| Literature DB >> 34831980 |
Qiaohui Liu1, Xiaoping Wang1, Jinglan Liu2, Guolin Zhang3, Congying An2, Yuqi Liu2, Xiaoli Fan2, Yishen Hu2, Heng Zhang4.
Abstract
Short-term exposure to a forest environment is beneficial to human physiological and psychological health. However, there is little known about the relationship between the restorative perception of environment and physiological and psychological restoration achieved by experiencing the forest environment. This study evaluated the relationship between the restorative perception of different types of forests and human physiological and psychological effects. A sample of 30 young adult students from Beijing Forestry University was exposed to coniferous, deciduous, and mixed forests as well as an urban site. Restorative perception of the environment was measured using the PRS questionnaire. Restorative effects were measured using physiological indicators (blood pressure and heart rate) and three psychological questionnaires (Restorative Outcome Scale; Subjective Vitality Scale; Warwick-Edinburgh Mental Well-being Scale). The results demonstrated the following: (1) There were significant differences in the perceived restorative power of the three types of forests, with the highest level in the mixed forest, followed by the coniferous forest and the deciduous forest. (2) All types of forests were beneficial to physiological and psychological restoration. The mixed forest had the greatest effect in lowering blood pressure and heart rate as well as increasing vitality, while the coniferous forest had the strongest increases in psychological restoration and positive mental health. (3) The level of perceived restorative power of environment was positively related to the physiological and psychological restoration. These findings provide practical evidence for forest therapy that can maximize the restorative potential of forests.Entities:
Keywords: forest therapy; forest types; human well-being; physiological restoration; psychological impact; restorative environment
Mesh:
Year: 2021 PMID: 34831980 PMCID: PMC8620764 DOI: 10.3390/ijerph182212224
Source DB: PubMed Journal: Int J Environ Res Public Health ISSN: 1660-4601 Impact factor: 3.390
Figure 1The map of experimental locations.
Figure 2Photos: (A) city site, (B) mixed forest, (C) deciduous forest, (D) coniferous forest.
Forest characteristics in forest sites.
| Forest Site | Mixed Forest | Deciduous Forest | Coniferous Forest |
|---|---|---|---|
| Dominant tree species |
|
|
|
| Tree height (m) | 7 ± 1.22 | 5 ± 1.00 | 8 ± 0.81 |
| Diameter breast height (cm) | 22 ± 3.67 | 15 ± 3.35 | 16 ± 1.81 |
| Canopy closure (%) | 0.7 ± 0.03 | 0.55 ± 0.01 | 0.6 ± 0.05 |
| Visual penetration through stand (m) | 40 ± 1.47 | 25 ± 3.74 | 45 ± 1.23 |
| Stand density (trees ha−1) | 525 ± 11 | 664 ± 10 | 825 ± 8 |
Data are presented as the means ± SD.
Figure 3Flow diagram for on-site experimental protocol.
Total and dimensional scores of PRS.
| Scores of PRS | Dimensional Scores of PRS | ||||
|---|---|---|---|---|---|
| Being Away | Fascination | Extent | Compatibility | ||
| CF | 4.29 ± 1.06 | 5.01 ± 0.96 | 3.83 ± 1.02 | 4.81 ± 0.81 | 3.89 ± 0.81 |
| DF | 4.25 ± 1.12 | 3.99 ± 1.17 | 4.17 ± 1.13 | 4.36 ± 1.11 | 4.53 ± 0.97 |
| MF | 4.84 ± 0.95 | 4.74 ± 1.05 | 4.85 ± 0.96 | 4.73 ± 0.91 | 5.03 ± 0.82 |
| CK | 1.56 ± 1.13 | 1.23 ± 1.00 | 1.91 ± 1.29 | 1.24 ± 0.78 | 1.57 ± 1.05 |
Data are presented as the means ± SD. CF = coniferous forest, DF = deciduous forest, MF = mixed forest, CK = city site.
Figure 4Comparison of the dimensional scores of PRS in four environmental sites. Data are presented as the means ± SEs. CK = city site, CF = coniferous forest, DF = deciduous forest, MF = mixed forest.
Mean and standard deviation (SD) of physiological parameters (systolic blood pressure (SBP), diastolic blood pressure (DBP), and heart rate (HR)) in the four experimental sites.
| City Site | Mixed Forest | Deciduous Forest | Coniferous Forest | ||||||
|---|---|---|---|---|---|---|---|---|---|
| Mean | SD | Mean | SD | Mean | SD | Mean | SD | ||
| SBP | Baseline (TO) | 113.30 | 4.71 | 117.10 | 4.44 | 114.33 | 6.48 | 116.07 | 5.35 |
| 116.13 | 7.21 | 107.10 | 7.88 | 108.72 | 7.30 | 113.73 | 7.19 | ||
| DBP | Baseline (TO) | 66.70 | 4.24 | 70.77 | 5.12 | 68.63 | 5.50 | 71.30 | 4.69 |
| 68.50 | 5.90 | 64.70 | 6.74 | 65.27 | 5.731 | 66.60 | 5.83 | ||
| HR | Baseline (TO) | 79.70 | 4.09 | 82.07 | 3.61 | 78.60 | 3.38 | 80.63 | 3.01 |
| 81.17 | 4.60 | 76.92 | 5.66 | 75.90 | 4.65 | 78.53 | 5.67 | ||
Figure 5Comparison of reduction in values of SBP and DBP as well as HR in the four experimental sites. Data are presented as the means ± SEs. CK = urban site, CF = coniferous forest, DF = deciduous forest, MF = mixed forest.
Mean and standard deviation (SD) of psychological parameters (ROS, SVS, and WEMWBS) in the four experimental sites.
| City Site | Mixed Forest | Deciduous Forest | Coniferous Forest | ||||||
|---|---|---|---|---|---|---|---|---|---|
| Mean | SD | Mean | SD | Mean | SD | Mean | SD | ||
| ROS | Baseline (TO) | 2.03 | 0.75 | 2.21 | 0.78 | 2.15 | 0.76 | 1.79 | 0.81 |
| 1.51 | 0.97 | 4.24 | 1.31 | 4.14 | 1.21 | 4.01 | 1.27 | ||
| SVS | Baseline (TO) | 1.83 | 1.03 | 1.74 | 0.88 | 1.80 | 0.95 | 1.97 | 0.91 |
| 0.95 | 0.72 | 4.60 | 1.07 | 4.35 | 1.22 | 3.94 | 1.42 | ||
| WEMWBS | Baseline (TO) | 1.86 | 0.710 | 1.93 | 0.715 | 2.01 | 0.72 | 1.89 | 0.73 |
| 1.57 | 1.04 | 2.95 | 0.89 | 2.95 | 0.92 | 3.02 | 0.87 | ||
Figure 6Comparison of the increased values of ROS, SVS, and WEMWBS in the four experimental sites. Data are presented as the mean ± SEs. CK = city site, CF = coniferous forest, DF = deciduous forest, MF = mixed forest.
Spearman rank correlations between the PRS and four sub-scales of PRS and the SBP, DBP, and HR.
| PRS | Four Sub-Scales of PRS | |||||
|---|---|---|---|---|---|---|
| Being Away | Fascination | Extent | Compatibility | |||
| SBP | Spearman Correlation | −0.506 ** | −0.370 ** | −0.468 ** | −0.327 ** | −0.506 ** |
| Sig. (two-tailed) | 0.000 | 0.000 | 0.000 | 0.000 | 0.000 | |
| DBP | Spearman Correlation | −0.352 ** | −0.328 ** | −0.345 ** | −0.373 ** | −0.352 ** |
| Sig. (two-tailed) | 0.000 | 0.000 | 0.000 | 0.000 | 0.000 | |
| HR | Spearman Correlation | −0.347 ** | −0.258 ** | −0.328 ** | −0.357 ** | −0.347 ** |
| Sig. (two-tailed) | 0.000 | 0.000 | 0.000 | 0.000 | 0.000 | |
** Correlation is significant at the p < 0.01 level (two-tailed).
Spearman rank correlations between the PRS and four sub-scales of PRS and the ROS, SVS, and WEMWBS.
| PRS | Four Sub-Scales of PRS | |||||
|---|---|---|---|---|---|---|
| Being Away | Fascination | Extent | Compatibility | |||
| ROS | Spearman Correlation | 0.541 ** | 0.737 ** | 0.570 ** | 0.538 ** | 0.541 ** |
| Sig. (two-tailed) | 0.000 | 0.000 | 0.000 | 0.000 | 0.000 | |
| SVS | Spearman Correlation | 0.708 ** | 0.678 ** | 0.673 ** | 0.542 ** | 0.708 ** |
| Sig. (two-tailed) | 0.000 | 0.000 | 0.000 | 0.000 | 0.000 | |
| WEMWBS | Spearman Correlation | 0.458 ** | 0.669 ** | 0.535 ** | 0.502 ** | 0.458 ** |
| Sig. (two-tailed) | 0.000 | 0.000 | 0.000 | 0.000 | 0.000 | |
** Correlation is significant at the p < 0.01 level (two-tailed).