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Abstract

Indonesia is one of the largest contributors to global marine litter deposition, given its high population and the largest archipelagic country. The increasing problem of plastic littering has recently attracted the attention of researchers. This study aims to identify marine and macroplastic litter in Semarang City. A field survey was conducted by dividing the beach into 18 sampling grids, each with an area of 1 × 1 m2. A literature survey was also conducted using the Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) methodology to identify literature that can be used to develop recommendations. The results showed that 6.26–11.16 grams/m2/ day of marine litter and approximately 1.61–4.89 items/m2/day of plastic litter would be deposited on Semarang City beaches. The greatest contributors to macroplastic litter were polypropylene (PP) and low-density polyethylene (LDPE), which should be considered for further intervention. Strategic recommendations were developed based on an in-depth literature survey and best practices in the current field. These also include recommendations that can be used as a reference by policymakers and other stakeholders to reduce marine pollution. The results of this study are expected to provide a multiplier effect on reducing marine pollution for the city.
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Bibliography

[1]. Beaumont, N.J., Aanesen, M., Austen, M.C., Börger, T., Clark, J.R., Cole, M., Hooper, T., Lindeque, P.K., Pascoe, C. & Wyles, K.J. (2019). Global ecological, social and economic impacts of marine plastic. Marine Pollution Bulletin, 142, pp. 189–195. DOI:10.1016/j.marpolbul.2019.03.022
[2]. Binetti, U., Silburn, B., Russell, J., van Hoytema, N., Meakins, B., Kohler, P., Desender, M., Preston-Whyte, F., Fa’abasu, E., Maniel, M. & Maes, T. (2020). First marine litter survey on beaches in Solomon Islands and Vanuatu, South Pacific: Using OSPAR protocol to inform the development of national action plans to tackle land-based solid waste pollution. Marine Pollution Bulletin, 161, p. 111827. DOI:10.1016/j.marpolbul.2020.111827
[3]. Chitrakar, P., Baawain, M.S., Sana, A. & Al-Mamun, A. (2019). Current status of marine pollution and mitigation strategies in arid region: A detailed review. Ocean Science Journal, 54, pp. 317–348. DOI:10.1007/s12601-019-0027-5
[4]. Corbau, C., Nardin, W., Vaccaro, C., Vona, I., & Simeoni, U. (2023). Experimental design and field deployment of an artificial bio-reef produced by mollusk shell recycling. Marine Environmental Research, 183, 105833. DOI:10.1016/j.marenvres.2022.105833
[5]. Cordova, M.R., Iskandar, M.R., Muhtadi, A., Nurhasanah, Saville, R. & Riani, E. (2022). Spatio-temporal variation and seasonal dynamics of stranded beach anthropogenic debris on Indonesian beach from the results of nationwide monitoring. Marine Pollution Bulletin, 182, p. 114035. DOI:10.1016/j.marpolbul.2022.114035
[6]. Dasgupta, S., Sarraf, M. & Wheeler, D. (2022). Plastic waste cleanup priorities to reduce marine pollution: A spatiotemporal analysis for Accra and Lagos with satellite data. Science of the Total Environment, 839, p. 156319. DOI:10.1016/j.scitotenv.2022.156319
[7]. Dobler, D., Maes, C., Martinez, E., Rahmania, R., Gautama, B.G., Farhan, A.R. & Dounias, E. (2022). On the fate of floating marine debris carried to the sea through the main rivers of Indonesia. Journal of Marine Science and Engineering, 10, p. 1009. DOI:10.3390/jmse10081009
[8]. Galgani, L., Beiras, R., Galgani, F., Panti, C. & Borja, A. (2019). Editorial: Impacts of marine litter. Frontiers in Marine Science, 6, p. 208. DOI:10.3389/fmars.2019.00208
[9]. Ghaffari, S., Bakhtiari, A.R., Ghasempouri, S.M. & Nasrolahi, A. (2019). The influence of human activity and morphological characteristics of beaches on plastic debris distribution along the Caspian Sea as a closed water body. Environmental Science and Pollution Research, 26, pp. 25712–25724. DOI:10.1007/s11356-019-05790-y
[10]. Hayati, Y., Adrianto, L., Krisanti, M., Pranowo, W.S. & Kurniawan, F. (2020). Magnitudes and tourist perception of marine debris on small tourism island: Assessment of Tidung Island, Jakarta, Indonesia. Marine Pollution Bulletin, 158, p. 111393. DOI:10.1016/j.marpolbul.2020.111393
[11]. Kaviarasan, T., Naik, S., Sivadas, S.K., Dhineka, K., Sambandam, M., Sivyer, D., Mishra, P. & Ramana Murthy, M.V. (2020). Assessment of litter in the remote beaches of Lakshadweep Islands, Arabian Sea. Marine Pollution Bulletin, 161, p. 111760. DOI:10.1016/j.marpolbul.2020.111760
[12]. Lauer, N.E. & Nowlin, M.B. (2022). A framework for inland cities to prevent marine debris: A case study from Durham, North Carolina. Frontiers in Marine Science, 9, p. 983256. DOI:10.3389/fmars.2022.983256
[13]. Löhr, A., Savelli, H., Beunen, R., Kalz, M., Ragas, A. & Van Belleghem, F. (2017). Solutions for global marine litter pollution. Current Opinion in Environmental Sustainability, 28, pp. 90–99. DOI:10.1016/j.cosust.2017.08.009
[14]. Monteiro, R. J., Lopes, C. B., Rocha, L. S., Coelho, J. P., Duarte, A. C., & Pereira, E. (2016). Sustainable approach for recycling seafood wastes for the removal of priority hazardous substances (Hg and Cd) from water. Journal of Environmental Chemical Engineering, 4(1), 1199-1208. DOI:10.1016/j.jece.2016.01.021
[15]. Nguyen, T. T., Huang, H., Nguyen, T. A. H. & Soda, S. (2022). Recycling clamshell as substrate in lab-scale constructed wetlands for heavy metal removal from simulated acid mine drainage. Process Safety and Environmental Protection, 165, 950-958. DOI:10.1016/j.psep.2022.04.026
[16]. Nurulhaq, H. & Kismartini, (2019). The effect of green marketing of plastic bag ban policy in modern retail stores on consumer green behavior in Bogor City. E3S Web of Conference, 125, p. 08003. DOI:10.1051/e3sconf/201912508003
[17]. Popa, C. L., Carutasu, G., Cotet, C. E., Carutasu, N. L., & Dobrescu, T. (2017). Smart city platform development for an automated waste collection system. Sustainability, 9(11), 2064. DOI:10.3390/su9112064
[18]. Pratiwi, A.H., Budiyono, B. & Dewanti, N.A.Y. (2021). Identification types of the marine debris and factors related them in Semarang City. Jurnal Presipitasi: Media Pengembangan dan Komunikasi Teknik Lingkungan, 18, pp. 64–72. DOI:10.14710/presipitasi.v18i1.64-72
[19]. Ramadan, B.S., Rachman, I., Ikhlas, N., Kurniawan, S.B., Miftahadi, M.F. & Matsumoto, T. (2022). A comprehensive review of domestic-open waste burning: recent trends, methodology comparison, and factors assessment. Journal of Material Cycles and Waste Management, 24, pp. 1633–1647. DOI:10.1007/s10163-022-01430-9
[20]. Renjaan, E.A., Silubun, D.T., Latar, D.I. & Makailipessy, M. (2020). Beach orientation and exposure accumulate types of marine debris on the coast of Dullah Island, kei archipelago, Indonesia. IOP Conference Series: Earth and Environmental Science, 517, p. 012015. DOI:10.1088/1755-1315/517/1/012015
[21]. Sari, M.M., Inoue, T., Septiariva, I.Y., Suryawan, I.W.K., Kato, S., Harryes, R.K., Yokota, K., Notodarmojo, S., Suhardono, S. & Ramadan, B.S. (2022). Identification of face mask waste generation and processing in tourist areas with thermo-chemical process. Archives of Environmental Protection, 48, 2, pp. 79-85. DOI:10.24425/aep.2022.140768
[22]. Smith, E., Dziewatkoski, M., Henrie, T., Seidel, C. & Rosen, J. (2019). Microplastics: What drinking water utilities need to know. Journal American Water Works Association, 111, p. 26–37. DOI:10.1002/awwa.1393
[23]. Sukma, E., Ramadhan, S. & Indriyani, V. (2020). Integration of environmental education in elementary schools. Journal of Physics: Conference Series, 1481, p. 012136. DOI:10.1088/1742-6596/1481/1/012136
[24]. Suteja, Y., Atmadipoera, A.S., Riani, E., Nurjaya, I.W., Nugroho, D. & Purwiyanto, A.I.S. (2021). Stranded marine debris on the touristic beaches in the south of Bali Island, Indonesia: The spatiotemporal abundance and characteristic. Marine Pollution Bulletin, 173, p. 113026. DOI:10.1016/j.marpolbul.2021.113026
[25]. Syakti, A.D., Bouhroum, R., Hidayati, N.V., Koenawan, C.J., Boulkamh, A., Sulistyo, I., Lebarillier, S., Akhlus, S., Doumenq, P. & Wong-Wah-Chung, P. (2017). Beach macro-litter monitoring and floating microplastic in a coastal area of Indonesia. Marine Pollution Bulletin, 122, pp. 217–225. DOI:10.1016/j.marpolbul.2017.06.046
[26]. Ummatin, K.K. & Faria, N. (2021). Simulation of tipping fee policy to support municipal waste management into alternative fuel in the cement industry: a case study of Tuban landfill Indonesia. IOP Conf. Series: Earth and Environmental Science, 753, p. 012041. DOI:10.1088/1755-1315/753/1/012041
[27]. van Emmerik, T., Seibert, J., Strobl, B., Etter, S., den Oudendammer, T., Rutten, M., bin Ab Razak, M.S. & van Meerveld, I. (2020). Crowd-based observations of riverine macroplastic pollution. Frontiers in Earth Science, 8, p. 298. DOI:10.3389/feart.2020.00298
[28]. Westlake, E.L., Lawrence, E., Travaglione, N., Barnes, P. & Thomson, D.P. (2022). Low quantities of marine debris at the northern Ningaloo Marine Park, Western Australia, influenced by visitation and accessibility. Marine Pollution Bulletin, 174, p. 113294. DOI:10.1016/j.marpolbul.2021.113294
[29]. Wibowo, Y. G., Naswir, M., & Ramadan, B. S. (2022). Performance of a novel biochar-clamshell composite for real acid mine drainage treatment. Bioresource Technology Reports, 17, 100993. DOI:10.1016/j.biteb.2022.100993
[30]. Wu, W.-M., Yang, J. & Criddle, C.S. (2017). Microplastics pollution and reduction strategies. Frontiers in Environmental Science and Engineering, 11, p. 6. DOI:10.1007/s11783-017-0897-7
[31]. Yenici, E. & Turkoglu, M., 2023. Abundance and composition of marine litter on the coasts of the Dardanelles (Canakkale Strait, Turkey). Environmental Monitoring and Assessment 195, 4. DOI:10.1007/s10661-022-10511-z

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Authors and Affiliations

Badrus Zaman
1
Bimastyaji Surya Ramadan
2 3
Anik Sarminingsih
1
Ika Bagus Priyambada
1
Mochamad Arief Budihardjo
1

  1. Department of Environmental Engineering, Faculty of Engineering, Universitas Diponegoro Jl.Prof. H. Sudarto, SH Tembalang, Semarang, Indonesia
  2. Graduate Programs in Environmental Systems, Graduate School of Environmental Engineering,The University of Kitakyushu, Kitakyushu, Japan
  3. Environmental Sustainability Research Group, Department of Environmental Engineering,Faculty of Engineering, Universitas Diponegoro, Indonesia
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Abstract

This paper presents discussion on the results of subfossil Cladocera analyses from five lakes in Poland (Przedni Staw Lake, Perespilno Lake, Gościąż Lake, Imiołki- fossil lake and Ostrowite Lake). The Cladocera are represented in sediments by remains of planktonic (Bosminidae, Daphnidae) and littoral (Chydoridae) forms. Cladoceran assemblage phases ("ecostratigraphy") were determined on the basis of changes in dominance of indicator species and past ecological conditions were reconstructed. The results are being discussed from the viewpoint of climate change and anthropogenic activity and their role in the lake evolution. Moreover, an attempt to use the cladoceran phases for stratigraphic division of the Late Glacial and Holocene was made. During the Bolling/Allerod interstadial, distinguished on the basis of Pollen analysis, Cladocera indicated short phase of bad condition (dry or cold?), probably as the Old Dryas climate results. The beginning of Holocene are characterized, in mountain and lowland lakes, by high increase in the number of species and specimens of Cladocera. This described clear warming and marked the boundary Late Glacial/Holocene. It was indicated that the "ecostratigraphy" based on Cladocera can be useful for climatostratigraphy, if climate was the major factor controlling the development of freshwater lakes.
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Authors and Affiliations

Krystyna Szeroczyńska
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Abstract

In this paper we describe a fossil graben and associated normal faults and joints. The graben occurs in the section of the Vistulian (Weichselian) and Holocene sediments in an archaeological excavation site at Brzezie, in the central part of the Polish Carpathian Foredeep (Wieliczka-Gdów Upland, western part of the Sandomierz Basin). Normal faults strike mostly NNE-SSW and dip steeply about 65 - 850. Some of them, namely master normal faults, bound the fossil graben. The joints form orthogonal pattern and are closely spaced close to the faults. They developed simultaneously with faulting. Normal faulting took place during the Vistulian - Mesoholocene (Neoholocene?) time, according to age of the archaeological artefacts which were found in the faulted sediments. The faulting was probably finished during the Neolithic or even later, during the Bronze Age. The NNE-striking normal faults connected with graben formation could have been produced by reactivation of a NE-striking sinistral regional fault in the basement.
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Authors and Affiliations

Marta Rauch-Włodarska
Tomasz Kalicki
Wojciech Włodarski
Anna Budek
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Abstract

A bibliography of Jerzy Mańkowski, which includes his scholarly writings, translations and edited works, arranged in chronological order.
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Authors and Affiliations

Justyna Mańkowska

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