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Sources, Transport and Fate of Organic Pollutants in the Oceanic Environment.

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Sources, Transport and Fate of Organic Pollutants in the Oceanic Environment. / Gioia, Rosalinda; Dachs, Jordi; Nizzetto, Luca; Berrojalbiz, Naiara; Galban, Cristobal; Del Vento, Sabino; Méjanelle, Laurence; Jones, Kevin.

Persistent Pollution-Past, Present and Future. ed. / Markus Quante; Ralf Ebinghaus; Gotz Floser. 1st. ed. Berlin : Springer, 2011. p. 111-139.

Research output: Contribution in Book/Report/Proceedings - With ISBN/ISSNChapter

Harvard

Gioia, R, Dachs, J, Nizzetto, L, Berrojalbiz, N, Galban, C, Del Vento, S, Méjanelle, L & Jones, K 2011, Sources, Transport and Fate of Organic Pollutants in the Oceanic Environment. in M Quante, R Ebinghaus & G Floser (eds), Persistent Pollution-Past, Present and Future. 1st edn, Springer, Berlin, pp. 111-139. https://doi.org/10.1007/978-3-642-17419-3_8

APA

Gioia, R., Dachs, J., Nizzetto, L., Berrojalbiz, N., Galban, C., Del Vento, S., Méjanelle, L., & Jones, K. (2011). Sources, Transport and Fate of Organic Pollutants in the Oceanic Environment. In M. Quante, R. Ebinghaus, & G. Floser (Eds.), Persistent Pollution-Past, Present and Future (1st ed., pp. 111-139). Springer. https://doi.org/10.1007/978-3-642-17419-3_8

Vancouver

Gioia R, Dachs J, Nizzetto L, Berrojalbiz N, Galban C, Del Vento S et al. Sources, Transport and Fate of Organic Pollutants in the Oceanic Environment. In Quante M, Ebinghaus R, Floser G, editors, Persistent Pollution-Past, Present and Future. 1st ed. Berlin: Springer. 2011. p. 111-139 https://doi.org/10.1007/978-3-642-17419-3_8

Author

Gioia, Rosalinda ; Dachs, Jordi ; Nizzetto, Luca ; Berrojalbiz, Naiara ; Galban, Cristobal ; Del Vento, Sabino ; Méjanelle, Laurence ; Jones, Kevin. / Sources, Transport and Fate of Organic Pollutants in the Oceanic Environment. Persistent Pollution-Past, Present and Future. editor / Markus Quante ; Ralf Ebinghaus ; Gotz Floser. 1st. ed. Berlin : Springer, 2011. pp. 111-139

Bibtex

@inbook{fd1d669725654818a3bc796c589c4760,
title = "Sources, Transport and Fate of Organic Pollutants in the Oceanic Environment.",
abstract = "Industrial, agricultural and other anthropogenic activities have lead to the introduction of thousands of pollutants, most of them synthetic organic compounds to the marine environment (Dachs and M{\'e}janelle 2010). A fraction of these organic compounds, called persistent organic pollutants (POPs), are chemicals that have become a major concern because of their toxicity, persistence, bioaccumulation tendency, and susceptibility to undergo long-range atmospheric transport. Traditionally, much attention have been given to a few families of POPs, such as polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs) such as DDT and hexachlorobenzene (HCB) and other byproducts of industrial processes or combustion such as dioxins and furans (PCDD/Fs) and polynuclear aromatic hydrocarbons (PAHs). However, these chemicals are a small fraction of the total known pollutants in the marine environment (Dachs and M{\'e}janelle 2010) and presumably of the total potential pollutants occurring in the environment (Muir and Howard 2006). In any case, these few families of POPs have been detected everywhere on earth in abiotic and biotic matrices (Gioia et al. 2006, 2008a; Gilman et al. 1997; Jaward et al. 2004). Today, compounds with similar or different physical chemical properties (such as the polybrominated diphenyl ethers, PBDE and other fluorinated compounds, PFs) are being manufactured and widely used, potentially entering the environment and providing new challenges for the maintenance of its quality. Our current knowledge indicates that the cycling of these chemicals in the environment is highly complex; indeed their local, regional and global cycle is controlled by repeated air-surface exchange and interactions with the carbon cycle, especially the organic and soot carbon fractions. Because, a fraction of these chemicals are hydrophobic, they have the potential to accumulate in all the trophic levels of ecosystems, including those far away from sources. The number of known organic pollutants in marine waters, and other environmental compartments, has increased dramatically during the last decade, in part due to important analytical developments. Nowadays, even though much of our knowledge on organic pollutants is centered on a few chemical families (PCBs, HCHs, DDT, PAHs, etc.), these families should be viewed as markers or “surrogates” of other pollutants in marine waters with similar physical–chemical properties. In addition, other chemicals with different physical–chemical properties (i.e., greater water solubility, low volatility) may reach coastal and open oceans via rivers and undergo different environmental behavior, due to their ionic character. In fact, some of newly emerging compounds have been suggested to behave as passive tracers in waters (Yamashita et al. 2008), a behavior quite different from that shown by legacy POPs such as PCBs or HCHs.",
author = "Rosalinda Gioia and Jordi Dachs and Luca Nizzetto and Naiara Berrojalbiz and Cristobal Galban and {Del Vento}, Sabino and Laurence M{\'e}janelle and Kevin Jones",
year = "2011",
doi = "10.1007/978-3-642-17419-3_8",
language = "English",
isbn = "978-3-642-17420-9 ",
pages = "111--139",
editor = "Markus Quante and Ralf Ebinghaus and Gotz Floser",
booktitle = "Persistent Pollution-Past, Present and Future",
publisher = "Springer",
edition = "1st",

}

RIS

TY - CHAP

T1 - Sources, Transport and Fate of Organic Pollutants in the Oceanic Environment.

AU - Gioia, Rosalinda

AU - Dachs, Jordi

AU - Nizzetto, Luca

AU - Berrojalbiz, Naiara

AU - Galban, Cristobal

AU - Del Vento, Sabino

AU - Méjanelle, Laurence

AU - Jones, Kevin

PY - 2011

Y1 - 2011

N2 - Industrial, agricultural and other anthropogenic activities have lead to the introduction of thousands of pollutants, most of them synthetic organic compounds to the marine environment (Dachs and Méjanelle 2010). A fraction of these organic compounds, called persistent organic pollutants (POPs), are chemicals that have become a major concern because of their toxicity, persistence, bioaccumulation tendency, and susceptibility to undergo long-range atmospheric transport. Traditionally, much attention have been given to a few families of POPs, such as polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs) such as DDT and hexachlorobenzene (HCB) and other byproducts of industrial processes or combustion such as dioxins and furans (PCDD/Fs) and polynuclear aromatic hydrocarbons (PAHs). However, these chemicals are a small fraction of the total known pollutants in the marine environment (Dachs and Méjanelle 2010) and presumably of the total potential pollutants occurring in the environment (Muir and Howard 2006). In any case, these few families of POPs have been detected everywhere on earth in abiotic and biotic matrices (Gioia et al. 2006, 2008a; Gilman et al. 1997; Jaward et al. 2004). Today, compounds with similar or different physical chemical properties (such as the polybrominated diphenyl ethers, PBDE and other fluorinated compounds, PFs) are being manufactured and widely used, potentially entering the environment and providing new challenges for the maintenance of its quality. Our current knowledge indicates that the cycling of these chemicals in the environment is highly complex; indeed their local, regional and global cycle is controlled by repeated air-surface exchange and interactions with the carbon cycle, especially the organic and soot carbon fractions. Because, a fraction of these chemicals are hydrophobic, they have the potential to accumulate in all the trophic levels of ecosystems, including those far away from sources. The number of known organic pollutants in marine waters, and other environmental compartments, has increased dramatically during the last decade, in part due to important analytical developments. Nowadays, even though much of our knowledge on organic pollutants is centered on a few chemical families (PCBs, HCHs, DDT, PAHs, etc.), these families should be viewed as markers or “surrogates” of other pollutants in marine waters with similar physical–chemical properties. In addition, other chemicals with different physical–chemical properties (i.e., greater water solubility, low volatility) may reach coastal and open oceans via rivers and undergo different environmental behavior, due to their ionic character. In fact, some of newly emerging compounds have been suggested to behave as passive tracers in waters (Yamashita et al. 2008), a behavior quite different from that shown by legacy POPs such as PCBs or HCHs.

AB - Industrial, agricultural and other anthropogenic activities have lead to the introduction of thousands of pollutants, most of them synthetic organic compounds to the marine environment (Dachs and Méjanelle 2010). A fraction of these organic compounds, called persistent organic pollutants (POPs), are chemicals that have become a major concern because of their toxicity, persistence, bioaccumulation tendency, and susceptibility to undergo long-range atmospheric transport. Traditionally, much attention have been given to a few families of POPs, such as polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs) such as DDT and hexachlorobenzene (HCB) and other byproducts of industrial processes or combustion such as dioxins and furans (PCDD/Fs) and polynuclear aromatic hydrocarbons (PAHs). However, these chemicals are a small fraction of the total known pollutants in the marine environment (Dachs and Méjanelle 2010) and presumably of the total potential pollutants occurring in the environment (Muir and Howard 2006). In any case, these few families of POPs have been detected everywhere on earth in abiotic and biotic matrices (Gioia et al. 2006, 2008a; Gilman et al. 1997; Jaward et al. 2004). Today, compounds with similar or different physical chemical properties (such as the polybrominated diphenyl ethers, PBDE and other fluorinated compounds, PFs) are being manufactured and widely used, potentially entering the environment and providing new challenges for the maintenance of its quality. Our current knowledge indicates that the cycling of these chemicals in the environment is highly complex; indeed their local, regional and global cycle is controlled by repeated air-surface exchange and interactions with the carbon cycle, especially the organic and soot carbon fractions. Because, a fraction of these chemicals are hydrophobic, they have the potential to accumulate in all the trophic levels of ecosystems, including those far away from sources. The number of known organic pollutants in marine waters, and other environmental compartments, has increased dramatically during the last decade, in part due to important analytical developments. Nowadays, even though much of our knowledge on organic pollutants is centered on a few chemical families (PCBs, HCHs, DDT, PAHs, etc.), these families should be viewed as markers or “surrogates” of other pollutants in marine waters with similar physical–chemical properties. In addition, other chemicals with different physical–chemical properties (i.e., greater water solubility, low volatility) may reach coastal and open oceans via rivers and undergo different environmental behavior, due to their ionic character. In fact, some of newly emerging compounds have been suggested to behave as passive tracers in waters (Yamashita et al. 2008), a behavior quite different from that shown by legacy POPs such as PCBs or HCHs.

U2 - 10.1007/978-3-642-17419-3_8

DO - 10.1007/978-3-642-17419-3_8

M3 - Chapter

SN - 978-3-642-17420-9

SP - 111

EP - 139

BT - Persistent Pollution-Past, Present and Future

A2 - Quante, Markus

A2 - Ebinghaus, Ralf

A2 - Floser, Gotz

PB - Springer

CY - Berlin

ER -