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Factors of Variability in the Accumulation of Waste in a Mountain Region of Southern Poland

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Factors of Variability in the Accumulation of Waste in a Mountain Region of Southern Poland Environ Monit Assess (2020) 192: 153 https://doi.org/10.1007/s10661-020-8103-y Factors of variability in the accumulation of waste in a mountain region of southern Poland Grzegorz Przydatek & Klaudia Ciągło Received: 24 May 2019 /Accepted: 16 January 2020 /Published online: 31 January 2020 # The Author(s) 2020 Abstract The analysis of change factors in waste man- Introduction agementintheperiodfrom2012to2015inthree municipalities in a mountainous region of southern Po- Waste can be categorised as hazardous or non- land exhibited strong differentiation. This was hazardous and inert. Non-hazardous waste includes recognised based on multiple indicators of waste accu- kitchen waste, garden waste, paper and cardboard, tex- mulation. Such differences were investigated between tiles, metals and similar materials used in everyday life two periods, which highlighted the effect of changes in (Kawai and Tasaki 2016). Growth in terms of popula- waste management primarily resulting from Directive tion, economy and the standard of living has contributed 2008/98/EC. These changes relate to the development to by-products in the form of an increasing amount of of selective waste collection based on eight types of municipal solid waste (MSW) (Akdag et al. 2016). waste. On this basis, an increase was observed in the Factors such as the socioeconomic status of the popula- amount of waste collected in the communities. Particu- tion of a given area, demographics and environmental lar attention was paid to the community with the highest awareness affect the quantity of MSW generated during number of tourists, the waste accumulation rate a given year (Noori et al. 2009)andarecausedbythe (452.74 kg per capita) and the cost per year. An increase rapid technological development and population growth in the number of tourists is an important factor in terms experienced since the Industrial Revolution, resulting in of waste accumulation, and other factors made it possi- an increase in the amount of generated waste ble to recognise the direction of the changes taking place (Adamcová and Vaverková 2016). in waste management. In terms of changes in waste Effective waste strategies depend on local solutions accumulation, the implementation of the European and social awareness. The accumulation of waste in the Union law into the national law in the field of waste environment raises social awareness due to the issues it management is a significant factor. causes (Matsakas et al. 2017). Apart from negatively affecting the environment, the waste also constitutes economic, social and ecological issues and causes the Keywords Rate accumulation . Collection . destruction of the landscape. As a member state, Poland Community. Waste management is obliged to maintain sustainable waste management by limiting the generated amount of waste and minimising the deposited MSW on the basis of Directive 2008/98/ EC (Gharfalkar et al. 2015). In this respect, to increase * : ą ł G. Przydatek ( ) K. Ci g o recycling, the country is required to selectively gather at Engineering Institute, State University of Applied Sciences in Nowy Sącz, Zamenhofa 1a St, 33-300 Nowy Sącz, Poland least a fraction of the following waste products: paper, e-mail: [email protected] plastic and glass (Pomberger et al. 2017). 153 Page 2 of 16 Environ Monit Assess (2020) 192: 153 Such actions aim at improving waste management, own observations from field visits and (3) information environmental protection and the sanitary and aesthetic from Statistics Poland ((SP) n.d.; e.g. the number of qualities of an area. The analysis of the changes imple- tourists and inhabitants). In addition, the indicators of mented at the community level is essential to the issue of waste accumulation per capita have been extended to waste management, both on the basis of legal regula- include bulky, glass, plastic, metal, organic, paper, elec- tions and their effects on the level of collected waste trical and electronic equipment and other sorted wastes, (Malinowski and Kopytko 2014). Although many com- which are not usually differentiated as indicators of munities have not developed new waste management waste accumulation and are rarely used. The data in- practices and standards, some of them have managed to clude the size of the population, number of tourists, implement different solutions to waste problems in the number of households and cost of waste management mountain context (UNEP 2017). in the community areas. The obligations of communities and waste carriers Descriptive statistics were used, including the mini- are not without significance, as they bear many costs mum, maximum and average. Moreover, for analytical related to the management of solid waste, including the purposes, except for the mentioned data, the amounts of transport and maintenance of rolling stock, maintenance selectively (segregated waste) and non-selectively col- of waste collectors and operation of waste recovery and lected waste (mixed waste) in individual communities disposal plants (Semernya et al. 2017). were also used to determine the accumulation of waste Against this background, it is important to identify per capita, considering the period before and after the the trajectory and efficiency of the changes in waste changes related to the introduction of Directive 2008/98/ management in communities located in regions of high EC into Polish legislation. It was assumed that the data value in terms of the protection of nature, such as in the from 2012 to 2013 fell into the period before the chang- Carpathian Mountains. These factors were investigated es, while the years from 2014 to 2015 fell into the period based on the results of the accumulated waste per capita after the changes. in two different research periods. The per capita data are widely used to compare the intensity of MSW genera- Characteristics of the communities tion among different places (Abu Qdais et al. 1997; Zhang et al. 2010; Karak et al. 2012). The urban-rural communities of Krynica-Zdrój (49° 25′ The aim of this study was to assess the factors affect- 58″ N, 20° 58′ 02″ E), Piwniczna-Zdrój (49° 43′ 33″ N, ing the variability in the accumulation of municipal 20° 71′ 67″ E) and Stary Sącz (49° 33′ 49″ N, 20° 38′ waste. Three communities located in the south of Poland 05″ E) are located in Nowosądecki County, which is within the Carpathian Mountains are considered. The situated in the south-eastern part of Małopolskie accumulation rates relate to the changes in waste man- Voivodeship in the south of Poland. The communities agement that occurred between 2012 and 2013 and are located in the mountains of the Sądecki region, between 2014 and 2015. which are separated by the Dunajec river and its tribu- taries (the Poprad river with sources in Slovakia and Kamienica). The region is dominated by the following Materials and methods mountains: the Beskid Sądecki, the Low Beskids and the Island Beskids. Materials and methods The spa community of Krynica-Zdrój is situated on the northern side of the Carpathian Mountains in the east This paper discusses issues concerning the efficiency of part of the Beskid Sądecki and on the western edge of the changes in municipal waste management in three the Low Beskids. It is a spa, resort and tourist destina- large settlement units located in a mountainous region in tion with numerous sanatoriums and heath resorts due to Poland, which are distinguished by their unique envi- its medicinal water sources. It is situated in the Beskid ronmental conditions and attractiveness to tourists. In Sądecki within the area of the Poprad Landscape Park the analysis, the data came from the communities of near the border of Slovakia. Most buildings in the com- Krynica-Zdrój, Piwniczna-Zdrój and Stary Sącz for munity are approx. 550 to 1000 m above sea level (asl) 2012 to 2015 and are based on (1) a questionnaire in height, and some sanatoriums and private buildings distributed to these municipalities, (2) the researcher’s are located well above 650 m asl. Environ Monit Assess (2020) 192: 153 Page 3 of 16 153 The community of Piwniczna-Zdrój focuses on tour- Within the community, the collection of bulky waste ism and recreation. It has many holiday, health and was organised at least twice a year. In 2014 to 2015, recreation resorts and sanatoriums. The community area Piwniczna-Zdrój imposed an obligation to pay a extends from an altitude of 400 to 1140 m asl. The “waste” fee on all inhabitants. Both sorted and unsorted community of Stary Sącz is one of the oldest settlement MSW were collected in bags by the inhabitants. Such units of Poland, which also attracts tourists. It is located waste was collected at least once a month and twice a in Sądecka Valley in a fork between two mountain rivers month in the summer. (Poprad and Dunajec). These last two municipalities An obligation to pay the waste fee was also imposed were founded in the twelfth century. on all inhabitants in Stary Sącz after the introduction of the changes in waste management. The waste was col- Analysis of system solutions for waste management lected according to the following frequencies: Before the changes that resulted from Directive 2008/ & Sorted municipal waste was collected once a month. 98/EC, in the community of Krynica-Zdrój, MSW was & Mixed municipal waste was collected once or twice selectively collected to a small extent. In this period, a month, depending on the season. before changes did not collect Waste Electrical and Electronic Equipment (WEEE) and organic waste from Additionally, within the community, ashes from fur- household. Other selectively collected wastes like ash, naces were collected once a month during the 7 months hazardous waste, concrete and demolition waste seldom requiring heating. The collected waste was exported were collected. After these changes, in accordance with outside the communities for further disposal because the waste hierarchy (Gharfalkar et al.
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