Abstract
In the present study, polycyclic aromatic hydrocarbon (PAH) accumulation performances of four butyl rubber (BR) monophasic passive samplers with different pore structures were investigated and the results were compared with monophasic polydimethylsiloxane (PDMS) samplers and biphasic semipermeable membrane devices (SPMDs). Stainless steel cages containing passive samplers were deployed in the water column in Istinye Bay, Istanbul Strait, and retrieved after 7 and 28 days. Collected samplers were analyzed using high-performance liquid chromatography (HPLC) to determine their PAH contents. Results showed that BR passive samplers have sampled all PAHs for both short- and long-term sampling periods while SPMD samplers only collected twelve and thirteen PAHs after 7 and 28 days, respectively. PDMS samplers showed the poorest performance, having only sampled seven and ten PAHs after 7 and 28 days, respectively. Among the BR samplers, a monophasic BR sampler with a single pore network (SN10) showed the most feasible performance in terms of PAH sampling and its preparation cost. Results highlighted that the SN10 sampler with a wide absorption range and monophasic structure can be used as an alternative passive sampler for pollution monitoring in marine environments.
Highlights
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Butyl rubber samplers showed the highest accumulation performances for PAHs with high log Kow.
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Butyl rubber passive samplers were found suitable for marine pollution monitoring.
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The most efficient version of butyl rubber samplers for field studies has been determined.
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Data Availability
The datasets generated during the current study are available from the corresponding author on reasonable request.
References
Allan IJ, Vrana B, Greenwood R, Mills GA, Roig B, Gonzalez C (2006) A “toolbox” for biological and chemical monitoring requirements for the European Union’s Water Framework Directive. Talanta 69(2):302–322. https://doi.org/10.1016/j.talanta.2005.09.043
Bailon MX, Park MO, Hong Y (2019) Passive sampling methods for assessing the bioaccumulation of heavy metals in sediments. Curr Pollut Reports 5:129–143. https://doi.org/10.1007/s40726-019-00111-w
Balcıoğlu EB (2016) Potential effects of polycyclic aromatic hydrocarbons (PAHs) in marine foods on human health: a critical review. Toxin Rev 35:98–105. https://doi.org/10.1080/15569543.2016.1201513
Barut IF, Meriç E, Yokeş MB (2016) Assessment of recent and chalcolithic period environmental pollution using Mytilus galloprovincialis Lamarck, 1819 from Yarimburgaz Cave, the northern Marmara Sea and Bosphorus coasts. Oceanologia 58:135–149. https://doi.org/10.1016/j.oceano.2016.01.001
Belles A, Alary C, Aminot Y, Readman JW, Franke C (2017) Calibration and response of an agarose gel based passive sampler to record short pulses of aquatic organic pollutants. Talanta 165:1–9. https://doi.org/10.1016/j.talanta.2016.12.010
Benali I, Boutiba Z, Grandjean D, De Alencastro LF, Rouane-Hacene O, Chèvre N (2017) Spatial distribution and biological effects of trace metals (Cu, Zn, Pb, Cd) and organic micropollutants (PCBs, PAHs) in mussels Mytilus galloprovincialis along the Algerian west coast. Mar Pollut Bull 115:539–550. https://doi.org/10.1016/j.marpolbul.2016.12.028
Booij K, Robinson CD, Burgess RM, Mayer P, Roberts CA, Ahrens L, Allan IJ, Brant J, Jones L, Kraus UR, Larsen MM (2016) Passive sampling in regulatory chemical monitoring of nonpolar organic compounds in the aquatic environment. Environ Sci Technol 50:3–17. https://doi.org/10.1021/acs.est.5b04050
Booij K, Sleiderink HM, Smedes F (1998) Calibrating the uptake kinetics of semipermeable membrane devices using exposure standards. Environ Toxicol Chem An Int J 17:1236–1245. https://doi.org/10.1002/etc.5620170707
Booij K, Smedes F (2010) An improved method for estimating in situ sampling rates of nonpolar passive samplers. Environ Sci Technol 44:6789–6794. https://doi.org/10.1021/es101321v
Ceylan D, Dogu S, Karacik B, Yakan SD, Okay OS, Okay O (2009) Evaluation of butyl rubber as sorbent material for the removal of oil and polycyclic aromatic hydrocarbons from seawater. Environ Sci Technol 43:3846–3852. https://doi.org/10.1021/es900166v
Estoppey N, Schopfer A, Fong C, Delémont O, De Alencastro LF, Esseiva P (2016) An in-situ assessment of low-density polyethylene and silicone rubber passive samplers using methods with and without performance reference compounds in the context of investigation of polychlorinated biphenyl sources in rivers. Sci Total Environ 572:794–803. https://doi.org/10.1016/j.scitotenv.2016.07.092
European Commission (2009) CIS WFD, Guidance Document No. 19. Surface Water Chemical Monitoring
Fernandez LA, Lao W, Maruya KA, White C, Burgess RM (2012) Passive sampling to measure baseline dissolved persistent organic pollutant concentrations in the water column of the Palos Verdes shelf superfund site. Environ Sci Technol 46:11937–11947. https://doi.org/10.1021/ES302139Y/SUPPL_FILE/ES302139Y_SI_001.PDF
Jonker MTO, Van Der Heijden SA, Kotte M, Smedes F (2015) Quantifying the effects of temperature and salinity on partitioning of hydrophobic organic chemicals to silicone rubber passive samplers. Environ Sci Technol 49:6791–6799. https://doi.org/10.1021/acs.est.5b00286
Josefsson S, Arp HP, Kleja DB, Enell A, Lundstedt S (2015) Determination of polyoxymethylene (POM) - water partition coefficients for oxy-PAHs and PAHs. Chemosphere 119:1268–1274. https://doi.org/10.1016/j.chemosphere.2014.09.102
Karacık B, Okay OS, Henkelmann B, Bernhöft S, Schramm KW (2009) Polycyclic aromatic hydrocarbons and effects on marine organisms in the Istanbul Strait. Environ Int 35:599–606. https://doi.org/10.1016/j.envint.2008.11.005
Karacık B, Okay OS, Henkelmann B, Pfister G, Schramm KW (2013) Water concentrations of PAH, PCB and OCP by using semipermeable membrane devices and sediments. Mar Pollut Bull 70:258–265. https://doi.org/10.1016/j.marpolbul.2013.02.031
Ke CL, Gu YG, Liu Q, Li LD, Huang HH, Cai N, Sun ZW (2017) Polycyclic aromatic hydrocarbons (PAHs) in wild marine organisms from South China Sea: Occurrence, sources, and human health implications. Mar Pollut Bull 117:507–511. https://doi.org/10.1016/j.marpolbul.2017.02.018
Kumar V, Kothiyal NC, Saruchi, Vikas P, Sharma R (2016) Sources, distribution, and health effect of carcinogenic polycyclic aromatic hydrocarbons (PAHs) – current knowledge and future directions. J Chin Adv Mater Soc 4:302–321. https://doi.org/10.1080/22243682.2016.1230475
Lee BM, Shim GA (2007) Dietary exposure estimation of benzo [a] pyrene and cancer risk assessment. J Toxicol Environ Heal Part A 70:1391–1394. https://doi.org/10.1080/15287390701434182
Li Y, Wang C, Zou X, Feng Z, Yao Y, Wang T, Zhang C (2019) Occurrence of polycyclic aromatic hydrocarbons (PAHs) in coral reef fish from the South China Sea. Mar Pollut Bull 139:339–345. https://doi.org/10.1016/j.marpolbul.2019.01.001
Luellen DR, Shea D (2002) Calibration and field verification of semipermeable membrane devices for measuring polycyclic aromatic hydrocarbons in water. Environ Sci Technol 36:1791–1797. https://doi.org/10.1021/es0113504
Maruya KA, Lao W, Tsukada D, Diehl DW (2015) A passive sampler based on solid phase microextraction (SPME) for sediment-associated organic pollutants: Comparing freely-dissolved concentration with bioaccumulation. Chemosphere 137:192–197. https://doi.org/10.1016/j.chemosphere.2015.07.042
Muslumova S, Yetiskin B, Okay O (2019) Highly stretchable and rapid self-recoverable cryogels based on butyl rubber as reusable sorbent. Gels 5(1):1. https://doi.org/10.3390/gels5010001
Mutzner L, Bohren C, Mangold S, Bloem S, Ort C (2020) Spatial differences among micropollutants in sewer overflows: a multisite analysis using passive samplers. Environ Sci Technol 54:6584–6593. https://doi.org/10.1021/acs.est.9b05148
O’Brien D, Komarova T, Mueller JF (2012) Determination of deployment specific chemical uptake rates for SPMD and PDMS using a passive flow monitor. Mar Pollut Bull 64:1005–1011. https://doi.org/10.1016/j.marpolbul.2012.02.004
Commision OSPAR (2013) JAMP Guidelines for Monitoring of Contaminants in Seawater (Agreement 2013-03) Available at: http://mcc.jrc.ec.europa.eu/documents/OSPAR/Guidelines_forMonitoring_of_ContaminantsSeawater.pdf (last accessed 15.03.2022)
Page D, Miotliński K, Gonzalez D, Barry K, Dillon P, Gallen C (2014) Environmental monitoring of selected pesticides and organic chemicals in urban stormwater recycling systems using passive sampling techniques. J Contam Hydrol 158:65–77. https://doi.org/10.1016/j.jconhyd.2014.01.004
Reichenberg F, Mayer P (2006) Two complementary sides of bioavailability: Accessibility and chemical activity of organic contaminants in sediments and soils. Environ Toxicol Chem 25(5):1239–1245. https://doi.org/10.1897/05-458R.1
Rengarajan T, Rajendran P, Nandakumar N, Lokeshkumar B, Rajendran P, Nishigaki I (2015) Exposure to polycyclic aromatic hydrocarbons with special focus on cancer. Asian Pac J Trop Biomed 5(3):182–189. https://doi.org/10.1016/S2221-1691(15)30003-4
Tao Y, Liu D (2019) Trophic status affects the distribution of polycyclic aromatic hydrocarbons in the water columns, surface sediments, and plankton of twenty Chinese lakes. Environ Pollut 252:666–674. https://doi.org/10.1016/j.envpol.2019.05.139
Taylor AC, Fones GR, Vrana B, Mills GA (2021) Applications for passive sampling of hydrophobic organic contaminants in water—A review. Crit Rev Anal Chem 51:20–54. https://doi.org/10.1080/10408347.2019.1675043
ter Laak TL, Busser FJM, Hermens JLM (2008) Poly(dimethylsiloxane) as passive sampler material for hydrophobic chemicals: effect of chemical properties and sampler characteristics on partitioning and equilibration times. Anal Chem 80:3859–3866. https://doi.org/10.1021/ac800258j
Tureyen OE, Yilmaz A, Yakan SD, Yetiskin B, Okay O, Okay OS (2021) Performance of butyl rubber–based macroporous sorbents as passive samplers. Environ Sci Pollut Res 28:3766–3773. https://doi.org/10.1007/s11356-020-08945-4
Vinturella AE, Burgess RM, Coull BA, Thompson KM, Shine JP (2004) Use of passive samplers to mimic uptake of polycyclic aromatic hydrocarbons by benthic polychaetes. Environ Sci Technol 38:1154–1160. https://doi.org/10.1021/es034706f
Xia K, Hagood G, Childers C, Atkins J, Rogers B, Ware L, Armbrust K, Jewell J, Diaz D, Gatian N, Folmer H (2012) Polycyclic aromatic hydrocarbons (PAHs) in Mississippi seafood from areas affected by the deepwater horizon oil spill. Environ Sci Technol 46:5310–5318. https://doi.org/10.1021/es2042433
Xue R, Chen L, Lu Z, Wang J, Yang H, Zhang J, Cai M (2016) Spatial distribution and source apportionment of PAHs in marine surface sediments of Prydz Bay, East Antarctica. Environ Pollut 219:528–536. https://doi.org/10.1016/j.envpol.2016.05.084
Yetiskin B, Tureyen OE, Yilmaz A, Yakan SD, Okay OS, Okay O (2019) Single-, double-, and triple-network macroporous rubbers as a passive sampler. ACS Appl Mater Interfaces 11(31):28317–28326. https://doi.org/10.1021/acsami.9b08788
Yılmaz A, Karacık B, Henkelmann B, Pfister G, Schramm KW, Yakan SD, Barlas B, Okay OS (2014) Use of passive samplers in pollution monitoring: A numerical approach for marinas. Environ Int 73:85–93. https://doi.org/10.1016/j.envint.2014.07.013
Yılmaz A, Tolun LG, Okay OS (2019) Pollution and toxicity of sediment in potential dredging sites of the Marmara Sea, Turkey. J Environ Sci Heal - Part A Toxic/Hazardous. Subst Environ Eng 54:1206–1218. https://doi.org/10.1080/10934529.2019.1631656
Zendong Z, Bertrand S, Herrenknecht C, Abadie E, Jauzein C, Lemée R, Gouriou J, Amzil Z, Hess P (2016) Passive sampling and high resolution mass spectrometry for chemical profiling of french coastal areas with a focus on marine biotoxins. Environ Sci Technol 50:8522–8529. https://doi.org/10.1021/acs.est.6b02081
Acknowledgements
Part of the present research was initially presented at CEMEPE2021 Conference, July 20 to 24, 2021, Thessaloniki, Greece. The research was funded by the Scientific and Technical Research Council of Turkey (TUBITAK), CAYDAG, 117Y099.
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The research was funded by the Scientific and Technical Research Council of Turkey (TUBITAK), CAYDAG, 117Y099.
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All authors contributed to the study’s conception and design. Material preparation, data collection and analysis were performed also by all authors. The first draft of the manuscript was written by Oktay Eren Tureyen and all authors commented on previous versions of the manuscript. All authors read and approved the final manuscript.
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Tureyen, O.E., Yakan, S.D., Yilmaz, A. et al. Polycyclic Aromatic Hydrocarbon Accumulation Performances of Monophasic Butyl Rubber Passive Samplers. Environ. Process. 9, 34 (2022). https://doi.org/10.1007/s40710-022-00578-8
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DOI: https://doi.org/10.1007/s40710-022-00578-8