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