Chemical Composition of Atmospheric Air in Nemoral Scots Pine Forests and Submountainous Beech Forests: The Potential Region for the Introduction of Forest Therapy
Abstract
:1. Introduction
2. Materials and Methods
2.1. Description of Sampling Area and Location of Sampling Points
2.2. Collection of Organic Compound Samples and Screening Measurements of Ozone and Atmospheric Aerosol
2.3. Laboratory Analysis—Analytical Procedure, Extraction/Liberation, and Final Determination Conditions
2.4. Statistical Analysis
3. Results and Discussion
3.1. Meteorological Conditions over the Sampling Areas
3.2. Representatives of Volatile Organic Compounds Determined in the Investigated Forest Areas
3.3. Aerosol Concentration in Forest Air
4. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
Appendix A
Equipment Type Employed to Perform Analytes Thermal Extraction | ||
---|---|---|
System Acronym | TD-GC-FID | TD-GC-MS |
Type of thermal desorption unit | Markes’ Series 2 Thermal Desorption System; UNITY/TD-100 | Markes Unity v.2 |
Analyte sampling device | Sorption tubes filled with Tenax TA (O.D. × L ¼ in. × 3 ½ in.) | |
1st stage of thermal desorption process—working conditions | ||
Heating temperature | 290 °C | |
Inert gas (He) flow rate during the desorption stage | 50 mL·min−1 | |
Heating time | 15 min | |
Microtrap composition and temperature | Microtrap dedicated to measuring monoterpene compounds filled with Tenax TA and Carbotrap; 0 °C | |
2nd stage of thermal desorption process—working conditions | ||
Microtrap temperature (ballistic heating mode) | 300 °C | |
Microtrap heating time | 5 min | |
Flow rate of the inert gas (He) through the microtrap to the chromatographic column | 2.0 mL·min−1 | 1.0 mL·min−1 |
Final determination system working parameters | ||
Type of applied gas chromatography | Agilent 7820A GC | Agilent Technologies 6890 |
Detector | Flame ionization detector, detector temp. 280 °C | Mass spectrometer (5873 Network Mass Selective Detector, Agilent Technologies); transmission line temp. of GC-MS: 285 °C; ion source temp.: 230 °C; quadrupole mass analyzer temp.: 150 °C |
TD-GC transfer line temperature | 160 °C | |
Capillary column type | DB-1 (J&W, USA); 30 m × 320 µm × 5 μm | HP-1 ms (J&W, USA); 30 m × 0.25 µm × 1 μm |
Helium gas (flow rate) | 2.0 mL·min−1 | 1.0 mL·min−1 |
Oven temperature program | 50 °C for 1 min; 7 °C·min−1 up to 260 °C and held for 6 min | |
Data processing system | OpenLAB CDS ChemStation Workstation VL | Chemstation |
Retention Index/Chemical Name | Scent/Odor Quality | Chemical Structure | Formula |
---|---|---|---|
RI 950 α-Pinene | fir needle-like, resin-like | Bicyclic | C10H16 |
RI 972 Camphene | terpene-like, woody type | Bicyclic | C10H16 |
RI 987 β-Pinene | woody-green pine-like | Bicyclic | C10H16 |
RI 1026 3-Carene | terpene-like | Bicyclic | C10H16 |
RI 1041 Limonene | citrus-like | Cyclic, | C10H16 |
RI 1059 γ-Terpinene | petrol-like | Cyclic, | C10H16 |
RI 1089 Terpinolene | pine-like | Cyclic | C10H16 |
RI 1160 Camphor | camphor-like | Ketone, cyclic | C10H16 |
RI 1193 α-Terpineol | flowery, citrus-like, pleasant odor similar to lilac | Alcohol, cyclic | C10H18O |
RI 1240 Carvone | mint-like, caraway-like | Ketone | C10H14O |
RI 1356 Geranyl Acetate | pleasant floral or fruity rose aroma | Ester, linear | C12H20O2 |
RI 1448 Farnesene/Humulene | sweet, flowery/balsamic vinegar-like/woody type | Linear/cyclic, sesquiterpene | C15H24 |
RI 1536 Nerolidol/Farnesol | citrus-like, flowery | Alcohol, linear, sesquiterpene | C15H26O |
RI 1566 Germacene B | woody type odor | Cyclic, sesquiterpene | C15H24 |
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Forest District Units | Coordinates (°) | Area (ha) | SC (%) | Admixture Species | Age (Years) | UU (%) | H (m) |
---|---|---|---|---|---|---|---|
Hu27a | N50.14072 E22.03605 | 7.51 | 100P | Q, Pi, A, F, C | 89 | 70 | 25 |
Hu42f | N50.13173 E22.02485 | 8.53 | 100P | B | 77 | 20 | 21 |
Hu59c | N50.12437 E22.00373 | 18.17 | 100P | Q, B | 78 | 30 | 22 |
Kl204f | N50.14303 E21.52324 | 7.72 | 90F; 10Ac | Pi, C | 79 | 10 | 27 |
Kl213g | N50.14227 E21.53394 | 2.50 | 70F; 30Q | - | 76 | 10 | 29 |
Kl219d | N50.14136 E21.52017 | 4.29 | 80F; 20Q | Ac, C | 86 | 30 | 29 |
Date | Forest District Units | Land Field Measurements | Data from Meteo Station Rzeszów-Jasionka | ||||||
---|---|---|---|---|---|---|---|---|---|
T (°C) (avg.) | H (%) (avg.) | Ozone (avg.) * (µg·m−3) | Ozone (Min–Max) (µg·m−3) | AP (hPa) | T (°C) (avg.) | H (%) (avg.) | W (km/h) (avg.) | ||
17.06 | Hu27a | 21.1 | 75.1 | <LOQ | <LOQ | 1009 | 20 | 83 | 7 |
Hu42f | 24.3 | 64.5 | <LOQ | <LOQ | 1008 | 22 | 73 | 7 | |
Hu59c | 23.8 | 64.9 | <LOQ | 19–335 | 1008 | 23 | 69 | 15 | |
18.06 | Kl204f | 22.3 | 76.1 | <LOQ | 19–39 | 1008 | 19 | 94 | 6 |
Kl213g | 20.7 | 82.9 | <LOQ | <LOQ | 1008 | 23 | 69 | 22 | |
Kl219d | 23.9 | 71.3 | <LOQ | <LOQ | 1007 | 24 | 65 | 20 | |
15.07 | Hu27a | 20.5 | 51.6 | <LOQ | 19–270 | 1015 | 20 | 60 | 7 |
Hu42f | 22.1 | 49.6 | 19 | 19–510 | 1014 | 22 | 50 | 13 | |
Hu59c | 24.6 | 42.4 | <LOQ | 19–195 | 1014 | 24 | 41 | 0 | |
Urban area | 26.0 | 36.5 | 19 | 19–622 | 1014 | 23 | 41 | 6 | |
16.07 | Kl219d | 20.3 | 69.4 | <LOQ | <LOQ | 1012 | 21 | 64 | 13 |
Kl213g | 22.6 | 53.5 | <LOQ | <LOQ | 1012 | 23 | 53 | 20 | |
Kl204f | 22.7 | 57.3 | <LOQ | 19–19 | 1012 | 23 | 61 | 22 | |
Urban area | 24.3 | 52.9 | 19 | 19–409 | 1012 | 22 | 60 | 26 | |
11.08 | Hu27a | 24.2 | 69.9 | <LOQ | <LOQ | 1019 | 23 | 73 | 2 |
Hu42f | 27.5 | 58.7 | <LOQ | <LOQ | 1019 | 27 | 54 | 6 | |
Hu59c | 28.4 | 51.0 | <LOQ | <LOQ | 1018 | 27 | 45 | 9 | |
12.08 | Kl219d | 19.1 | 78.3 | <LOQ | <LOQ | 1020 | 20 | 68 | 4 |
Kl213g | 21.5 | 68.7 | <LOQ | <LOQ | 1020 | 23 | 57 | 13 | |
Kl204f | 23.1 | 61.7 | <LOQ | 19–158 | 1020 | 24 | 41 | 13 | |
22.09 | Hu27a | 15.7 | 70.6 | <LOQ | <LOQ | 1019 | 14 | 82 | 2 |
Hu42f | 19.1 | 64.0 | <LOQ | <LOQ | 1018 | 20 | 56 | 13 | |
Hu59c | 22.1 | 54.9 | <LOQ | <LOQ | 1018 | 23 | 50 | 13 | |
23.09 | Kl219d | 16.2 | 80.0 | <LOQ | <LOQ | 1012 | 17 | 72 | 4 |
Kl213g | 20.8 | 62.4 | <LOQ | <LOQ | 1012 | 23 | 50 | 15 | |
Kl204f | 23.5 | 51.3 | <LOQ | <LOQ | 1011 | 25 | 44 | 15 |
Chemical Compound | CAS No. | Formula | Range of LRI on DB-1 for Investigated Samples Based on GC-FID Analysis | Range of LRI on HP-1 MS for Investigated Samples Based on GC-MS Analysis | Range of LRI Based on Literature Data on Similar GC Column (a) |
---|---|---|---|---|---|
α-Pinene | 80-56-8 | C10H16 | 949–956 | 940–946 | 927–932 |
Camphene | 79-92-5 | C10H16 | 969–975 | 955–960 | 940–946 |
β-Pinene | 127-91-3 | C10H16 | 996–999 | 982–987 | 969–974 |
3-Carene | 13466-78-9 | C10H16 | 1025–1031 | 1014–1020 | 1002–1004 |
Limonene | 5989-27-5 | C10H16 | 1039–1045 | 1031–1036 | 1024–1026 |
γ-Terpinene | 99-85-4 | C10H16 | 1064–1070 | 1057–1062 | 1054–1056 |
Terpinolene | 586-62-9 | C10H16 | 1101–1106 | 1082–1086 | 1085–1090 |
Camphor | 464-49-3 | C10H16O | 1160–1166 | 1158–1063 | 1141–1148 |
α-Terpineol | 98-55-5 | C10H18O | 1182–1188 | 1170–1176 | 1186–1194 |
Carvone | 99-49-0 | C10H14O | 1248–1254 | 1231–1236 | 1239–1248 |
Geranyl Acetate | 105-87-3 | C12H20O2 | 1361–1367 | 1363–1369 | 1379–1385 |
Farnesene/Humulene | 6753-98-6 | C15H24 | 1474–1480 | 1443–1450 | 1440–1452 |
Nerolidol/Farnesol | 7212-44-4 | C15H26O | 1531–1537 | 1527–1533 | 1531–1542 |
Germacene B | 15423-57-1 | C15H24 | 1561–1568 | 1558–1563 | 1559–1565 |
Sampling Date | TVOC (µg/m3) | ∑TERPENES (µg/m3) | Benzene (µg/m3) | Toluene (µg/m3) | Ethylbenzene (µg/m3) | p, m-Xylene (µg/m3) | ΣBTEX (µg/m3) | |
---|---|---|---|---|---|---|---|---|
Hu 27a | 17 June 2020 | 70.9 | 39.5 | 0.098 | 0.152 | <LOQ | <LOQ | 0.25 |
Hu 27a | 15 July 2020 | 65.7 | 30.0 | <LOQ | 0.151 | <LOQ | 0.045 | 0.20 |
Hu 27a | 11 August 2020 | 37.0 | 13.9 | <LOQ | 0.079 | <LOQ | <LOQ | 0.08 |
Hu 27a | 22 September 2020 | 17.9 | 5.2 | 1.011 | 7.469 | <LOQ | 0.993 | 9.5 |
Hu 42f | 17 June 2020 | 98.9 | 29.7 | 0.469 | 9.102 | <LOQ | <LOQ | 9.6 |
Hu 42f | 15 July 2020 | 59.8 | 30.7 | <LOQ | <LOQ | <LOQ | <LOQ | <LOQ |
Hu 42f | 11 August 2020 | 57.8 | 22.1 | 0.346 | 0.060 | <LOQ | <LOQ | 0.41 |
Hu 42f | 22 September 2020 | 46.5 | 10.8 | 0.571 | 11.961 | 2.967 | 0.349 | 16 |
Hu 59c | 17 June 2020 | 141.0 | 45.3 | 0.934 | 18.586 | <LOQ | <LOQ | 19 |
Hu 59c | 15 July 2020 | 58.6 | 17.4 | <LOQ | <LOQ | <LOQ | <LOQ | <LOQ |
Hu 59c | 11 August 2020 | 79.7 | 22.8 | <LOQ | <LOQ | <LOQ | 0.192 | 0.19 |
Hu 59c | 22 September 2020 | 50.8 | 15.5 | 0.358 | 0.037 | <LOQ | 0.843 | 1.2 |
Kl 204f | 18 June 2020 | 64.8 | 30.9 | 2.094 | 1.983 | <LOQ | 2.295 | 6.4 |
Kl 204f | 19 July 2020 | 56.0 | 25.1 | 0.623 | <LOQ | <LOQ | 0.306 | 0.93 |
Kl 204f | 12 August 2020 | 49.1 | 16.0 | <LOQ | 2.297 | 1.343 | 1.390 | 5.0 |
Kl 204f | 23 September 2020 | 89.8 | 16.5 | <LOQ | <LOQ | <LOQ | <LOQ | <LOQ |
Kl 213g | 18 June 2020 | 201.5 | 44.4 | 2.141 | 0.937 | <LOQ | 2.961 | 6.0 |
Kl 213g | 19 July 2020 | 311.8 | 27.4 | <LOQ | 0.910 | 0.369 | 1.053 | 2.3 |
Kl 213g | 12 August 2020 | 137.2 | 20.9 | 0.965 | 0.184 | <LOQ | 1.870 | 3.0 |
Kl 213g | 23 September 2020 | 250.1 | 27.3 | 2.712 | 0.011 | <LOQ | 1.834 | 4.56 |
Kl 219d | 18 June 2020 | 263.6 | 73.7 | 0.237 | 0.646 | 0.641 | 0.344 | 1.87 |
Kl 219d | 19 July 2020 | 117.9 | 59.3 | 0.563 | 0.084 | 0.040 | 0.519 | 1.21 |
Kl 219d | 12 August 2020 | 46.0 | 18.2 | <LOQ | 0.209 | <LOQ | <LOQ | 0.21 |
Kl 219d | 23 September 2020 | 49.5 | 26.8 | 0.517 | 0.074 | <LOQ | 0.094 | 0.68 |
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Dudek, T.; Marć, M.; Zabiegała, B. Chemical Composition of Atmospheric Air in Nemoral Scots Pine Forests and Submountainous Beech Forests: The Potential Region for the Introduction of Forest Therapy. Int. J. Environ. Res. Public Health 2022, 19, 15838. https://doi.org/10.3390/ijerph192315838
Dudek T, Marć M, Zabiegała B. Chemical Composition of Atmospheric Air in Nemoral Scots Pine Forests and Submountainous Beech Forests: The Potential Region for the Introduction of Forest Therapy. International Journal of Environmental Research and Public Health. 2022; 19(23):15838. https://doi.org/10.3390/ijerph192315838
Chicago/Turabian StyleDudek, Tomasz, Mariusz Marć, and Bożena Zabiegała. 2022. "Chemical Composition of Atmospheric Air in Nemoral Scots Pine Forests and Submountainous Beech Forests: The Potential Region for the Introduction of Forest Therapy" International Journal of Environmental Research and Public Health 19, no. 23: 15838. https://doi.org/10.3390/ijerph192315838