The coenotic role of acer negundoin forestsdominated by salixalbain the valley of Pina river (Belarus)

Размещено на http://www.allbest.ru/

The coenotic role of acer negundoin forestsdominated by salixalbain the valley of Pina river (Belarus)

M.N. Yakhnovets

Master of Biol. Sc.¹

E.O. Yurchenko

, Cand. of Biol. Sc.

Associate Professor of the Department

of Biotechnology^{1 1}Polessky State University, Pinsk, Republic of Belarus

Objective of the research was assessing the influence of A. negundo invasion on the coenotic structure of willow river valley forests in conditions of Belarusian Polesie.

Materials and methods. The structure and floristic composition of communities were studied by permanent sample plot, forest valuation, Ramensky and Raunkiaer methods, on 400 m²plots.

Results. All studied communities belong to Salix alba-Rubuscaesius association, and had up to 33/100 m² trees of A. negundo older than 3 years, with the total trunk volume of A. negundo up to 4.75 m³/100 m². With the increase of A. negundo projection coverage on a plot from 0-13% to 25-46%, Shannon diversity index (SDI) for vascular plants declined from 3.2 -3.3 to 2.7-3.0. For the species of lower community level (living ground cover), SDI = 3.1 on the plot without A. negundo trees, and SDI = 2.6 on the plot with the highest A. negundo concentration. The light intensity under A. negundo crowns was 3 -8 times lower, than under S. alba. On 5 sample plots 59 vascular plant species were recorded, of which 6 herbaceous species had various degree of gravitation or preference to the crown projections of A. negundo.

Conclusion. The communities of Salix alba-Rubuscaesius association are favourable for the propagation and growth of A. negundo. Development of A. negundo simplifies the coenotic flora. Along with this negative effect, the possible positive effects of A. negundo growth are: saving soil humidity, prevention of soil erosion, accumulating humus, protecting the neighbouring water bodies.

What this paper adds It was stated for Salix alba forest communities, that Shannon diversity index for vascular plant coenotic flora decreased with the increase of A. negundo tree concentration. The correlation between A. negundoprojection coverage and number of vascular plant species in community was calculated (r = -0.81). The plants gravitating to A. negundo crown projections (6 species) and avoiding them (8 species) were stated by Raunkiaer 1 m² plot method.

Keywords: community cluster analysis, community mosaics, crown shadow effect, Drude abundance, Negundoaceroides, Pripyat' Polesie, tree stand formula.

ЯХНОВЕЦ М.Н.

магистр биологических наук¹

ЮРЧЕНКО Е.О., канд. биол. наук, доцент кафедры биотехнологии¹

^{1Полесский государственный университет, г. Пинск, Республика Беларусь}

ЦЕНОТИЧЕСКАЯ РОЛЬ ACERNEGUNDOВ ЛЕСАХ С ПРЕОБЛАДАНИЕМ SALIXALBAВ ДОЛИНЕ РЕКИ ПИНА (БЕЛАРУСЬ)

Цель исследования - оценка влияния инвазии Acernegundoна ценотическую структуру долинно - речных ивовых лесов в условиях Белорусского Полесья.

Материалы и методы исследования. Использованы: метод постоянных пробных площадей (по 400 м² каждая), методы лесной таксации, определение проективного покрытия и обилия видов по Раменскому, Раункиеру и Друде.

Результаты. Все изученные сообщества представляют ассоциацию Salixalba-Rubuscaesius. Максимальная концентрация A. negundoв них достигала 33 дерева старше 3 лет на 100 м², с запасом древесины до 4.75 м³/100 м². С увеличением проективного покрытия клена на площадках от 0-13% до 25-46% индекс разнообразия Шеннона для ценофлоры сосудистых растений уменьшался с 3.2-3.3 до 2.7-3.0. Для живого напочвенного покрова этот индекс составлял от 2.6 (сообщество с максимальной концентрацией клена) до 3.1 (сообщество без деревьев A. negundo). Освещенность под кронами клена была в 3-8 раз меньше, чем под кронами ивы белой. Всего на 5-ти площадках отмечено 59 видов сосудистых растений, из которых 6 видов имели различную степень тяготения к проекциям крон A. negundo.

Заключение. Сообщества ассоциации Salixalba-Rubuscaesiusблагоприятны для размножения и развития A. negundo. Массовое развитие A. negundoв них упрощает ценотическую флору и создает мозаику. Наряду с негативным эффектом данной инвазии допускается, что существуют позитивные эффекты развития A. negundo: сохранение влаги в почве, накопление гумуса, предотвращение почвенной эрозии, водоохранная роль.

Научная новизна статьи

Впервые количественно изучена связь между видовым разнообразием (индекс Шеннона) и видовым богатством сообществ с доминированием Salixalba,в зависимости от концентрации деревьев Acernegundoи их общего проективного покрытия. Методом Раункиера на 1 м² площадках установлены виды растений, которые в разной степени предпочитают проекцию кроны A. negundo(6 видов) или избегают A. negundo(8 видов).

Ключевые слова: кластерный анализ сообществ, мозаичность структуры фитоценоза, Припят-ское Полесье, прирост деревьев, формула древостоя, эффект затенения, Negundoaceroides.

Introduction

acernegundo river willow forest

The vegetation cover, both vegetation and flora, are undergone strong changes in the areas of human agricultural and industrial activity. Such transformations are associated not only with the change in the abundances of indigenous species, but also with appearance and population progress (invasion) of alien species. There are the estimations that invasive plants development can lead to large economic losses [13]. One of such invasive species is boxelder maple - Acer negundo L. (NegundoaceroidesMoench), indigenout to east-central parts of North America, but now known in Europe and northern Asia [2; 22]. It is remarkable that the species is classified as invasive in North America too [17]. It is a middle-sized dioecious tree with wide crown, which starts to fructify in age of 6 years, and has soft, easily broken wood [22]. It is anemophilous and anemochoric species [12], but hydrochoric manner of seed spreading is much more effective, where it occurs [2; 22]. The plant has the tendency to form bush-like trees or (in conditions of limited light) trees with strongly inclined and curved trunks [11]; the trunk has a tendency to develop burls [10]. In general the species has high phenotypic plasticity in physiologically beneficial foliage allocation [18]. The species prefers well-watered, but enough drained soils and it is of middle shadow- tolerance [9]. In wild state the tree lives usually 65-70 years [8]. The ability of A. negundo to form regular arbuscular mycorrhiza was communicated [21]. In Eurasia the plant is usually not attacked by any serious disease or pest [7]. Initially A. negundo was brought in Europe and Asia with the aim to create ornamental and protective plantations, but later it started to spread as naturalized one [23]. In Belarus the species was brought to culture in XIX century [14]. Today, the activity on introduction of A. negundo in Belarus is prohibited on the legal base (the decree by the Ministry of Natural Resources and Environmental Protection of the Republic of Belarus No. 106 of 28 November 2008, with modifications according to the decree No. 35 of 28 October 2016).

More than 4000 populations (localities) are estimated to grow in Belarus, with the occupied area of more than 300 ha [15]. There were a special research devoted to geography and ecology of A. negundo near Dobrush, in southeast Belarus [3], showed the diversity of life forms of this species depending on the conditions of juvenile development, and the differences in ontogenetic structure of populations grown in different environmental conditions.

The aim of this work was assessing of the influence of A. negundo invasion on the coenotic structure of Sa/ix-dominated river valley forests in conditions of Belarusian Polesie.

Material and methods.The field research was carried out in 2017-2018. Five permanent sample plots, 400 m² each, sized 15 x 27 m, were put along the Pina river, south of Pinsk town (Table 1). The area of research belongs to Polesie Lowland, Pina-Prypyats' valley; the plots were situated on flat, occasionally or never flooded (but with high ground water level during high flooding) river terrace, with old alluvial soils. Selecting the size of plots we followed the recommendations [1; 6]. We were guided by the principle of physiographical and ecological identity of all sample plots, i.e. they have similar position in landscape above the water level of the river, similar micro-relief, soil and watering conditions. Before fixing the plots, the general distribution of A. negundo in the Pina rivel valley (both banks) south of Pinsk was studied by route method. Plots were selected using the principle to create a gradient of density of A. negundo plants from zero (A. negundo absent) to high density, typical to this area, but keeping similar physiognomy of the main tree level of Sa/ix a/ba. The presence of the set of characteristic plant species in lower levels of all communities was also taken into account.

Sample plot corners were fixed by pegs and also bound on a paper sketch to small local objects (e.g. forest roads). Plot sides were kept using a compass. During the total tree inventory the trees were marked by paper patches with numbers. For the measurements of annual growth sampled trees were marked by color threads; three occasional lower branches were taken for the measurements on each sample tree. Vascular plants were identified directly in field, or using the detailed photographs or temporary herbarium.

Tree level was studied according to the methods of forest inventory, or forest valuation [6]. Tree diameters were measured 1.3 m above the ground; tree heights were determined by altimeter. Tree crown projections were accepted as elliptical and determined from the length of these projections in directions north-south and west-east. Age of trees was determined on kerns after boring four different-aged sample trees by a trunk bore; then the diagram age/trunk diameter was built and the age of non-bored trees was determined.

Projection coverage of plant species was determined according to Ramensky and Raunkiaer methods [19; 24], on 1 m² subplots; 10 such subplots were put uniformly within each 400 m² plot. Within each 1 m² subplot, each species was measured in 9 smaller quadrates (for herbs), and in 5 smaller quadrates - 4 in corners and 1 in center (for A. negundo in upper level). For the estimation of species abundance, 6-grade scale of Drude [19] was used. Light intensity under crowns was determined by light meter Testo 545, in the conditions of clear heaven, between 12 and 14 h, in period 31 Jul - 23 Aug.

Cluster analysis of communities was carried out in STATISTICA 6.0, with unweighted pair- group average amalgamation rule. Correlation analysis was carried out in MS Excel. Shannon diversity index was calculated according the formula from [4]. For this index calculation, the shares of species were taken from their Drude abundances, which were summarized for the all species in community. Then the Drude abundance for each individual species was converted to the proportional fractional value, if accept the sum of all abundances = 1.

Table 1.Position of plots and valuation characteristics for the tree level of sample communities

*Some individual trees of S. alba on the plots were from 55 to about 100 year old.

**excluding seedlings

***An - Acer negundo,Sa - Salix alba

Results and discussion

.After study the tree level (Tab. 1) and floristic composition on the plots (Tab. 2), it was confirmed that all sample plots belong to one community type, called here Sa/ix a/ba-Rubuscaesius association. The values of A. negundo concentration were obtained after total inventory of all trees on the plots and taking their biometric characteristics (Tab. 2). Regardless the community No.3 had no saplings or large A. negundo plants, several seedlings of this species were recorded there, which indicated a potential of future invasion of A. negundo on this plot too.

A more exact characteristic that illustrates the abundance of A. negundo in community, and, consequently, the degree of its invasion, is trunk wood volume. It is seen (Tab. 1) that having bigger number of trees,A. negundo has lesser volume of wood, than S. alba. Thus the stand formulas, based on woodvolume, aresignificantly different from those based on tree quantity. From the average age of A. negundo it is seen that the most of invasion began only about 3-5 year ago. Tree level of the communities contains uneven-aged plants of both S. alba and A. negundo. However, seldom trees of A. negundo on the plots were 10-18 years old. Since the fruiting of A. negundobegins on the 6th year, the most of plants in sample communities are not the source of seeds. The stand quality of Salix alba, as a feature illustrating its productivity (based on average age and height), was the highest in the community No.3 lacked the influence of A. negundo (Tab. 1). However, the relative decrease of stand quality in other plots, possibly associated with A. negundo, is not high.

The dependence was observed between the number of vascular plant species in community(species richness) and the concentration of A. negundo (Tab. 2). The number of species in tree and underbush levels clearly increases with the decrease of A. negundo concentration in the raw: plots 1-2-4-5. A reason may be the mutual concurrence between A. negundo and other tree species at earlier stages of their ontogeny. In respect to the plants of living ground cover, the richest list (24 species) was in community without perennial A. negundo, and the poorest list (15 species) - in community with the highest abundance of A. negundo. In respect to the diversity, estimated via Shannon index (SDI), the most diverse was the community without

A. negundo trees, SDI=3.1; the least diverse was phytocoenoses with the highest abundance of A. negundo, SI=2.6 (Tab. 2). Also the plot with the highest concentration of A. negundo had the lowest average number of plant species in ground cover level per 1 m² (3.2 species). There is a strong inverse correlation between boxelder maple projection coverage and the number of ground cover plant species in community (r = -0,81).

Table 2. - Floristic composition and the abundance (Drude grades) of vascular plant species in sample communities

Table continuation 2.

Cluster analysis of similarity between sample communities, based on vascular plant species lists with the values of their abundances, is illustrated by dendrogram (Fig.). The communities with the highest abundance of A. negundo (1, 2, 4) occurred to be the most similar. This analysis shows the clear increase in dissimilarity between communities along with the decrease of A. negundo concentration.

Figure - Dendrogram of similarity between coenotic floras of sample plots. Plots are numbered according to Tab. 1. Distance measure: 1-Pearson r

We have studied the changes in light regime under crowns of A. negundo. Shadow effect, provided by a plant species, is considered here as a part of its phytogenic field [5]. Depending on the complexity of tree level (number of tree species and their abundance), from 20 to 35 measurements of light intensity were done in different points on a plot. The change in light under A. negundo was compared with other tree species (Tab. 3). In the row plot 4-2-1 there is a distinct decrease of light under crowns of:

A. negundo, associated with the increase of this plant concentration. Each of sparsely distributed

A. negundo trees gives less shadow, than those growing as closed groups. It is seen that A. negundo provides the greatest shadow effect amongthe trees, inhabiting studied phytocoenoses, except of Ulmusscabra. Light stream under A. negundo is in average 3.3 time less, than under denser part of S. alba crowns, and 8 times less, than under S. alba crown periphery. Consequently, shadow-preferring and shadow-tolerate herbaceous and bush species are able to develop under A. negundo, whereas more light-preferring plants gravitate to Salix alba, Betula pendula, and Populus alba.

Acer negundo changes the horizontal structure of communities by creating the mosaic. First of all, the higher diversity of ground cover was observed on the 1 m² subplots with zero or minimal coverage of A. negundo. Some subplots, which were 77-86% covered by negundo crown, contained a single lower level species (Rubuscaesius), or even naked litter only. Contrary, some 1 m² subplots with zero coverage of A. negundo contained 10-12 species of living ground cover. The number of species in dense A. negundo groups (plot 1) did not exceed 5 per 1 m². The number of plant species of lower level were 0-7 per 1 m² subplots with presence of A. negundo, and 3-12 without A. negundo. A specific parcelles of A. negundo (covered 70-85% by this species) were observed on plots 1 and 2: they had 3-4 species in ground cover, with abundance 6 for Glechoma hederacea and Geranium robertianum. The preference of phytogenic field of A. negundo was observed for these two species. Other species, having gravitation to A. negundo, were Lysimachianummularia, Impatiens noli-tangere, Epipactispalustris, Trifolium repens. They were recorded on subplots with A. negundo shadow only. Contrary, there were 8 species, recorded on plot 3 only, and thus avoiding boxelder maple. The abundance of Carexacutifomis decreased near A. negundo, whereas the abundance of Urticadioica - increased. The horizontal structure of community No.3 looked uniform, almost lacked any mosaic. The herbaceous level here had dense, vigorous, and aesthetic appearance.

The growth dynamics of A. negundo in studied communities, determined after measurements at the end of vegetation seasons 2017-2018, is shown in Table 4. There are no a dependence between A. negundo plants concentration and growth of branches in length and trunks in diameter. The highest phytomass accumulation was observed on plot 4, where trunks become thicker and crown projection become broader about 1.5 times.

Table 3 - Values of light intensity under the crowns of tree species

*lc, average within the plot, rounded to 10 (in brackets: number of measurement points)

Table 4. - Annual enlargement in dimensions (%) of A. negundo in sample communities

Other workers described various negative effects of A. negundo on the communities, similar with those observed by us, e.g. stopping the renewal of Salix and Populus in river valley stands [22], the descrease of biometric characteristics of Alnusglutinosa of the main tree level [20], the release of allelopatic toxins by living shoots and roots [25].

We consider the spread of new plant species is various areas (including Belarus) as an element of evolution of plant cover. Because of too mass distribution of A. negundo, its full removal is economically and strategically impossible, but measures to reduce population growth rate are applicable. The measures that cause minimal damage to communities may be trunk girding [16] and arboricide infusion in trunk [7]; these actions must be applied first to the female individuals of A. negundo.

Conclusions

The communities belonged to Salix alba-Rubuscaesius association are favourable for the development of A. negundobecause of ecological requirements of the latter coincide well with those of Salix alba and the accompanying plants. The number of A. negundo trees older than 3 years in this association can reach 33/100 m², the total trunks volume - 4.75 m³/100 m², projection coverage - up to 46%. In stands of Salix alba with average age 23 years, the average age of A. negundo is 4 years. The phytomass accumulation by A. negundo is classified as rapid and seen from the average annual enlargement in branch length (7%), trunk diameter 1.3 m above the ground (23%), and crown projection (24%). The shadow created by A. negundo crowns was about 3 times stronger, than by Salix alba. As a consequence, A. negundo development simplifies the coenotic flora: the species richness and species diversity were declined. It also creates certain mosaic, i.e. changes the horizontal structure of communities. The plant species, avoiding A. negundo and less frequent under it coverage, were recorded in lower level of Salix alba-Rubuscaesiusassociation. Besides, 6 herbaceous species (of 59 vascular plant species, recorded on all 5 plots) had various degree of gravitation to crown projections of A. negundo.

However, along with negative effect on the floristic diversity in river valley forests, we believe the growing of A. negundo has positive effects: saving soil humidity, prevention of soil erosion by root system, accumulating humus, protecting the neighbouring water bodies, i.e. the maple strengthens the environment-building functions of the phytocoenoses.

Acknowledgements.The authors are grateful to M.A. Dzhus (Minsk), G.Yu. Konechnaya (St- Petersburg), and N.N. Sychak (Lviv) for the help in identification of some plant species.

References

1. AndreevaYe.N. et al. Metodyizucheniya lesnykhsoobshchestv [Methods for study of forest communities]. St-Petersburg: NIIKhimii SPBGU, 2002.240 p. (In Russian)

2. ChernayaknigaflorySibiri [Black book of Siberian flora] / Edited by Yu.K. Vinogradova, A.N. Kupriyanov. Novosibirsk: Geo, 2016. 440 p. (In Russian)

3. DainekoN.M., TimofeevS.F., BulokhovA.D., PanasenkoN.N. Invaziyaklenayasenelistnogo (AcernegundoL.) vusloviyakhDobrushskogoraionaGomel'skoioblasti [InvasionofboxeldermapleinDobrushdistrictofGomel' region]. Izvestiya GGU. Series: Natural sciences, 2017, no. 3(102), pp. 35-39. (In Russian)

4. Daly A.J., Baetens J.M., De Baets B. Ecological diversity:measuring the unmeasurable. Mathematics, 2018, Vol. 6, article no. 119.

5. Dedyu I.I. Ekologicheskiientsiklopedicheskiislovar' [Ecological encyclopaedical dictionary]. Kishinev: Glavnayaredaktsiya Moldavskoisovetskoientsiklopedii, 1989. 406 p. (In Russian)

6. Ipatov V.S., Mirin D.M. Opisaniefitotsenoza: Metodicheskierekomendatsii [Phytocoenosis description: Methodical recommendations]. SPb., 2008. 71 p. (In Russian)

7. Kling A.P., Gaivas A.A., Kumpan V.N. Sredstvabor'by s klenomyasenelistnym v sadakhiparkakh v usloviyakhZapadnoiSibiri [The means for control of boxelder maple in gardens and parks in West Siberia]. PlodovodstvoiyagodovodstvoRossii, 2014, Vol. 39, pp. 105-109. (In Russian)

8. KoltunovaA.I..Kuz'min N.I. Klenyasenelistnyi (Acer negundo L.) v Orenburzh'e [Boxelder maple in Orenburg region]. IzvestiyaOrenburgskogogosudarstvennogoagrarnogouniversiteta, 2017, no. 5(67), pp. 211-213. (In Russian)

9. KoropachinskiiI.Yu., Vstovskaya T.N. DrevesnyerasteniyaAziatskoiRossii[Wooden plants of Asian Russia]. Novosibirsk: Izdatel'stvo SO RAN, 2002. 707 p. (In Russian)

10. Korovin V.V., Shcherbinina A.A. Obrazovaniekapov u klenayasenelistnogo v gorodskikhusloviyakh [The development of burls on boxelder maple in towns]. Lesnoivestnik, 2000, no. 6, pp. 148-151. (In Russian)

11. Kostina M.V., Min'kova V.O., Yasinskaya

O.I. O biologiiklenayasenelistnogo v zelenykhnasazhdeniyakhMoskvy [On the biology of boxelder maple in Moscow plantations]. Russian Journal of Biological Invasions, 2013, vol. 6, no. 4, pp. 32-43. (In Russian)

12. Leont'ev D.F., Zvereva K.A. InvaziyaklenayasenelistnogoioblepikhipoMoskovskomutraktunauchastke Irkutsk--Angarsk [Invasion of boxelder maple and sandthorn along Moscow road in the part Irkutsk-Angarsk]. Byulleten' naukiipraktiki (Nizhnevartovsk), 2016, no. 11(12), pp. 40-44. (In Russian)

13. Marbuah G., Gren I.-M., McKie B. Economics of harmful invasive species: A review. Diversity, 2014, no. 6, pp. 500-523.

14. Maslovskii O.M et al. KharakteristikarasprostraneniyanekotorykhinvazivnykhvidovrasteniinaterritoriiSvetlogorskogoiZhlobinskogoraionovGomel'skoioblasti[The characteristic of distribution of some invasive plant species in Svetlogorsk and Zhlobin districts of Gomel' region]. Problemysokhraneniyabiologicheskogoraznoobraziyaiispol'zovaniyabiologicheskikhresursov: Materialy III konferentsii. Part 1. Minsk: Konfidom, 2015, pp. 136-139. (In Russian)

15. Maslovskii O.M et al. Ekspansiyai osobennostiprostranstvennogo raspredeleniyanaiboleeopasnykhvidovinvazivnykhrasteniinaterritoriiRespubliki Belarus' [Expansion and the features of spatial distribution of the most harmful invasive plants in the Republic of Belarus]. Botanika: issledovaniya (Minsk), 2016, issue 45, pp. 129-144. (In Russian)

16. Merceron N.R., Lamarque L.J., Delzon S., Portй A.J. Killing it softly: girdling as an efficient eco-friendly method to locally remove invasive Acer negundo. Ecological Restoration, 2016, vol. 34, no. 4, pp. 297-305.

17. Planty-Tabacchi A.M., Tabacchi E., Naiman R.J., Deferrari C., Dйcamps H. Invasibility of species-rich communities in riparian zones. Conservation Biology, 1996, Vol. 10, pp. 598-607.

18. Portй A.J., Lamarque L.J., Lortie C.J., Michalet R., Delzon S. Invasive Acer negundo outperforms native species in nonlimiting resource environments due to its higher phenotypic plasticity. BMC Ecology, 2011, Vol. 11, article no. 28.

19. Ramenskii L.G. Izbrannyeraboty. Problemyimetodyizucheniyarastitel'nogopokrova[Selected papers. Problems and methods of plant cover research]. Leningrad: Nauka, 1971. 334 pp. (In Russian)

20. Turchina T.A. Introduktsiyaklena

yasenelistnogoi ego desruktivnayarol' v chernool'khovykhlesakhstepi [Introduction of boxelder maple and its destructive role in black alder forests of steppe]. Plodovodstvo, semenovodstvo, introduktsiyadrevesnykhrastenii:Sbornikmaterialov XX mezhdunarodnoinauchnoikonferentsii. Krasnoyarsk, 2017, pp. 199-202. (In Russian)

21. Veselkin D.V., Prokina N.E. Mycorrhiza formation in ash-leaf maple (Acer negundoL.) within gradient of urbanization. Russian Journal of Biological Invasions, 2016, vol. 9, no. 1, pp. 31-40. (In Russian)

22. VinogradovaYu.K., Maiorov S.R., Khorun L.V. ChernayaknigaflorySredneiRossii. Chuzherodnyevidyrastenii v ekosistemakhSredneiRossii [Black book of the Middle Russian flora. Alien plant species in Middle Russia ecosystems]. Moscow: GEOS, 2010. 502 p. (In Russian)

23. Yakushina E.I. Drevesnyerasteniya v ozeleneniiMoskvy [Woody plants in greenery of Moscow]. Moscow: Nauka, 1982. 158 p. (In Russian)

24. Yaroshenko P.D. Geobotanika [Geobotany]. Moscow: Prosveshchenie, 1969. 200 p. (In Russian)

25. Zolotukhin A.I., SuligaYe.M. Sornye drevesnyerasteniya [Woody weeds]. Voprosyekologiiiokhranyprirody v lesostepnoiistepnoizonakh: Mezhdunarodnyimezhvedomstvennyisborniknauchnykhtrudov. Samara:Samara University, 1999, pp. 192-197. (In Russian)

Список литературы

1. Андреева, Е. Н. Методы изучения лесных сообществ / Е. Н. Андреева [и др.]. - СПб.: НИИ химии СПбГУ, 2002. - 240 с.

2. Черная книга флоры Сибири / А. Л. Эбель

[и др.]; науч. ред. Ю.К. Виноградова, отв. ред. А. Н. Куприянов. - Новосибирск: Академическое изд-во «Гео», 2016. - 440 с.

3. Дайнеко, Н. М. Инвазия клена ясенелистного(AcernegundoL.) в условиях Доб-рушского района Гомельской области / Н. М. Дайнеко, С. Ф. Тимофеев, А.Д. Було- хов, Н. Н. Панасенко // Известия ГГУ. Сер. Естеств. науки. - 2017. - № 3(102). - С. 35-39.

4. Daly, A. J. Ecological diversity: measuring the unmeasurable / A. J. Daly, J. M. Baetens,

A. De Baets// Mathematics. - 2018. - Vol. 6, article no. 119.

5. Дедю, И. И. Экологический энциклопедический словарь / И. И. Дедю. - Кишинев: Гл. ред. Молд. сов.энцикл., 1989. - 406 с.

6. Ипатов, В. С. Описание фитоценоза: Методические рекомендации / В. С. Ипатов, Д.М. Мирин. - СПб.: Изд-во СПбГУ,

2008. - 71 с.

7. Клинг, А. П. Средства борьбы с кленом ясенелистным в садах и парках в условиях Западной Сибири / А. П. Клинг, А. А. Гайвас, В.Н. Кумпан // Плодоводство и ягодоводство России. - 2014. - Т. 39. - С. 105-109.

8. Колтунова, А. И. Клен ясенелистный(AcernegundoL.) в Оренбуржъе/ А. И. Колту- нова, Н. И. Кузьмин // Известия Оренбургского государственного аграрного университета. - 2017. - Вып. 5 (67). - С. 211-213.

9. Коропачинский, И. Ю. Древесные растения Азиатской России / И. Ю. Коропачинский, Т. Н. Встовская. - Новосибирск: Изд-во СО РАН, филиал «Гео», 2002. - 707 с.

10. Коровин, В. В. Образование капов у клена ясенелистного в городских условиях / В.

В.Коровин, А. А. Щербинина // Лесной вестник. - 2000. - №6. - С. 148-151.

11. Костина, М. В. О биологии клена ясенелистного в зеленых насаждениях Москвы / М. В. Костина, Н. О. Минькова, О. И. Ясинская // Российский журнал биологических инвазий. - 2013. - Т. 6, №4. - С. 32-43.

12. Леонтьев, Д. Ф. Инвазия клена ясенелистного и облепихи по Московскому тракту на участке «Иркутск-Ангарск» / Д. Ф. Леонтьев, К. А. Зверева // Бюллетень науки и практики. -2016. - №11 (12). - С. 40-44.

13. Marbuah, G. Economics of harmful invasive species: A review / G. Marbuah, I.-M. Gren,

B. McKie// Diversity. - 2014. - No. 6. - P. 500-523.

14. Масловский, О. М. Характеристика распространения некоторых инвазивных видов растений на территории Светлогорского и Жлобинского районов Гомельской области / О. М. Масловский, Л. С. Чумаков, А. В. Шевкунова, И. П. Сысой // Проблемы сохранения биологического разнообразия и использования биологических ресурсов: Мат-лы III Междунар. конф.; отв. ред. В.В. Титок. - Минск: Конфидо,

2015. - Ч. 1. - C. 136-139.

15. Масловский, О. М. Экспансия и особенности пространственного распределения наиболее опасных видов инвазивных растений на территории Республики Беларусь / О. М. Масловский [и др.] // Ботаника (исследования). - 2016. - Вып. 45. - C. 129-144.

16. Merceron, N. R. Killing it softly: girdling as an efficient eco-friendly method to locally remove invasive Acer negundo/ N.R. Merceron, L.J. Lamarque, S. Delzon, A.J. Portй // Ecological Restoration. - 2016. - Vol. 34, no. 4. - P. 297-305.

17. Planty-Tabacchi, A.M. Invasibility of species-rich communities in riparian zones / M. Planty-Tabacchi, E. Tabacchi, R.J. Naiman, C. Deferrari, H. Dйcamps //

Conservation Biology.- 1996. - Vol. 10. -

P.598-607.

18. Portй, A. J. Invasive Acer negundo outperforms native species in non-limiting resource environments due to its higher phenotypic plasticity / A. J. Portй [et al.] // BMC Ecology. - 2011. - Vol. 11, article no. 28.

19. Раменский, Л. Г. Избранные работы. Проблемы и методы изучения растительного покрова / Л. Г. Раменский. - Л.: Наука, 1971. - 334 с.

20. Турчина, Т. А. Интродукция клена ясенелистного и его деструктивная роль в черноольховых лесах степи / Т. А. Турчина // Плодоводство, семеноводство, интродукция древесных растений: Сб. мат. XX Междунар. науч. конф. / отв. ред. Р.Н. Матвеева. - Красноярск: СибГУ, 2017. -

С.199-202.

21. Веселкин, Д. В. Микоризообразование у клена ясенелистного(AcernegundoL.) в градиенте урбанизации / Д. В. Веселкин, Н. Э. Прокина // Российский журнал биологических инвазий. - 2016. - Т. 9. - №1.

- С. 31-40.

22. Виноградова, Ю. К. Черная книга флоры Средней России. Чужеродные виды растений в экосистемах Средней России / Ю. К. Виноградова, С. Р. Майоров, Л. В. Хорун. М.: ГЕОС, 2010. - 502 с.

23. Якушина, Э. И. Древесные растения в озеленении Москвы / Э. И. Якушина. - М.: Наука, 1982. - 158 с.

24. Ярошенко, П. Д. Геоботаника / П.Д. Ярошенко. - М.: Просвещение, 1969. - 200 с.

25. Золотухин, А. И. Сорные древесные растения / А. И. Золотухин, Е. М. Сулига // Вопросы экологии и охраны природы в лесостепной и степной зонах: Межд. меж- вед. сб. науч. тр. - Самара : Самарский университет, 1999. - С. 192-196.

Размещено на Allbest.ru