,在青岛近岸水体中未检出α-硫丹和β-硫丹,检出硫丹衍生物:硫丹醚(N.D.～1.758μg/L),硫丹内酯(1.040～11.260μg/L)和硫丹硫酸酯(1.009～6.091μg/L)。实际应用表明该方法前处理简便易行、灵敏度高,并可满足海水中硫丹及其衍生物的快速检测分析。     

海水中铋(Ⅲ)的微分电位溶出分析

利用微分电位溶出分析法研究了海水中痕量铋（III）的最适测定条件。结果表明，实验条件选择电解电位（E）为-1．10V，溶出上限电位（E上）为-0.70V，溶出下限电位（E下）为-0．00V，工作电极旋转速度2500rpm.洗电极时间和富集时间分别为30s和600s。适宜的盐度和酸度为5．8－29．0×10-2mol／L和1．00-2.00×10-mol／LHNO3。对在海水中加入5μg／L铋（III）的样品8次测定的相对标准偏差为53％。校正曲线方程为Y=4.77＋55X,相关系数（γ）为0．9993。对青岛沿岸海水测定的加入回收率为96．5％。1994年利用该方法测定青岛沿岸海水中铋（III）的浓度为0．017－0．103μg／L。     

A simplified automated chelometric method for the determination of sulfate in interstitial water and seawater

A method is described for the determination of sulfate in interstitial water and seawater. After BaSO₄ precipitation, the Ba²⁺ excess is titrated with EDTA using an amalgated silver electrode for end-point detection. An accuracy better than 0.5% is obtained using this method.     

Calibration of a chalcogenide glass membrane ion-selective electrode for the determination of free Fe in seawater: I. Measurements in UV photooxidised seawater

Calibration of a chalcogenide glass membrane, Fe(III)ISE [Fe_2.5(Ge₂₈Sb₁₂Se₆₀)_97.5], in buffered saline media has been undertaken in order to assess the suitability of this ISE for seawater analyses. The electrode slopes in saline citrate and salicylate buffers were 26.3 and 28.2 mV/decade, respectively, for Fe³⁺ concentrations ranging from 10⁻¹⁰ M to less than 10⁻²⁵ M Fe³⁺. The calibration lines in the citrate and salicylate buffers were essentially collinear with the response in unbuffered chloride-free standards containing >10⁻⁵ M Fe³⁺, demonstrating that the response of the FeISE is unaffected by chloride ions. A mechanism involving a combination of charge transfer and ion-exchange of Fe(III), at the electrode diffusion layer, can be used to explain the ≈30 mV/decade slope of the FeISE. The response of the FeISE in UV photooxidised seawater containing 8 nM total Fe was measured as the pH was changed from 8.27 to 3.51. The slope of the response was 24.2 mV/decade [Fe³⁺] calculated as a function of pH using Fe(III) hydrolysis constants for seawater. Moreover, the response was essentially collinear with that in citrate buffers and in unbuffered solutions containing >10⁻⁵ M Fe³⁺ and the slope for the combined data was 26.2 mV/decade. This study was restricted to organic-free seawater because the certainty in Fe(III)–ligand stability constants is insufficient to warrant the selection of an ideal calibration buffer system, and there is evidence that powerful chelating ligands (e.g., EDTA along with humic and fulvic acids) may alter the response of the Fe(III)ISE. The Fe dissolution rate of the FeISE in UV photooxidised seawater was found to be 1.6×10⁻² nmol Fe/min, as measured by cathodic stripping voltammetry (CSV). This would contaminate a 100-ml sample by 0.8–1.6 nM Fe over a typical measurement period of 5–10 min obtained using a stability criterion of 0.5 mV/min. Various methods are proposed for reducing the level of contamination in open ocean samples that contain sub-nanomolar concentrations of iron. The FeISE has the potential to detect free Fe³⁺ at concentrations typically found in natural seawater.     

The determination of sulfide in seawater by flow-analysis with voltammetric detection

Preliminary measurements of sulfide in seawater using cathodic stripping voltammetry and a hanging mercury drop electrode (HMDE) in batch-mode showed that the sulfide peak decreased rapidly with time. This decrease was not caused by O₂, H₂O₂ or IO₃⁻, and the sulfide peak was not stabilised by trace metal additions. A home-made flow-cell was constructed to enable the determination of sulfide in seawater using voltammetry with an HMDE. A stable sulfide peak was obtained by flow-analysis with voltammetric detection, with a precision of 2.8% and detection limit of 0.5 nM at a 60 s adsorption time. Several thiol compounds were found to produce a peak at, or very close to, the peak potential for sulfide. Their interference was evaluated by allowing the sulfide peak in conventional (batch) voltammetry to decay. Comparative experiments showed that waste metallic mercury is responsible for removal of sulfide in batch-mode analysis due to formation of insoluble mercuric sulfide salts causing the rapid decay of the sulfide peak. The problem is circumvented by using flow-analysis to determine sulfide.     

Flow injection analysis of nanomolar level orthophosphate in seawater with solid phase enrichment and colorimetric detection

Phosphomolybdenum blue (PMB) paired with cetyltrimethylammonium bromide (CTAB) can be extracted using a solid phase extraction technique on C18 sorbent. Based on this, a novel on-line solid phase extraction method coupled with flow injection (FI) analysis and colorimetric detection has been established to determine nanomolar level orthophosphate in seawater. A stopped flow technique was employed to assure the complete formation of the PMB–CTAB compound, which was sequentially extracted on an in-line Sep-Pak C₁₈ cartridge. The adsorbed PMB–CTAB can be rapidly eluted by 0.56 mol/L H₂SO₄ in ethanol, and determined with a spectrophotometer at 700 nm. Experimental parameters, including reaction temperature, sample loading flow rate, stopped time and eluting flow rate, were optimized throughout the experiments based on univariate experimental design. The results show that reaction temperature and stopped time were the major factors affecting the formation of PMB–CTAB. Silicate concentration up to 5000 times higher than that of orthophosphate would not interfere with the determination of orthophosphate. Using artificial seawater with salinity of 35 as a matrix under the optimized conditions, the standard curve shows a linear range between 3.2 and 48.5 nmol/L, and the recovery and the detection limit of the proposed method are 96.4% and 1.57 nmol/L, respectively. The relative standard deviation (RSD) (n = 8), which was determined daily for 8 days, was 4.52% for the artificial seawater at a concentration of 32.4 nmol/L orthophosphate. Two typical seawater samples were analyzed using both the proposed method and the MAGnesium hydroxide-Induced Coprecipitation (MAGIC) method. The results of the two methods show no significant difference using the t test. Compared to the MAGIC method, the proposed method has the advantage of being more sensitive, faster, sample saving and easy for on-line analysis.     

Impact of environmental factors on in situ determination of iron in seawater by flow injection analysis

A sensitive method for iron determination in seawater has been adapted on a submersible chemical analyser for in situ measurements. The technique is based on flow injection analysis (FIA) coupled with spectrophotometric detection. When direct injection of seawater was used, the detection limit was 1.6 nM, and the precision 7%, for a triplicate injection of a 4 nM standard. At low iron concentrations, on line preconcentration using a column filled with 8-hydroxyquinoline (8HQ) resin was used. The detection limit was 0.15 nM (time of preconcentration = 240 s), and the precision 6%, for a triplicate determination of a 1 nM standard, allowing the determination of Fe in most of the oceanic regimes, except the most depleted surface waters. The effect of temperature, pressure, salinity, copper, manganese, and iron speciation on the response of the analyser was investigated. The slope of the calibration curves followed a linear relation as a function of pressure (C_p = 2.8 × 10^{− 5}P + 3.4 × 10^{− 2} s nmol^{− 1}, R² = 0.997, for Θ = 13 °C) and an exponential relation as a function of temperature (C_Θ = 0.009e^0.103Θ, R² = 0.832, for P = 3 bar). No statistical difference at 95% confidence level was observed for samples of different salinities (S = 0, 20, 35). Only very high concentration of copper (1000 × [Fe]) produced a detectable interference. The chemical analyser was deployed in the coastal environment of the Bay of Brest to investigate the effect of iron speciation on the response of the analyser. Direct injection was used and seawater samples were acidified on line for 80 s. Dissolved iron (DFe, filtered seawater (0.4 μm), acidified and stored at pH 1.8) corresponded to 29 ± 4% of Fe_a (unfiltered seawater, acidified in line at pH 1.8 for 80 s). Most of Fe_a (71 ± 4%) was probably a fraction of total dissolvable iron (TDFe, unfiltered seawater, acidified and stored at pH 1.8).     

Cu2+/SnO2复合纳米光催化剂的制备及其对海洋柴油污染物的降解

采用化学沉淀法成功制备了Cu2+/SnO2复合纳米光催化剂,采用XRD、SEM等测试手段对复合纳米光催化剂的粒径、形态等进行表征。在紫外光条件下,分别改变催化剂掺杂比、催化剂煅烧温度、催化剂投加量、柴油初始含量和光照时间等单因素,探究不同条件对Cu2+/SnO2复合纳米光催化剂降解海洋柴油污染物的影响。结果表明,自制复合纳米光催化剂可以有效降解海水中的柴油污染物,在紫外光作用下,于400℃下煅烧Cu/Sn掺杂比为0. 03的Cu2+/SnO2复合纳米光催化剂、投加量为0. 2 g/dm3、柴油初始含量为0. 15 g/dm3、H2O2溶液含量为0. 2 g/dm3、溶液的p H为7、光照时间3 h时效果最好,海水中柴油的去除率最高,达到86. 98%。Cu2+/SnO2复合纳米光催化剂用聚丙烯纳米球负载后可以实际应用于海洋中,便于回收。     

光谱法测定海水中溶解态无机氮的研究进展

溶解态无机氮(dissolved inorganic nitrogen,DIN)主要由亚硝酸盐-氮(NO^-₂-N)、硝酸盐-氮(NO^-₃-N)和铵氮(NH⁺₄-N)组成,它们在海洋的生物地球化学循环过程中起重要作用。但人类活动向海洋输入了大量无机氮,导致一系列环境问题。为了更好地开展海洋氮循环研究和环境污染管理,需对海水中的DIN进行测定。在众多分析方法中,光谱法因其通用性好、适用范围广、所需设备简单,成为测定海水DIN的首选。本文总结了近10年来基于光谱法测定海水DIN的研究进展,包括紫外分光光度法测定NO^-₃-N、萘乙二胺分光光度法测定NO^-₂-N和NO^-₃-N、次溴酸盐氧化-分光光度法测定NH⁺₄-N、靛酚蓝分光光度法测定NH⁺₄-N...     

Determination of thorium isotopes in seawater by moored MnO2-fiber method

A method is described for the determination of Th isotopes (²³²Th,²³⁰Th,²²⁸Th and²²⁷Th) in seawater through analysis of Th adsorbed on MnO₂-impregnated fiber that has been moored in the deep sea for up to 10 months. Since the MnO₂-fiber adsorbs Th from seawater at a constant rate, natural²³⁴Th can be used as a yield monitor by making a correction for its decay during the period of deployment. The results obtained by the method showed good reproducibility and accuracy. The method has the advantage over the chemical coprecipitation method that the time and labor for sampling and processing a large-volume of seawater is reduced.     

Experiments on the uptake of zinc and cadmium by manganese oxides

Experiments on the uptake of Zn and Cd by synthetic hydrous Mn oxides were carried out in an ionic medium at pH 3.5 and at pH 4. A slight preference for uptake of Cd²⁺ over Zn²⁺ was observed with both birnessite and nsutite, the Cd/Zn ratio being different for each mineral. Subsequently, the desorption of Zn and Cd from the obtained products in artificial seawater was studied. In this medium Cd is desorbed from the Mn oxides to a much higher extent than is Zn. The latter observations can be satisfactorily explained by the large difference of complex formation for the two metals in seawater, slightly counteracted by the preferential uptake of Cd²⁺ over Zn²⁺. The order of magnitude of the Zn/Cd ratio in natural manganese nodules is compatible with the ratio calculated on the basis of experimental results, taking fair estimates of the actual inorganic Zn/Cd ratio in seawater and of the pH of deep ocean water.