气相色谱-负化学源-质谱法检测水中10种全氟羧酸化合物

建立了气相色谱-负化学源-质谱（GC-NCI-MS）检测水中10种全氟羧酸化合物的分析方法。使用硅烷衍生化试剂N-甲基-N-三甲基硅基三氟乙酰胺（MSTFA）对全氟羧酸化合物进行衍生化，水样经弱阴离子交换固相萃取柱净化富集后进样。实验优化了样品前处理、衍生化和仪器条件。结果表明，10种全氟羧酸化合物在0.1~10 mg/L范围内线性关系良好，相关系数为0.9956~0.9993；方法的检测限（LOD）和定量限（LOQ）分别为0.5~1.5 μg/L和1.5~4.5 μg/L。在空白水样中进行了3个添加水平的加标回收试验，10种全氟羧酸化合物的平均回收率为70.2%~112.6%，相对标准偏差（RSD）为2.1%~14.5%（n=6）。该法原理简单，灵敏度高，准确、精密，可实现水体中10种全氟羧酸化合物同时检测的要求。     

漩涡辅助离子液体-分散液液萃取环境水样中的紫外线吸收剂

建立了漩涡辅助离子液体-分散液液萃取(VA-IL-DLLME)的样品前处理技术,并与高效液相色谱联用检测环境水样中的紫外线吸收剂。以1-己基-3-甲基咪唑六氟磷酸为萃取剂,考察了离子液体用量、分散剂种类和用量、漩涡时间、离心时间、稀释剂种类和用量、p H等因素对萃取效率的影响。在最佳萃取条件下,2,4-二羟基二苯甲酮在4~1000 ng/m L、2-羟基-4-甲氧基二苯甲酮在3.5~1000 ng/m L、二苯甲酮,水杨酸-2-乙基己酯和3,3,5-三甲基环己烷水杨酸酯在10~1000 ng/m L浓度范围内具有良好的线性关系(R20.993),检出限为0.8~2.8 ng/m L,相对标准偏差(RSD)为2.6%~7.8%,加标回收率为55.8%~118.9%。方法可用于环境水样中痕量紫外线吸收剂的测定。     

顶空衍生固相微萃取-气相色谱质谱法测定聚碳酸酯树脂中的环境雌激素

建立了固相微萃取-气相色谱质谱联用测定聚碳酸酯树脂中环境雌激素4-枯基苯酚和双酚A的分析方法。优化了固相微萃取纤维、萃取温度和时间、解吸时间、搅拌速度、pH等萃取条件及衍生化温度和时间、衍生化方式等衍生化条件，并对样品浸泡时间、浸泡温度等进行了研究。方法的线性范围为0．05μg/L～1mg／L，4-枯基苯酚和双酚A的检出限分别为50ng／L和0．5ng／L，相对标准偏差（RSD，n=5）分别为5．2％和1．6％，平均回收率（n=3）在90．50％～107．3％之间，该方法简单、快速、灵敏。     

液相色谱-串联质谱法快速测定水及鱼肉中的苯胺

为快速准确测定水及鱼肉中的苯胺,采用乙腈提取、高效液相色谱-串联质谱测定,建立了水及鱼肉中苯胺的快速测定方法。水样与乙腈以4：1的体积比混合,1.00 g鱼肉中加入2.00 mL乙腈,涡旋提取1 min,水样和鱼肉样品的提取液离心5 min后取上清液测定。以C₁₈柱为分离柱,乙腈-0.5%（v/v）甲酸水溶液（85：15,v/v）为流动相,目标物质在3 min内分离。在0.5~500 μg/L范围内,苯胺峰面积与内标峰面积之比与质量浓度的线性关系良好（R²>0.999）。基质加标试验结果表明,苯胺在水中的回收率分别为93.7%（加标水平为40 ng）和86.7% （加标水平为400 ng）,苯胺在鱼肉中的回收率分别为96.8%、 92.6%和81.8%（加标水平分别为5、50和500 ng）,相对标准偏差在1.5%~9.2%之间。水样和鱼肉样品中苯胺的检出限分别为0.50 μg/L和1.00 μg/kg,定量限分别为1.00 μg/L和2.00 μg/kg。应用该方法测定了从受苯胺污染的水库中采集的13份水样和12份鱼肉样品,结果表明,水和鱼肉中苯胺的最大含量分别为1943.6 μg/L和60.8 μg/kg。本方法快速、准确,适用于水和鱼肉中苯胺的快速测定。     

气相色谱-质谱法测定酱猪蹄和酱猪肘中5种胆固醇氧化物

建立了气相色谱-质谱（GC-MS）测定酱猪蹄和酱猪肘中7 β-羟基胆固醇、5 α，6 α-环氧化胆固醇、胆甾烷-3 β，5 α，6 β-三醇、25-羟基胆固醇和7-酮基胆固醇5种胆固醇氧化物（COPs）含量的方法。样品经甲醇-氯仿（1：2，v/v）混合溶液提取，硅胶固相萃取小柱净化后，加入N，O-双（三甲基硅基）乙酰胺-三甲基氯硅烷-三甲基硅基咪唑（3：2：3，v/v/v）（Sylon BTZ）进行衍生化处理，设置合理的柱温升温程序，采用选择离子扫描（SIM）模式进行检测。在优化条件下，5种COPs在22 min内实现分离，且分离度良好。5种COPs的线性范围满足测定要求，3个加标水平下的平均回收率为61.16%~96.96%，相对标准偏差≤ 7.80%（n=3），检出限（以信噪比为3计）和定量限（以信噪比为10计）分别为0.02~47.07 ng/g和0.06~156.90 ng/g。该法快速简便，线性范围广，灵敏度高，可作为测定实际样品中COPs的有效方法。     

超高效液相色谱-串联质谱法测定环境水体/污泥中5种痕量雌激素

对固相萃取条件、加速溶剂萃取条件进行了优化,采用内标法结合超高效液相色谱-串联三重四极杆质谱仪进行测定,建立了环境水样、污泥中5种典型雌激素的测定方法。在最佳条件下,水样中5种雌激素的检出限为0.8 ng/L(除E3的检出限为1 ng/L),线性范围为3～1000 ng/L,相关系数在0.9566～0.9999之间;污泥样品中5种雌激素的检出限为0.5 ng/g(除E3的检出限为0.8 ng/g),线性范围为2.5～500 ng/g,相关系数在0.9224～0.9999之间。方法用于实际环境水样、泥样中痕量雌激素的测定。     

超声辅助衍生-液相色谱/串联质谱法快速测定养殖水体中硝基呋喃类代谢物的残留量

建立了超声辅助衍生结合液相色谱/串联质谱(UAD-LC-MS/MS)快速测定水产养殖水体中4种硝基呋喃代谢物的方法。实验对比了超声辅助衍生和传统振荡衍生的效果,优化了色谱质谱条件以及衍生时间。水样经超声辅助的方式衍生,以2-硝基苯甲醛为衍生化试剂,再经乙酸乙酯提取,在正离子模式下以电喷雾电离串联质谱进行测定,内标法定量。在优化的实验条件下,4种代谢物在0.5~50 ng/m L范围内线性良好,相关系数0.998,方法检出限为0.02 ng/m L,定量限为0.05 ng/m L。在0.1,0.5和5 ng/m L的添加水平下,4种代谢物的平均回收率处于91.9%~104%之间,相对标准偏差(RSDs)处于2.1%~8.1%之间。测定了12份养殖水体中4种硝基呋喃代谢物的残留量,其中2份样本中检出呋喃西林代谢物氨基脲。方法可以准确测定养殖水体中硝基呋喃代谢物的残留量。     

直接进样超高效液相色谱-三重四极杆质谱法快速测定环境水样中草甘膦、氨甲基膦酸、草铵膦及乙烯利残留

建立了一种简便、直接进样的超高效液相色谱-三重四极杆质谱法（UPLC-MS/MS）快速测定环境水样中草甘膦、氨甲基膦酸、草铵膦及乙烯利的残留。环境水样经0.22 μm滤膜过滤或冷冻离心去除杂质后,滤液无需衍生化直接进行定量分析。4种农药通过Metrosep A Supp 5柱（150 mm×4.0 mm,5 μm）分离,以碳酸氢铵-氨水溶液为流动相进行梯度洗脱,在负离子模式下以MRM方式进行检测。结果表明,4种农药在0.50~50.0 μg/L范围内相关系数（r）均大于0.999,线性关系良好,方法检出限为0.05~0.09 μg/L。实际水样在低、中、高3种加标浓度水平下,回收率分别为76.3%~108%、83.0%~107%和87.0%~105%,相对标准偏差分别为2.0%~12.3%、2.4%~5.6%和2.7%~6.8%。使用该方法对海南省34个水样进行测定,其中30个饮用水源地水样中均未检出4种农药,槟榔园附近3个水样均检出草甘膦和氨甲基膦酸,香蕉园附近的1个水样检出草铵膦和氨甲基膦酸。与传统的衍生化方法比较,该方法操作简便,重现性好,准确性高,不受基体干扰,适用于环境水样中草甘膦、氨甲基膦酸、草铵膦及乙烯利的残留检测。     

柱前衍生-超高效液相色谱-串联质谱测定茶叶中草甘膦、草铵膦及主要代谢物氨甲基膦酸残留

采用柱前衍生-超高效液相色谱-串联质谱测定茶叶中草甘膦、草铵膦及其主要代谢物氨甲基膦酸残留。利用正交试验方法,系统研究了提取与净化等前处理条件对茶叶中草甘膦、草铵膦和代谢物氨甲基膦酸检测的影响。实验结果表明,最优的前处理方案为茶叶样品经纯水旋涡提取,阳离子交换柱净化,0.5%（v/v）甲酸水溶液洗脱和9-芴甲基氯甲酸酯衍生,C₁₈色谱柱分离,超高效液相色谱-串联质谱定量分析（电喷雾正离子）。结果表明：在1~100 μ g/L范围内,草甘膦、草铵膦和氨甲基膦酸呈现良好的线性关系,相关系数（R²）均大于0.991,该方法检出限为0.0160~0.0300 mg/kg,定量限为0.0530~0.100 mg/kg。在0.0500、0.400和1.20 mg/kg 3个添加水平下,草甘膦、草铵膦和氨甲基膦酸的平均回收率为78.3%~108%,相对标准偏差为5.46%~9.63%。利用该方法检测837份茶叶中草甘膦、草铵膦和氨甲基磷酸残留,检出率分别为3.46%、0.24%和4.42%,超标率为0.24%。该方法简单、快速、灵敏、准确,能够满足大批量茶叶中草甘膦、草铵膦和氨甲基膦酸残留的检测需要。     

衍生化固相微萃取与气相色谱-质谱联用测定生活垃圾渗沥液中双酚A

建立了固相微萃取-顶空衍生化与色谱-质谱联用技术测定水中双酚A定量分析方法。对影响萃取和衍生化过程的参数进行了条件优化,实验选用聚丙烯酸酯(PA)萃取纤维,在搅拌速度为1200r/min、溶液离子强度100g/L、pH2和25℃的条件下萃取60min后,N,O双(三甲基硅烷基)三氟乙酰胺(BSTFA)顶空衍生化5min。方法的线性范围是0.09~200μg/L;检出限0.03μg/L;相对标准偏差为3·88%。应用本方法对广州大田山垃圾填埋场的垃圾渗沥液中的双酚A进行了测定。     

Simultaneous determination of benzotriazoles and ultraviolet filters in ground water, effluent and biosolid samples using gas chromatography-tandem mass spectrometry

A new method using gas chromatography-tandem mass spectrometry (GC-MS/MS) was developed for the determination of four benzotriazoles, i.e. benzotriazole (BT), 5-methylbenzotriazole (5-TTri), 5-chlorobenzotriazole (CBT), 5,6-dimethylbenzotriazole (XTri), and six UV filters, i.e. benzophenone-3 (BP-3), 3-(4-methylbenzylidene)camphor (4-MBC), octyl 4-methoxycinnamate (OMC), 2-(3-t-butyl-2-hydroxy-5-methylphenyl)-5-chloro benzotriazole (UV-326), 2-(2'-hydroxy-5'-octylphenyl)-benzotriazole (UV-329), and octocrylene (OC) in ground water, effluent and biosolid samples. Solid phase extraction (SPE) and pressurized liquid extraction (PLE) were applied as the preconcentration method for water samples (ground water and effluent) and biosolid samples, respectively. The optimized method allowed us to quantify all target compounds with the method detection limits ranging from 0.29 to 11.02 ng/L, 0.5 to 14.1 ng/L and 0.33 to 8.23 ng/g in tap water, effluent and biosolid samples, respectively. The recoveries of the target analytes in tap water, effluent and biosolid samples were 70-150%, 82-127% and 81-133%, respectively. The developed analytical method was applied in the determination of these target compounds in ground water, effluent and biosolid samples collected from Bolivar sewage treatment plants in South Australia. In effluent samples, the target compounds BT, 5-TTri, CBT, XTri and BP-3 tested were detected with the maximum concentration up to 2.2 μg/L for BT. In biosolid samples, eight out of ten compounds tested were found to be present at the concentrations ranging between 18.7 ng/g (5-TTri) and 250 ng/g (4-MBC).     

Sensitive determination of salicylate and benzophenone type UV filters in water samples using solid-phase microextraction, derivatization and gas chromatography tandem mass spectrometry

A sensitive procedure for the determination of three UV filters: ethylhexyl salicylate (EHS), 3,3,5-trimethylcyclohexyl salicylate (Homosalate, HMS), 2-hydroxy-4-methoxybenzophenone (BP-3) and two related hydroxylated benzophenones (2,4-dihydroxybenzophenone, BP-1 and 2,2′-dihydroxy-4-methoxybenzophenone, BP-8) in water samples is presented. Analytes were first concentrated on the coating of a solid-phase microextraction (SPME) fibre, on-fibre silylated and then determined using gas chromatography combined with tandem mass spectrometry (GC-MS/MS). Factors affecting the performance of extraction and derivatization steps are thoroughly evaluated and their effects on the yield of the sample preparation discussed. Under final working conditions, a PDMS-DVB coated SPME fibre was exposed directly to 10 mL of water, adjusted at pH 3, for 30 min. After that, the fibre was placed in the headspace (HS) of a 1.5 mL vial containing 20 μL of N-methyl-N-(trimethylsilyl)-trifluoroacetamide (MSTFA). On-fibre silylation of hydroxyl groups contained in the structure of target compounds was performed at 45 °C for 10 min. The whole sample preparation process was completed in 40 min, providing limits of quantification from 0.5 to 10 ng L⁻¹ and acceptable precision (RSDs under 13%) for samples spiked at different concentrations. All compounds could be accurately determined in river and treated wastewater (relative recoveries from 89 to 115%) using standards in ultrapure water, whereas standard addition is recommended to quantify their levels in untreated wastewater. Analysis of wastewater revealed the systematic presence of BP-3 and BP-1 in raw samples with maximum concentrations close to 500 and 250 ng L⁻¹, respectively.     

基于石墨烯海绵的固相萃取-液相色谱法测定化妆品中6种紫外吸收剂

以石墨烯海绵（GS）为固相萃取材料,建立了固相萃取-高效液相色谱（SPE-HPLC）同时测定化妆品中6种紫外吸收剂的分析方法。样品经甲醇超声提取,用自制的石墨烯海绵固相萃取小柱净化富集,丙酮洗脱。采用Agilent Zorbax SB-C18色谱柱（150 mm×4.6 mm,5 μm）进行分离,甲醇-水（95∶5,v/v）为流动相,紫外检测波长为340 nm。结果表明,6种紫外吸收剂均在各自的范围内线性关系良好,2-（2'-羟基-5'-甲基苯基）苯并三氮唑的相关系数（r） > 0.997,其他5种r > 0.999。方法的检出限（LOD,S/N=3）和定量限（LOQ,S/N=10）分别为0.08~1.82 μg/L和0.26~6.07 μg/L。在20、50和100 μg/L 3个加标水平下,6种目标物的加标回收率为61.1%~119.0%,相对标准偏差（RSD）小于1%（n=6）。该法简便、快速,灵敏度高,重复性好,适用于不同类型化妆品中紫外吸收剂的检测。     

Non-porous membrane-assisted liquid–liquid extraction of UV filter compounds from water samples

A method for the determination of nine UV filter compounds [benzophenone-3 (BP-3), isoamyl methoxycinnamate, 4-methylbenzylidene camphor, octocrylene (OC), butyl methoxydibenzoylmethane, ethylhexyl dimethyl p-aminobenzoate (OD-PABA), ethylhexyl methoxycinnamate (EHMC), ethylhexyl salicylate and homosalate] in water samples was developed and evaluated. The procedure includes non-porous membrane-assisted liquid–liquid extraction (MALLE) and LC–atmospheric pressure photoionisation (APPI)–MS/MS. Membrane bags made of different polymeric materials were examined to enable a fast and simple extraction of the target analytes. Among the polymeric materials tested, low- and high-density polyethylene membranes proved to be well suited to adsorb the analytes from water samples. Finally, 2 cm length tailor-made membrane bags were prepared from low-density polyethylene in order to accommodate 100 μL of propanol. The fully optimised protocol provides recoveries from 76% to 101% and limits of detection (LOD) between 0.4 ng L⁻¹ (OD-PABA) and 16 ng L⁻¹ (EHMC). The interday repeatability of the whole protocol was below 18%. The effective separation of matrix molecules was proved by only marginal matrix influence during the APPI-MS analysis since no ion suppression effects were observed. During the extraction step, the influence of the matrix was only significant when non-treated wastewater was analysed. The analysis of lake water indicated the presence of seven UV filter compounds included in this study at concentrations between 40 ng L⁻¹ (BP-3) and 4381 ng L⁻¹ (OC). In non-treated wastewater several UV filters were also detected at concentration levels as high as 5322 ng L⁻¹ (OC).     

Study of some UV filters stability in chlorinated water and identification of halogenated by-products by gas chromatography-mass spectrometry

This work studies the stability of three UV filters: 2-ethylhexyl salicylate (ES), 2-ethylhexyl 4-(dimethylamino) benzoate (EHPABA) and 2-hydroxy-4-methoxybenzophenone (BP-3), in water samples containing low concentrations of free chlorine. Moreover, 2,4-dihydroxybenzophenone (2,4-DHBP), a metabolite of BP-3, was also included in some of the performed assays. Experiments were carried out considering free chlorine and analytes concentrations at the microg mL(-1) and ng mL(-1) level, respectively. Gas chromatography with mass spectrometry was used to follow the time course of target compounds and to identify their halogenated by-products. Concentration of water samples with solid-phase extraction cartridges and derivatization (silylation) of some species were also employed to improve their detectability. Under the experimental conditions explored in this work, ES showed an acceptable stability whereas the rest of species reacted with free chlorine at significant rates following pseudo-first-order kinetics. Their half-lives ranged from 0.4 to 25 min depending on the UV filter, chlorine concentration, water pH and presence of bromide traces. For EHPABA a relatively simple degradation pathway was established. It consisted of aromatic substitution of one atom of hydrogen per chlorine or bromide. The same reaction pattern was observed for BP-3 leading, in this case, to mono- and di-halogenated by-products. In addition, several halogenated forms of 3-methoxyphenol were identified as BP-3 cleavage by-products.     

Simultaneous analysis of benzophenone sunscreen compounds in water sample by stir bar sorptive extraction with in situ derivatization and thermal desorption-gas chromatography-mass spectrometry

A method for the simultaneous measurement of benzophenone (BP) sunscreen compounds, its derivatives 2,4-dihydroxybenzophenone (BP-1), 2-hydroxy-4-methoxybenzophenone (BP-3), 2-hydroxy-4-methoxy-4'-methylbenzophenone (BP-10), 2-hydroxybenzophenone (2OH-BP), 3-hydroxybenzophenone (3OH-BP) and 4-hydroxybenzophenone (4OH-BP), in water samples was developed using stir bar sorptive extraction (SBSE) with in situ derivatization followed by thermal desorption (TD)-gas chromatography-mass spectrometry (GC-MS). The detection limit is 0.5-2 ng L(-1) (ppt) for the seven BPs. The method shows good linearity and the correlation coefficients are equal to or higher than 0.990 for all the analyte. The average recoveries of BPs range from 102.0 to 128.1% (RSD<15.4%, n=6). Trace amounts of BPs in river water samples were determined by the present method.     

Simultaneous determination of benzophenone-type UV filters in water and soil by gas chromatography-mass spectrometry

A novel method has been developed to simultaneously determine and quantify seven organic UV filters employing liquid (solid)-liquid extraction, derivatization with N-methyl-N-(trimethylsilyl) trifluoroacetamide (MSTFA) and gas chromatography with mass spectrometric detection in various environmental matrices. The UV filters determined were: benzophenone (BP), benzhydrol (BH), 4-hydroxybenzophenone (HBP), 2-hydroxy-4-methoxybenzophenone (HMB), 2,4-dihydroxybenzophenone (DHB), 2,2'-dihydroxy-4-methoxybenzophenone (DHMB) and 2,3,4-trihydroxylbenzophenone (THB). Under optimal conditions, the analysis required 23 min and good linearity over the range of 10-2,500 ng/L in water and 100-25,000 ng/kg in soil for each UV filter obtained. The high recovery (62-114% and 60-125% for water and soil samples, respectively) and the low RSD values (less than 13.9 and 17.2% for water and soil samples, respectively) indicated the high performance of this method. The method detection limits (MDLs) were relatively low, ranging from 5 to 100 ng/L or kg and quantification limits ranged between 25 and 500 ng/L or kg for all test compounds. This validated method was applied in the analysis of seven BP-type UV filters collecting water and soil samples in Korea, between April and May 2003. The overall concentration of UV filters in the soil sample (500-18,380 ng/kg) was highly distributed in water sample (27-204 ng/L). The established method was successfully applied to monitor the residue measurement of the BP-type UV filters in environmental water and soil samples.     

固相萃取-大体积程序升温进样气相色谱-三重四极杆串联质谱测定饮用水中3种挥发性N-亚硝胺

建立了固相萃取大体积程序升温进样气相色谱-三重四极杆质谱联用（GC-QqQ-MS/MS）同时测定饮用水中N-亚硝基二甲胺、N-亚硝基甲基乙基胺及N-亚硝基二乙基胺的分析方法。用椰壳活性炭固相萃取小柱萃取水样中待测物组分，少量二氯甲烷洗脱、无水硫酸钠脱水，大体积程序升温进样，气相色谱-三重四极杆质谱联用仪进行多反应监测（MRM）模式检测，外标法定量。3种N-亚硝胺在1~50 ng/L范围内线性关系良好，相关系数（r²）均大于0.999，在饮用水中进行10、20和50 ng/L水平的添加，3种待测物平均加标回收率为94.8%~109%，相对标准偏差（RSD）为4.44%~8.10%（n=5），定量限（LOQ）为0.08~0.7 ng/L。该法灵敏、准确、简单、可靠，适用于饮用水中3种N-亚硝胺组分的痕量检测。     

Polyamide as an efficient sorbent for simultaneous interference-free determination of three Sudan dyes in saffron and urine using high-performance liquid chromatography-ultra violet detection北大核心CSCD

With polyamide( PA)as an efficient sorbent for solid phase extraction( SPE)of Sudan dyes II,III and Red 7B from saffron and urine,their determination by HPLC was performed. The optimum conditions for SPE were achieved using 7 mL methanol/water( 1:9,v/v,pH 7)as the washing solvent and 3 mL tetrahydrofu-ran for elution. Good clean-up and high( above 90%)recoveries were observed for all the analytes. The opti-mized mobile phase composition for HPLC analysis of these compounds was methanol-water( 70:30,v/v). The SPE parameters,such as the maximum loading capacity and breakthrough volume,were also determined for each analyte. The limits of detection( LODs),limits of quantification( LOQs),linear ranges and recoveries for the analytes were 4. 6-6. 6 μg/L,13. 0-19. 8 μg/L,13. 0-5 000 μg/L( r2> 0. 99)and 92. 5% -113. 4%,respec-tively. The precisions( RSDs)of the overall analytical procedure,estimated by five replicate measurements for Sudan II,III and Red 7B in saffron and urine samples were 2. 3%,1. 8% and 3. 6%,respectively. The developed method is simple and successful in the application to the determination of Sudan dyes in saffron and urine sam-ples with HPLC coupled with UV detection.     

Determination of ultraviolet filters in environmental water samples by temperature-controlled ionic liquid dispersive liquid-phase microextraction

In the present study, a rapid, highly efficient and environmentally friendly sample preparation method named temperature-controlled ionic liquid dispersive liquid-phase microextraction (TC-IL-DLPME), followed by high performance liquid chromatography (HPLC) was developed for the extraction, preconcentration and determination of four benzophenone-type ultraviolet (UV) filters (viz. benzophenone (BP), 2-hydroxy-4-methoxybenzophenone (BP-3), ethylhexyl salicylate (EHS) and homosalate (HMS)) from water samples. An ultra-hydrophobic ionic liquid (IL) 1-hexyl-3-methylimidazolium tris(pentafluoroethyl)trifluorophosphate ([HMIM][FAP]), was used as the extraction solvent in TC-IL-DLPME. Temperature served two functions here, the promotion of the dispersal of the IL to the aqueous sample solution to form infinitesimal IL drops and increase the interface between them and the target analytes (at high temperature), and the facilitation of mass transfer between the phases, and achievement of phase separation (at low temperature). Due to the ultra-hydrophobic feature and high density of the extraction solvent, complete phase separation could be effected by centrifugation. Moreover, no disperser solvent was required. Another prominent feature of the procedure was the combination of extraction and centrifugation in a single step, which not only greatly reduced the total analysis time for TC-IL-DLPME but also simplified the sample preparation procedure. Various parameters that affected the extraction efficiency (such as type and volume of extraction solvent, temperature, salt addition, extraction time and pH) were evaluated. Under optimal conditions, the proposed method provided good enrichment factors in the range of 240–350, and relative standard deviations (n = 5) below 6.3%. The limits of detection were in the range of 0.2–5.0 ng/mL, depending on the analytes. The linearities were between 1 and 500 ng/mL for BP, 5 and 1000 ng/mL for BP-3, 10 and 1000 ng/mL for HMS and 5 and 1000 ng/mL for EHS. Finally, the proposed method was successfully applied to the determination of UV filters in swimming pool and tap water samples and acceptable relative recoveries over the range of 88.0–116.0% were obtained.