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1.
探讨了利用连续流动分析仪测定水溶肥料中的硝态氮的方法.选择含腐植酸、有机、微量元素、大量元素等4类水溶肥料样品,采用水振荡浸提试样,利用连续流动分析仪对浸提液中硝态氮的含量进行测定,并与紫外分光光度计测定数据进行对比,探讨利用连续流动分析仪测定化学肥料中硝态氮含量可行性.结果表明,流动分析仪法的方法检出限为0.008 ...  相似文献   

2.
快速准确测定土壤中铵态氮、硝态氮含量对监测土壤肥力水平和生态环境,指导作物氮肥施用非常重要。选择30份土样,利用全波长扫描式多功能读数仪(酶标仪)结合靛酚蓝分光光度法、硫酸肼还原法测定土壤中铵态氮和硝态氮含量,探讨利用酶标仪测定土壤无机氮含量的可行性。结果显示,利用酶标仪测定土壤铵态氮、硝态氮含量与连续流动分析仪测定结果之间无明显差异,彼此间呈显著线性相关。铵态氮回归直线方程为Y(连续流动分析仪-NH_4~+-N)=0.997 6 X(酶标仪-NH_4~+-N)-0.012 3,相关系数R=0.961 9(n=30,P0.01);硝态氮回归方程为Y(连续流动分析仪-NO_3~--N)=0.959 3 X(酶标仪-NO_3~--N)+0.021 9,相关系数R=0.964 0(n=30,P0.01)。酶标仪测定铵态氮回收率在96.2%~108%,相对标准偏差在10%以内;硝态氮测定回收率为94.9%~110%,且相对标准偏差在5%以内,酶标仪测定土壤铵态氮和硝态氮方法检出限分别为0.068mg/L和0.028mg/L。酶标仪测定土壤无机氮速度快,精密度、准确度较高,消耗试剂少,可用于大批量土壤浸提液中铵态氮和硝态氮含量的快速分析。  相似文献   

3.
快速准确测定土壤中铵态氮、硝态氮含量对监测土壤肥力水平和生态环境,指导作物氮肥施用非常重要。选择30份土样,利用全波长扫描式多功能读数仪(酶标仪)结合靛酚蓝分光光度法、硫酸肼还原法测定土壤中铵态氮和硝态氮含量,探讨利用酶标仪测定土壤无机氮含量的可行性。结果显示,利用酶标仪测定土壤铵态氮、硝态氮含量与连续流动分析仪测定结果之间无明显差异,彼此间呈显著线性相关。铵态氮回归直线方程为Y(连续流动分析仪-NH_4~+-N)=0.997 6 X(酶标仪-NH_4~+-N)-0.012 3,相关系数R=0.961 9(n=30,P<0.01);硝态氮回归方程为Y(连续流动分析仪-NO_3~--N)=0.959 3 X(酶标仪-NO_3~--N)+0.021 9,相关系数R=0.964 0(n=30,P<0.01)。酶标仪测定铵态氮回收率在96.2%~108%,相对标准偏差在10%以内;硝态氮测定回收率为94.9%~110%,且相对标准偏差在5%以内,酶标仪测定土壤铵态氮和硝态氮方法检出限分别为0.068mg/L和0.028mg/L。酶标仪测定土壤无机氮速度快,精密度、准确度较高,消耗试剂少,可用于大批量土壤浸提液中铵态氮和硝态氮含量的快速分析。  相似文献   

4.
快速准确测定土壤中铵态氮、硝态氮含量对监测土壤肥力水平和生态环境,指导作物氮肥施用非常重要。选择30份土样,利用全波长扫描式多功能读数仪(酶标仪)结合靛酚蓝分光光度法、硫酸肼还原法测定土壤中铵态氮和硝态氮含量,探讨利用酶标仪测定土壤无机氮含量的可行性。结果显示,利用酶标仪测定土壤铵态氮、硝态氮含量与连续流动分析仪测定结果之间无明显差异,彼此间呈显著线性相关。铵态氮回归直线方程为Y(连续流动分析仪-NH_4~+-N)=0.997 6 X(酶标仪-NH_4~+-N)-0.012 3,相关系数R=0.961 9(n=30,P0.01);硝态氮回归方程为Y(连续流动分析仪-NO_3~--N)=0.959 3 X(酶标仪-NO_3~--N)+0.021 9,相关系数R=0.964 0(n=30,P0.01)。酶标仪测定铵态氮回收率在96.2%~108%,相对标准偏差在10%以内;硝态氮测定回收率为94.9%~110%,且相对标准偏差在5%以内,酶标仪测定土壤铵态氮和硝态氮方法检出限分别为0.068mg/L和0.028mg/L。酶标仪测定土壤无机氮速度快,精密度、准确度较高,消耗试剂少,可用于大批量土壤浸提液中铵态氮和硝态氮含量的快速分析。  相似文献   

5.
保存、分析方法等因素对土壤中硝态氮测定的影响   总被引:6,自引:0,他引:6  
为探明土壤中硝态氮测定的影响因素,采用黑土、潮土、红壤为材料,研究样品的保存方法、浸提剂种类、分析方法、实验用水及试剂纯度对土壤中硝态氮测定的影响。结果表明,测定土壤硝态氮时,土样在冷冻条件下保存优于冷藏条件。冷冻条件下保存可在45 d内完成测试,而冷藏保存则需在7 d内完成测试。采用0.01 mol/L CaCl2和2 mol/L KCl为浸提剂时,对土壤中硝态氮的测定结果无显著差异。紫外比色法的测定结果与林业标准法(LY/T1230-1999)相比无显著差异,但显著高于流动注射法,且紫外比色法与流动注射法之间有显著相关性。流动注射法的测定结果与林业标准法相比也无显著差异。实验用水的杂质可使土壤中硝态氮的测定结果显著偏高,对其进行加热煮沸、蒸馏及无氨化蒸馏后可显著降低水中杂质的含量。  相似文献   

6.
土壤硝态氮反映土壤短期氮素供应水平,实时了解土壤硝态氮的含量为精准农业和农业面源污染防控提供支撑,因此,在线实时检测土壤硝态氮方法突破就显得十分迫切。土壤硝态氮中的硝酸根离子在土壤中的高水溶性和流动性为全固态硝酸根离子选择电极高敏感检测土壤中硝态氮提供了条件,固态硝态氮离子选择电极的离子选择膜反应硝酸根离子在被测溶液中的浓度。采用全固态硝酸根离子选择电极ELIT NO3-,且与温度电极和pH电极融合组成电极阵列对土壤饱和溶液中的硝酸根离子进行检测。设计了高输入阻抗运算放大电路对电极信号进行采集,并通过微处理控制蠕动泵完成土壤硝态氮待测溶液连续流动测定及实时传输结果。实验结果表明,电极响应时间≤15 s,斜率-51.63 mV/decade,线性范围10-5~10-2.2 mol/L,最低检测限10-5.23 mol/L。相对标准差在0.78%~4.5%,加标回收率均在90.0%~110%。与紫外可见分光光度法测试结果相比,相关系数(R2)为0.9952,为土壤硝态氮在现场检测奠定技术基础。  相似文献   

7.
建立凯氏定氮仪法测定植物营养液中铵态氮和硝态氮的方法。将10 mL植物营养液置于凯氏定氮管中,加入4.5 mol/L氢氧化钠溶液10 mL,利用锌-硫酸亚铁还原剂将营养液中硝态氮(NO_(3)^(-)-N)转化为铵态氮(NH_(4)^(+)-N),经蒸馏后被定量吸收在硼酸溶液中,用标准酸进行滴定,计算营养液中总氮含量;不加锌-硫酸亚铁还原剂时,测定营养液中的NH_(4)^(+)-N含量,采用差减法计算出营养液中NO_(3)^(-)-N含量。方法的检出限(以铵态氮计)为0.15 mg/L,硝态氮和铵态氮测定结果的相对标准偏差分别为1.23%~2.75%、0.83%~2.84%(n=5),加标回收率为98.7%~100.8%。该方法满足LY/T 1228—2015《森林土壤氮的测定》标准要求。  相似文献   

8.
连续浸提-分光光度法测定硼泥中不同形态的硼   总被引:1,自引:0,他引:1  
采用连续浸提法将硼泥中的硼划分为七种物理形态,即:水溶态、醇溶态、盐溶态、络合态、硫酸盐等结合态、Fe-Mn结合态及残渣态。用分光光度法测定各形态硼的含量。测定结果的相对标准偏差为4.4%(n=4),回收率为91.7%~102.4%。  相似文献   

9.
用连续流动分析仪测定水溶肥中氧化钾含量,并与农业部规定的标准分析方法(NY/T1977—2010)结果进行比较,结果表明,样品溶液中氧化钾在0~400 mg/L范围内线性良好,相关系数r=0.999 5,与四苯硼酸钾重量法结果比对结果接近,绝对偏差小于0.23%,准确度高,加标回收率在98.2%~101%,重现性良好,10次重复测定相对标准偏差为0.22%,可用于水溶肥中氧化钾的分析测定。  相似文献   

10.
土壤硝态氮反映土壤短期氮素供应水平,实时了解土壤硝态氮的含量为精准农业和农业面源污染防控提供支撑,因此,在线实时检测土壤硝态氮方法突破就显得十分迫切。土壤硝态氮中的硝酸根离子在土壤中的高水溶性和流动性为全固态硝酸根离子选择电极高敏感检测土壤中硝态氮提供了条件,固态硝态氮离子选择电极的离子选择膜反应硝酸根离子在被测溶液中的浓度。采用全固态硝酸根离子选择电极,且与温度电极和pH电极融合组成电极阵列对土壤饱和溶液中的硝态根离子进行检测。设计了高输入阻抗运算放大电路对电极信号进行采集,并通过微处理控制蠕动泵完成土壤硝态氮待测溶液连续流动测量及实时传输结果。实验结果表明,电极响应时间≤15 s,斜率-51.63 mV/decade,线性范围10-5-10-2.2 mol/L,最低检测限10-5.23 mol/L。相对标准差在0.78%-4.47%范围内,加标回收率均在90%-110%以内。与国家标准紫外可见分光光度法测试结果相比,相关系数(R2)为0.9952,为土壤硝态氮在现场检测奠定技术基础。  相似文献   

11.
Jing-Fu L  Gui-Bin J 《Talanta》2001,54(2):329-332
The applicability of reagent-injection flow injection (FI) technique in elimination of background absorption was evaluated by using the FI determination of water-soluble chloride in cigarettes, based on the mercury thiocyanate method, as a model. Some parameters of the proposed reagent-injection FI method were optimized and the proposed procedure had a linear range of 0-7.5 mg l(-1) Cl, a detection limit of 0.02 mg l(-1) Cl, a sampling rate of 60 h(-1) and a relative standard deviation of 0.1% at 5 mg l(-1) Cl. Eight cigarette samples were analyzed by this proposed reagent-injection FI method and the referential membrane dialysis FI procedure. The relative errors were <4.3%, and paired t-test shows that there are no significant differences between these two methods. As no dialysis unit was needed, the reagent-injection FI method has much simpler flow system than the existed CFA and FI methods.  相似文献   

12.
Two flow-injection manifolds have been investigated for the determination of nitrate. These manifolds are based on the reduction of nitrate to nitrite and determination of nitrite by gas-phase molecular absorption spectrophotometry. Nitrate sample solution (300 microL) which is injected to the flow line, is reduced to nitrite by reaction with hydrazine or passage through the on-line copperized cadmium (Cd-Cu) reduction column. The nitrite produced reacts with a stream of hydrochloric acid and the evolved gases are purged into the stream of O2 carrier gas. The gaseous phase is separated from the liquid phase using a gas-liquid separator and then swept into a flow-through cell which has been positioned in the cell compartment of an UV-visible spectrophotometer. The absorbance of the gaseous phase is measured at 204.7 nm. A linear relationship was obtained between the intensity of absorption signals and concentration of nitrate when Cd-Cu reduction method was used, but a logarithmic relationship was obtained when the hydrazine reduction method was used. By use of the Cd-Cu reduction method, up to 330 microg of nitrate was determined. The limit of detection was 2.97 microg nitrate and the relative standard deviations for the determination of 12.0, 30.0 and 150 microg nitrate were 3.32, 3.87 and 3.6%, respectively. Maximum sampling rate was approximately 30 samples per hour. The Cd-Cu reduction method was applied to the determination of nitrate and the simultaneous determination of nitrate and nitrite in meat products, vegetables, urine, and a water sample.  相似文献   

13.
建立了使用紫外分光光度法测定硫酸中氮氧化物的方法。利用高锰酸钾将试样中的亚硝酸根氧化成硝酸根,然后在硫酸(30%)介质中,于210nm波长处定量测定试样中氮氧化物的含量。方法检出限为0.0000075%,线性相关系数(r)为0.999 0,平均加标回收率为97.2%~102.8%,平均相对标准偏差(RSD,n=6)为2.9%~3.1%。方法灵敏度高、检出限低,操作简便、成本低,可应用于蓄电池电解液中氮氧化合物的检测。  相似文献   

14.
The complexation between Cu(II) and naphthochrome green (NG) is very sensitive at pH 4.09 with the formation of complex ion [Cu(NG)2(H2O)2](2-). It can thus used for the determination of Cu(II) by the light-absorption ratio variation approach (LARVA) with a good selectivity. Both the ordinary detection procedure and continuous flow analysis (CFA) were carried out, where the latter is fit for continuous and rapid analysis of samples. The limit of detection (LOD) of Cu(II) is only 1 ng/ml, which is favorable for direct monitoring of natural water. About 30 samples could be analyzed per hour by CFA. Cu(II) contents in Yangtze River, West Lake, Taihu Lake of China and seawater near Shanghai were determined with satisfactory results. The CFA-LARVA spectrophotometry was the first to be coupled and it will play an important role in the in-situ analysis of natural water quality.  相似文献   

15.
建立了一种利用连续流动-分光光度法测定固废中氰化物的浸出毒性的方法,当氰化物浓度在0~200μg/L范围内,校准曲线的相关系数r为0.9998;方法的检出限可以达到0.33μg/L;不同浓度样品测定的相对标准偏差低于2.6%,实际固体废物样品加标回收率为96%~103%,方法精密度良好并且准确度较高;通过实际样品测定结果比对,证明方法与传统国家标准方法测定结果有着较高的吻合度,具有良好的应用前景。  相似文献   

16.
The sensitive complication between Cu(II) and of azocarmine B (ACB) at pH 6.03 was characterized by the spectral correction method and the complex Cu(ACB)2 was formed. Because of a good selectivity, this reaction was used for the determination of Cu(II) by the light‐absorption ratio variation approach combined with the continuous flow analysis (CFA). The limit of detection of Cu(II) is 0.04 mg/L, the recovery is between 97 and 100% and about 30 samples could be analyzed per hour by CFA. By means of the recommended method, the organic species and inorganic ion species of Cu(II) in two wastewater samples were determined respectively and the former occupies less than 20% of total dissolved Cu(II).  相似文献   

17.
采用传统分析仪器测定汞元素,需要对样品进行化学消解,存在操作繁杂、效率低以及易交叉污染等问题。故建立了电热蒸发-直接进样-HGA-100测汞仪测定土壤以及沉积物中汞的方法,无需对样品进行化学前处理,降低环境污染。通过优化HGA-100测汞仪参数条件,汞质量浓度在0~20ng以及20~200ng,相关系数优于0.998,准确称量样品0.05g(精确至0.000 1g),方法检出限为0.5μg/kg,相对标准偏差1.6%~4.6%,加标回收率在90.1%~100%。方法用于对土壤和沉积物标准物质测定,结果与标准值相符。方法高效、准确,可用于测定土壤以及沉积物中的汞。  相似文献   

18.
电位滴定法快速测定磷肥中的水溶性磷   总被引:2,自引:0,他引:2  
建立了电位滴定法快速测定磷肥中水溶性磷含量的方法。用蒸饮水溶解磷肥中的水溶性磷,通过硝酸钡和阳离子交换树脂除去干扰离子,用六次甲基四胺-硝酸缓冲溶液制试液的酸度(pH=5.4),在乙醇体系中,用一定浓度的硝酸铅标准溶液进行电位滴定,用二阶微分法确定硝酸铅标准溶液的滴定终点体积。方法的RSD为0.66%-0.97%,回收率为100.00%-100.10%。  相似文献   

19.
Yamini Y  Tamaddon A 《Talanta》1999,49(1):119-124
A simple method for rapid and selective extraction, preconcentration and determination of copper as it's neocuproine complex by using octadecylsilica membrane disks and spectrophotometry is presented. Extraction efficiency and the influence of flow rates of sample solution and eluent, pH, amount of neocuproine and hydroxylamine hydrochloride, type and least amount of eluent for elution of copper complex from disks, break through volume and limit of detection were evaluated. Also the effects of various cationic interferences on percent recovery of copper were studied. Extraction efficiencies >99% were obtained by elution of the disks with minimal amount of solvent. The limit of detection of the proposed method is 0.12 ppb. The method was applied to the recovery and determination of copper in different water samples.  相似文献   

20.
Ion-exchange chromatography using a high-capacity anion exchanger with UV detection was applied to the determination of nitrate in seawater. Major ions in seawater samples did not affect the peak shape and the retention time of the nitrate when an alkaline metal cation-chloride solution was used as an eluent at high concentrations (0.5-2 mol/l). At a wavelength of 220 nm, the peak of bromide was very small because of low absorption, while its separation from the nitrate peak was good at high concentrations. Among the eluents tested, lithium chloride gave the best separation of nitrate from bromide. It was estimated that the lithium ion had the least potential for ion-pair formation with nitrate, and its retention time was prolonged compared with the retention times when using other cations; with bromide and nitrite, such an effect was not observed. The results of shipboard seawater nitrate determination by our method in the South Pacific Ocean and Antarctic Sea showed good agreement with those by the conventional photometric method using continuous flow.  相似文献   

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