超声波萃取-高效液相色谱法测定土壤中邻苯二甲酸酯

邻苯二甲酸酯类(PAEs)是环境激素类物质中的一类化合物。文章对土壤中6种被美国EPA列入"优先监测污染物名单"的PAEs类物质邻苯二甲酸二甲酯(DMP)、二乙酯(DEP)、二丁酯(DBP)、邻苯二甲酸二(2-乙基己基)酯(DEHP)、二辛酯(DOP)、丁基苄基酯(BBP)邻苯二甲酸酯经超声波萃取、柱层析净化后,采用高效液相色谱法测定。对影响加标回收率的实验条件如萃取溶剂比例、萃取时间和萃取溶剂的选择等进行优化。方法回收率为94.1%～108.2%,相对标准偏差(RSD,n=7)为0.70%～2.42%,方法检出限为0.003～0.009μg/g。建立的方法样品前处理简单、快速,溶剂用量少,液相色谱法分析6种PAEs类物质仅用10 min,适用于大批量土壤样品中PAEs类物质的测定。     

气相色谱-质谱联用法测定土壤中邻苯二甲酸酯类增塑剂

应用加速溶剂萃取,气相色谱-质谱联用法测定土壤中6种邻苯二甲酸酯类有机污染物。对邻苯二甲酸酯类污染物的提取溶剂进行了优化选择,确定二氯甲烷作为最佳提取溶剂。对色谱柱升温程序进行了优化,以使两个出峰时间较接近的目标物邻苯二甲酸二甲酯(DMP)、邻苯二甲酸二乙酯(DEP)能够达到基线分离。方法标准曲线的线性范围为0.50～20.0mg/L,线性相关系数均大于0.9970,方法检出限为67μg/kg,加标回收率为81.9%～111.4%。方法检出限较低,精密度好,简便快速,可满足大批量样品分析对质量和进度的要求。     

振荡提取-荧光分光光度法分析土壤样品中石油类物质

石油类物质是中国建设用地土壤污染风险管控的污染物之一,开展土壤中石油类物质的检测对土壤污染防治工作具有重要意义。本文采用正己烷为萃取溶剂,土壤经振荡提取后,以荧光光度法为检测手段,建立了一种绿色环保、灵敏高效的土壤石油类物质检测方法。通过对实验过程进行优化,该方法的线性相关系数r≥0.999,检出限为3mg/kg。使用10种不同类型土壤进行方法精密度和准确度验证,精密度为2.5%~9.2%,基体加标回收率为80.0%～110%。为验证方法可比性,分别使用本方法和《土壤 石油类的测定 红外分光光度法》(HJ 1051—2019)对5种不同类型土壤进行检测比对,测定结果相对偏差在5.0%~15%之间,具有较好的一致性。     

在线净化-气相色谱法测定土壤中有机磷农药

建立了一套利用加速溶剂萃取仪在线净化,气相色谱氮磷检测器测定土壤中20种有机磷农药的方法。考察了加速溶剂萃取仪的萃取温度、氧化铝的类型和加入方式、溶剂萃取体系、分散剂用量等因素对土壤中有机磷农药残留测定的影响。合适的萃取温度在萃取效率和回收效率之间找到最佳平衡点,酸性氧化铝和底部加入方式保证了土壤的净化效果和有机磷的回收率,分散剂的加入使得土壤中有机磷分布更加均匀。以酸性氧化铝和石墨碳黑为净化剂,水为分散剂,土壤样品经加速溶剂萃取仪在线净化萃取,浓缩后采用气相色谱氮磷检测器检测。在萃取温度为60℃,酸性氧化铝底部加入,分散剂水为1.0 mL的条件下,20种有机磷的检出限为0.005～0.014 mg/L。本方法将萃取过程与净化过程合二为一,简化了操作步骤,提高了工作效率。     

在线渗析-离子色谱法测定土壤中有效氟

土壤样品经超声波超声静置,提取上清液,经渗析进入色谱柱,采用Metrohm A Supp 4-250阴离子交换柱,以1.8 mmol/L碳酸钠-1.7 mmol/L碳酸氢钠混合溶液作为流动相,用在线渗析技术与离子色谱法联用测定土壤中的有效氟。与常规方法相比,建立的方法操作简单,避免了繁琐的样品前处理。加标回收率为90.5%～95.7%,精密度(RSD,n=6)为1.60%。该方法具有高效、快速、灵敏等特点,能够用于环境土壤样品中有效氟的检测。     

离子色谱法测定土壤中有效氟

利用离子交换-电导检测离子色谱法对土壤中有效氟进行测定。选用30 mmol/L氢氧化钾溶液作为淋洗液,流速1.20 mL/min,准确测定有效态(可提取态)氟含量。方法加标回收率为95%~108%,精密度好,检出限低,操作简单,对环境无污染,适合于土壤污染状况的调查。     

超声提取-气相色谱法测定覆盖区土壤中的六六六和滴滴涕

将超声波提取技术引入到覆盖区土壤样品六六六、滴滴涕组分的预处理中,建立了超声提取,磺化法净化,气相色谱测定的分析方法。对被测组分在超声波提取中的稳定性进行了试验,对超声提取时间、提取温度、提取溶剂用量以及磺化净化过程可能导致组分损失的各种相关条件逐个试验筛选,采用样品加标回收法对六六六、滴滴涕的8种组分进行了两种浓度的精密度和准确度试验,RSD值均小于10％,平均回收率92．5％-103．9％。方法对各种异构体的六六六、滴滴涕的最低检测浓度为0．30-3．89ng／g。     

气相色谱法测定土壤中有机氯农药残留量

报告了利用填充玻璃柱，恒温气相色谱法，选用电子捕获检测器，简便、快速地分离测定土壤中八种有机氯农药残留量的实验条件及测定结果。     

超声提取-固相萃取小柱净化-气相色谱法测定土壤中14种有机氯农药

对土壤中14种有机氯农药的超声提取技术和磺化、固相萃取小柱两种净化方法进行系统研究。结果表明,超声提取节省提取时间,提高分析效率;磺化法和固相萃取小柱法都有净化作用,但磺化法使样品中的艾氏剂、狄氏剂和异狄氏剂全部损失;固相萃取小柱净化当丙酮-正己烷淋洗液体积比为1∶9、淋洗液收集8 mL时回收率>90%,干扰最小。方法检出限为0.63~2.59μg/kg,精密度(RSD,n=7)为1.17%~14.66%,基体加标平均回收率为82.78%~106.94%。方法用于生态地球化学调查评价批量土壤样品的实际分析,检测结果满足评价工作需要。     

加速溶剂萃取-气相色谱法测定土壤中有机氯农药和多氯联苯

试验了加速溶剂萃取土壤中有机氯农药和多氯联苯残留的最佳条件。结果表明,采用正己烷-丙酮混合溶剂(体积比1:1)为提取剂,萃取温度100℃,压力为10.3MPa;采用弗罗里硅土固相萃取柱对样品净化,毛细管柱分离,用配有电子捕获检测器的气相色谱进行检测,平均加标回收率为83.6%～109.0%,相对标准偏差(RSD,n=11)为1.11%～5.88%,检出限为0.69～1.85ng/g。方法简单、快捷、经济,适应于土壤中的有机氯农药和多氯联苯的测定。     

Biodegradation of phthalic acid esters in sewage sludge by composting with pig manure and rice straw

To comparatively study the biodegradation of phthalic acid esters (PAEs) in sewage sludge by composting with pig manure or with rice straw, four composting modes were designed: Mode 1 (sewage sludge + pig manure + intermittent aeration), Mode 2 (sewage sludge + pig manure + continuous aeration), Mode 3 (sewage sludge + rice straw + intermittent aeration) and Mode 4 (sewage sludge + rice straw + continuous aeration). Physicochemical parameters of composts were measured according to standard methods and PAEs were analyzed by gas chromatography coupled with mass spectrometry (GC/MS). The biodegradation of each PAE was also discussed. The results showed that Mode 1 was the best mode to biodegrade PAEs, which might be related to the wide class of indigenous microbial communities in pig manure and high efficiency of intermittent ventilation for providing oxygen. During the biodegradation process, di(2-ethylhexyl) phthalate was the most abundant and decisive for the removal of total PAEs. It showed a first-order kinetic degradation model. In conclusion, composting with pig manure could be suggested as an effective detoxification process for the removal of PAEs from sewage sludge, providing a safe end product.     

高效液相色谱法测定鱼肌肉中的孔雀石绿残留

采用高效液相色谱法测定鱼组织中孔雀石绿的残留量.样品经高速均质后,用乙腈提取,合并提取液,用二氯甲烷再次萃取,有机相浓缩后过酸性氧化铝和PRS复合小柱洗脱,用乙腈定容.以乙腈-乙酸盐缓冲溶液为流动相,高效液相色谱分离,用荧光检测器检测,外标法定量.其检出限为0.75μg/kg,加标回收率为84.0%～90.1%,相对标准偏差RSD为2.98%～6.21%.     

气相色谱法测定水中丙烯酰胺

采用溴化衍生-气相色谱法测定水中的丙烯酰胺,方法检测限为0．02μg／L,平均加标回收率为99．1％～104．5％,相对标准偏差为0．8％～2．6％,方法实用准确。     

扩散-离子色谱法测定植物样中的氟

采用扩散法提取植物样中的氟,用离子色谱法检测氟的含量。经试验,样品加标回收率在94.7%～104.7%之间,样品质量分数为7.10μg/g时,RSD为1.41%。此法操作简单,准确度高,精密度好,是一种测量植物样中氟含量的有效方法。     

Ultrasonic wave extraction and simultaneous analysis of polycyclic aromatic hydrocarbons (PAHs) and phthalic esters in soil

A method is developed for detection of polycyclic aromatic hydrocarbons(PAHs) and Phthalic Acid Esters(PAEs) in soil samples. Ultrasonic Wave Extraction under airtight circumstances is adopted to extract the analytes in soil samples with n-hexane–acetone(V:V=1:1) as extraction solvent. This method has several advantages, including high extraction efficiency, short time, convenience and simplicity. It can be used to detect polycyclic aromatic hydrocarbons(PAHs) and Phthalic Acid Esters(PAEs) in soil.     

Metal species in a Boreal river system affected by acid sulfate soils

The bioavailability of metals and their potential for environmental pollution depends not simply on total concentrations but on their chemical form. Consequently, knowledge of aqueous metal speciation is essential in investigating potential metal toxicity and mobility. Dissolved (<1 kDa), colloidal (1 kDa–0.45 μm) and particulate (>0.45 μm) size fractions of sulfate, organic C (OC) and 18 metals/metalloids were investigated in the extremely acidic Vörå River system in Western Finland, which is strongly affected by acid sulfate (AS) soils. In addition, geochemical modelling was used to predict the formation of free ions and complexes in these acidic waters. The most important finding of this study is that the very large amounts of elements known to be released from AS soils (including Al, Ca, Cd, Co, Cu, Mg, Mn, Na, Ni, Si and U) occur and can prevail mainly in toxic forms throughout acidic river systems; as free ions and/or sulfate-complexes. This has serious effects on the biota and particularly dissolved Al can be expected to have acute effects on fish and other organisms. In the study area, only the relatively forested upstream area (higher pH and contents of OC) had significant amounts of a few bioavailable elements (including Al, Cu, Ni and U) due to complexation with the more abundantly occurring colloidal OC in the upstream area. It is, however, notable that some of the colloidal/particulate metals were most likely associated with metal bearing phyllosilicates eroded from clay soils. Moreover, the mobilisation of Fe and As was small and As was predicted to be associated with Fe oxides, indicating a considerable influence of Fe oxides on the mobilisation/immobilisation processes of As. Elements will ultimately be precipitated in the recipient estuary, where the acidic metal-rich river water will gradually be diluted/neutralised with brackish seawater in the Gulf of Bothnia. According to speciation modelling, such a pH rise may first cause precipitation of Al, Cu and U together with organic matters closest to the river mouth, in line with previous sediment studies from the estuary.     

离子色谱梯度淋洗技术检测水中阴离子

通过实验确定了使用梯度淋洗技术检测矿泉水中阴离子的方法。检出限能够达到5.4～25.5ng/mL,精密度能够达到0.33%～1.10%。     

Salinity effect on the liquid limit of soils

Acta Geotechnica - Previous studies stated that, with increasing salinity, the decreased liquid limit for expansive soils was attributed to the shrinkage of diffuse double layer, while the...     

The precision of amino acid geochronology and paleothermometry

Uncertainties in the measurements necessary for the calculation of amino acid age estimates and paleotemperatures can be propagated through age and temperature equations to yield estimates of precision. It is found that aIle/Ile ratios can be used to calculate numerical ages with a precision generally no better than ±40–50% if the age equation is not calibrated locally and with a precision approaching 15% if appropriate calibration samples are available locally. The effective diagenetic temperature of a sample of known age can be calculated to within about 2°C, although the local relationship between ground and air temperatures may add additional uncertainty when interpreting the effective temperature in terms of climate. The effective temperature for an interval of time bracketed by samples of known age can be known to within about 2–4°C under favorable circumstances. The change in effective temperature between an interval of time bracketed by two samples of known age and the period of time following that interval can be calculated to within 1–2°C in may instances.