CC BY
35
#
Вестник РУДН. Серия: АГРОНОМИЯ И ЖИВОТНОВОДСТВО
RUDN Journal of Agronomy and Animal Industries
2019; 14(2):154—161
http://agrojournal.rudn.ru
БОТАНИКА BOTANY
DOI: 10.22363/2312-797X-2019-14-2-154-161
Research article
Ecological functions of forest stands in urbanized environment of Moscow
Nikolay N. Dubenok, Valeriy V. Kuzmichev*, Alexandr V. Lebedev
Russian State Agrarian University — Moscow Timiryazev Agricultural Academy, Moscow, Russian Federation Corresponding author: [email protected]
Abstract. In urban forests, stock production is not the main function of stands. Carbon sequestration, the release of oxygen and phytoncides, dust precipitation, and changing wind conditions et al. are the main environmental functions. Phyto-organic substances emitted by trees help to reduce the number of microorganisms in air make the air cleaner and fresher. The purpose of the study is to evaluate the ecological functions of forest stands based on long-term observations of the forest stands of the Forest Experimental District of the Russian State Agrarian University — Moscow Timiryazev Agricultural Academy. The study used data about 7 permanent trial plots in natural pine stands, 7 — in pine plantations (planting density — 32 000 trees per 1 ha), 13 — in larch plantations (planting density — 700—4000 trees per 1 ha), 8 — in oak stands (natural stands and plantations) and 9 — in birch stands (natural stands and plantations). For a year, 1 ha of forest covered area produces 10 tons of oxygen, and the entire territory of the Forest Experimental District produces about 2.5 thousand tons of oxygen. In the year, the stands of the Forest Experimental District absorb about 3 thousand tons of carbon dioxide. The forest stands of the Forest Experimental District are capable of precipitating 135 tons of dust and they emit about 130 tons of phytoncides into the air during the growing season. Under urban conditions, forest stands are subject to the influence of negative factors: emissions from industrial enterprises and transport, recreational loads, disruption of natural conditions, and many others. Negative factors lead to a decrease in the performance of ecological functions. Therefore, in urban forests it is necessary to carry out silvicultural measures to increase the sustainability and productivity of stands.
Key words: urbanized environment, ecological functions, forest stands
Introduction
In urban forests, stock production is not the main function of stands. Carbon sequestration, the release of oxygen and phytoncides, dust precipitation, and changing wind conditions et al. are the main environmental functions. Phyto-organic substances
© Dubenok N.N., Kuzmichev V.V., Lebedev A.V., 2019.
This work is licensed under a Creative Commons Attribution 4.0 International License ica^Bi^* https://creativecommons.Org/licenses/by/4.0/
emitted by trees help to reduce the number of microorganisms in the air, make the air cleaner and fresher. In addition, urban forests are the resting place of citizens. The numerical evaluation of the ecological functions of forest stands can be calculated using biological productivity data. Biological productivity is an integral indicator characterizing the intensity of biochemical processes occurring in trees.
In forest stands, the intensity of their ecological functions is changed with age. The long-term data of inventories of permanent trial plots show that the growth of forest stands does not take place according to the patterns that are reflected in numerous yield tables [1—5]. Therefore, the study of the dynamics of the ecological functions of forest stands on the basis of multiple observations on permanent trial plots is becoming especially important.
The purpose of the study was to evaluate the ecological functions of forest stands based on long-term observations of the forest stands of the Forest Experimental District of the Russian State Agrarian University — Moscow Timiryazev Agricultural Academy.
Materials and methods
The materials for the study were the inventory data of the permanent trial plots of the Forest Experimental District of the Russian State Agrarian University — Moscow Timiryazev Agricultural Academy. Forest Experimental District was located in the north of Moscow. According to the results of the forest inventory in 2009, the area of the Forest Experimental District was 248.7 ha, including 233.4 ha (93.8 %) covered with forests. Observations on permanent trial plot have been carried out for more than 100 years. The study used data about 7 permanent trial plots in natural pine stands, 7 — in pine plantations (planting density — 32 000 trees per 1 ha), 13 — in larch plantations (planting density — 700—4000 trees per 1 ha), 8 — in oak stands (natural stands and plantations) and 9 — in birch stands (natural stands and plantations).
Aligned rows of stands were used for the study [2, 3]. Average values for groups of permanent trial plots were given with a 95% confidence interval. The text for the average shows the standard error values. Oxygen productivity was determined from the calculation that the formation of 1 t of absolutely dry organic matter led to the release of 1393 kg of oxygen [6]. The amount of deposited carbon was calculated according to the conventional methods through a phytomass conversion factor of 0.5. The potential dust holding capacity was calculated through LAI [7] and data on the deposition of dust by the leaf surface of trees [8].
Results and discussion
Plants produce oxygen during the process of photosynthesis. Fig. 1 shows the production of oxygen by stands, calculated from the net primary production of phytomass. Natural pine stands (maximum 40 years — 10.9 ± 1.0 tha-1yr-1) and birch stands (maximum 60 years — 10.3 ± 0.8 tha-1yr-1) produce the least amount of oxygen. Pine plantations with a planting density of 32 000 plants per 1 ha produce more oxygen than natural pine stands. In pine plantations, the maximum value of oxygen production is reached at the age of 30 years (23.9 ± 0.6 tha-1yr-1). Larch stands for 120 years of growing show quite high values of oxygen production — 16.0 ± 1.1 tha-1yr-1.
Pine plantations
25
--Natural pine stands
--Larch
--Oak
--Birch
20
0
20 30 40 50 60 70 80 90 100 110 120
Age,year
Fig. 1. Oxygen productivity of forest stands and 95 % confidence interval
300 Pine plantations
- Natural pine stands
- Larch
0
20 30 40 50 60 70 80 90 100 110 120
Age,year
Fig. 2. Carbon sequestration in available phytomass and 95% confidence interval
Currently, the average daily value of oxygen production by the stands of the Forest Experimental District was 27 kgha-1. Tree stands produced the maximum amount of oxygen on favorable summer days. In winter, the amount of oxygen produced was minimal. In general, for a year, 1 ha of forest covered area produced 10 tons of oxygen,
and the entire territory of the Forest Experimental District produced about 2.5 thousand tons of oxygen.
In the process of photosynthesis, forest stands absorb atmospheric carbon dioxide. In conditions of increasing concentration of carbon dioxide in the atmosphere, the issue of carbon sequestration in the stands is important. In young stands, the largest amount of carbon is sequestered in pine plantations with a planting density of 32 000 trees per 1 ha (Fig. 2). Compared to other forest stands, larch stands sequester the largest amount of carbon. In 100 years available phytomass contains 222 ± 14 tha-1. Least of all carbon stock in natural pine stands (maximum 80 years — 81.3 ± 10.7 tha-1) and birch stands (maximum 60 years — 77.0 ± 8.7 tha-1).
At present, on average, 80 tons of carbon are contained in stands for 1 ha of forest area. In total, the stands of the Forest Experimental District contain about 20 thousand tons of carbon. The average daily value of carbon dioxide uptake by trees is 35 kgha-1. And in the year, the stands of the Forest Experimental District absorb about 3 thousand tons of carbon dioxide.
City air contains a large amount of dust and microorganisms. Crowns of trees contribute to the reduction of dust in the air. For example, dust content in Petrozavodsk squares is 300—500% less than the average in the city [9]. The dust holding capacity of trees depends on the leaf area and the morphological characteristics of the leaf. In the Forest Experimental District, up to 60—70 years, pine plantations with planting density 32 000 trees per 1 ha (maximum 30 years — 1375 ± 30 kgha-1) and oak stands (maximum 40 years — 873±57 kgha-1) had the greatest potential dust holding capacity (Fig. 3). After 70—80 years, larch stands had the greatest dust holding capacity (in 100 years — 853 ± 57 kgha-1).
1400
Pine plantations - Natural pine stands
1200
- Larch
- Oak
- Birch
1000
20 30 40 50 60 70 80 90 100 110 120
Age.year
Fig. 3. Potential dust holding capacity of forest stands and 95% confidence interval
On average, 1 ha of forest area of the Forest Experimental District is capable of precipitating 550 tons of dust. In general, forest stands of the Forest Experimental District are capable of precipitating 135 tons of dust, which is washed away with precipitation water into the soil.
In the conditions of cities, an important sanitary and hygienic indicator is the quantitative composition of air microflora. Forest stands emit phytoncides and are good regulators of air quality. The canopy of trees is a natural filter where dust particles and microorganisms linger. Under the action of volatile microorganisms die and the sediments are washed into the soil.
The volatile secretions of trees have a positive effect on the cardiovascular, respiratory, and nervous systems of humans, and contribute to an increase in immunity. There is extremely low percentage of people with respiratory diseases and nervous system disorders in conditions of forest area [10].
As a result of the enlarged assessment, the average daily release of phytoncides by forest stands of the Forest Experimental District is 3.7 kgha-1. The forest stands of the Forest Experimental District emit about 130 tons of phytoncides into the air during the growing season. This indicates a high antimicrobial activity of tree stands and their great importance for the local population.
Under urban conditions, forest stands are subject to the influence of negative factors: emissions from industrial enterprises and transport, recreational loads, disruption of natural conditions, and many others. Negative factors lead to a decrease in the performance of ecological functions. Therefore, it is necessary to carry out silvicultural measures in urban forests to increase the sustainability and productivity of stands.
Conclusions
The best oxygen-producing and carbon-sequestration functions were expressed in larch stands, which show high resistance to adverse factors in the conditions of the city. Least of all these functions were expressed in birch stands, which were characterized by a high decorative effect. In general, for a year, 1 ha of forest covered area produces 10 tons of oxygen, and the entire territory of the Forest Experimental District produced about 2.5 thousand tons of oxygen. During the year, the stands of the Forest Experimental District absorbed about 3 thousand tons of carbon dioxide.
Pine, oak and larch stands were characterized by a high dust holding capacity. In general, forest stands of the Forest Experimental District were capable of precipitating 135 tons of dust which was washed away with precipitation into the soil.
The forest stands of the Forest Experimental District emitted about 130 tons of phy-toncides into the air during the growing season. This indicates a high antimicrobial activity of tree stands and their great importance for the local population.
Under urban conditions, forest stands are subject to the influence of negative factors: emissions from industrial enterprises and transport, recreational loads, disruption of natural conditions, and many others. Negative factors lead to a decrease in the performance of ecological functions. Therefore, it is necessary to carry out silvicultural measures in urban forests to increase the sustainability and productivity of stands.
REFERENCES
1. Bogachev AV. Forest Taxation Researches. Moscow: VNIILM Publ.; 2007. (In Russ).
2. Dubenok NN, Kuzmichev VV, Lebedev AV. Analysis of ecological functions of birch and oak stands in the conditions of an urbanized environment based on the materials of long-term observations. Russian Agricultural Sciences. 2018; (5): 29—31. Available from: doi: 10.3103/S1068367418060046 (In Russ).
3. Dubenok NN, Kuzmichev VV, Lebedev AV. Growth and productivity of pine and larch stands under conditions of urban environment. Vestnik of Volga State University of Technology. Series: Forest. Ecology. Nature. 2018; (1):54—71. Available from: doi: 10.15350/2306-2827.2018.1.54 (In Russ).
4. Kuzmichev VV. Regularities of stand growth. Novosibirsk: Nauka Publ.; 1977. (In Russ).
5. Rogozin MV, Razin GS. Models of dynamics and modeling of tree stand development. Siberian Forest Journal. 2015; (2):55—70. (In Russ).
6. Liepa IY. Dynamics of wood stock: Forecasting and ecology. Riga: Zinatne Publ.; 1980. (In Russ).
7. Utkin AI, Ermolova LS, Utkina IA. Surface area of forest plants: essence, parameters, use. Moscow: Nauka Publ.; 2008. (In Russ).
8. Kretinin VM, Selyanina ZM. Retention of dust by the leaves of trees and shrubs and its accumulation in light chestnut soils under the forest belts. Soil science. 2006; (3):373—377. (In Russ).
9. Ioffe AO. Determination of the level of dust in the territory of Petrozavodsk. Basic research. 2014; (6-4): 753—759. (In Russ).
10. Artyuhovsky AK. Sanitary hygienic and medicinal properties of forest. Voronezh: VGU Publ.; 1985. (In Russ).
Article history:
Received: 5 March 2019 Accepted: 8 April 2019
About authors:
Dubenok Nikolay Nikolaevich — Academician of the Russian Academy of Sciences, Professor, Doctor of Sciences in Agriculture, Head of the Department of Agricultural Land Reclamation, Forestry and Land Management; 49, Timiryazevskaya st., Moscow, 127550, Russian Federation; e-mail: [email protected]
Kuzmichev Valeriy Vasilyevich — Professor, Doctor of Sciences in Biology, Senior Researcher at 'Forest Experimental Dacha'; 49, Timiryazevskaya st., Moscow, 127550, Russian Federation; e-mail: [email protected]
Lebedev Alexandr Vyacheslavovich — postgraduate student, of Agricultural Land Reclamation, Forestry and Land Management; 49, Timiryazevskaya st., Moscow, 127550, Russian Federation; e-mail: [email protected]
For citation:
Dubenok NN, Kuzmichev VV, Lebedev AV. Ecological functions of forest stands in urbanized environment of Moscow. RUDN Journal of Agronomy and Animal Industries. 2019; 14(2):154—161. doi: 10.22363/2312-797X-2019-14-2-154-161.
DOI: 10.22363/2312-797X-2019-14-2-154-161
Научная статья
Экологические функции древостоев в условиях урбанизированной среды на примере города Москвы
Н.Н. Дубенок, В.В. Кузьмичев*, А.В. Лебедев
Российский государственный аграрный университет — Московская сельскохозяйственная академия имени К.А. Тимирязева, Москва, Российская Федерация *[email protected]
Аннотация. В городских лесах продуцирование запаса не является главной функцией древостоев. Депонирование углерода, выделение кислорода и фитонцидов, осаждение пыли, изменение ветрового режима и другие являются основными экологическими функциями. Фитоорганические вещества, выделяемые деревьями, способствуют снижению количества микроорганизмов в воздухе, делают его чище и свежее. Цель исследования — оценка экологических функций древостоев по материалам многолетних наблюдений за насаждениями Лесной опытной дачи Российского государственного аграрного университета — Московская сельскохозяйственная академия имени К.А. Тимирязева. В исследовании использовались данные о 7 постоянных пробных площадях в естественных сосновых насаждениях, 7 — в культурах сосны (густота посадки — 32 000 деревьев на 1 га), 13 — в культурах лиственницы (густота посадки — 700—4000 деревьев на 1 га), 8 — в дубовых насаждениях (естественного и искусственного происхождения) и 9 — на березовых насаждениях (естественного и искусственного происхождения). За год 1 га покрытой лесом площади производит 10 тонн кислорода, а вся территория Лесной опытной дачи — около 2,5 тысяч тонн кислорода. В год древостои Лесной опытной дачи поглощают около 3 тысяч тонн углекислого газа. В целом древостои Лесной опытной дачи способны осаждать 135 тонн пыли и выделяют в воздух около 130 тонн фитонцидов в течение вегетационного периода. В городских условиях лесные насаждения подвержены влиянию негативных факторов: выбросов промышленных предприятий и транспорта, рекреационных нагрузок, нарушения природных условий и многих других. Негативные факторы приводят к снижению выполнения ими экологических функций. Поэтому в городских лесах необходимо проводить лесоводственные мероприятия для повышения устойчивости и продуктивности древостоев.
Ключевые слова: урбанизированная среда, экологические функции, древостои
БИБЛИОГРАФИЧЕСКИЙ СПИСОК
1. Богачёв А.В. Лесотаксационные исследования. М.: ВНИИЛМ, 2007. 344 с.
2. Дубенок Н.Н., Кузьмичев В.В., Лебедев А.В. Анализ экологических функций древостоев березы и дуба в условиях урбанизированной среды по материалам долгосрочных наблюдений // Российская сельскохозяйственная наука. 2018. № 5. C. 29—31. doi: 10.31857/ S250026270000632-0.
3. Дубенок Н.Н., Кузьмичев В.В., Лебедев А.В. Рост и продуктивность древостоев сосны и лиственницы в условиях городской среды // Вестник Поволжского государственного технологического университета. Серия: Лес. Экология. Природопользование. 2018. № 1. С. 54—71. doi: 10.15350/2306-2827.2018.1.54.
4. Кузьмичев В.В. Закономерности роста древостоев. Новосибирск: Наука, 1977. 160 с.
5. Рогозин М.В., Разин Г.С. Модели динамики и моделирование развития древостоев // Сибирский лесной журнал. 2015. № 2. С. 55—70.
6. Лиепа И.Я. Динамика древесных запасов: Прогнозирование и экология. Рига: Зинатне, 1980. 170 с.
7. Уткин А.И., Ермолова Л.С., Уткина И.А. Площадь поверхности лесных растений: сущность, параметры, использование. М.: Наука, 2008. 292 с.
8. Кретинин В.М., Селянина З.М. Задержание пыли листьями деревьев и кустарников и ее накопление в светло-каштановых почвах под лесными полосами // Почвоведение. 2006. № 3. С. 373—377.
9. Иоффе А.О. Определение уровня запыленности на территории г. Петрозаводска // Фундаментальные исследования. 2014. № 6-4. С. 753—759.
10. Артюховский А.К. Санитарно-гигиенические и лечебные свойства леса. Воронеж: Изд-во ВГУ, 1985. 104 с.
История статьи:
Поступила в редакцию: 5 марта 2019 г. Принята к публикации: 8 апреля 2019 г.
Об авторах:
Дубенок Николай Николаевич — академик РАН, профессор, доктор сельскохозяйственных наук, заведующий кафедрой сельскохозяйственных мелиораций, лесоводства и землеустройства, Российская Федерация, 127550, г. Москва, ул. Тимирязевская, д. 49; e-mail: [email protected]
Кузьмичев Валерий Васильевич — профессор, доктор биологических наук, старший научный сотрудник УНКЦ «Лесная опытная дача»; Российская Федерация, 127550, г. Москва, ул. Тимирязевская, д. 49; e-mail: [email protected]
Лебедев Александр Вячеславович — аспирант кафедры сельскохозяйственных мелиораций, лесоводства и землеустройства; Российская Федерация, 127550, г. Москва, ул. Тимирязевская, д. 49; e-mail: [email protected].
Для цитирования:
Dubenok N.N., Kuzmichev V.V., Lebedev A.V. Ecological functions of forest stands in urbanized environment of Moscow // Вестник Российского университета дружбы народов. Серия: Агрономия и животноводство. 2019. Т. 14. № 2. С. 154—161. doi: 10.22363/2312-797X-2019-14-2-154-161.
