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Leaf reflectance and functional traits as environmental indicators of urban dust deposition

BMC Plant Biology volume 21, Article number: 533 (2021) Cite this article

Abstract

Background

How to quickly predict and evaluate urban dust deposition is the key to the control of urban atmospheric environment. Here, we focus on changes of plant reflectance and plant functional traits due to dust deposition, and develop a prediction model of dust deposition based on these traits.

Results

The results showed that (1) The average dust deposition per unit area of Ligustrum quihoui leaves was significantly different among urban environments (street (18.1001 g/m2), community (14.5597 g/m2) and park (9.7661 g/m2)). Among different urban environments, leaf reflectance curves tends to be consistent, but there were significant differences in leaf reflectance values (park (0.052–0.585) > community (0.028–0.477) > street (0.025–0.203)). (2) There were five major reflection peaks and five major absorption valleys. (3) The spectral reflectances before and after dust removal were significantly different (clean leaves > dust-stagnant leaves). 695 ~ 1400 nm was the sensitive range of spectral response. (4) Dust deposition has significant influence on slope and position of red edge. Red edge slope was park > community > street. After dust deposition, the red edge position has obviously “blue shift”. The moving distance of the red edge position increases with the increase of dust deposition. The forecast model of dust deposition amount established by simple ratio index (y = 2.517x + 0.381, R2 = 0.787, RMSE (root-mean-square error) = 0.187. In the model, y refers to dust retention, x refers to simple ratio index.) has an average accuracy of 99.98%. (5) With the increase of dust deposition, the specific leaf area and chlorophyll content index decreased gradually. The leaf dry matter content, leaf tissue density and leaf thickness increased gradually.

Conclusion

In the dust-polluted environment, L. quihoui generally presents a combination of characters with lower specific leaf area, chlorophyll content index, and higher leaf dry matter content, leaf tissue density and leaf thickness. Leaf reflectance spectroscopy and functional traits have been proved to be effective in evaluating the changes of urban dust deposition.

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Background

With the acceleration of urbanization, coal combustion, industrial waste gas and traffic exhaust gas are increasing, and urban environmental pollution problems become increasingly prominent, especially urban air quality problems [1,2,3]. In recent years, smog and dusty weather have occurred frequently in northern China, and air pollution has become one of the most serious environmental problems in many cities, which attracted extensive attention from many researchers [4]. According to the data of Beijing Environmental Monitoring Center, the primary pollutant in Beijing is inhalable particulate matter. In order to further strengthen the dust control work, the Beijing Municipal Government established an atmospheric coarse particulate matter monitoring network of atmospheric coarse particles covering all streets and towns in the city in 2018 [4, 5]. Dust particulate air pollutants not only seriously poison the respiratory system of urban residents, but also threaten the normal growth of urban vegetation [6]. Studies show that the influence of dust on trees is mainly through dust deposition on leaves and stomatal blockage [4,5,6]. Dust stagnation on leaf surface will block out 60% of light intensity and reduce photosynthesis of leaves by about 20% [5, 6]. At the same time, dust will also affect the gas exchange between leaves and the outside world, and then affects transpiration, photosynthesis and respiration [5,6,7]. Therefore, it is urgent to monitor and control air pollution.

Although the current air quality monitoring technology and methods have become increasingly mature, including positioning monitoring stations, multi-dimensional monitoring of unmanned aerial vehicle, vehicle-mounted monitoring and so on [7]. However, the coverage of current monitoring methods is generally small, and there are big time and space limitations. As an important part of the city, urban greening vegetation can not only beautify the landscape, but also improve a series of urban environmental pollution problems to a certain extent. In particular, it plays a vital role in dust prevention and noise reduction, air purification, etc. At the same time, it can also play a sensitive biological indicator role in environmental changes [8]. For example, the monitoring of heavy metals in the air by mosses and ozone by Malus pumila mainly involves the response of plants to air pollution and the traditional biological monitoring methods [9, 10]. Therefore, a comprehensive understanding of the ability of urban vegetation to purify the atmosphere and its response to dust pollution is of great significance for urban greening construction and allocation, as well as to deal with dust pollution. Hyperspectrum has many advantages, such as high resolution, abundant information, simple data acquisition, etc. [11,12,13]. The related research based on forestry hyperspectral mainly focuses on the estimation of plant yield, plant diseases and plant physical and chemical parameters, while the application of plant monitoring in dust pollution is relatively few [14, 15]. In the past, in the process of studying the relationship between leaf dust deposition and spectral characteristics, attention was paid to the changes of spectral characteristics of plant leaves before and after dust deposition, while the comparison of plants in different urban environments was often neglected, and the universal applicability of the prediction model was not verified [16].

During the growth process, plants will form morphological, physiological, phenological and other traits in response to the changes in the external environment during growth process, and to a certain extent, affect the functions of ecosystems [17,18,19,20]. Leaves are the basic organs of plant photosynthesis, and their functional traits can better reflect the adaptation strategies formed by plants adapting to environmental changes [21, 22]. The response of plant traits to the environment and adaptation strategies have always been the core issues in ecological research. Plants adapt to environmental changes by adjusting and changing some of their own functional traits, and form different survival strategies such as growth, reproduction and defense [21, 23, 24]. Recent studies show that the relationship between vegetation and environment based on plant functional traits can better reveal the response and adaptation of plants to the environment [25,26,27,28,29,30,31,32]. Generally speaking, the total resources available to plants are limited. If plants invest more resources in one functional trait, they will inevitably reduce the resources investment in other traits, that is, at the expense of the construction and functional maintenance of other traits [17, 33]. The research on plant functional traits mainly focuses on the responses of traits to drought, high temperature, ozone and fertilization [34,35,36,37]. At present, there are relatively few studies on plant functional traits by urban atmospheric particulates. As one of the structures with the largest contact area between plants and the external environment, leaves are highly sensitive to their growth environment. It can directly reflect the influence of environment on plants, and is often used to diagnose the relationship between plants and their growing environment. Under the long-term stress of dust pollution, the leaves of plants are covered by dust, which causes their growth to be affected to some extent. Therefore, by analyzing the response of spectral reflectance characteristics of leaves to dust pollution, we can further monitor and predict the environmental quality, and provide theoretical basis for environmental governance decision-making.

Therefore, in order to fully understand the response of leaf hyperspectral characteristics and leaf functional characteristics to urban atmospheric particulate matter, the universal applicability of the constructed prediction model in different urban environments was fully verified. In this study, the common greening tree species (Ligustrum quihoui Carr.) in Beijing was taken as the study material, and the leaf samples were collected from three typical urban environments, namely streets, campuses and parks. The spectral reflectance characteristics of Ligustrum quihoui leaves before and after dust deposition and under different conditions of dust deposition on leaves were analyzed, and the spectral response characteristics of L. quihoui leaves in different urban environments were further verified to be consistent, and the sensitive bands of L. quihoui leaves to dust deposition were obtained. Finally, according to the typical spectral parameters, the prediction model of dust deposition on leaves is constructed, and the response of plant functional traits to dust deposition on leaves and its trade-off strategy (allocation mechanism of leaf traits to resources) are explored, which provides theoretical reference for the allocation and selection of urban greening plants and the prediction of dust particle pollution.

Results

Amount of dust deposition on leaves in different urban environments

Streets, communities and parks are typical environments in an urban ecosystem. As the urban dust particles mainly come from automobile exhaust and dust, these three types of environments are divided into relatively obvious dust pollution gradients (streets - high pollution areas, community-moderate pollution areas, parks - relatively clean areas), which are characterized by long-term, stable and real-time. As shown in Fig. 1, the average dust accumulation per unit area of L. quihoui leaves was significantly different in different urban environments (p < 0.01). The values of dust deposition were streets (18.1001 g/m2), communities (14.5597 g/m2) and parks (9.7661 g/m2).

Fig. 1
figure 1

Dust deposition of 180 leaves from the urban tree L. quihoi in three urban environments from Beijing, China. “*” indicates that the significant level between treatments is at the p < 0.05 level, and “**” indicates that the significant level is reached between the treatments at p < 0.01

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Spectral response of L. quihoui to dust deposition on leaves

Original spectral characteristics

Leaf reflectance curves (350–2500 nm) significantly varied in three urban environments, from the park (0.052 ~ 0.585), community (0.028 ~ 0.478), and street (0.027 ~ 0.204), thus being negatively associated to the level of dust deposition pollution (Fig. 2). In addition, in the range of 340 ~ 2500 nm, there were five main reflection peaks and five main absorption valleys of L. quihoui in three different urban environments, and their positions and ranges were basically the same. The reflection peaks were at 830 nm, 1090 nm, 1276 nm, 1659 nm and 2231 nm, respectively. The absorption valleys were located in the ranges of 360 ~ 678 nm, 940 ~ 1026 nm, 1149 ~ 1231 nm, 1356 ~ 1596 nm and 1885 ~ 2100 nm respectively.

Fig. 2
figure 2

Spectral Signature (350 ~ 2500 nm) of 180 leaves from the urban tree L. quihoi in three urban environments from Beijing, China

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Leaf reflectivity characteristics with or without dust stagnation

It can be seen from Fig. 3 that the spectral reflectance of dust particles on the leaves of L. quihoui was obviously different. In the range of 695 ~ 1400 nm, regardless of the environment, the spectral reflectance of L. quihoui with or without dust was the most distinguished, which indicates that this band was the sensitive range of the spectral response. This feature has universal applicability in different environments. In addition, the slope of spectral reflectance curves of plants increased sharply in the range of 686 ~ 780 nm, which is the typical “red edge effect” of plants. However, there was a highly reflective platform in the range of 750 ~ 1310 nm.

Fig. 3
figure 3

Original leaf reflectance (350 ~ 2500 nm) of 180 leaves from the urban tree L. quihoi in three urban environments from Beijing before and after the leaf dust removal. A Park, B Community, C Street

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Spectral characteristics of the first derivative

It can be seen from Fig. 4 that the general trend of the first derivative spectrum (350 ~ 2500 nm) of L. quihoui leaves in different urban environments was basically the same, and the dust deposition on leaves has a significant impact on the slope and position of red edge. Among them, in different urban environments, the red edge slopes were parks, communities and streets from large to small. Combined with Fig. 2, it can be seen that the dust deposition amount per unit area in different environments was in the order of park, community and street from large to small, which indicates that L. quihoui grows in an environment with high dust concentration, and the greater the dust deposition amount on its leaves, which will directly lead to a sharp decline in the slope of red edge of plant leaf spectrum.

Fig. 4
figure 4

The first derivative spectral curves (350 ~ 2500 nm) of 180 leaves from the urban tree L. quihoi in three urban environments from Beijing before and after the leaf dust removal. A Park, B Community, C Street

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Prediction model for dust deposition of leaves

Previous studies generally believed that leaf water content index (LWI), red edge index (SDr), normalized index (ND705) and simple ratio index (SR) could better characterize the spectral reflectance of plants (Table 1) [38,39,40,41]. Therefore, in this study, the spectral parameters were taken as independent variables, and the dust deposition amount per leaf of L. quihoui was taken as dependent variable to establish a linear regression model. Sixty leaf samples were randomly selected from each environment to check whether there was a linear relationship between dust deposition and spectral parameters. The stability and accuracy of the prediction model were tested by using the determination coefficient R2 and root-mean-square error (RMSE). As shown in Table 2, the coefficient of determination R2 was extremely significant, and the model with simple ratio index (y = 2.517x + 0.381, R2 = 0.787, RMSE = 0.187) has the best goodness of fit. Finally, we test the model with simple ratio index as independent variable and the predicted value of dust deposition as dependent variable. The results show that the R2 of the prediction model was 0.793 and the average prediction accuracy was 99.98% (Fig. 5).

Table 1 The prediction model of dust deposition based on four typical spectral parameters
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Fig. 5
figure 5

Test of dust deposition prediction model of 180 leaves from the urban tree L. quihoi in three urban environments from Beijing based on simple ratio index

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Response of plant functional traits to urban atmospheric particulates

There were significant differences in plant functional traits in different urban environments (Fig. 6). With the increase in dust deposition on the leaf surface, the specific leaf area and chlorophyll content index gradually decreased, and reached extremely significant differences in different environments. Change extremely significant to highly significant (p <0.01). On the contrary, leaf dry matter content, leaf tissue density and leaf thickness increased gradually.

Fig. 6
figure 6

Effect of leaf dust deposition on leaf functional traits of L. quihoi in three urban environments from Beijing, China. a Specific leaf area, b Leaf dry matter content, c Leaf tissue density, d Leaf thickness, e Chlorophyll content index. “*” indicates that the significant level between treatments is at the p < 0.05 level, and “**” indicates that the significant level is reached between the treatments at p < 0.01

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Correlation between plant functional traits and its ecological strategy under the influence of dust deposition

Leaf functional traits do not function in isolation, and there was a certain correlation among functional traits (Fig. 7). The specific leaf area was positively correlated with chlorophyll content index. Specific leaf area was negatively correlated with leaf dry matter content, leaf tissue density and leaf thickness. Leaf thickness was negatively correlated with chlorophyll content index. There was a significant positive correlation between dry matter content and tissue density. Chlorophyll content index was negatively correlated with leaf dry matter content and leaf tissue density.

Fig. 7
figure 7

Correlation analysis among plant functional traits of L. quihoi. “*” indicates that the significant level between treatments is at the p < 0.05 level, and “**” indicates that the significant level is reached between the treatments at p < 0.01

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Discussion

Environmental pollution is one of the main factors affecting the growth of urban plants. In fact, for the purpose of biological monitoring and bioremediation projects, the assessment of plant morphological and anatomical changes has been used to solve the selective tolerance of plant species to the affected environment. In recent years, with the aggravation of automobile exhaust, urban construction, sandstorm and other multiple pollution, atmospheric particulate pollution has become one of the major topics in urban environmental research. Therefore, a comprehensive understanding of the response of urban vegetation to dust pollution is of great significance for urban greening construction and allocation and coping with dust pollution.

Studies show that with the rapid development of spectral technology, the characteristics of high resolution, large amount of information, strong data continuity and simple access are also highlighted [38, 39]. For example, under the conditions of heavy metal pollution, pest and disease threat, drought stress, etc., its position often deviates to a certain extent, but the response law of the red edge position to dust pollution stress has not been verified at present. Generally speaking, there are two main directions for the shift of red edge position, one is the shift to long wave direction, that is, “red shift” phenomenon, the other is the shift to short wave direction, that is, “blue shift” phenomenon. The slope of red edge can reflect the chlorophyll content of plants and is often closely related to the photosynthetic rate of plants [38,39,40,41,42,43]. Therefore, the application of spectrum technology to dust pollution monitoring can achieve the purpose of obtaining air pollution information in a large scale, quickly and in real time. Data analysis shows that hyperspectral data can quickly predict the dust deposition on leaf surface of L. quihoui in real time, and a prediction model of dust deposition on leaf surface is established according to its reflection spectrum. Studies have shown that the slope of red edge has a good indication of chlorophyll content index. Therefore, we suspect that the cause of this phenomenon may be related to the influence of leaf covering on plant photosynthesis. In addition, the change trend of red edge position of L. quihoui before and after dust deposition was consistent in different urban environments. Compared with clean leaves, the red edge position of leaves after dust deposition has obvious “blue shift”. In different urban environments, the biggest moving distance of “blue shift” was the street, the next was the community, and the smallest was the park. This shows that the greater the dust deposition on leaves, the more severe the impact on the red edge position of leaves. To sum up, the slope and position of red edge were extremely sensitive to the disturbance of dust stagnation on leaf surface.

Some studies have shown that urban dust pollution leads to slight changes in leaf structure [36, 37] and this conclusion has been confirmed in our research. Different from previous studies, we chose the open urban environment as the experimental environment, which is more conducive to accurately explain the response of plants to dust pollution. In addition, we found that in the studied species, the observed changes in plant functional traits are relatively obvious. In different gradients of pollution, with the increase in dust deposition on the leaf surface, the specific leaf area and chlorophyll content index gradually decreased, and reached extremely significant differences in different environments. Specific leaf area can represent the adaptability of plants to the environment and the ability to obtain resources, which is closely related to the survival strategies of plants [16]. Plants with lower leaf area have stronger adaptability to arid environment with poor resources, while plants with higher leaf area have stronger ability to maintain nutrition in vivo [27, 38, 44, 45]. In this study, with the increase of dust deposition, the specific leaf area of plants decreased significantly. This shows that urban plants adapt to the influence of urban atmospheric particulate matter by reducing the specific leaf area. Our conclusion is consistent with the change of specific leaf area under high temperature and drought environment [46]. Chlorophyll content index can reflect the photosynthetic capacity of plant leaves [16]. In this study, with the increase of dust deposition, chlorophyll content index in plants decreased significantly. We suspect that this may be related to dust coverage. The leaves were covered by dust, the area of the leaves receiving light was greatly reduced. Leaf thickness plays a key role in determining the physical structure strength of plant leaves [47, 48]. In this study, with the increase of dust deposition, the leaf thickness increased significantly. This shows that in the environment polluted by dust, increasing the leaf thickness can avoid the mechanical damage to leaves caused by dust deposition on leaves. Leaf dry matter content can reflect the ability of plants to retain nutrients. Leaf tissue density is closely related to the defense ability and mechanical organization ability of plant leaves [49, 50]. In this study, with the increase of dust deposition on leaves, the dry matter content and tissue density of leaves increased significantly. This shows that plants use more resources for the construction of defense structures in order to reduce the damage degree of leaves.

There are various relationships among functional traits of species, the most common of which is trade-off [51]. This trade-off relationship is a combination of traits formed after natural selection, also called “ecological strategy”, that is, species are arranged in the most suitable or competitive position along a certain ecological strategy axis [19, 49, 52]. In this study, there was a significant positive correlation between specific leaf area and chlorophyll content index. Specific leaf area is related to drought tolerance of plants [48]. With the increase in dust deposition, specific leaf area decreases to reduce transpiration. At the same time, due to the decrease of specific leaf area, the leaf area of photosynthesis is also reduced, which leads to the decrease of chlorophyll content index. Chlorophyll content index was negatively correlated with leaf dry matter content and leaf tissue density. The leaf dry matter content can reflect the ability of plants to retain nutrients [53]. The leaf tissue density is closely related to the defense ability and mechanical organization ability of plant leaves [54, 55]. This shows that plants can slow down their growth by increasing the density of leaf tissues and the content of dry matter in leaves, reserve more carbon for defensive structures, and use more synthetic substances to increase the construction of protective tissues, so as to adapt to the environment polluted by urban atmospheric particulate matter. Among the limited resources, because plants use more resources and nutrition for the construction of leaf defense structure, the resources for photosynthesis are correspondingly reduced [56, 57]. This also reflects an “ecological strategy” for plants to cope with the adverse external environment.

Conclusion

(1) The average amount of dust deposition per unit area of L. quihoui leaves was significantly different in different urban environments, and the overall performance was street > community > park. In different urban environments, the trend of leaf reflection spectrum curve tends to be consistent. There were five main reflection peaks and five main absorption valleys in L. quihoui in three different urban environments, and their positions and ranges were basically the same.

(2) The spectral reflectance of dust particles on the leaves of L. quihoui before and after removal was obviously different (clean leaves > dust-stagnant leaves). In the range of 695 ~ 1400 nm, the spectral reflectance of L. quihoui with or without dust was the most distinguished, which indicates that this band is the sensitive range of its spectral response. This characteristic has universal applicability in the environment. The dust deposition on leaves has significant influence on the slope and position of red edge. The slope of red edge was the largest in park environment, the second in community environment and the smallest in street environment. After dust deposition, the red edge position of the leaf surface has obvious “blue shift”, and the greater the dust deposition on the leaf surface, the more severe the influence on the red edge position of the leaf surface.

(3) The forecast model of dust deposition amount established by simple ratio index (y = 2.5171x + 0.3806, R2 = 0.7873, RMSE = 0.187) has an average accuracy of 99.98%.

(4) With the increase in dust deposition on the leaf surface, the specific leaf area and chlorophyll content index decreased gradually. The leaf dry matter content, leaf tissue density and leaf thickness increased gradually. In the environment polluted by dust, L. quihoui generally presents a combination of characters with low specific leaf area, low chlorophyll content index, high leaf dry matter content, high leaf tissue density and large leaf thickness, which reflects the trade-off strategy between investment and return of plant leaves in structure construction, and fully demonstrates that plants adjust their own functional traits in order to adapt to the adverse stress caused by the habitat characteristics of urban environmental pollution.

Materials and methods

Study area and sample collection

Haidian District, located between the central city of Beijing and the ecological public welfare zone in the outer suburbs. It is an important urban function expansion area in Beijing, with a total area of 431 km2, accounting for 2.53% of the total area of Beijing, ranging from 116°03′—116°23 east longitude to 39°53 ′—40°09 ′ north latitude (Data from http: //www.weather.com.cn/). Haidian District is located in the warm temperate semi-humid and semi-arid continental monsoon climate zone, with an average annual precipitation of 483.5 mm and an average annual temperature of 12.3 °C. As shown in Fig. 8, the sampling areas are located in Wudaokou Street, Beijing Forestry University Campus and Bajia country parks, representing the highway environment (low density urban green area or high pollution area, T1), community environment (medium density urban green area or medium pollution area, T2) and park environment (high density urban green area or relatively clean area, T3). The results show that the parameters such as leaf surface coat density, leaf mass, leaf area and crown structure are important factors affecting the dust deposition benefits of plants. Ligustrum quihoui Carr. is a small shrub of Ligustrum in Oleaceae. In Beijing, it is often used as an important hedge material in landscaping. It has the characteristics of dense villi, slightly concave veins, abundant leaves and evergreen all the year round. It is mainly responsible for the decomposition, absorption and fixation of atmospheric particulate matter by vegetation in Beijing in winter.

Fig. 8
figure 8

Study area and location of sampling. a Street environment, b Community environment, c Park environment. The map of Fig. 8a-c was downloaded from Google Maps (maps.google.com.hk). We only intercepted the study area and did not change any position in the map. The map of China is downloaded from the website of China Bureau of Surveying and Mapping (http://www.sbsm.gov.cn/), and the map is complete

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In this study, the age of the studied tree species is 8 years. Leaf samples were collected from 10: 00 am to 12: 00 am in December, 2018. Thirty healthy L. quihoui seedlings were selected from three experimental sites, and the planting location was not covered by tall buildings and large trees. Three hundred sixty mature and healthy leaves were cut evenly in each test environment, put into a clean tray gently, and immediately brought back to the laboratory to measure related indexes. The linear distance between the sampling site and the experimental test site was about 10 km, and the time from in vitro to spectral collection of leaf samples was controlled within 30 min, thus ensuring that the leaf samples maintain their original growth activity. Under FlexSEM1000 electron scanning microscope (Hitachi, Osaka, Japan), it was observed that the shape of leaf particles was irregular block, sphere and polymer, and the particle size was less than 10 μm, in which the proportion of PM10 was 67.16%. Prof. Chengyang Xu was responsible for the identification of plant samples involved in this study (refer to Flora of China for identification information).

Collection of leaf reflection spectrum and determination of dust deposition

The experimental steps were as follows: first leaf mass measurement, first spectral data collection, second leaf mass measurement, second spectral data collection and leaf area measurement. Leaf spectrum was collected by ASD (Analytical Spectral Device, Almero, Netherlands) FieldSpec3 portable near infrared spectrometer, and the wavelength range of the instrument was 300 ~ 2500 nm. The resolution was 3 ~ 700 nm. Sampling interval were 1.4 nm (350 ~ 1000 nm) and 2 nm (1000 ~ 2500 nm). Angle of view was 30. Scanning time was 0.1 s, the spectral reflection curve was measured for 10 times, and the final output curve was automatically averaged. The spectrum acquisition processes were dark scanning, whiteboard scanning, transmission mode adjustment, instrument probe avoiding the center vein perpendicular to 4 cm above the sample center, and saving the value after reading was stable (Fig. 9).

Fig. 9
figure 9

Flow chart of spectral measurement [58]

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According to the particle size, dust can be divided into floating dust, floating dust (D < 1 μm) and falling dust (D < 10 μm). There are three main movement modes (suspension, floating and desposition) [5]. Here, we mainly study the dust on the leaves. First, measure the initial mass of leaves with a balance of 1/10000, immerse them in deionized water, and scrub off the dust and impurities on the leaves with sanitary napkins. Then, clean absorbent paper will absorb the moisture on the leaves and measure the mass of leaves for the second time. The leaf area was measured by LI-3000C portable leaf area scanner (LI-COR, Boston, USA). Dust deposition per unit area was the ratio of leaf mass to leaf area before and after dust removal.

Determination of leaf functional traits

The functional characteristics of plant leaves can intuitively reflect the response strategies of plants to environmental changes, among which specific leaf area, leaf thickness, leaf dry matter content, chlorophyll content index, leaf tissue density and other indicators directly affect the basic behavior, function and ecological strategy of plants, which are often considered as one of the best variables on the axis of plant utilization of environmental resources [59]. Therefore, in this study, we selected the above five functional traits. After spectrum collection, the leaf area (LA, mm2) was measured by LI-3000C leaf area scanner (LI-COR, Boston, USA). Chlorophyll content index (CCI) was measured by CCM-200 Plus portable chlorophyll meter (OPTI-Science, Tyngsboro, MA, USA). The leaf thickness (LT, mm) was measured by TM004 digital vernier caliper (Jinnuo, Nanjing, China). The fresh weight of leaves was measured by XPR5003S electronic balance (SAID, Shaoxing, China), then soaked in deionized water for 12 h, and the saturated fresh weight of leaves (LFW, g) was weighed. Finally, put all the leaves into an oven (65 °C) to dry to a constant mass, and weigh the dry mass of leaves (LDW, g).

$$\mathrm{SLA}=\mathrm{LA}/\mathrm{LDW},{\mathrm{cm}}^2/\mathrm{g}$$
(1)
$$\mathrm{LDMC}=\mathrm{LDW}/\mathrm{LFW},\mathrm{g}/\mathrm{g}$$
(2)
$$\mathrm{LTD}=\mathrm{LDW}/\left(\mathrm{LT}\times \mathrm{LA}\right),\mathrm{g}/{\mathrm{cm}}^3$$
(3)

Data processing

Spectral data were preprocessed by using Viewspecpro software, and then analyzed by using Origin 2019b software. Linear regression model was selected as the prediction model of dust deposition on leaves, and spectral parameters were used as independent variables and dust deposition as dependent variables for linear fitting. Pearson correlation analysis was used to analyze the correlation between leaf functional traits. In this study, all drawings and tables were made in Origin 2019b software. The accuracy calculation formula of the prediction model was as follows:

$$\mathrm{Model}\ \mathrm{accuracy}\ \left(\%\right)=1-\frac{\left|w1-w2\right|}{100}\times 100\%$$
(4)

In the formula, w1 is the measured value and w2 is the predicted value.

Availability of data and materials

The data involved in the article were all shown in the figures and tables. However, there are still available from the first author on reasonable request.

Abbreviations

SLA:

Specific leaf area

LDMC:

Leaf dry matter content

CCI:

Chlorophyll content index

LTD:

Leaf tissue density

LT:

Leaf thickness

LFW:

Leaf saturated fresh weight

LV:

Leaf volume

LDW:

Leaf dry weight

References

  1. Eriksson G, Jensen S, Kylin H, Strachan W. The pine needle as a monitor of atmospheric pollution. Nature. 1989;341:42–4.

    Article  CAS  Google Scholar 

  2. Chen ZH, Cheng SY, Li JB, Guo XR, Wang WH, Chen DS. Relationship between atmospheric pollution processes and synoptic pressure patterns in northern China. Atmos Environ. 2008;42:6078–87.

    Article  CAS  Google Scholar 

  3. Pey J, Perez N, Querol X, Alastuey A, Cusack M, Reche C. Intense winter atmospheric pollution episodes affecting the western mediterranean. Sci Total Environ. 2010;408:1951–9.

    Article  CAS  Google Scholar 

  4. Dan Y, Lei Y, Shi Y, Zhu Q, Zhang Z. Evolution of the spatiotemporal pattern of PM2.5 concentrations in China – a case study from the Beijing-Tianjin-Hebei region. Atmos Environ. 2018;183:1–25.

  5. Hu Z, Tang X, Zheng C, Guan M, Shen J. Spatial and temporal analyses of air pollutants and meteorological driving forces in Beijing-Tianjin-Hebei region, China. Environ Earth Sci. 2018;77:1–19.

    Article  Google Scholar 

  6. Freer-Smith SP. Estimating the removal of atmospheric particulate pollution by the urban tree canopy of London, under current and future environments. Landsc Urban Plan. 2011.

  7. Wuyts K, Hofman J, Wittenberghe SV, Nuyts G, Wael KD, Samson R. A new opportunity for biomagnetic monitoring of particulate pollution in an urban environment using tree branches. Atmos Environ. 2018;190:177–87.

    Article  CAS  Google Scholar 

  8. Nadgorska-Socha A, Kandziora-Ciupa M, Trzesicki M, Barczyk G. Air pollution tolerance index and heavy metal bioaccumulation in selected plant species from urban biotopes. Chemosphere. 2017;183:471–82.

    Article  CAS  Google Scholar 

  9. Gerdol R, Bragazza L, Marchesini R. Monitoring of heavy metal deposition in northern Italy by moss analysis. Environ Pollut. 2000;108:201–8.

    Article  CAS  Google Scholar 

  10. El-Khatib AA. The response of some common Egyptian plants to ozone and their use as biomonitors. Environ Pollut. 2003;124:419–28.

    Article  CAS  Google Scholar 

  11. Thenkabail PS, Smith RB, Pauw ED. Hyperspectral vegetation indices and their relationships with agricultural crop characteristics. Remote Sens Environ. 2000;71:158–82.

    Article  Google Scholar 

  12. Melgani F, Bruzzone L. Classification of hyperspectral remote sensing images with support vector machines. IEEE T Geosci Remote. 2004;42:1778–90.

    Article  Google Scholar 

  13. Fauvel M, Tarabalka Y, Benediktsson JA, Chanussot J, Tilton JC. Advances in spectral-spatial classification of hyperspectral images. P IEEE. 2013;101:652–75.

    Article  Google Scholar 

  14. Osborne SL, Schepers JS, Francis DD, Schlemmer MR. Detection of phosphorus and nitrogen deficiencies in corn using spectral radiance measurements. Agron J. 2002;94:1215–21.

    Article  Google Scholar 

  15. Daranas N, Roselló G, Cabrefiga J, Donati I, Bonaterra A. Biological control of bacterial plant diseases with lactobacillus plantarum strains selected for their broad-spectrum activity. Ann Appl Biol. 2018;74:1–14.

  16. Zhu J, Zhang X, He W, Yan X, Wang R. Response of plant reflectance spectrum to simulated dust deposition and its estimation model. Sci Rep-UK. 2020;10:15803.

    Article  Google Scholar 

  17. Pausas JG, Bradstock RA, Keith DA, Keeley JE. Plant functional traits in relation to fire in crown-fire ecosystems. Ecology. 2004;85:1085–100.

  18. Biase LD, Fattorini S, Cutini M, Bricca A. The role of inter- and intraspecific variations in grassland plant functional traits along an elevational gradient in a Mediterranean mountain area. Plants. 2021;10:359.

    Article  Google Scholar 

  19. Bullock, JM, Franklin J, Stevenson MJ, Silvertown J, Coulson SJ, Tofts GR. A plant trait analysis of responses to grazing in a long‐term experiment. J Appl Ecol. 2001;38:253-67.

  20. Wright IJ, Westoby M. Nutrient concentration, resorption and lifespan: leaf traits of Australian sclerophyll species. Funct Ecol. 2010;17:10-9.

  21. Díaz S, Cabido M, Zak M, Araníbar CJ. Plant functional traits, ecosystem structure and land-use history along a climatic gradient in Central-Western Argentina. J Veg Sci. 2020;10:651–60.

    Article  Google Scholar 

  22. McGill BJ, Enquist, Weiher, Westoby. Rebuilding community ecology from functional traits. Trend Ecol Evolut. 2006;21:178-85.

  23. Lavorel S. Plant functional effects on ecosystem services. J Ecol. 2013;101:4–8

  24. Vendramini F, Diaz S, Gurvich DE, Wilson PJ, Thompson K, Hodgson JG. Leaf traits as indicators of resource–use strategy in floras with succulent species. New Phytol. 2002;154:147–57.

  25. Cornwell WK, Cornelissen JH. Plant species traits are the predominant control on litter decomposition rates within biomes worldwide. Ecol Lett. 2008;11:1065–71

  26. Chin CS, Potts MD. The role of plant functional traits in understanding forest recovery in wet tropical secondary forests. Sci Total Environ. 2018;642:1252–62.

    Article  Google Scholar 

  27. Huang LC, Niinemets U, Ma JZ, Schrader J, Wang R, Shi PJ. Plant age has a minor effect on non-destructive leaf area calculations in moso bamboo (Phyllostachys edulis). Symmetry. 2021;13:369.

    Article  Google Scholar 

  28. Huang WW, Ratkowsky DA, Hui C, Wang P, Su JL, Shi PJ. Leaf fresh weight versus dry weight: which is better for describing the scaling relationship between leaf biomass and leaf area for broad-leaved plants? Forests. 2019;10:256.

    Article  Google Scholar 

  29. Shi PJ, Niinemets U, Hui C, Niklas KJ, Yu XJ, Holscher D. Leaf bilateral symmetry and the scaling of the perimeter vs. the surface area in 15 vine species. Forests. 2020;11:246.

    Article  Google Scholar 

  30. Lin SY, Niklas KJ, Wan YW, Holscher D, Hui C, Ding YL, et al. Leaf shape influences the scaling of leaf dry mass vs. area: a test case using bamboos. Ann Forest Sci. 2020;77:11.

    Article  Google Scholar 

  31. Liu MD, Niklas KJ, Niinemets U, Holscher D, Chen L, Shi PJ. Comparison of the scaling relationships of leaf biomass versus surface area between spring and summer for two deciduous tree species. Forests. 2020;11:1010.

    Article  Google Scholar 

  32. Shi PJ, Li YR, Hui C, Ratkowsky DA, Yu XJ, Niinemets U. Does the law of diminishing returns in leaf scaling apply to vines? – evidence from 12 species of climbing plants. Glob Ecol Conserv. 2020;21:e00830.

    Article  Google Scholar 

  33. Yu XJ, Hui C, Sandhu HS, Lin ZY, Shi PJ. Scaling relationships between leaf shape and area of 12 Rosaceae species. Symmetry. 2019;11:1255.

    Article  Google Scholar 

  34. Colin Y, Goberna M, Verdu M, Navarro-Cano JA. Successional trajectories of soil bacterial communities in mine tailings: the role of plant functional traits. J Environ Manag. 2019;241:284–92.

    Article  CAS  Google Scholar 

  35. Mccormack ML, Adams TS, Smithwick E, Eissenstat DM. Predicting fine root lifespan from plant functional traits in temperate trees. New Phytol. 2012;195:823–31.

    Article  Google Scholar 

  36. Pérez-Camacho L, Rebollo S, Hernández-Santana V, García-Salgado G, Pavón-García J, Gómez-Sal A. Plant functional trait responses to interannual rainfall variability, summer drought and seasonal grazing in Mediterranean herbaceous communities. Funct Ecol. 2012;26:740–9.

    Article  Google Scholar 

  37. Barkaoui K, Roumet C, Volaire F. Mean root trait more than root trait diversity determines drought resilience in native and cultivated Mediterranean grass mixtures. Agric Ecosyst Environ. 2016;231:122–32.

    Article  Google Scholar 

  38. Zhu J, Zhu H, Cao Y, Li J, Xu C. Effect of simulated warming on leaf functional traits of urban greening plants. BMC Plant Biol. 2020;20:1-13.

  39. Richardson AD, Berlyn GP. Spectral reflectance and photosynthetic properties of Betula papyrifera (Betulaceae) leaves along an elevational gradient on mt, vol. 89. Mansfield: Ame Bot; 2002. p. 88–94.

    Google Scholar 

  40. Zhu J, Yu Q, Liu X, Yu Y, Yao J, Su K, et al. Effect of leaf dust deposition on spectral characteristics of Euonymus japonicus and its dust deposition prediction. Spectrosc Spectr Anal. 2020;40:517–22.

    CAS  Google Scholar 

  41. Curran PJ, Dungan JL, Peterson DL. Estimating the foliar biochemical concentration of leaves with reflectance spectrometry. Remote Sens Environ. 2001;76:349–59.

    Article  Google Scholar 

  42. Yang CM, Chen RK. Modeling rice growth with hyperspectral reflectance data. Crop Sci. 2004;44:1283–90.

    Article  Google Scholar 

  43. Maletsika PA, Nanos GD, Stavroulakis GG. Peach leaf responses to soil and cement dust pollution. Environ Sci Pollut Res. 2015;22:15952–60.

    Article  CAS  Google Scholar 

  44. He JY, Reddy GVP, Liu MD, Shi PJ. A general formula for calculating surface area of the similarly shaped leaves: evidence from six Magnoliaceae species. Glob Ecol Conserv. 2020;23:e01129.

    Article  Google Scholar 

  45. Murphy M, Jordan GJ, Brodribb TJ. Acclimation to humidity modifies the link between leaf size and the density of veins and stomata. Plant Cell Environ. 2013;37:124-31.

  46. Siqueira-Silva AI, Pereira EG, Modolo LV, Paiva E. Leaf structural traits of tropical woody species resistant to cement dust. Environ Sci Pollut Res. 2016;23:16104–14.

    Article  CAS  Google Scholar 

  47. Wilson PJ, Thompson K, Hodgson JG. Specific leaf area and leaf dry matter content as alternative predictors of plant strategies. New Phytol. 2010;143:155–62.

    Article  Google Scholar 

  48. Richards JH, Henn JJ, Sorenson QM, Adams MA, Smith DD, Mcculloh KA, et al. Mistletoes and their eucalypt hosts differ in the response of leaf functional traits to climatic moisture supply. Oecologia. 2021;195:759–71.

    Article  Google Scholar 

  49. Franco AC, Bustamante M, Caldas LS, Goldstein G, Meinzer FC, Kozovits AR, Rundel P, Coradin VTR. Leaf functional traits of neotropical savanna trees in relation to seasonal water deficit. Trees. 2005;19:326–35.

    Article  Google Scholar 

  50. Shipley B, Vu TT. Dry matter content as a measure of dry matter concentration in plants and their parts. New Phytol. 2020;153:359–64.

    Article  Google Scholar 

  51. Poorter L, Bongers BF. Architecture of 54 moist-forest tree species, traits, trade-offs, and functional groups. Ecology 2006;87:1289–301.

  52. Tomáš H, Zuzana N, Jitka K, Lubomír H. Species traits and plant performance, functional trade-offs in a large set of species in a botanical garden. J Ecol. 2012;100:1522–33.

  53. Hoffmann WA, Franco AC, Moreira MZ, Haridasan M. Specific leaf area explains differences in leaf traits between congeneric savanna and forest trees. Funct Ecol. 2005;19:932–40.

  54. Eamus TD. Coordinating leaf functional traits with branch hydraulic conductivity, resource substitution and implications for carbon gain. Tree Physiol. 2008;28:1169-77.

  55. Wright IJ, Reich PB, Westoby M, Ackerly DD, Baruch Z, Bongers F, Cavender-Bares J, Chapin T, Cornelissen JHC, Diemer M, Flexas J, Garnier E, Groom PK, Gulias J, Hi-kosaka K, Lamont BB, Lee T, Lee W, Lusk C, Midgley JJ, Navas ML, Niinemets U, Oleksyn J, Osada N, Poorter H, Poot P, Prior L, Pyankov VI, Roumet C, Thomas SC, Tjoelker MG, Veneklaas EJ, Villar R. The world-wide leaf economics spectrum. Nature. 2004;428:821–27.

  56. Wright JP, Sutton-Grier A. Does the leaf economic spectrum hold within local species pools across varying environmental conditions? Funct Ecol. 2012;26:1390–98.

  57. Westoby M. Plant ecological strategies. S Afr J Bot. 2007;73:275-76.

  58. Chave JD, Coomes, Jansen S, Lewis SL, Zanne AE. Towards a worldwide wood economics spectrum. Ecol Lett. 2010;12:351-66.

  59. Chaturvedi RK, Raghubanshi AS, Singh JS. Growth of tree seedlings in a tropical dry forest in relation to soil moisture and leaf traits. J Plant Ecol. 2012;508:156–60.

    Google Scholar 

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Acknowledgments

The English in this document has been checked by at least two professional editors; both were native speakers of English.

Funding

This research is supported by the “Integration and Demonstration of Key Technologies for Oriented Tending of Plain Ecological Forest in Chaoyang District (CYSF-1904)”. The funders are one of the co-authors of this study. We declare that the funded institutions are not involved in the process of research design, data collection, analysis and interpretation, and manuscript writing.

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Authors and Affiliations

  1. Research Center for Urban Forestry, The Key Laboratory for Silviculture and Conservation of Ministry of Education, Beijing Forestry University, Key Laboratory for Silviculture and Forest Ecosystem of State Forestry and Grassland Administration , Beijing Forestry University, Beijing, 100083, China

    Jiyou Zhu, Jingliang Xu, Yujuan Cao, Jing Fu, Guangpeng Sun, Xinna Zhang & Chengyang Xu

  2. Production and Operation Management Department, China Communications Construction Company, Beijing, 100088, China

    Benling Li

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  1. Jiyou Zhu
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Contributions

JZ, JX and BL designed the experimental scheme (JZ and JX participated in plant monitoring, and BL participated in the division of urban environment-traffic area). JZ and JX analyzed the data, made the charts, wrote and revised the manuscript. JZ, YC, JF, GS, XZ and CX involved in the preparation of the tools and instruments needed for the experiment. JZ, JX, JF and YC carried out the field trial experiments. JZ, JX, JF and CX contributed to the literature collection, materials and tools, supervision and project administration and plant identification (Identification information refers to Flora of China). All the authors have read the manuscript, approved the manuscript and declared that they have no competing interests.

Corresponding author

Correspondence to Chengyang Xu.

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Ethics approval and consent to participate

This experiment does not involve human experiments and animal experiments. The field trial experiments in the current study were permitted by the local government in China (Beijing Gardening and Greening Bureau), including the collection of leaf samples.

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The authors declare no conflict of interest.

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Zhu, J., Xu, J., Cao, Y. et al. Leaf reflectance and functional traits as environmental indicators of urban dust deposition. BMC Plant Biol 21, 533 (2021). https://doi.org/10.1186/s12870-021-03308-8

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BMC Plant Biology

ISSN: 1471-2229

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