| Literature DB >> 28362327 |
Genxiang Mao1, Yongbao Cao2, Bozhong Wang3, Sanying Wang4, Zhuomei Chen5, Jirong Wang6, Wenmin Xing7, Xiaoxu Ren8, Xiaoling Lv9, Jianhua Dong10, Shasha Chen11, Xiuyuan Chen12, Guofu Wang13, Jing Yan14.
Abstract
<b/> The aim of the current study was to test the hypothesis that forest bathing would be beneficial for elderly patients with chronic heart failure (CHF) as an adjunctive therapy. Two groups of participants with CHF were simultaneously sent to the forest or an urban control area for a four-day trip, respectively. Subjects exposed to the forest site showed a significant reduction of brain natriuretic peptide (BNP) in comparison to that of the city group and their own baseline levels. The values for the cardiovascular disease related pathological factors, including endothelin-1 (ET-1), and constituents of the renin-angiotensin system (RAS), including renin, angiotensinogen (AGT), angiotensin II (ANGII), and ANGII receptor type 1 or 2 (AT1 or AT2) in subjects exposed to the forest environment were lower than those in the urban control group. Obviously, a decreased level of inflammatory cytokines and improved antioxidant function was observed in the forest group rather than in the city group. The assessment of the profile of mood states (POMS) indicated that the negative emotional mood state was alleviated after forest bathing. As anticipated, a better air quality in the forest site was observed according to the detection of PM2.5 (particulate matter <2.5 μm) and negative ions. These results provided direct evidence that forest bathing has a beneficial effect on CHF patients, and thus may pave the way for potential development of forest bathing as an effective adjunctive therapy on cardiovascular disorders.Entities:
Keywords: PM2.5; chronic heart failure; forest bathing; inflammation
Mesh:
Substances:
Year: 2017 PMID: 28362327 PMCID: PMC5409569 DOI: 10.3390/ijerph14040368
Source DB: PubMed Journal: Int J Environ Res Public Health ISSN: 1660-4601 Impact factor: 3.390
Clinical characteristics of the participants (mean ± SD or number (%)).
| Forest Group ( | City Group ( | ||
|---|---|---|---|
| Age (years) | 72.86 ± 5.85 | 70.70 ± 3.68 | 0.341 |
| Gender (M/F) | 12/11 | 7/3 | 0.455 * |
| Hight (cm) | 162.45 ± 8.56 | 163.50 ± 9.01 | 0.755 |
| Weight (kg) | 65.18 ± 7.40 | 65.20 ± 10.90 | 0.996 |
| BMI (kg/m2) | 24.72 ± 2.38 | 24.35 ± 3.45 | 0.722 |
| SBP (mmHg) | 141.4 ± 15.1 | 142.5 ± 15.7 | 0.849 |
| DBP (mmHg) | 80.6 ± 10.5 | 75.9 ± 14.1 | 0.296 |
| HR (bmp) | 76.2 ± 11.5 | 69.0 ± 12.2 | 0.113 |
| New York Heart Association Class | 0.845 * | ||
| I | 1 (4.3%) | 1 (10.0%) | |
| II | 16 (69.6%) | 6 (60.0%) | |
| III | 6 (26.1%) | 3 (30.0%) |
* Fisher’s Exact Test was used; others were analyzed by using the independent-samples t-test. BMI, body mass index; SBP, systolic blood pressure; DBP, diastolic blood pressure; HR, heart rate.
Figure 1Location of the two experimental sites. Huangtan Forest Park is located in Pan’an County, Zhejiang Province, China. It is about 160 km from the urban experimental site, which is situated in the downtown area of Hangzhou, a city near Shanghai.
Figure 2The experimental protocol for subjects exposed to the forest or city environment.
Figure 3Effect of forest bathing on change of CHF biomarkers including brain natriuretic peptide (BNP) and NT-proBNP in the experimental subjects (forest group (n = 23) and control group (n = 10)). ** p < 0.01; ## p < 0.01, analyzed by the Kruskal-Wallis test, followed by the Dunn-Bonferroni test.
Figure 4Effect of forest bathing on change for the endothelin-1 (ET-1) production and components of the renin-angiotensin system (RAS). Renin, angiotensinogen (AGT), angiotensin II (Ang II), angiotensin II type 1 receptor (AT1), and angiotensin II type 2 receptor (AT2) of subjects were evaluated before and after the experiment (forest group (n = 23) and control group (n = 10)). ** p < 0.01, # p < 0.05, analyzed by the Kruskal-Wallis test followed by the Dunn-Bonferroni test.
Figure 5Effect of forest bathing on serum levels of pro-inflammatory indicators. Interleukin-6 (IL-6), tumor necrosis factor α (TNF-α), and C-reactive protein (CRP) of subjects were evaluated before and after the experiment in the forest bathing group (n = 23) as well as in the urban control group (n = 10). * p < 0.05, analyzed by the Kruskal-Wallis test followed by the Dunn-Bonferroni test.
Figure 6Effect of forest bathing on human oxidative stress alteration reflected by total superoxide dismutase (T-SOD) activity and malondialdehyde (MDA) level in the experimental subjects (forest group (n = 23) and control group (n = 10). * p < 0.05; # p < 0.05, analyzed by the Kruskal-Wallis test followed by the Dunn-Bonferroni test.
Figure 7Profile of mood states (POMS) evaluation of subjects exposed to forest (n = 23) or city environments (n = 10). The standard version of POMS including negative subscales (T: tension-anxiety; D: depression-dejection; A: anger-hostility; F: fatigue-inertia; and C: confusion-bewilderment) and a positive subscale (V: vigor-activity) was used to evaluate the subjects’ mood changes before and after the experiment. * p < 0.05, # p < 0.05, analyzed by the Kruskal-Wallis test, followed by the Dunn-Bonferroni test.
Quantitative detection of air quality in the two experimental sites (mean ± SD).
| City Site | Forest Site | ||
|---|---|---|---|
| Negative ion (cm−3) | 397.6 ± 230.8 | 11,575.0 ± 1399.7 | 0.003 * |
| PM2.5 (μg/m3) | 160.1 ± 41.3 | 9.4 ± 4.1 | <0.001 |
| T (°C) | 29.3 ± 4.3 | 25.2 ± 2.5 | 0.040 |
| RH (%) | 51.8 ± 15.2 | 77.3 ± 3.7 | 0.042 |
Note: * Mann-Whitney U test was used; others were analyzed by using the independent-samples t-test. PM2.5, particulate matter <2.5 μm in aerodynamic diameter; T, temperature; RH, relative humidity.