Journal articles on the topic 'Coastal waters'

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1

Gan, Jay. "Clean Coastal Waters." Journal of Environment Quality 31, no. 1 (2002): 363. http://dx.doi.org/10.2134/jeq2002.0363.

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2

Gan, Jay. "Clean Coastal Waters." Journal of Environmental Quality 31, no. 1 (January 2002): 363–64. http://dx.doi.org/10.2134/jeq2002.3630.

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3

Samuelson, William F. "Dividing Coastal Waters." Journal of Conflict Resolution 29, no. 1 (March 1985): 83–111. http://dx.doi.org/10.1177/0022002785029001005.

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4

Stalcup, Dana, Gary Yoshioka, Ellen Mantus, and Brad Kaiman. "CHARACTERISTICS OF OIL SPILLS: INLAND VERSUS COASTAL." International Oil Spill Conference Proceedings 1997, no. 1 (April 1, 1997): 939–40. http://dx.doi.org/10.7901/2169-3358-1997-1-939.

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ABSTRACT The Emergency Response Notification System database was searched for information on the size of spills, the sources of spills, and the types of oils spilled for both inland and coastal waters. The results of this analysis indicate that the vast majority of spills for both inland and coastal waters are minor discharges, that the sources of the spills differ for inland versus coastal waters, with pipelines representing a minor source for both water systems, and that a wide variety of materials are spilled in both inland and coastal water systems, with crude oil being a more significant contributor for coastal waters.
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5

Mouw, Colleen, and Steven Greb. "Inland and coastal waters." Eos, Transactions American Geophysical Union 93, no. 39 (September 25, 2012): 375. http://dx.doi.org/10.1029/2012eo390006.

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6

Palca, Joseph. "Coastal waters in jeopardy." Nature 327, no. 6117 (May 1987): 9. http://dx.doi.org/10.1038/327009a0.

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7

Showstack, Randy. "U.S. coastal waters graded." Eos, Transactions American Geophysical Union 83, no. 16 (2002): 174. http://dx.doi.org/10.1029/eo083i016p00174-04.

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8

Schnoor, Jerald L. "Coastal waters need action." Environmental Science & Technology 39, no. 3 (February 2005): 55A. http://dx.doi.org/10.1021/es053176f.

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9

Abe, Sho. "Water quality conservation of enclosed coastal waters." Japan journal of water pollution research 13, no. 4 (1990): 202–6. http://dx.doi.org/10.2965/jswe1978.13.202.

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10

Hooker, Stanford B., Giuseppe Zibordi, Jean-François Berthon, and James W. Brown. "Above-water radiometry in shallow coastal waters." Applied Optics 43, no. 21 (July 20, 2004): 4254. http://dx.doi.org/10.1364/ao.43.004254.

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11

Jozić, Slaven, Vanja Baljak, Arijana Cenov, Dražen Lušić, Dominik Galić, Marin Glad, Daniel Maestro, et al. "Inland and Coastal Bathing Water Quality in the Last Decade (2011–2020): Croatia vs. Region vs. EU." Water 13, no. 17 (September 5, 2021): 2440. http://dx.doi.org/10.3390/w13172440.

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Europe is one of the leading tourist destinations where tourism is one of the key economic sectors. The quality of bathing waters is a very important factor when choosing a vacation destination. Croatia recognized this early and was one of the first Mediterranean countries to start systematic monitoring of bathing waters. On the other hand, monitoring of inland bathing waters is relatively new and includes a much smaller number of sites (41) compared to coastal waters (894). The aim of this paper was to summarize and analyze the water quality of inland and coastal bathing sites of Croatia, closer regions (non-EU Member States) and in the EU for the last decade. The share of excellent water quality in EU Member States increased by 10.1% and 6.6% for inland and coastal waters, respectively (2011–2020). Germany recorded the highest proportion of excellent water quality for inland waters (92.2%) and Cyprus for coastal waters (99.3%). Looking at the 10-year average of the proportion of bathing waters with excellent quality, the proportion of coastal bathing sites exceeds that of inland waters by 7.1%. It is clear that additional efforts should be made to improve the management and monitoring of inland waters.
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12

Boikova, Elmīra, Uldis Botva, and Vita Līcīte. "Implementation of Trophic Status Index in Brackish Water Quality Assessment of Baltic Coastal Waters." Proceedings of the Latvian Academy of Sciences. Section B. Natural, Exact, and Applied Sciences. 62, no. 3 (January 1, 2008): 115–19. http://dx.doi.org/10.2478/v10046-008-0016-z.

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Implementation of Trophic Status Index in Brackish Water Quality Assessment of Baltic Coastal Waters The assessment of the trophic state of marine coastal waters is one of the leading initiatives declared in the European Water Framework Directive (WFD). The Baltic Sea is a semi-enclosed ecosystem which consists of subregions with wide salinity and seasonality gradients. Anthropogenic impact results in eutrophication processes on different scales. Efficient eutrophication control and environmental management in the Baltic Sea, according to WFD, requires a prerequisite of common and sensitive indicators for the European coastal waters including the Baltic Sea. In this article the Trophic Status Index TRIX, recently succcesfully implemented in Mediterranean and Northern European sea coastal waters as a holistic approach indicator, was implemented for the Gulf of Rīga and Latvian Baltic Sea coastal water quality assessment between 1999 and 2005.
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13

Hughes, M. S., P. V. Coyle, and J. H. Connolly. "Enteroviruses in recreational waters of Northern Ireland." Epidemiology and Infection 108, no. 3 (June 1992): 529–36. http://dx.doi.org/10.1017/s0950268800050020.

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SUMMARYVirus surveillance of Northern Ireland recreational waters, between April 1986 and May 1989 demonstrated widespread enteroviral contamination of coastal and inland waters. In 1986, enteroviruses were detected in 4 of 46 (8·7%) water samples, collected from 6 coastal bathing waters. In 1987, 49 of 107 (45·8%) samples, from 16 coastal bathing waters, yielded enteroviruses; 33 of the enterovirus positive samples passed one or both of the coliform standards outlined by the European Economic Community (EEC) bathing water directive (76/160/EEC). Enteroviruses were also detected in 33 of 39 (84·6%) samples tested from 3 inland recreational waters.
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14

Lestari, Febrianti. "Nutrient distribution models and flow patterns in Coastal Waters and Small Islands, Tanjungpinang City, Indonesia." Akuatikisle: Jurnal Akuakultur, Pesisir dan Pulau-Pulau Kecil 4, no. 1 (May 31, 2020): 36. http://dx.doi.org/10.29239/j.akuatikisle.4.1.36-40.

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Research has been done on the model of nutrient distribution and current pattern in coastal water of Tanjungpinang City. The research objective was to develop a model of nutrient distribution and current patterns in coastal waters and small islands as an effort to manage the eutofication of coastal waters and small islands in the archipelago. Determining the location of the observations was done by purposive sampling at high tide and low tide at several predetermined research stations. The results showed the nutrient distribution model in the waters of Tanjungpinang Bay, a different distribution pattern compared to the waters of the Dompak Strait, with the distribution of nutrients from the yield model at low tide and at high tide shows the same pattern, which tends to decrease offshore and high in some coastal locations. around the waters of the Sei. Carang estuary which is connected to the waters of Tanjungpinang Bay. The pattern of currents during the highest tide is bandage and full moon in coastal waters and small islands in the area of Tanjungpinang City, which shows that the inlet flows from the west of the waters, then exits towards the north into open water. However, part of the water mass in the presence of small islands around it becomes fragmented causing a turn to the south of the coastal waters of the city of Tanjungpinang, with a maximum current speed of 1.1 m/s.
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15

Alipour, Majid, Reza Hajiesmaili, Maryam Talebjannat, and Yousef Yahyapour. "Identification and Antimicrobial Resistance ofEnterococcusSpp. Isolated from the River and Coastal Waters in Northern Iran." Scientific World Journal 2014 (2014): 1–5. http://dx.doi.org/10.1155/2014/287458.

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As fecal streptococci commonly inhabit the intestinal tract of humans and warm blooded animals, and daily detection of all pathogenic bacteria in coastal water is not practical, thus these bacteria are used to detect the fecal contamination of water. The present study examined the presence and the antibiotic resistance patterns ofEnterococcusspp. isolated from the Babolrud River in Babol and coastal waters in Babolsar. Seventy samples of water were collected in various regions of the Babolrud and coastal waters. Isolated bacteria were identified to the species level using standard biochemical tests and PCR technique. In total, 70Enterococcusspp. were isolated from the Babolrud River and coastal waters of Babolsar.Enterococcus faecalis(68.6%) andEnterococcus faecium(20%) were the most prevalent species. Resistance to chloramphenicol, ciprofloxacin, and tetracyclin was prevalent. The presence of resistantEnterococcusspp. in coastal waters may transmit resistant genes to other bacteria; therefore, swimming in such environments is not suitable.
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16

Sobsey, M. D., R. Perdue, M. Overton, and J. Fisher. "Factors influencing faecal contamination in coastal marinas." Water Science and Technology 47, no. 3 (February 1, 2003): 199–204. http://dx.doi.org/10.2166/wst.2003.0195.

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Recreational pleasure and fishing boats are potential sources of human faecal contamination because the sanitary wastes from boat occupants may be discharged into the surrounding water. The impacts of such faecal contamination from boats is potentially high in marinas where boats are often kept and occupied for varying periods of time. The nature and extent of such faecal contamination from boats in marinas of different design and use is still inadequately understood. In this study the levels of faecal coliform (FC) bacteria were measured in the waters of a confined and an open water marina over a 6 d period encompassing a holiday weekend. Levels of FC rose with increasing occupancy by boats and boaters during the study period and then declined again. FC levels were higher in waters of a confined or basin marina than in waters of an open or unconfined marina. In both confined and open water marinas, FC levels were highest in water samples collected near boats but they also became elevated on occasion in water samples taken a distance of 305 m from boats. Concentrations of FC in marina waters exceeded the standards and guidelines for shell-fishing and primary contact recreation waters. Therefore, greater consideration of human health risks from enteric microbes in marina waters and shellfish is recommended.
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17

Ashok kumar, N., V. Arutchelvan, and P. Chandramohan. "Horizontal Diffusion in Shallow Coastal Waters of Tamil Nadu." International Journal of Engineering and Technology 3, no. 6 (2011): 634–37. http://dx.doi.org/10.7763/ijet.2011.v3.297.

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18

Ivanov, V. A., A. S. Kuznetsov, and A. N. Morozov. "Monitoring the circulation of coastal waters off the Southern coast of Crimea." Доклады Академии наук 485, no. 4 (May 22, 2019): 507–10. http://dx.doi.org/10.31857/s0869-56524854507-510.

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The paper presents the results of integrated monitoring of water dynamics in the coastal zone off the Southern coast of the Crimea for 2008-2016. The regime and features of circulation of coastal waters were determined. An intensive contribution of low-frequency oscillations of coastal currents at the seasonal and synoptic scales was identified based on the results of spectral analysis of a nine-year set of vector dynamics series. For water fluctuations in the coastal zone, the alongshore structure of reciprocating jet streams caused by water dynamics at the shelf and continental slope dominates.
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19

Rabalais, Nancy N., R. Eugene Turner, Robert J. Díaz, and Dubravko Justić. "Global change and eutrophication of coastal waters." ICES Journal of Marine Science 66, no. 7 (March 28, 2009): 1528–37. http://dx.doi.org/10.1093/icesjms/fsp047.

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Abstract Rabalais, N. N., Turner, R. E., Díaz, R. J., and Justić, D. 2009. Global change and eutrophication of coastal waters. – ICES Journal of Marine Science, 66: 1528–1537. The cumulative effects of global change, including climate change, increased population, and more intense industrialization and agribusiness, will likely continue and intensify the course of eutrophication in estuarine and coastal waters. As a result, the symptoms of eutrophication, such as noxious and harmful algal blooms, reduced water quality, loss of habitat and natural resources, and severity of hypoxia (oxygen depletion) and its extent in estuaries and coastal waters will increase. Global climate changes will likely result in higher water temperatures, stronger stratification, and increased inflows of freshwater and nutrients to coastal waters in many areas of the globe. Both past experience and model forecasts suggest that these changes will result in enhanced primary production, higher phytoplankton and macroalgal standing stocks, and more frequent or severe hypoxia. The negative consequences of increased nutrient loading and stratification may be partly, but only temporarily, compensated by stronger or more frequent tropical storm activity in low and mid-latitudes. In anticipation of the negative effects of global change, nutrient loadings to coastal waters need to be reduced now, so that further water quality degradation is prevented.
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20

Muqsith, Abdul, Nuddin Harahab, Mohammad Mahmudi, and Muhammad Fadjar. "ESTIMATION OF COASTAL ASIMILATION CAPACITY BASED ON STANDARD EFFLUENT WASTE NITROGEN AND PHOSFORUS OF SHRIMP CULTIVATION." Samakia : Jurnal Ilmu Perikanan 9, no. 2 (October 29, 2018): 81–87. http://dx.doi.org/10.35316/jsapi.v9i2.229.

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This research was conducted in May 2018 in the coastal area of ​​Banyuputih Subdistrict, Situbondo Regency, East Java with the aim of estimating the volume of seawater available in coastal waters and the capacity of coastal waters in assimilating N and P waste load based on N and P effluent standards for cultivation shrimp. The results showed that the coastal waters of Banyuputih had a volume of water available for dilution of N and P wastes of 43,198,298 m3. The maximum N and P waste load that can be assimilated by water according to the standard effluent of N waste for shrimp farming is 172, 8 tons and for the P waste load is 17.28 tons. The results of this study can be used as a reference in determining the environmental carrying capacity of coastal waters in the development of intensive shrimp ponds in the study area.
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21

Sulistiono, Sulistiono, Dudi Muhamad Wildan, Ayu Ervinia, Nur Rohim, Dimas Angga Hedianto, Faqih Baihaqi, Didit Abdillah, I. Nyoman Yoga Parawangsa, Gema Wahyudewantoro, and Masashi Yokota. "Diversity, distribution, and species status of the fish in Banten Bay, Indonesia." E3S Web of Conferences 339 (2022): 03003. http://dx.doi.org/10.1051/e3sconf/202233903003.

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This study aims to analyze the species diversity, distribution and status of fish found in the coastal waters of Banten Bay. Samplings were carried out 7 times at three locations namely Cengkok coastal waters (on February-March 2019), Bojonegara coastal waters (January-February, August-September 2020), and Kemayungan-Linduk coastal waters (February-April 2021) of the Banten Bay, using gill nets, trammel net, cast net, hand-line, beach seine, and mini trawl. Results of this study showed that the fish caught in the Banten Bay coastal waters consisted of 111 species, distributed at the three areas, namely Cengkok (32 species), Bojonegara (58 species), and Kemayungan-Linduk coastal waters (51 species). The diversity, eveness, and dominance indices were 2.185 - 3.763, 0.630 - 0.781, and 0.072 - 0.233 respectively, indicating the medium-high species diversity. These fish were spreading in marine water, fresh water, estuary, freshwater and estuary, marine and estuary, and marine, estuary and freshwater. The common species found at the study location were Ellochelon vaigiensis, Planiliza subviridis, and Leiognathus equula. In general, most of the fish found in Banten Bay were classified as least concern (LC), while two species were vulnerable (VU), one species was near threatened (NT), and ones species was endangered species (EN).
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22

van Soest, Rob W. M., Mario J. de Kluijver, Peter H. van Bragt, Marco Faasse, Reindert Nijland, Elly J. Beglinger, Wallie H. de Weerdt, and Nicole J. de Voogd. "Sponge invaders in Dutch coastal waters." Journal of the Marine Biological Association of the United Kingdom 87, no. 6 (December 2007): 1733–48. http://dx.doi.org/10.1017/s002531540705816x.

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Continuous monitoring by scientists and volunteers of the Biological Working Group of the Dutch SubAqua Union and the ‘Anemoon’ Foundation over the past four years, yielded a surprising six new records of sponges for Dutch coastal waters. Oscarella lobularis, Celtodoryx girardae, Suberites virgultosus, Haliclona (Haliclona) simulans, Halisarca aff. dujardini, and a species identified as Leucosolenia somesii were unknown from Dutch coastal waters before 2000. The latter is a giant calcareous sponge, seemingly belonging to the common Leucosolenia variabilis, but here assumed to be an invader as well, as it has spicular characters well outside the variation found in the majority of Dutch L. variabilis specimens. It is likely a member of a ‘forgotten’ species, L. somesii. Habit photographs, SEM images of the spicules, and for O. lobularis and H. aff. dujardini, photographs of histological sections are provided to substantiate these new records. With the exception of C. girardae, most of the species resemble previously described widespread north-east Atlantic species, occurring in the area to the south and west of the Netherlands, so it is assumed pending future genetic research that at least several of the invaders comprise range extensions related to rising winter temperatures. Possibly, recent shellfish imports may be an additional causal agent. We also report the occurrence of unprecedented spicular deviations observed in three sponge species commonly occurring in Dutch waters, Halichondria (Halichondria) panicea, Hymeniacidon perlevis and Haliclona (Soestella) xena, which grew in small inland water bodies. Possibly, the limited space in these inland waters with possible stress factors for sponges such as reduced water exchange, and deviating chemistry, have caused the sponges to form stunted growth in spicules varying from rhabds with rounded endings to silica spheroids. We provide an updated list of sponges found in Dutch waters and a list of suspected or proven invaders of Dutch waters.
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23

Kim, Hyun-Suk, Eunkyu Lee, Eui-Jong Lee, Jin-Won Hyun, In-Young Gong, Kyungsup Kim, and Yun-Sok Lee. "A Study on Grid-Cell-Type Maritime Traffic Distribution Analysis Based on AIS Data for Establishing a Coastal Maritime Transportation Network." Journal of Marine Science and Engineering 11, no. 2 (February 5, 2023): 354. http://dx.doi.org/10.3390/jmse11020354.

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Recently, marine development plans such as offshore wind farms and marina port facilities have been established to use Korean coastal waters, and research on the development of operational ships such as autonomous ships and water-surface flying ships is being rapidly promoted. Since the marine traffic in Korean coastal waters is expected to increase, the government intends to construct a coastal maritime transportation network that connects Korean coastal waters to guarantee safe ship navigation. Therefore, this study used automatic-identification-system data analysis to obtain quantitative evaluation results on maritime traffic distribution characteristics and utilization levels for the entire Korean coastal waters in grid cell for greater consistency and compatibility. The characteristics of marine traffic distribution at a certain site in coastal Korean waters can be quantitatively examined using the findings of this study, and they may be used as grid-cell-type data-based information. Moreover, the vessel traffic index allows for extensive research while quickly understanding the present level of use of the passing ships by the sea area. In this regard, the findings of this study are expected to be useful for the future development of maritime transportation networks in Korean coastal waters.
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24

Panda, Uma Sankar, Uma Kanta Pradhan, Saka Sujith Kumar, Subrat Naik, Mehmuna Begum, Pravakar Mishra, and Mallavarapu Venkata Ramana Murthy. "Bathing Water Quality Forecast for Chennai Coastal Waters." Journal of Coastal Research 89, sp1 (June 1, 2020): 111. http://dx.doi.org/10.2112/si89-019.1.

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25

Trombetta, Thomas, Francesca Vidussi, Sébastien Mas, David Parin, Monique Simier, and Behzad Mostajir. "Water temperature drives phytoplankton blooms in coastal waters." PLOS ONE 14, no. 4 (April 5, 2019): e0214933. http://dx.doi.org/10.1371/journal.pone.0214933.

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26

Nwankwo, D. I., and A. Akinsoji. "Epiphyte community on water hyacinth Eichhornia crassipes (Mart.) Solms in coastal waters of southwestern Nigeria." Archiv für Hydrobiologie 124, no. 4 (June 16, 1992): 501–11. http://dx.doi.org/10.1127/archiv-hydrobiol/124/1992/501.

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27

Meirinawati, Hanny, and A'an Johan Wahyudi. "Deepening Knowledge of Nutrient Dynamics in Coastal Waters." ASEAN Journal on Science and Technology for Development 39, no. 1 (April 28, 2022): 23–33. http://dx.doi.org/10.29037/ajstd.747.

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Nutrients are important compounds in waterbodies that regulate primary productivity and phytoplankton growth, the basis of food webs. Increased nutrient concentration has become a serious concern because it causes eutrophication and threatens the sustainability of ecosystems. Eutrophication is the process of nutrient enrichment in water bodies that affects their productivity and decreases water quality. Although information about nutrient distribution, limiting nutrients, and nutrient budgets is important for coastal water management, studies of wide-scale nutrient dynamics in Indonesian waters remain limited. To provide comprehensive data on nutrients, this review summarized the concentrations and compositions of nutrients in coastal waters, compared the limiting nutrients in various coastal waters based on the Redfield ratio, and described the factors affecting nutrient budgets using the database in ScienceDirect and Google Scholar. Curation was performed to summarize the nutrient dynamics in coastal waters. Results showed that nutrient concentration differed in each region due to many factors. Anthropogenic inputs greatly affected nutrients in tropical areas, such as Jakarta Bay (Indonesia). Understanding the quality and characteristics of water can help in managing waterbodies. This study provided knowledge related to nutrient dynamics in Indonesian waters and global biogeochemistry.
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28

Sugai, Susan. "Loss Carved in Coastal Waters." Northern Review 46 (December 12, 2017): 200. http://dx.doi.org/10.22584/nr46.2017.041.

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29

Lohmann, P. "Thermal mapping of coastal waters." Marine Geodesy 11, no. 1 (January 1987): 43–56. http://dx.doi.org/10.1080/15210608709379548.

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30

Christen, Kris. "U.S. coastal waters graded poorly." Environmental Science & Technology 36, no. 13 (July 2002): 266A. http://dx.doi.org/10.1021/es0223473.

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31

Elliott, A. J., A. G. Barr, and D. Kennan. "Diffusion in Irish coastal waters." Estuarine, Coastal and Shelf Science 44 (January 1997): 15–23. http://dx.doi.org/10.1016/s0272-7714(97)80003-0.

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32

Vincent, C. E. "Physical oceanography of coastal waters." Dynamics of Atmospheres and Oceans 9, no. 2 (July 1985): 212–13. http://dx.doi.org/10.1016/0377-0265(85)90006-5.

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33

Bange, Hermann W., Spyridon Rapsomanikis, and Meinrat O. Andreae. "Nitrous oxide in coastal waters." Global Biogeochemical Cycles 10, no. 1 (March 1996): 197–207. http://dx.doi.org/10.1029/95gb03834.

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34

Piontkovski, Sergey A., Asila Al-Maawali, Ward Al-Muna Al-Manthri, Khalid Al-Hashmi, and Elena A. Popova. "Zooplankton of Oman Coastal Waters." Journal of Agricultural and Marine Sciences [JAMS] 19 (January 1, 2014): 37. http://dx.doi.org/10.24200/jams.vol19iss0pp37-50.

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Monthly sampling during daytime was carried out in 2007-2011 at Bandar Al-Khyran (23.51oN, 58.72oE) which is the largest semi-enclosed bay on the southern end of the Sea of Oman with about 4 km2 in surface area and an average depth of 10 m. Zooplankton were represented by Copepoda (79%), Cladocera (9%), Oikopleuriddae (7%), Chaetognatha (3%), and Decapoda (~2%) comprising the major part of the total zooplankton abundance. Among copepods, 27 species constituted ~75% of total copepod abundance. Changes of copepod abundance have not had a pronounced seasonal pattern. Instead, a multiple peak structure in monthly fluctuations was observed, on the level of genera as well as the abundance of species. Amplitudes and timing of the copepod peak abundance were markedly different during the studied years.
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35

Gallagher, M. W., K. M. Beswick, and H. Coe. "Ozone deposition to coastal waters." Quarterly Journal of the Royal Meteorological Society 127, no. 572 (January 2001): 539–58. http://dx.doi.org/10.1002/qj.49712757215.

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36

Sundar, V., H. Noethel, and K. P. Holz. "Velocity fields in coastal waters." Marine Structures 8, no. 3 (January 1995): 309–33. http://dx.doi.org/10.1016/0951-8339(94)00003-b.

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37

Howarth, M. J. "Physical oceanography of coastal waters." Estuarine, Coastal and Shelf Science 23, no. 3 (September 1986): 429–30. http://dx.doi.org/10.1016/0272-7714(86)90040-5.

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38

Vilibić, Ivica, Hrvoje Mihanović, Ivica Janeković, Cléa Denamiel, Pierre-Marie Poulain, Mirko Orlić, Natalija Dunić, et al. "Wintertime dynamics in the coastal northeastern Adriatic Sea: the NAdEx 2015 experiment." Ocean Science 14, no. 2 (March 23, 2018): 237–58. http://dx.doi.org/10.5194/os-14-237-2018.

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Abstract. The paper investigates the wintertime dynamics of the coastal northeastern Adriatic Sea and is based on numerical modelling and in situ data collected through field campaigns executed during the winter and spring of 2015. The data were collected with a variety of instruments and platforms (acoustic Doppler current profilers, conductivity–temperature–depth probes, glider, profiling float) and are accompanied by the atmosphere–ocean ALADIN/ROMS modelling system. The research focused on the dense-water formation (DWF), thermal changes, circulation, and water exchange between the coastal and open Adriatic. According to both observations and modelling results, dense waters are formed in the northeastern coastal Adriatic during cold bora outbreaks. However, the dense water formed in this coastal region has lower densities than the dense water formed in the open Adriatic due to lower salinities. Since the coastal area is deeper than the open Adriatic, the observations indicate (i) balanced inward–outward exchange at the deep connecting channels of denser waters coming from the open Adriatic DWF site and less-dense waters coming from the coastal region and (ii) outward flow of less-dense waters dominating in the intermediate and surface layers. The latter phenomenon was confirmed by the model, even if it significantly underestimates the currents and transports in the connecting channels. The median residence time of the coastal area is estimated to be approximately 20 days, indicating that the coastal area may be renewed relatively quickly by the open Adriatic waters. The data that were obtained represent a comprehensive marine dataset that can be used to calibrate atmospheric and oceanic numerical models and point to several interesting phenomena to be investigated in the future.
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39

Pérez-Ruzafa, Angel, Concepción Marcos, Isabel María Pérez-Ruzafa, and María Pérez-Marcos. "Coastal lagoons: “transitional ecosystems” between transitional and coastal waters." Journal of Coastal Conservation 15, no. 3 (April 8, 2010): 369–92. http://dx.doi.org/10.1007/s11852-010-0095-2.

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40

Dreizis, Y. I. "Modelling of water quality management in the sea coastal zone." E3S Web of Conferences 224 (2020): 02001. http://dx.doi.org/10.1051/e3sconf/202022402001.

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Coastal territories are one of the most dynamically developing regions. Sea resorts focused on recreational and tourist activities are developing especially quickly. For such territories, their ecological status, especially the quality of coastal zone water resources, plays an important role in their sustainable development. Analysis of physical factors of water exchange and assessment of water resources quality of the coastal zone of the sea, including in closed and semi-enclosed water areas, was carried out. It has been shown that water exchange is the most important factor in the management of the quality of marine waters of partially enclosed coastal areas. 0-dimensional and system-dynamic models were used to analyze water exchange in the coastal zone of the sea. Results of studies made it possible to assess the circulation of coastal marine waters and the change in certain indicators of the quality of water resources, including in the presence of various coastal protection construction.
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41

Purwanto, Anang Dwi, Teguh Prayogo, Sartono Marpaung, and Argo Galih Suhada. "ANALYSIS OF POTENTIAL FISHING ZONES IN COASTAL WATERS: A CASE STUDY OF NIAS ISLAND WATERS." International Journal of Remote Sensing and Earth Sciences (IJReSES) 17, no. 1 (August 20, 2020): 9. http://dx.doi.org/10.30536/j.ijreses.2020.v17.a3298.

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The need for information on potential fishing zones based on remote sensing satellite data (ZPPI) in coastal waters is increasing. This study aims to create an information model of such zones in coastal waters (coastal ZPPI). The image data used include GHRSST, SNPP-VIIRS and MODIS-Aqua images acquired from September 1st-30th, 2018 and September 1st-30th, 2019, together with other supporting data. The coastal ZPPI information is based on the results of thermal front SST detection and overlaying this with chlorophyll-a. The method of determining the thermal front sea surface temperature (SST) used Single Image Edge Detection (SIED). The chlorophyll-a range used was in the mesotropic area (0.2-0.5 mg/m3). Coastal ZPPI coordinates were determined using the polygon centre of mass, while the coastal ZPPI information generated was only for coastal areas with a radius of between 4-12 nautical miles and was divided into two criteria, namely High Potential (HP) and Low Potential (LP). The results show that the coastal ZPPI models were suitable to determine fishing locations around Nias Island. The percentage of coastal ZPPI information generated was around 90% information monthly. In September 2018, 27 days of information were produced, consisting of 11 HP sets of coastal ZPPI information and 16 sets of LP information, while in September 2019 it was possible to produce 29 days of such information, comprising 11 sets of HP coastal ZPPI information and 18 LP sets. The use of SST parameters of GHRSST images and the addition of chlorophyll-a parameters to MODIS-Aqua images are very effective and efficient ways of supporting the provision of coastal ZPPI information in the waters of Nias Island and its surroundings.
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42

Yang, Dongfang, Linzhen Wei, Ming Feng, Shengjun Zhang, and Danfeng Yang. "Transmit the heat of rivers to surface seawater." E3S Web of Conferences 276 (2021): 01010. http://dx.doi.org/10.1051/e3sconf/202127601010.

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Based on the survey materials of the waters of Jiaozhou Bay in April and August 1981, this article studies the water temperature and horizontal distribution in the surface waters of Jiaozhou Bay. The results have showed that the water temperature ranged within 7.52–30.90°C in April and August, and the length of interval of water temperature was 23.38°C. The water temperature of the ocean was above 7.00°C. It indicated that the water temperature of the entire water body of Jiaozhou Bay was relatively high in April and August, in terms of the changes of water temperature. In April, the water temperature in the water body of Jiaozhou Bay ranged within 7.52–13.70°C, and the length of temperature interval was 6.18°C. In Jiaozhou Bay, from the northeastern coastal waters along the northern coastal waters to the northwestern coastal waters, the range of water temperature changes was 12.82–13.70°C, and the interval length of seawater temperature changes was 0.88°C. From the northern area to the southern area, the range of water temperature changes was 7.52–13.70°C, and the interval length of seawater temperature was 6.18°C. In August, the range of water temperature changes was 24.60–30.90°C, and the interval length of seawater temperature was 6.30°C. In the eastern area of Jiaozhou Bay, the water temperature in the coastal waters of the estuary of Jiaozhou Bay was 30.90°C, forming a high temperature area. In the coastal waters of Jiaozhou Bay from the northwest to the north, the range of water temperature changes was 27.32–27.37°C and the interval length of seawater temperature was 0.05°C. In April and August, the increase of water temperature in the coastal waters from the northeast along the north to the northwest of Jiaozhou Bay was mainly caused by the shortwave radiation from the sun and sky and the longwave radiation from the atmosphere which continuously offered heat to the seawater. In April, it formed a circular water area with low temperature centered with the central water area of Jiaozhou Bay, whose water temperature ranged within 7.52–8.51°C. Thus, there was no heat source to provide heat to the central waters of Jiaozhou Bay, resulting a loop-locked low water temperature area in the center of the bay. In August, in the eastern part of Jiaozhou Bay, that is, the coastal waters in the estuary of Haibo River, the water temperature reached a relatively high value, 30.90°C. The source of the increase in water temperature was the transportation of heat from Haibo River, which transferred the heat of the river to the surface seawater.
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43

Fujioka, R. S. "Monitoring coastal marine waters for spore-forming bacteria of faecal and soil origin to determine point from non-point source pollution." Water Science and Technology 44, no. 7 (October 1, 2001): 181. http://dx.doi.org/10.2166/wst.2001.0419.

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The US Environmental Protection Agency (USEPA) and the World Health Organization (WHO) have established recreational water quality standards limiting the concentrations of faecal indicator bacteria (faecal coliform, E. coli, enterococci) to ensure that these waters are safe for swimming. In the application of these hygienic water quality standards, it is assumed that there are no significant environmental sources of these faecal indicator bacteria which are unrelated to direct faecal contamination. However, we previously reported that these faecal indicator bacteria are able to grow in the soil environment of humid tropical island environments such as Hawaii and Guam and are transported at high concentrations into streams and storm drains by rain. Thus, streams and storm drains in Hawaii contain consistently high concentrations of faecal indicator bacteria which routinely exceed the EPA and WHO recreational water quality standards. Since, streams and storm drains eventually flow out to coastal marine waters, we hypothesize that all the coastal beaches which receive run-off from streams and storm drains will contain elevated concentrations of faecal indicator bacteria. To test this hypothesis, we monitored the coastal waters at four beaches known to receive water from stream or storm drains for salinity, turbidity, and used the two faecal indicator bacteria (E. coli, enterococci) to establish recreational water quality standards. To determine if these coastal waters are contaminated with non-point source pollution (streams) or with point source pollution (sewage effluent), these same water samples were also assayed for spore-forming bacteria of faecal origin (Cl. perfringens) and of soil origin (Bacillus species). Using this monitoring strategy it was possible to determine when coastal marine waters were contaminated with non-point source pollution and when coastal waters were contaminated with point source pollution. The results of this study are most likely applicable to all countries in the warm and humid region of the world.
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44

Arifin, Nur, Sofyan Husein Siregar, and Syafrudin Nasution. "DETERMINATION OF WATER QUALITY IN PHYSIC AND CHEMICAL USE STORET INDEX AND POLLUTION INDEX IN COASTAL WATERS DUMAI RIAU PROVINCE." AQUASAINS 8, no. 1 (November 18, 2019): 743. http://dx.doi.org/10.23960/aqs.v8i1.p743-752.

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The condition of good water quality is essential to support the survival of organisms that live in it. Determination of the status of water quality needs to be done as a reference in monitoring the water quality pollution.The purpose of this study to analyze and determine the status of water quality physically and chemically in the coastal waters Dumai. The method used in this research is survey method was conducted in December 2018 - April 2019 in the Coastal Water Dumai in Riau province. Sampling sites physical and chemical parameters determined by purposive sampling. Based on consideration of environmental conditions and Dumai City Regulation No. 11 In 2002, it was determined sampling consisted of four stations, with each station there are 5 sampling points were used as replicates. Determining the status of water quality using storet index and the index of pollution. Water quality measurement results About Coastal Dumai use Storet index and the pollution index shows that the coastal waters of Dumai categorized as Heavy Polluted waters.
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45

Gruzinov, V. M., N. N. Dyakov, I. V. Mezenceva, Yu A. Malchenko, N. V. Zhohova, and A. N. Korshenko. "Sources of coastal waters pollution near Sevastopol." Океанология 59, no. 4 (September 17, 2019): 579–90. http://dx.doi.org/10.31857/s0030-1574594579-590.

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The results of current ecological investigations of marine waters in Sevastopol region are presented. The main sources of water pollution described for Sevastopol Bay and other part of coastal line from cup Lukull till cup Foros were described. The position of Waste Water Treatment Plant underwater outlets, the volume of waste-waters discharges and the degree of their purification were estimated. With the help of the side-scan sonar, the state of the heads of the sewage treatment plants in the region was examined. The features of the vertical distribution of hydrological and hydrochemical characteristics are shown. The preliminary estimation of the currents near the sewages outlets were studied using autonomic buoys and mathematical modeling. Based on historical data and results of recent cruises in 2016–2017 the nutrient concentration, and total petroleum hydrocarbons and organic matter by biological oxygen demand BOD5 content were described. The nutrients content for all studied forms was much lower then Maximum Allowed Concentration and no significant difference between different parts of Crimea coastal waters were marked. Marine waters pollution by TPHs is much higher in Sevastopol region and in Kerch Strait in comparison with Yalta port.
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46

Karås, Peter. "Recruitment of perch (Perca fluviatilis L.) from Baltic coastal waters." Archiv für Hydrobiologie 138, no. 1 (November 29, 1996): 99–121. http://dx.doi.org/10.1127/archiv-hydrobiol/138/1996/99.

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47

Lu, Douding, Yuzao Qi, Haifeng Gu, Xinfeng Dai, Hongxia Wang, Yahui Gao, Ping-Ping Shen, Qingchun Zhang, Rencheng Yu, and Songhui Lu. "Causative species of harmful algal blooms in Chinese coastal waters." Algological Studies 145-146 (October 1, 2014): 145–68. http://dx.doi.org/10.1127/1864-1318/2014/0161.

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48

Yang, Dongfang, Jianxun Chai, Xiaoye Gao, Yunjie Wu, and Sixi Zhu. "The consistency of Arsenic’s high value regions in surface and bottom waters in Jiaozhou Bay." E3S Web of Conferences 38 (2018): 01026. http://dx.doi.org/10.1051/e3sconf/20183801026.

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This paper analyzed the contents and distributions of As in Jiaozhou Bay in 1982. Results showed that As’s contents in bottom waters in coastal waters in the southwest of the bay and the bay mouth in Jiaozhou Bay in July and October 1982 were 0.88-4.48 μg L-1 and 0.84-1.16 μg L-1, respectively. As’s contents were much lower than the guide line of Grade I, and the pollution level of As in bottom waters in Jiaozhou Bay in 1982 was still very slight. There was high value region in coastal waters in the southwest of the bay in July 1982 (4.48 μg L-1), while in October 1982 high value region was in the bay mouth (1.16 μg L-1). The source input of As from overland runoff in the southwest was strong in July, resulted in relative high value region in surface waters in coastal waters in the southwest of the bay, and therefore resulted in high value region in bottom waters in same region by means of rapid sedimentation of As. October was wet season and there was little As input to the bay, resulted in low As’s contents in surface waters, as well as bottom waters. At any time, the terrigenous As was foremost transported to surface waters, and was subsided to sea bottom through water body by vertical water’s effect. Hence, the high value regions of As’s contents in surface and bottom waters had characteristic of consistency in Jiaozhou Bay.
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49

Mellawati, June. "DISTRIBUTION OF URANIUM IN WATER OF GRESIK COASTAL WATERS." Indonesian Journal of Chemistry 9, no. 2 (June 22, 2010): 211–16. http://dx.doi.org/10.22146/ijc.21532.

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Determination of uranium in water sample at Gresik coastal waters around Gresik industrial area have been carrid out. The purpose of research is to find the distribution of uranium at the coastal where the phosphate industry standing and potencially to contribute uranium pollutant to the waters. The measurement of uranium was pasive of Gamma Spectrometry, and uranium was measured as 234Th (uranium daughters) on 92.80 and 1001.03 keV gamma energies. Sea water sample was taken up by water pump sampler as a vertical mixing. The sample was sampling on the highest tide and lowest ebb, at the east season (March-August) west season (September-February). The concentration of 238U on higher tide of the west season are range between 0.0016-0.0128 Bq/l, while on lowest ebb of the east season are 0,0013-0,0877 Bq/l. There was significantly different (α= 5%) of uranium concentration in water between two seasons (east and west) in tide and ebb respectively. According to Quality Standard from Dirjen BATAN No.293/Dj/VII/1995 (radioactivity on environment), the concentration of 238U in water obtained from coastal around phosphate industry are still lower than that of recomended values (10.000 Bq/l). Keywords: uranium, sea water, coastal of Gresik
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50

Hoyer, Mark V., Thomas K. Frazer, Sky K. Notestein, and Daniel E. Canfield, Jr. "Nutrient, chlorophyll, and water clarity relationships in Florida's nearshore coastal waters with comparisons to freshwater lakes." Canadian Journal of Fisheries and Aquatic Sciences 59, no. 6 (June 1, 2002): 1024–31. http://dx.doi.org/10.1139/f02-077.

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Models relating chlorophyll to nutrients and Secchi depth to chlorophyll using data from nearshore coastal waters of Florida were successfully developed. The models suggest that phosphorus is the primary limiting factor for phytoplankton in the nearshore coastal waters of Florida and that total phosphorus concentration accounts for 81% of the variance in chlorophyll concentration. The models also show that chlorophyll is the dominant factor determining Secchi depth in nearshore coastal waters of Florida and that chlorophyll concentrations account for 68% of the variance in Secchi depth. Thus, these models are robust and should be useful for eutrophication management of Florida's coastal marine systems. The models developed with data from nearshore coastal waters of Florida are similar to models developed for freshwater lakes in Florida, but the amount of chlorophyll per unit of phosphorus and Secchi depth per unit of chlorophyll are both significantly less for marine samples. This suggests that the chlorophyll to biovolume ratios in the nearshore coastal waters of Florida are less than in freshwater systems of Florida. Therefore, nutrient to chlorophyll and chlorophyll to Secchi depth models developed for freshwater systems are probably ill suited for use in Florida's marine systems.
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