{"id":27765,"date":"2021-08-27T12:56:17","date_gmt":"2021-08-27T10:56:17","guid":{"rendered":"https:\/\/oneearth-oneocean.com\/2021\/08\/27\/tire-wear-particles-in-the-aquatic-environment-a-review-on-generation-analysis-occurrence-fate-and-effects\/"},"modified":"2023-07-05T07:48:25","modified_gmt":"2023-07-05T05:48:25","slug":"tire-wear-particles-in-the-aquatic-environment-a-review-on-generation-analysis-occurrence-fate-and-effects","status":"publish","type":"post","link":"https:\/\/oneearth-oneocean.com\/en\/international-marine-litter-database-es-en\/2021\/tire-wear-particles-in-the-aquatic-environment-a-review-on-generation-analysis-occurrence-fate-and-effects\/","title":{"rendered":"Tire wear particles in the aquatic environment &#8211; a review on generation, analysis, occurrence, fate and effects"},"content":{"rendered":"<p>Stephan Wagner, Thorsten H\u00fcffer, Philipp Kl\u00f6ckner, Maren Wehrhahn, Thilo Hofmann, Thorsten Reemtsma,<\/p>\n<p>Tire wear particles in the aquatic environment &#8211; a review on generation, analysis, occurrence, fate and<br \/>\neffects,<\/p>\n<p>Water Research, Available online 24 March 2018, ISSN 0043-1354,<\/p>\n<p>Abstract:<br \/>\nTire wear particles (TWP), generated from tire material during use on<br \/>\nroads have gained increasing attention as part of organic particulate<br \/>\ncontaminants, such as microplastic, in aquatic environments. The<br \/>\navailable information on properties and generation of TWP, analytical<br \/>\ntechniques to determine TWP, emissions, occurrence and behavior and<br \/>\necotoxicological effects of TWP are reviewed with a focus on surface<br \/>\nwater as a potential receptor. TWP emissions are traffic related and<br \/>\ncontribute 5 \u2013 30 % to non-exhaust emissions from traffic. The mass of<br \/>\nTWP generated is estimated at 1,327,000 t\/a for the European Union,<br \/>\n1,120,000 t\/a for the United States and 133,000 t\/a for Germany. For<br \/>\nGermany, this is equivalent to four times the amount of pesticides used.<br \/>\nThe mass of TWP ultimately entering the aquatic environment strongly<br \/>\ndepends on the extent of collection and treatment of road runoff, which<br \/>\nis highly variable. For the German highways it is estimated that up to<br \/>\n11,000 t\/a of TWP reach surface waters. Data on TWP concentrations in<br \/>\nthe environment, including surface waters are fragmentary, which is also<br \/>\ndue to the lack of suitable analytical methods for their determination.<br \/>\nInformation on TWP properties such as density and size distribution are<br \/>\nmissing; this hampers assessing the fate of TWP in the aquatic<br \/>\nenvironment. Effects in the aquatic environment may stem from TWP itself<br \/>\nor from compounds released from TWP. It is concluded that reliable<br \/>\nknowledge on transport mechanism to surface waters, concentrations in<br \/>\nsurface waters and sediments, effects of aging, environmental half-lives<br \/>\nof TWP as well as effects on aquatic organisms are missing. These<br \/>\naspects need to be addressed to allow for the assessment of risk of TWP<br \/>\nin an aquatic environment.<\/p>\n<p><a href=\"https:\/\/drive.google.com\/open?id=1XW4YwVz84_O8AWLa21beJ53p4rNYKM7Z\">https:\/\/drive.google.com\/open?id=1XW4YwVz84_O8AWLa21beJ53p4rNYKM7Z<\/a><br \/>\nhttps:\/\/doi.org\/10.1016\/j.watres.2018.03.051.(https:\/\/www.sciencedirect.com\/science\/article\/pii\/S0043135418302471)<\/p>\n<p><a href=\"https:\/\/www.theoceancleanup.com\/updates\/the-exponential-increase-of-the-great-pacific-garbage-patch\/\">https:\/\/www.theoceancleanup.com\/updates\/the-exponential-increase-of-the-great-pacific-garbage-patch\/<\/a><\/p>\n","protected":false},"excerpt":{"rendered":"<p>Stephan Wagner, Thorsten H\u00fcffer, Philipp Kl\u00f6ckner, Maren Wehrhahn, Thilo Hofmann, Thorsten Reemtsma, Tire wear particles in the aquatic environment &#8211; a review on generation, analysis, occurrence, fate and effects, Water Research, Available online 24 March 2018, ISSN 0043-1354, Abstract: Tire wear particles (TWP), generated from tire material during use on roads have gained increasing attention as part of organic particulate contaminants, such as microplastic, in aquatic environments. The available information on properties and generation of TWP, analytical techniques to determine TWP, emissions, occurrence and behavior and ecotoxicological effects of TWP are reviewed with a focus on surface water as a potential receptor. TWP emissions are traffic related and contribute 5 \u2013 30 % to non-exhaust emissions from traffic. The mass of TWP generated is estimated at 1,327,000 t\/a for the European Union, 1,120,000 t\/a for the United States and 133,000 t\/a for Germany. For Germany, this is equivalent to four times the amount of pesticides used. The mass of TWP ultimately entering the aquatic environment strongly depends on the extent of collection and treatment of road runoff, which is highly variable. For the German highways it is estimated that up to 11,000 t\/a of TWP reach surface waters. Data on TWP concentrations in the environment, including surface waters are fragmentary, which is also due to the lack of suitable analytical methods for their determination. Information on TWP properties such as density and size distribution are missing; this hampers assessing the fate of TWP in the aquatic environment. Effects in the aquatic environment may stem from TWP itself or from compounds released from TWP. It is concluded that reliable knowledge on transport mechanism to surface waters, concentrations in surface waters and sediments, effects of aging, environmental half-lives of TWP as well as effects on aquatic organisms are missing. These aspects need to be addressed to allow for the assessment of risk of TWP in an aquatic environment. https:\/\/drive.google.com\/open?id=1XW4YwVz84_O8AWLa21beJ53p4rNYKM7Z https:\/\/doi.org\/10.1016\/j.watres.2018.03.051.(https:\/\/www.sciencedirect.com\/science\/article\/pii\/S0043135418302471) https:\/\/www.theoceancleanup.com\/updates\/the-exponential-increase-of-the-great-pacific-garbage-patch\/<\/p>\n","protected":false},"author":8,"featured_media":0,"comment_status":"closed","ping_status":"closed","sticky":false,"template":"","format":"standard","meta":{"footnotes":""},"categories":[2215],"tags":[4172,4173,4174,4175,4176,4160],"yoast_head":"<!-- This site is optimized with the Yoast SEO plugin v24.1 - https:\/\/yoast.com\/wordpress\/plugins\/seo\/ -->\n<title>Tire wear particles in the aquatic environment - a review on generation, analysis, occurrence, fate and effects - One Earth - One Ocean e. V.<\/title>\n<meta name=\"robots\" content=\"index, follow, max-snippet:-1, max-image-preview:large, max-video-preview:-1\" \/>\n<link rel=\"canonical\" href=\"https:\/\/oneearth-oneocean.com\/en\/international-marine-litter-database-es-en\/2021\/tire-wear-particles-in-the-aquatic-environment-a-review-on-generation-analysis-occurrence-fate-and-effects\/\" \/>\n<meta property=\"og:locale\" content=\"en_US\" \/>\n<meta property=\"og:type\" content=\"article\" \/>\n<meta property=\"og:title\" content=\"Tire wear particles in the aquatic environment - a review on generation, analysis, occurrence, fate and effects - One Earth - One Ocean e. 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The mass of TWP generated is estimated at 1,327,000 t\/a for the European Union, 1,120,000 t\/a for the United States and 133,000 t\/a for Germany. For Germany, this is equivalent to four times the amount of pesticides used. The mass of TWP ultimately entering the aquatic environment strongly depends on the extent of collection and treatment of road runoff, which is highly variable. For the German highways it is estimated that up to 11,000 t\/a of TWP reach surface waters. Data on TWP concentrations in the environment, including surface waters are fragmentary, which is also due to the lack of suitable analytical methods for their determination. Information on TWP properties such as density and size distribution are missing; this hampers assessing the fate of TWP in the aquatic environment. Effects in the aquatic environment may stem from TWP itself or from compounds released from TWP. It is concluded that reliable knowledge on transport mechanism to surface waters, concentrations in surface waters and sediments, effects of aging, environmental half-lives of TWP as well as effects on aquatic organisms are missing. These aspects need to be addressed to allow for the assessment of risk of TWP in an aquatic environment. https:\/\/drive.google.com\/open?id=1XW4YwVz84_O8AWLa21beJ53p4rNYKM7Z https:\/\/doi.org\/10.1016\/j.watres.2018.03.051.(https:\/\/www.sciencedirect.com\/science\/article\/pii\/S0043135418302471) https:\/\/www.theoceancleanup.com\/updates\/the-exponential-increase-of-the-great-pacific-garbage-patch\/\" \/>\n<meta property=\"og:url\" content=\"https:\/\/oneearth-oneocean.com\/en\/international-marine-litter-database-es-en\/2021\/tire-wear-particles-in-the-aquatic-environment-a-review-on-generation-analysis-occurrence-fate-and-effects\/\" \/>\n<meta property=\"og:site_name\" content=\"One Earth - One Ocean e. 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The mass of TWP generated is estimated at 1,327,000 t\/a for the European Union, 1,120,000 t\/a for the United States and 133,000 t\/a for Germany. For Germany, this is equivalent to four times the amount of pesticides used. The mass of TWP ultimately entering the aquatic environment strongly depends on the extent of collection and treatment of road runoff, which is highly variable. For the German highways it is estimated that up to 11,000 t\/a of TWP reach surface waters. Data on TWP concentrations in the environment, including surface waters are fragmentary, which is also due to the lack of suitable analytical methods for their determination. Information on TWP properties such as density and size distribution are missing; this hampers assessing the fate of TWP in the aquatic environment. Effects in the aquatic environment may stem from TWP itself or from compounds released from TWP. It is concluded that reliable knowledge on transport mechanism to surface waters, concentrations in surface waters and sediments, effects of aging, environmental half-lives of TWP as well as effects on aquatic organisms are missing. These aspects need to be addressed to allow for the assessment of risk of TWP in an aquatic environment. https:\/\/drive.google.com\/open?id=1XW4YwVz84_O8AWLa21beJ53p4rNYKM7Z https:\/\/doi.org\/10.1016\/j.watres.2018.03.051.(https:\/\/www.sciencedirect.com\/science\/article\/pii\/S0043135418302471) https:\/\/www.theoceancleanup.com\/updates\/the-exponential-increase-of-the-great-pacific-garbage-patch\/","og_url":"https:\/\/oneearth-oneocean.com\/en\/international-marine-litter-database-es-en\/2021\/tire-wear-particles-in-the-aquatic-environment-a-review-on-generation-analysis-occurrence-fate-and-effects\/","og_site_name":"One Earth - One Ocean e. 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