Journal of Hazardous Materials 170 (2009) 320–331
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Journal of Hazardous Materials
journal homepage: www.elsevier.com/locate/jhazmat
Development of site-specific sediment quality guidelines for North and
South Atlantic littoral zones: Comparison against national and
international sediment quality benchmarks
R.B. Choueri
a,b,∗
, A. Cesar
b
, D.M.S. Abessa
c
, R.J. Torres
d
, R.D. Morais
b
, I. Riba
a,e
,
C.D.S. Pereira
b,f
, M.R.L. Nascimento
g
, A.A. Mozeto
d
, T.A. DelValls
a
a
Cátedra UNESCO/UNITWIN/WiCop, Department of Physical Chemistry, Faculty of Marine and Environmental Sciences, University of Cádiz, CP 11510,
Puerto Real, Cádiz, Spain
b
Department of Ecotoxicology, Santa Cecília University, Oswaldo Cruz St, no. 266, 11045-907 Santos, SP, Brazil
c
São Paulo State University, Campus São Vicente, Infante Dom Henrique Plaza, s/n, 11330-900 São Vicente, SP, Brazil
d
Laboratório de Biogeoquímica Ambiental – DQ/UFSCar, Rod. Washington Luis km 235, CEP 13565-905, São Carlos, SP, Brazil
e
Institute of Marine Sciences of Andalucía, CSIC, Avda. Saharaui s/n, Campus Universitario de Puerto Real, 11510 Puerto Real, Cadiz, Spain
f
Laboratório de Ecotoxicologia Marinha, Instituto Oceanográfico, Universidade de São Paulo - Prac ¸a do Oceanográfico, 191 São Paulo, Brazil
g
CNEN, Laboratório de Poc ¸os de Caldas, Rod. Andradas km 13, Caixa Postal 913, CEP 3771-970 Poc ¸ os de Caldas, MG, Brazil
article info
Article history:
Received 10 December 2008
Received in revised form 13 March 2009
Accepted 21 April 2009
Available online 3 May 2009
Keywords:
Sediment quality guidelines
Multivariate analysis
Dredged material
Marine pollution
Estuary
abstract
We aimed to develop site-specific sediment quality guidelines (SQGs) for two estuarine and port zones
in Southeastern Brazil (Santos Estuarine System and Paranaguá Estuarine System) and three in Southern
Spain (Ría of Huelva, Bay of Cádiz, and Bay of Algeciras), and compare these values against national and
traditionally used international benchmark values. Site-specific SQGs were derived based on sediment
physical–chemical, toxicological, and benthic community data integrated through multivariate analysis.
This technique allowed the identification of chemicals of concern and the establishment of effects range
correlatively to individual concentrations of contaminants for each site of study. The results revealed
that sediments from Santos channel, as well as inner portions of the SES, are considered highly polluted
(exceeding SQGs-high) by metals, PAHs and PCBs. High pollution by PAHs and some metals was found
in São Vicente channel. In PES, sediments from inner portions (proximities of the Ponta do Félix port’s
terminal and the Port of Paranaguá) are highly polluted by metals and PAHs, including one zone inside
the limits of an environmental protection area. In Gulf of Cádiz, SQGs exceedences were found in Ria of
Huelva (all analysed metals and PAHs), in the surroundings of the Port of Cádiz (Bay of Cádiz) (metals),
and in Bay of Algeciras (Ni and PAHs). The site-specific SQGs derived in this study are more restricted than
national SQGs applied in Brazil and Spain, as well as international guidelines. This finding confirms the
importance of the development of site-specific SQGs to support the characterisation of sediments and
dredged material. The use of the same methodology to derive SQGs in Brazilian and Spanish port zones
confirmed the applicability of this technique with an international scope and provided a harmonised
methodology for site-specific SQGs derivation.
© 2009 Elsevier B.V. All rights reserved.
1. Introduction
Dredging activities can cause several negative impacts to the
aquatic ecosystems, such as the elimination of benthic habitats
and resuspension of nutrients and contaminants. Special concern
arises on the disposal of the dredged material; the simple discharge
in marine waters implies several environmental consequences,
∗
Corresponding author at: Department of Physical Chemistry, Faculty of Marine
and Environmental Sciences, University of Cadiz, Poligono Rio San Pedro, 11510
Puerto Real, Cadiz, Spain. Tel.: +34 956 01 67 64; fax: +34 956 01 60 40.
E-mail address: rodrigobrasilchoueri@yahoo.com.br (R.B. Choueri).
including physical disturbance (burrowing, smothering) of benthic
communities [1] and chemical contamination [2].
There are different options to deal with dredged material, which
include [3,4]: (i) beneficial uses—land creation and improvement,
beach nourishment, agricultural uses, wetlands restoration, cre-
ation of nesting islands, etc.; (ii) disposal in ocean or continental
waters; (iii) treatment, such as the separation of sediment contam-
inated fractions; and (iv) discharge into confined disposal facilities.
The selection of the best management option is in a great extent
dependent on the quality of the dredged material. Therefore, a reli-
able assessment of the sediments to be dredged is needed to assure
that the disposal of such material will be environmentally harmless
as well as cost-effective.
0304-3894/$ – see front matter © 2009 Elsevier B.V. All rights reserved.
doi:10.1016/j.jhazmat.2009.04.093