Analysis of the impact of road noise on urban green spaces: a case study of the dendrological garden in Poznań, Poland
31 ene 2025
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Publicado en línea: 31 ene 2025
Páginas: 11 - 20
Recibido: 14 may 2024
Aceptado: 11 dic 2024
DOI: https://doi.org/10.2478/mgrsd-2025-0004
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© 2025 Ryszard Staniszewski et al., published by Sciendo
This work is licensed under the Creative Commons Attribution 4.0 International License.
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Figure 6.

Changes in area of zones affected by road noise according to studies from the years 2014 and 2020 (average values)
1. | Area exposed to road noise according to the index | 40–45 | A40–45 | 1058 | 10981 | 0.196 |
2. | 45–50 | A45–50 | 17143 | 15088 | −0.041 | |
3. | 50–55 | A50–55 | 15294 | 12858 | −0.048 | |
4. | 55–60 | A55–60 | 10575 | 6779 | −0.075 | |
5. | 60–65 | A60–65 | 5301 | 3744 | −0.031 | |
6. | 65–70 | A65–70 | 1338 | 1259 | −0.002 | |
7. | Percentage of area exposed to above-normal noise LAeqD | >65 | PA>65 | 2.64% | 2.48% | |
25th May 2014 Sunday | 16th May 2020 Saturday | |||||
8. | Area exposed to road noise according to the index | 40–45 | A40–45 | 9951 | 18237 | 0.163 |
9. | 45–50 | A45–50 | 13502 | 10857 | −0.052 | |
10. | 50–55 | A50–55 | 12899 | 10589 | −0.046 | |
11. | 55–60 | A55–60 | 9416 | 7219 | −0.043 | |
12. | 60–65 | A60–65 | 4053 | 3109 | −0.019 | |
13. | 65–70 | A65–70 | 888 | 698 | −0.004 | |
14. | Percentage of area exposed to above-normal noise LAeqD | >65 | PA>65 | 1.75% | 1.38% |
Changes in areas exposed to road noise described by LN and LDWN for the years 2012 and 2017
Area exposed to road noise in accordance with LN | 45–50 | ALN45-50 | 1,018 | 12,804 | 0.232 | |
50–55 | ALN50-55 | 16,461 | 16,380 | −0.002 | ||
55–60 | ALN55-60 | 23,634 | 13,613 | −0.198 | ||
60–65 | ALN60-65 | 9,596 | 7,293 | −0.045 | ||
65–70 | ALN65-70 | 0 | 619 | 0.012 | ||
Area exposed to excessive noise, LN | >59 | A>59LN | 27.8% | 20.9% | ||
Area exposed to road noise in accordance with LDWN | 50–55 | ALDWN50-55 | 0 | 750 | 0.015 | |
55–60 | ALDWN55-60 | 1,086 | 17,918 | 0.332 | ||
60–65 | ALDWN60-65 | 23,903 | 15,974 | −0.157 | ||
65–70 | ALDWN65-70 | 18,616 | 10,704 | −0.156 | ||
70–75 | ALDWN70-75 | 7,104 | 5,387 | −0.034 | ||
Area exposed to excessive noise, LDWN | >68 | A>68LDWN | 28.1% | 18.8% |
Results of the LAeq analyses
59.2 | 60.1 | 57.3 | 56.8 | |
59.3 | 61.0 | 56.6 | 60.7 | |
60.0 | 62.2 | 60.1 | 60.4 | |
56.1 | 57.2 | 54.1 | 54.9 | |
55.7 | 56.4 | 56.2 | 52.3 | |
55.1 | 55.6 | 52.0 | 54.6 | |
51.9 | 52.3 | 50.5 | 52.2 | |
52.0 | 52.4 | 53.4 | 50.6 | |
50.6 | 52.9 | 48.4 | 49.4 | |
52.4 | 52.6 | 47.9 | 52.8 | |
50.0 | 51.2 | 44.2 | 49.3 | |
49.9 | 50.9 | 47.7 | 47.5 | |
49.1 | 50.3 | 47.0 | 47.2 | |
47.0 | 49.9 | 44.0 | 46.6 | |
46.1 | 49.1 | 43.8 | 46.5 | |
45.2 | 48.7 | 43.7 | 45.3 | |
45.7 | 48.2 | 43.8 | 44.9 | |
44.5 | 46.0 | 43.2 | 44.1 | |
43.3 | 45.6 | 43.1 | 43.2 | |
42.9 | 44.6 | 42.0 | 40.7 | |
66.1 | 67.3 | 67.3 | 72.4 | |
71.1 | 71.3 | 71.1 | 71.7 | |
72.9 | 72.6 | 72.4 | 74.1 |