Menu:

 

 

Volume 11, Issue 1 - March 2011

 

Download (989KB, PDF)

 

 

  • Abstract / Resumo
  • References / Bibliografia
  • Citations / Citações

Revista de Gestão Costeira Integrada
Volume 11, Número 1, Março 2011, Páginas 31-39

DOI: 10.5894/rgci189
* Submissão – 27 Fevereiro 2010; Avaliação – 1 Setembro 2010; Recepção da versão revista – 21 Setembro 2010; Disponibilização on-line – 11 Fevereiro 2011

Variação sazonal, espacial e composicional de lixo ao longo das praias da margem oriental da Baía de Guanabara (Rio de Janeiro) no período de 1999-2008 *

Seasonal, spatial and compositional variation of beach debris along of the eastern margin of Guanabara Bay (Rio de Janeiro) in the period of 1999-2008

José Antônio Baptista Neto @, 1, Estefan Monteiro da Fonseca 1


@ Autor correspondente: José Antônio Baptista Neto, e-mail: jneto@igeo.uff.br
1 UFF- Universidade Federal Fluminense, Instituto de Geociências, Departamento de Geologia, LAGEMAR - Laboratório de Geologia Marinha, Av. General Milton Tavares de Souza, s/nº - 4º andar - Campus da Praia Vermelha, Gragoatá, Niterói, RJ, Brasil


RESUMO
A Baía de Guanabara é uma das maiores baías do litoral brasileiro. No entanto, é considerada um dos ambientes mais degradados do país. O desenvolvimento acelerado dos centros urbanos no entorno da Baía de Guanabara tem provocado vários impactos ambientais nos últimos 100 anos. O despejo de um grande volume de esgoto não tratado, diversos derrames acidentais de óleo nas suas águas, até o grande aporte de lixo através dos seus sistemas fluviais, provocam com isto o atual estágio de degradação ambiental da Baía. Durante os anos de 1999-2008, foram feitos levantamentos de campo para se quantificar e analisar a composição do lixo depositado em seis praias da orla oriental da Baía de Guanabara, através de transects, com medidas de 10 x 1 metros, ao longo do ponto máximo da maré alta, em três pontos de cada praia, nas extremidades do arco praial e na parte central. Os levantamentos foram feitos em duas estações do ano distintas, uma representando o período de chuva (verão) e uma no período seco (inverno). Um total de 21.841 itens foram catalogados ao longo dos dez anos de monitoramento, com uma média anual superior a 2.000 itens, sendo que deste total 14.505 itens foram catalogados no verão e 7.336 itens no inverno. Os itens mais abundantes catalogados nas praias analisadas foram: plástico (70,6%), material de construção (10%), vidro (8,1%), isopor (7,0%), papel (6,7%), lata (4,8%), madeira modificada (4,6%), tecidos (3,6%), metais diversos (3,2%), calçados (1,6%), restos de material de pesca (1,3%) e lâmpadas (1,1%). As praias mais poluídas da Baía são, em ordem decrescente: Brandoas, Pedrinhas, Boa Viagem, Luz, Charitas e São Francisco. No entanto, somente a praia do Brandoas representa 52% de todos os itens catalogados, fazendo com que esta praia seja tanto uma área de acumulação como fonte de lixo para as outras praias da Baía. Os resultados obtidos nestes levantamentos em relação a quantidade e composição do lixo depositado nas praias refletem fortemente as áreas fontes (rios), as práticas de limpeza por parte do poder público e a influência do transporte de lixo por correntes de maré. Um outro fator que tem grande influência na composição dos lixos encontrados nas praias é a flutuabilidade dos materiais. Como se sabe, materiais mais pesados tendem a permanecer próximos às áreas fontes. O tipo de lixo depositado nas praias da Baía de Guanabara é mais uma ameaça à fauna marinha, pelo fato dos mesmos representarem riscos aos animais deste habitat e também aos humanos. Os plásticos são, provavelmente, o mais perigoso por causa da ingestão devido tanto a ingestão quanto ao embaraçamento por parte dos animais.

Palavras-chave:Baía de Guanabara, poluição marinha, lixo em praias

ABSTRACT
Guanabara Bay is one of the largest bays on the Brazilian coastline and has an area of approximately 384 km2, including it islands, however, has been identified as one of the main polluted coastal environments on the Brazilian coastline. In the last 100 years the catchment area around Guanabara Bay has been strongly modified by human activities, in particular deforestation and uncontrolled settlement, which increased the amounts of contaminants introduced from sewage effluents, industrial discharge, urban and agricultural runoff, atmospheric fallout, and the combined inputs from the rivers. This study quantifies the distribution and composition of beach debris during surveys of beaches in the eastern margin of Guanabara Bay during the years of 1999-2008, field surveys was carried out using transects, all of the transects with the same measurement (10 X 1 meters), and it were set parallel to the water line and located on top of the high tide mark, in three stations of each beach, the extremities of the beach arc and in the central part of the beach, the surveys was carried out in two distinct seasons of the year, one representing the rainy period (summer) and one in the dry period (winter). Debris was categorized into 13 predetermined types of anthropogenic debris: plastic bag, plastic bottles, glass bottles, metal, paper, fishing material, modified wood, fabrics, footwear, construction material, light bulbs, cans and expanded polystyrene. A total of 21841 items were quantified on the Guanabara Bay beaches during the ten years of surveying, with an annual average of more then 2000 item. Temporal differences in the accumulation of debris were also assessed, a total of 14505 items were quantified in the summer and 7336 items in the winter, reflecting the increase capacity of the rivers in the debris transport during the rainy season (summer). Plastic comprised 70.6% of debris deposited in the Guanabara bay beaches, significantly higher than construction material, which was the second most abundant debris type at 10%, followed by glass (8.1%), expanded polystyrene (7.0%), paper (6.7%), cans (4.8%), modified wood (4.6%), fabrics (3.6%), diverse metals (3.2%), footwear (1.6%), remaining fishing material (1.3%) and light bulbs (1.1%). Comparisons, based on debris counts average across transects and areas, indicated that the Brandoas beach was the most contaminated site, followed by Pedrinhas, Boas Viagem, Luz, Charitas and São Francisco. However, 77% of all the catalogued items were counted in the São Gonçalo Municipality, and the Brandoas beach the most contaminated site, representing 52% of counted items, indicating that this beach was the main site for debris deposition, and it can also be source of debris for the other sites. Differently from others areas of the world where the debris has its origin in activities based in the ocean, such as ships, recreation and fishing. The abundance and distribution of debris through the Guanabara Bay beaches appears to be from local land-based or near shore sources, where the rivers represent the main source of debris, due to the use of the rivers by the municipally inhabitant to discard their garbage. The results gotten in these surveys in relation to the amount and composition of the debris deposited on beaches also reflect the cleanness practice by the municipality. One another factor that has great influence in the composition of the debris, found in beaches, is the buoyancy capacity of the materials, since the heaviest material tends to concentrate and remain closer to the source areas. Anthropogenic debris constitutes a significant threat to the marine environment, represent a hazard not only for the marine animals, but also for human activities, health and tourism.

Keywords: Guanabara Bay, marine pollution, beach debris.

 

Acha, E.M.; Mianzan, H.W.; Iribarne, O.; Gagliardini, D.A.; Lasta, C.; Daleo, P. (2003) - The role of the Rio de la Plata bottom salinity front in accumulating debris. Marine Pollution Bulletin, 46(2):197-202. DOI:10.1016/S0025-326X(02)00356-9.

Araújo, M.C.B.; Costa, M. (2004) - Análise quali-quantitativa do lixo deixado na Baía de Tamandaré-PE-Brasil, por excursionistas. Jornal de Gerenciamento Costeiro Integrado, 3:58–61.

Araújo, M.C.B.; Costa, M. (2007) - An analysis of the riverine contribution to the solid wastes contamination of an isolated beach at the Brazilian Northeast. Management of Environmental Quality, 18(1):6-12. DOI:10.1108/14777830710717677.

Arnould, J.P.Y.; Croxall, J.P. (1995) - Trends in the entanglement of Antarctic fur seals Arctocephalus gazella in man-made debris at South Georgia. Marine Pollution Bulletin, 30(11):707-712. DOI:10.1016/0025-326X(95)00054-Q.

Baptista Neto, J.A.; Gingele, F.X.; Leipe, T.; Brehme, I. (2006) - Spatial distribution of trace elements in surficial sediments from Guanabara Bay - Rio de Janeiro/Brazil. Environmental Geology. 49(7):1051-1063.
DOI:10.1007/s00254-005-0149-1.

Baptista Neto, J.A.; Smith, B.J.; McAlister, J.J., (1999) - Sedimentological evidence of human impact on a nearshore environment: Jurujuba Sound, Rio de Janeiro State, Brazil. Applied Geography, 19(2):153-177. DOI:10.1016/S0143-6228(98)00041-1.

Benton, T.G. (1995) - From castaways to throwaways: marine litter in the Pitcairn Island. Biological Journal of the Linnean Society, 56(1-2):415-422. DOI:10.1111/j.1095-8312.1995.tb01101.x

Bravo, M.; Gallardo, M.A.; Jonquera, G.L.; Núñez, P.; Vásquez, N.; Thiel, M. (2009) - Anthropogenic debris on beaches in the SE Pacific (Chile): Results from a national survey supported by volunteers. Marine Pollution Bulletin, 58(11):1718–1726. DOI:10.1016/j.marpolbul.2009.06.017.

Carpenter, E.J.; Smith, K.L. (1972) - Plastic on the Sargasso Sea surface. Science, 175(#4027):1240-1241. DOI:10.1126/science.175.4027.1240.

Carr, A. (1987) - The impact of nondegradable marine debris on the ecology and survival outlook of sea turtles. Marine Pollution Bulletin, 18(6B):352-356. DOI:10.1016/S0025-326X(87)80025-5.

Coe, J.M.; Rogers, D.B. (eds.) (1997) - Marine Debris: Sources, Impacts, and Solutions. 432p., Springer-Verlag, New York, NY, USA. ISBN: 9780387947594.

Colton, J.B.; Knapp, F.D.; Burns, B.R. (1974) - Plastic particles in the surface water of the northwestern Atlantic. Science, 185(4150):491-497. DOI:10.1126/science.185.4150.491.

Day, R.H.; Shaw, D.G. (1987) - Patterns in the abundance of pelagic plastic and tar in the north pacific ocean, 1976–1985. Marine Pollution Bulletin, 18(6):311-316. DOI:10.1016/S0025-326X(87)80017-6.

Derraik, J.G.B. (2002) - The pollution of the marine environment by plastic debris: a review. Marine Pollution Bulletin, 44(9):842-852. DOI:10.1016/S0025-326X(02)00220-5.

FEEMA - Fundação Estadual de Engenharia do Meio Ambiente (1990) - Projeto de Recuperação Gradual do Ecossistema da Baía de Guanabara, indicadores ambientais de degradação, obras e projetos de recuperação. 1:152–160, Fundação Estadual de Engenharia do Meio Ambiente, Governo do Estado do Rio de Janeiro, Secretaria de Estado de Meio Ambiente, Rio de Janeiro, RJ, Brasil.

Fowler, C.W. (1987) - Marine debris and northern fur seals: a case study. Marine Pollution Bulletin, 18(6B):326-335. DOI:10.1016/S0025-326X(87)80020-6.

Galgani, F.; Leaute, J.P.; Moguedet, P.; Souplet, A.; Verin, Y.; Carpentier, A.; Goraguer, H.; Latrouite, D.; Andral, B.; Cadiou, Y.; Mahe, J.C.; Poulard, J.C.; Nerisson, P. (2000) - Litter on the Sea Floor along European Coasts. Marine Pollution Bulletin, 40(6):516-527. DOI:10.1016/S0025-326X(99)00234-9.

Gilligan, M.R.; Pitts, S.; Richardson, P.J.; Kozel, T.R. (1992) - Rates of accumulation of marine debris in Chatham County, Georgia. Marine Pollution Bulletin, 24(9):436-441. DOI:10.1016/0025-326X(92)90342-4.

Goldberg, E. (1997) - Plasticizing the seafloor: an overview. Environmental Technology, 18(2):195-202.
DOI:10.1080/09593331808616527.

Gregory, M.R.; Ryan, P.G. (1997) - Pelagic Plastics and other seaborne persistent synthetic debris: a review of Southern Hemisphere perspectives. In: Coe, J. & Rogers, D. (eds.), Marine Debris: Sources, impacts and solutions. pp.49-66. Springer-Verlag, New York, NY, USA.
ISBN: 9780387947594.

Hansen, J. (1990) - Draft position statement on plastic debris in marine environments. Fisheries, 15:16-17.

Ivar do Sul, J.A.; Costa, M. (2007) - Marine debris review for Latin America and the Wider Caribbean Region: from the 1970s until now, and where do we go from here. Marine Pollution Bulletin, 54(8):1087-1104. DOI:10.1016/j.marpolbul.2007.05.004.

Ivar do Sul, J.A.; Spengler, A.; Costa, M.F. (2009) - Here, there and everywhere. Small plastic fragments and pellets on beaches of Fernando de Noronha (Equatorial Western Atlantic). Marine Pollution Bulletin, 58(89:1236-1238. DOI:10.1016/j.marpolbul.2009.05.004.

Jones, M.M. (1995) - Fishing debris in the Australian marine environment. Marine Pollution Bulletin, 30(1):25-33. DOI:10.1016/0025-326X(94)00108-L.

Kehrig, H.A.; Pinto, F.; Moreira, I.; Malm, O. (2003) - Heavy metals and methylmercury in a tropical coastal estuary and a mangrove in Brazil. Organic Geochemistry, 34(5):661-669. DOI:10.1016/S0146-6380(03)00021-4.

Kierfvre, B.; Ribeiro, C.H.; Dias, G.T.M.; Filippo, M; Quaresma, V.S. (1996) - Oceanographic characteristics of an impacted coastal bay: Baía de Guanabara, Rio de Janeiro, Brazil. Continental Shelf Research, 17(13):1609-1643. DOI:10.1016/S0278-4343(97)00028-9.

Laist, D.W. (1987) - Overview of the biological effects of lost and discarded plastic debris in the marine environment. Marine Pollution Bulletin, 18(6B):319-326. DOI:10.1016/S0025-326X(87)80019-X.

Leal, M.; Wagener, A. (1993) - Remobilization of anthropogenic copper deposited in sediments of a tropical estuary. Chemical speciation and bioavailability, 24(1):31-39.

Madzena, A.; Lasiak, T., (1997) - Spatial and Temporal Variations in Beach Litter on the Trankei Coast of South Africa. Marine Pollution Bulletin, 34(11):900-907. DOI:10.1016/S0025-326X(97)00052-0.

Mascarenhas, R.; Batista, C.P.; Moura, I.F.; Caldas, A.R.; Costa Neto, J.M.; Vasconcelos, M.Q.; Rosa, S.S.; Barros, T.V.S. (2008) - Lixo marinho em áreas de reprodução de tartarugas marinhas no Estado da Paraíba (Nordeste do Brasil). Revista da Gestão Costeira Integrada, 8(2):221-231. http://www.aprh.pt/rgci/pdf/RGCI-138_Mascarenhas.pdf

Michel, J. (2000) - Assessment and Recommendations for the Oil Spill Cleanup of Guanabara Bay, Brazil. Spill Science & Technology Bulletin, 6(1):89-96. DOI:10.1016/S1353-2561(00)00056-6.

Moore, S.L.; Allen, M.J. (2000) - Distribuition of Antropogenic and Natural Debris on the Mainland Shelf of the Southern California Bight. Marine Pollution Bulletin, 40(1):83-88. DOI:10.1016/S0025-326X(99)00175-7.

Morishige, C.; Donohue, M.J.; Flint, E.; Swenson, C.; Woolaway, C. (2007) - Factors affecting marine debris deposition at French Frigate Shoals, Northwestern Hawaiian Island Marine National Monument, 1990-2006. Marine Pollution Bulletin, 54(8):1162-1169. DOI:10.1016/j.marpolbul.2007.04.014.

Perin, G.F.R.; Manente, S.; Rebello, A.H.; Hamacher, C.; Scotto, S. (1997) - A five-year study on the heavy-metal pollution of Guanabara Bay sediments (Rio de Janeiro, Brazil) and evaluation of the metal bioavailability by means of geochemical. Water Research, 31(12):3017-3028. DOI:10.1016/S0043-1354(97)00171-1.

Pruter, A.T. (1987) - Sources, quantities and distribuition of persistent plastics in the marine environment. Marine Pollution Bulletin, 18(6B):305-310. DOI:10.1016/S0025-326X(87)80016-4.

Quaresma, V.S.; Dias, G.T.M.; Baptista Neto, J.A. (2000) - Caracterização de padrões de sonar de varredura lateral e 3,5 e 7,0 kHz na porção sul da Baía de Guanabara - RJ. Revista Brasileira de Geofísica, 18(2):201-214. http://www.scielo.br/pdf/rbg/v18n2/8829.pdf

Rebello, A.; Haekel, W.; Moreira, I.; Santelli, R.; Schroeder, F. (1986) - The fate of heavy metals in an estuarine tropical system. Marine Chemistry, 18(2-4):215-225. DOI:10.1016/0304-4203(86)90009-5.

Ryan, P. (1987) - The origin and fate of artifacts stranded on islands in the African sector of the Southern Ocean. Environmental Conservation, 14(4):341-346. DOI:10.1017/S0376892900016854.

Ryan, P.G.; Moloney, C.L. (1991) - Prey selection and temporal variation in the diet of Subantarctic Skuas at Inaccessible Island, Tristan da Cunha. Ostrich, 62(1-2):52-58. DOI:10.1080/00306525.1991.9639641.

Santos, I.R.; Friedrich, A.C.; Wallner-Kersanach, M.; Fillmann, G.; Shiller, R.V.; Costa, R. (2003) - Geração de resíduos sólidos pelos usuários da praia do Cassino, RS, Brasil. Revista de Gestão Costeira Integrada, 3: 12–14.

Santos. I.R.; Friedrich, A.C.; Barretto, F.P. (2005) - Overseas garbage pollution on beaches of Northeast Brazil. Marine Pollution Bulletin, 50(7):783-786. DOI:10.1016/j.marpolbul.2005.04.044.

Santos. I.R.; Friedrich, A.C.; Ivar do Sul, J.A. (2009) - Marine debris contamination along undeveloped tropical beaches from Northeast Brazil. Environmental Monitoring and Assessment, 148(1-4):455-462. DOI:10.1007/s10661-008-0175-z.

Shaw, D. (1977) - Pelagic tar and plastic in the Gulf of Alaska and Bering Sea: 1975. Science of the Total Environment, 8(1):13-20. DOI:10.1016/0048-9697(77)90058-4.

Shaw, D.; Mapes, G. (1979) - Surface circulation and the distribution of pelagic tar and plastic. Marine Pollution Bulletin, 10(69:160-162. DOI:10.1016/0025-326X(79)90421-1.

Silva, J.S.; Araújo, M.C.B.; Costa, M.F. (2009) - Plastic litter on an urban beach - a case study in Brazil. Waste Management & Research, 27: 93-97. DOI:10.1177/0734242X08088705.

Spengler, A.; Costa, M. (2008) - Methods Applied in Studies of Benthic Marine Debris. Marine Pollution Bulletin, 56(2):226-230. DOI:10.1016/j.marpolbul.2007.09.040.

Thiel, M.; Hinojosa, I.; Vásquez, N.; Macaya, E. (2003) - Floating marine debris in coastal waters of the SE-Pacific (Chile). Marine Pollution Bulletin, 46(2):224-231. DOI:10.1016/S0025-326X(02)00365-X.

Velander, K.A. & Mocogni, M. (1998) - Maritime litter and sewage contamination at Cramond Beach, Edimburgh – a compartative study. Marine Pollution Bulletin, 36(5):385-389. DOI:10.1016/S0025-326X(97)00204-X.

Willoughby, N.G. (1986) - Man-made Litter on the Shores of the Thousand Island Archipelago, Java. Marine Pollution Bulletin, 17(5):224-228. DOI:10.1016/0025-326X(86)90605-3.

Willoughby, N.G.; Sanfgkoyo, H.; Lakaseru, B. (1997) - Beach litter: an increasing and changing problem for Indonesia. Marine Pollution Bulletin, 34(6):469-478. DOI:10.1016/S0025-326X(96)00141-5.

 

em construção