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Reconstruction of mercury pollution trends in Cartagena Bay (Colombia) with high temporal resolution Regional Project RLA/7/012 Use of Nuclear Techniques to Address the Management Problems of coastal zones in the Caribbean Region J.A.


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Regional Project RLA/7/012 “Use of Nuclear Techniques to Address the Management Problems of coastal zones in the Caribbean Region”

Reconstruction of mercury pollution trends in Cartagena Bay (Colombia) with high temporal resolution

J.A. Sanchez-Cabeza, J. Garay-Tinoco, J. Betancourt, J.P. Parra, L. Espinosa, C.M. Alonso-Hernández, Y. Bolaños- Alvarez, A.J. Quejido, M. Fernandez-Garcia, A.C. Ruiz- Fernandez

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Introduction

latitude: 10º26’ - 10º16’ N longitude: 75º30’ - 75º36’ W Depth 16 m to 26 m. Dimensions: 14.4 x 6.4 km Surface: 82 km2

Bocagrande Bocachica

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Cartagena is an area of great interest to Colombia, as many activities are present:

  • Tourism
  • Artisanal fisheries
  • Industries
  • Port services

Introduction

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The Dique Canal is in the southern part of the bay. It discharges 100-1000 m3/sec of fresh water to the bay, giving the water body the characteristics of an estuary.

Introduction

Cartagena Bay receives approximately 80,000 m3/sec of urban wastewater from the city which has a current population of 1.000.000 inhabitants.

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Cartagena Bay is one of the most studied water bodies in Colombia. Studies on heavy metal pollution began in the late 1970s when mercury (Hg) pollution became evident in the bay due to the operation of a Chlor- Alkali plant which discharged Hg residues to the sea. Studies show that the main metal pollution sources were the industrial zone of Mamonal and the Dique Canal. Research on the accumulation of Hg in humans and species used for human consumption concluded that even though the current Hg levels in the bay have diminished drastically, the metal is still bioavailable and can thus enter the food web and eventually reach the human population.

Introduction

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C E D

Methods

Sampling stations: (C) the southern part of the Bay (D) across from the island “Tierra Bomba” (E) across from the old Chlor-Alkali Plant Three sediment cores (<65 cm) were collected with an UWITEC corer:

1.radionuclide, geochemical, and heavy metal analyses. 2.organic contaminants 3.a reference sample

The cores were sectioned at 1 cm intervals.

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Based on Loss On Ignition (LOI) in UNAM (Mexico), site E (Chlor-Alkali Plant) was chosen as the most reliable for dating.

Methods

Total Hg analyses were performed at the CEAC laboratory (Cuba), with a mercury DMA-80 analyzer.

210Pb, 226Ra, and 137Cs were analysed

at CEAC (Cuba), using gamma and alpha spectrometry.

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The 210Pb profile was incomplete. The CFCS model was used for dating. The sedimentation rate was 1.8 cm/y. An increase in the sedimentation rate in recent years was evident. This can be related to land use change and climatic events affecting the Dique Canal watershed, which is the major source of sediments discharged to Cartagena Bay.

10 20 30 40 50 60 70 10 20 30 Depht (cm)

210Pb ex Bq.kg-1

0,0 0,5 1,0 1,5 2,0 2,5 3,0 3,5 1970 1980 1990 2000 2010

SAR (cm.y-1) Year

Results

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Distribution of Hg in the sediment profile of the Cartagena Bay At a depth of 61 cm, a maximum value of 18.8 µg/g is observed, well above the benchmark value of 0.7 µg/g proposed by NOAA as a level indicative of risk.

Results

2 4 6 8 10 12 14 16 18 20 5 10 15 20 25 30 35 40 45 50 55 60 65 70

Hg concentration µg/ g Depth (cm)

Above 60 cm, concentrations begin to decrease, until they reach 0.3 µg/g at the surface..

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When using the dating model, the profile shows that the main input of mercury occurred in the 1970s, in coincidence with one of the major environmental problems impacting Cartagena Bay: the discharge of mercury due to the industrial activities of Colombia’s Alkali company.

Results

0,0 2,0 4,0 6,0 8,0 10,0 12,0 14,0 16,0 18,0 20,0 1972 1976 1980 1984 1988 1992 1996 2000 2004 2008 2012

Hg (µg/g) Year

This factory began activities in March 1967 and continued

  • peration until

1978, when it was closed due to pollution problems.

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We concluded that Hg pollution still persists in Cartagena Bay and that high concentrations continue to be present, accumulated in the deeper sediment layers. Hg can become resuspended by the mobilization of sediment, through activities such as dredging, emphasizing the need and importance of heavy metal pollution control in Cartagena Bay.

Conclusions

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Thank you for your attention Contact: lespinosa@invemar.org.co