International Research Journal of Public and Environmental Health Vol.2 (9),pp. 122-126, September 2015
Available online at http://www.journalissues.org/IRJPEH
http://dx.doi.org/10.15739/irjpeh.029
Copyright © 2015 Author(s) retain the copyright of this article ISSN 2360-8803
Original Research Article
Galaxolide
®
pollution of Gracilaria bursa-pastoris
collected in Dardanelles: An ecotoxicological marker of
Danube River water route to Aegean Sea
Received 15 August, 2015 Revised 4 September, 2015 Accepted 7 September, 2015 Published 14 September, 2015
Kasim Cemal Guven
1*
,
Burak Coban
2
and
Hüseyin Erdugan
3
1
Turkish Marine Research
Foundation (TUDAV), P.O. Box: 10,
Beykoz, 81650, Istanbul, Turkey.
2
Bulent Ecevit University,
Department of Chemistry, Zonguldak,
67100, Turkey.
3
18 Mart University, Faculty of
Science, Department of Biology,
Çanakkale, Turkey.
*Corresponding Author
E-mail: kcguven@yahoo.com.tr
In this work, Galaxolide
®
pollution is reported in the alga Gracilaria bursa-
pastoris (S. G. Gmelin) P. C. Silva collected from Sogandere, Dardanelles. The
identification was made by GC/MS analysis. Galaxolide
®
, widely used in
perfumery was detected in water, river, marine organisms and algae. This
pollutant was earlier detected in Danube River water, in the Bulgarian coast
and in red alga Laurencia pyramidalis collected from the İğneada, western
Black Sea coast of Turkey. These findings can generate a proof of Danube
River water circulation to the Aegean Sea and the potential use of
Galaxolide
®
as a chemical tracer for the assessment of hydrological pollution
sources in the region.
Key words: Galaxolide
®
, pollution, seaweed, Gracilaria bursa-pastoris.
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INTRODUCTION
The pollutant, Galaxolide
®
(HHCB) 1,3,4,6,7,8-Hexahydro-
4,6,6,7,8,8-hexamethylcyclopenta (alpha)-2-benzopyran
(Figure 1), is a synthetic musk with widespread use in
perfumery. It has been reported as an emerging
contaminant in waters and may produce harmful effects on
aquatic ecosystems (Parolini et al., 2015) and human health
(Kumar and Xagoraraki, 2010). It was identified in ground
water (Stuart et al., 2012), drinking water (Kumar and
Xagoraraki, 2010), wastewater (Gomez et al., 2011;
Antoniou et al., 2009; Machado et al. 2011; Yu et al., 2012),
sediment (Tian et al., 2011; Spozhnikova et al., 2010; Che et
al. 2011), rivers (Sengi et al., 2008; Schwarzbauer and
Ricking 2010; Sang et al., 2012), marine organisms (Bulk
and Ford, 1999; Franke et al., 1999; Subedi et al., 2011;
Ramirez et al., 2009) and in air (Ramirez et al., 2010;
Kubwabo et al., 2012).
Earlier ecotoxicological and pharmaceutical studies
carried out on Gracilaria sp. include endogenic fatty acids
and exogenic petroleum products, butylated
hydroxytoluene, hexachloroethane from G. bursa-pastoris
(Güven et al., 2014), lipase released by substances obtained
from G. verrucosa (Aktin and Güven, 1969), β-
phenylethylamine (Percot et al., 2009), sterol glycoside
(Aydogmus et al., 2009), antiprotozoal and
antimycobacterial (Selcuk et al., 2011).
The Black Sea’ water circulation has two separate cycles;
west and east. The west part of the circulation starts from
the Ukrainian coasts down to Romania, Bulgaria and runs
through the western part of Turkey’s coasts including the
opening of the Bosphorus (Ovchinnikov, 1991). There are
two flows in Bosphorus; the upper flow (Black Sea water)
and under flow (Mediterranean Sea water) (Marsilii, 1681).
The amounts of these waters were calculated by Merz
(1918). Black Sea water circulation was determined in the
Bosphorus, the Sea of Marmara and the Dardanelles
(Vyazilov and Michailov, 1999). Danube River waters flows
into the Black Sea containing many pollutants from 17
countries. In addition, an accident occurred in Feb 2002 at
the gold mines of Baia, Romania, where approximately 83
million liters of cyanide ran off into the Tissa River