Indirect Green Facades: Exploring the Efficiency of Ornamental Climbers

S
S. Dariqul Hameed1
S
S. Anandhi1,*
C
C. Kanimozhi1
P
P. Chandrasekaran2
1Department of Floriculture and Landscape Architecture, SRM College of Agricultural Sciences, SRM Institute of Science and Technology, Baburayanpettai, Chengalpattu-603 201, Tamil Nadu, India.
2Department of Basic Sciences, SRM College of Agricultural Sciences, SRM Institute of Science and Technology, Baburayanpettai, Chengalpattu-603 201, Tamil Nadu, India.

Background: Urban air pollution and environmental stress can be mitigated by vertical greening systems (VGS), where indirect green facades enhance thermal regulation, air quality, biodiversity and psychological well-being. However, comprehensive screening of ornamental climbers for their morphological, physiological, biochemical and anatomical suitability to indirect green facades is lacking. This study aimed to assess these traits to determine climbers’ potential resistance to air pollution and growth performance on indirect green facades.

Methods: Twelve ornamental climbers were screened for indirect green facade adaptation using randomized block design with 3 replications on a 7 ft × 5 ft iron-framed structure. Frame coverage, stem girth, branches per plant, leaves per branch, leaf area, stomatal density, trichome density, total chlorophyll, ascorbic acid, leaf pH, relative water content and air pollution tolerance index (APTI) were recorded at 180 days after planting.

Result: Clitoria ternatea, Basella alba, Passiflora edulis, Ipomoea purpurea, Thunbergia grandiflora, Antigonon leptopus, Jacquemontia pentanthos and Dolichandra unguis-cati recorded 100% frame coverage, while maximum stem girth occurred in Basella alba (3.16 cm). Ipomoea purpurea (18.68) and Antigonon leptopus (18.21) recorded the highest APTI values (tolerant category), followed by Passiflora edulis (17.80, moderately tolerant); remaining climbers fell in the intermediate category. Abaxial stomatal density was highest in Dolichandra unguis-cati (61.00 mm²) and abaxial trichome density was highest in Clitoria ternatea (92.00 mm²). Ipomoea purpurea, Antigonon leptopus and Passiflora edulis evergreen, simple leaved and fast covering emerged as the most suitable climbers for indirect green facades.

Ornamental climbers are frequently favored in urban environments, a preference stemming from their swift growth, visual appeal and capacity to acclimate to diverse environmental factors. On the other hand, there are significant variations among climbing plant species in terms of growth rate, branching patterns, leaf size, canopy density and area coverage. These features have a direct impact on the effectiveness of shade and the degree to which wall temperatures are lowered. Climbing plants are better at concealing sunlight and enhancing thermal performance because they have denser leaves and grow more quickly in both height and width (Köhler, 2008). Despite the growing prevalence of ornamental climbing plants in green facade systems, a comprehensive assessment of their efficacy in controlled environments is lacking. Instead than focusing on the unique performance characteristics of certain species, current research emphasizes the overall advantages of vertical greenery. Even with vertical greening systems becoming more common, the process behind choosing which plants to use hasn’t really caught up. Farrokhirad et al. (2024) point out that most existing design frameworks skip over a proper species-selection step altogether, defaulting instead to generic approaches that treat all climbers as roughly interchangeable. That assumption doesn’t hold up well in practice. Sethupathy et al., (2025) found that even common, easily available ornamental climbers can vary quite a bit in how well they actually cool a building. This is exactly the gap the present study sets out to close, through a systematic, multi-parameter comparison of ornamental climbing species for indirect green facade use. Therefore, an assessment of decorative climbers is essential to find species that, when incorporated into indirect green facades, demonstrate quick establishment, ideal coverage and improved cooling benefits (Perini et al., 2011). The purpose of this study is to evaluate specific decorative climbing plants’ compatibility and performance for indirect green facade systems. The assessment will concentrate on foliar density, coverage extent, branching frequency and essential growth features. As a result, the findings of this study will help choose the best climbing plants, supporting sustainable urban landscaping techniques and improving building thermal management.
At SRM College of Agricultural Sciences, Chengalpattu, an experiment was carried out to assess ornamental climbers appropriate for indirect green façades during the year 2025-26. The location lies between latitudes 12°23′19.7"N and longitudes 79°44′37.4"E, with an average elevation of 50 m and a relative humidity of 50-70%. The region’s average temperature varied between 23°C and 38°C. An iron frame construction with supporting poles on both sides and a frame height of seven feet and width of five feet was used for the experiment (Fig 1). The experiment was laid out in a randomaized block design (RBD) with three replications. The treatment involves twelve ornamental climbers viz., T1-Butterfly pea (Clitoria ternatea L.), T2-Malabar spinach (Basella alba L.), T3-Passion fruit (Passiflora edulis Sims.), T4-Garlic vine (Mansoa alliacea (Lam.) A.H.Gentry),T5-Morning glory [Ipomoea tricolor (L.) Roth], T6-Blue Trumpet Vine [Thunbergia grandiflora (Roxb. ex Rottler) Roxb], T7-Rangoon creeper [Quisqualis indica (L.) DeFilipps], T8-Coral vine (Antigonon leptopus Hook. and Arn.), T9-Skyblue clustervine [Jacquemontia pentanthos (Jacq.) G.Don.], T10-Rock trumpet [Mandevilla splendens (Hook.f.) woodson], T11-ornamental Grape vine (Vitis vinifera L.), T12-Cat’sclaw vine (Dolichandra unguis-cati). The observations were recorded on the botanical (habit, evergreen or deciduous and leaf type), morphological (frame coverage, stem girth, number of branches/plant and number of leaf per branch, leaf area), anatomical (stomatal density and trichome density), biochemical (chlorophyll content, ascorbic acid, leaf pH), physiological (relative water content, APTI value) characteristics. The Air Pollution Tolerance Index was calculated following the method of Singh and Rao (1983). 



Where,
A = Ascorbic acid content (mg/g).
T= Total chlorophyll content (mg/g).
P= Leaf extract pH.
R= Relative water content (%) of the leaf sample.

Fig 1: Dimensions of the Iron frame designed for this experiment.


       
ANOVA was performed on the collected data using statistical software RStudio in accordance with the design. The F-test was used to determine whether there were significant changes between treatments and CD was used to compare means at the 5% level.
Botanical characteristics
 
Among the ornamental climbers studied, Clitoria ternatea, Basella alba, Antigonon leptopus, Jacquemontia pentanthos are herbaceous perennial, Passiflora edulis, Mansoa alliacea, Thunbergia grandiflora, Quisqualis indica, Vitis vinifera, Dolichandra unguis-cati are woody perennials, while Ipomoea purpurea is a herbaceous annual climber. Ipomoea purpurea and Vitis vinifera are deciduous in nature while all the other species are evergreen. The leaf type of Clitoria ternatea, Mansoa alliacea and Dolichandra unguis-cati are compound while all the other species should bears simple leaf (Table 1).

Table 1: Botanical characteristics of ornamental climbers.


 
Morphological parameters
 
All the morphological parameters showed significant difference among the treatments (Table 2). At 180 days of planting, Clitoria ternatea, Basella alba, Passiflora edulis, Ipomoea purpurea, Thunbergia grandiflora, Antigonon leptopus, Jacquemontia pentanthos, Dolichandra unguis-cati species covered 100.00% of the installed iron frame, while Vitis vinifera covered 75.00%, Mansoa alliacea covered 50.00% and Quisqualis indica and Mandevilla splendens covered only 25.00% of the frame. The maximum stem girth was recorded in T2 (3.16 cm), followed by T3 (2.90 cm), whereas the minimum was found in T10 (1.80 cm). The number of branches per plant was highest in T5 (47.00), followed by T1 (33.96), whereas the lowest was recorded in T10 (1.00). The highest number of leaves per branch was observed in T5 (62.00), followed by T3 and T4 (47.00), while the lowest was recorded in T11 (5.00).

Table 2: Morphological and anatomical characteristics of ornamental climbers.


 
Physiological and biochemical characteristics
 
To examine the possible role of physiological and biochemical components influencing air pollution tolerance index were analysed and presented in Table 3. Ascorbic acid content was significantly varied across the 11 species that were studied and it ranges from 14.01 to 6.94 mg/g FW across the species. Ipomoea purpurea (14.01 mg/g FW) followed by Passiflora edulis (13.99 mg/g FW) and Antigonon leptopus (13.99 mg/g FW) recorded the highest ascorbic acid compared to species like Thunbergia grandiflora which recorded the least ascorbic acid of 6.94 mg/g FW. It is observed that all the ornamental climbers exhibited a leaf pH towards acidic side from 4.57 to 6.24. Plants like Mansoa alliacea recorded the highest pH among them i.e., 6.24 pH, followed by Basella alba and Thunbergia grandiflora with the pH of 5.94, while Mandevilla recorded the lowest pH of 4.57. The relative water content (RWC) varied from 84.75 % to 65.70 % across the studied species. The relative water content was high in some of the species like Thunbergia grandiflora (84.75%), Passiflora edulis (83.23%), Basella alba (82.45%), Vitis vinifera (82.62%) and Dolichandra unguis-cati (82.05%) and low in Mandevilla splendens (65.70%). Among the studied species total chlorophyll content was found to be highest (1.51 mg/g FW) in Clitoria ternatea and Antigonon leptopus, followed by Ipomoea purpurea (1.28 mg/g FW). The climbers like Basella alba showed the lowest total chlorophyll content (0.36 mg/g FW).

Table 3: Biochemical, physiological characteristics and the APTI value of ornamental climbers.


 
Air pollution tolerance index (APTI) value
 
The APTI value estimated using the four biochemical parameters in plant leaves namely, RWC, total chlorophyll content, leaf pH and ascorbic acid value, can be used as a predictor of air quality.
       
In the present study, Ipomoea purpurea and Antigonon leptopus recorded the APTI of 18.68 and 18.21 respectively coming under tolerant category, followed by Passiflora edulis (17.80) being moderately tolerant. All the other species falls in intermediate category of APTI response with the values ranging from 10.95 to 13.73.
 
Anatomical characteristics
 
The leaf stomatal density was higher on the abaxial surface in the species studied ranging from 61.00 mm2 in Dolichandra unguis-cati to 26.66 mm2  in Basella alba (Table 2). Stomata was absent on the adaxial leaf surface in other species. Basella albarecorded the maximum stomatal density (67.33 mm2) on the adaxial leaf surface, while Ipomoea purpurearecorded the minimum stomatal density (5.66 mm²). Clitoria ternatea, Passiflora edulis, Thunbergia grandiflora, Quisqualis indica and Antigonon leptopus bears trichomes on both abaxial and adaxial leaf surface. Jacquemontia pentanthos bears trichomes only on the adaxial surface while Vitis vinifera bears only on the abaxial surface. The trichome density on the adaxial surface was highest in Passiflora edulis (69.66 mm2), followed by Clitoria ternatea (41.00 mm2). The trichome density on the abaxial surface was highest in Clitoria ternatea (92.00 mm2), followed by Antigonon leptopus (62.33 mm2).
       
Climbing plants have a lot of potential for urban vertical greening since they use unique vertical growth processes. The suitability of ornamental climbers for use in indirect green façades has been tested using an inexpensive iron-framed indirect green façade construction. In green facade systems, frame coverage that influences climbers’ capacity to spread also enhances shade effectiveness and helps control the microclimate. In the present study, Clitoria ternatea, Basella alba, Passiflora edulis, Ipomoea purpurea, Thunbergia grandiflora, Antigonon leptopus, Jacquemontia pentanthos, Dolichandra unguis-cati exhibited faster growth and covered the frame at 180 days of planting (Fig 2). Azhar et al., (2018) revealed similar results regarding frame coverage by Anemopaegma chamberlaynii, Antigonon leptopus and Quisqualis indica. Because of the pattern of foliage coverage, Vitis vinifera, Mansoa alliacea, Quisqualis indica and Mandevilla splendens displayed slow frame coverage. According to Azhar et al., (2018), Quisqualis indicafoliage pattern cascades downward and the stem climbs twinning vertically over the supporting structure with less leaf coverage before reaching the highest point of the structure. These findings are consistent with the current study.

Fig 2: Plant coverage on the iron frame


       
Climbing plants’ canopy expansion and productivity are significantly influenced by their stem girth, number of branches per plant and leaf output, which indicates the plants’ capacity for photosynthetic processes.In the present study, Passiflora edulis, Ipomoea purpurea, Antigonon leptopus, Thunbergia grandiflora and Jacquemontia pentanthos showed higher values for stem girth, number of branches and number of leaves per plant. These species are evergreen and bears simple leaf. According to earlier research, shoot branching is crucial in defining the overall performance and architecture of plants (Leyser, 2009). Perini et al., (2017) found that dense foliage development in climbers enhances thermal regulation and environmental performance of green facade systems, which is corresponding to the current findings on big leaf area in Vitis vinifera and Thunbergia grandiflora. Better photosynthesis and growth are supported by increased branching, which also increases light interception and plant spread. In general, plants with more leaves have more photosynthetic surface area. Additionally, it helps to increase the density of the canopy. Increased leaf numbers improve photosynthetic capability and growth performance, according to research by Larcher (2003). Antigonon leptopus had the lowest number of leaves per plant and the highest number of branches in the current study. This is in accordance with Azhar et al. (2018). The leaf has a tendency to expand quickly before experiencing rapid withering and death. As a result, the leaf has a shorter lifespan, which is thought to be caused by the fast rate of photosynthetic absorption, particularly in tropical plants.
       
The water in the plant tissue can be determined using Relative Water Content (RWC). According to Seyyednejad et al., (2017), a significant amount of water in plant tissue aids in preserving its physiological equilibrium under stressful circumstances. The relative water content was highest in Basella alba, Passiflora edulis, Thunbergia grandiflora, Quisqualis indica, Vitis vinifera and Dolichandra unguis-cati ranging from 84.75% to 82.05%. Relative water content, which indicates the water balance and cellular stability of plant tissues, is one of the key physiological activities used to assess plant tolerance to atmospheric contaminants, according to a similar study published by. The plant species’ resistance to stress is increased by high RWC (Kumar et al., 2014).  According to Joshi et al. (2009) and Pavlović et al. (2014), total chlorophyll is regarded as a measure of photosynthetic activity, growth and biomass productivity. Clitoria ternatea and Antigonon leptopus had the greatest total chlorophyll content (1.51 mg/g FW) in the current investigation. The result illustrates how plants’ physiological health and photosynthetic efficiency differ. Environmental stressors like air pollution can lower the content of chlorophyll by damaging the architecture of chloroplasts and interfering with the synthesis of pigments.The outcome is similar to that of who discovered that plants exposed to external pollutants frequently exhibit chlorophyll degradation.  Higher leaf pH values were recorded by Mansoa alliacea, Basella alba and Thunbergia grandiflora, indicating their greater resistance to air contaminants. Early research by Chaudhary and Rao (1977) found that leaf pH plays a major influence in influencing a plant’s sensitivity to air contaminants. An essential antioxidant molecule in plant defense mechanisms against oxidative stress is ascorbic acid. Because ascorbic acid protects cellular components and photosynthetic pigments from oxidative damage, plants with higher ascorbic acid contents are more resilient to contaminants. Increased ascorbic acid concentration enhances plant resilience to air contaminants, a conclusion corroborated by Keller and Schwager (1977).
       
APTI is an effective method for green belt development, according to studies done by different academics. Plants’ degree of tolerance to air pollutants is assessed using the Air Pollution Tolerance Index (APTI). When the APTI value is ≤11, the plant is sensitive; when it is 12-16, it is intermediate; and when it is ≥17, it is tolerant of air pollution (Padmavathi et al., 2013; Shrestha et al., 2021). Higher APTI values in the current study indicate that Ipomoea purpurea (18.68) and Antigonon leptopus (18.21) are typically thought to be tolerant of contaminated settings. In a similar vein, earlier research by showed that plants with higher APTI values have better physiological defense mechanisms and are appropriate for planting in metropolitan areas that are contaminated.This result is consistent with that of Pandey et al., (2016), who found that Ipomoea palmata, Thunbergia grandiflora, C. splendens, A. elegans, Q. indica, Petria volubilis and Antigonon leptopus had the highest APTI values and were excellent choices for green façade. Additionally, Ipomoea purpurea had the highest APTI value in the current study, which is in line with finding that deciduous species have high APTI. Additionally, Quisqualis indica (12.35 ATPI value) in this study indicated an intermediate response, that corresponds to Jim (2015) findings. Similar APTI based screening was conducted by Akilan and Nandhakumar (2016) in Vellore district, Tamil Nadu, where plant species growing in industrial and transportation-heavy zones consistently recorded higher APTI values than those from less polluted college farm sites, reinforcing the reliability of ascorbic acid, chlorophyll, leaf pH and relative water content as robust biochemical indicators for species screening.
       
In general, plants with dense stomata use water more efficiently and have higher stomatal conductance. On the other hand, because stomatal conductance and transpiration are reduced, a drop in stomatal density may result in a conservative use of water (Dittberner et al., 2018). In the present study, the Dolichandra unguis-cati followed by Quisqualis indica and Passiflora edulisrecorded higher values for stomatal density per mm2. Hypostomatic leaves were observed in Thunbergia grandiflora, Quisqualis indica, Antigonon leptopus, Jacquemontia pentanthos, Mandevilla splendens, Vitis vinifera, Dolichandra unguis-cati, Passiflora edulis, Mansoa alliacea. Because stomata are the main entrance point for gaseous contaminants into leaves, related research by Winner (1981) demonstrates that stomatal features have a substantial impact on plant exposure to air pollutants. The results of Durodola et al. (2025) are in line with the stomatal density of Quisqualis indica in the current investigation. This trade off pattern between structural traits is consistent with findings by Ramírez-Soto et al. (2026), who reported a significant negative correlation between stomatal area and trichome density on both leaf surfaces in Kabuli chickpea cultivars, suggesting that species investing more in trichome development tend to develop smaller, more conservative stomata as part of an adaptive water-use strategy.
       
Increased trichome density may improve plants’ ability to fend off contaminants. The quantity of particulate matter adsorbed on the leaf surface is correlated with the number of trichomes on the leaf surface (Chen et al., 2017). Clitoria ternatea, Passiflora edulis, Thunbergia grandiflora, Quisqualis indica, Antigonon leptopus, Jacquemontia pentanthosbears trichomes on the both the abaxial and adaxial surface of the leaf which is one of the selection criteria for pollution control. In the present study, the ultrastructure of the trichomes in Vitis vinifera was explored with transmission electron microscopy. On the abaxial surface, the ribbon trichomes are twisted, greatly elongated possessing erect and prostrate trichomes, the prostrate type completely covered the erect form (Fig 3). Domanda et al. (2023); Fambrini et al. (2021) and Gago et al. (2016) have reported similar findings regarding the existence of prostrate and erect trichomes. According to earlier research, trichomes serve as protective structures that lessen environmental harm and increase a plant’s resistance to external stress (Werker, 2000). According to Jeong et al., (2021) and Hellebaut et al. (2022), trichomes on the leaf surface exhibit the highest level of particulate matter reduction. This investigation likewise produced comparable results. This protective function of trichome density aligns with the findings of Satish et al., (2023), who demonstrated in pigeonpea that genotypes with higher pod trichome density and length experienced significantly reduced pest damage, indicating that dense trichome coverage functions as a physical barrier against external stressors, whether biotic pests or airborne particulate matter.

Fig 3: Scanning electron microscopic (SEM) images of trichomes present in the ornamental climbers.

This study indicated that ornamental climbers exhibit a wide range of morphological, physiological, biochemical and anatomical traits that affect their adaptation to green façades. Ipomoea purpurea, Antigonon leptopus and Passiflora edulis are among the climbers that are most suited for indirect green façades.
The authors declare no conflicts of interest regarding this manuscript.

  1. Akilan, M. and Nandhakumar, S. (2016). Air pollution tolerance index of selected plants in industrial and urban areas of Vellore district. Agricultural Science Digest. 36(1): 66-68. doi: 10.18805/asd.v35i1.9315.

  2. Arnon, D.I. (1949). Copper enzymes in isolated chloroplasts: Polyphenoloxidase in Beta vulgaris. Plant Physiology. 24(1): 1-15.

  3. Azhar, M.S.M.K., Shahidan, M.F., Jamil, M. and Mohd, Z.M. F. (2018). Percentage coverage of tropical climbing plants of green facade. IOP Conference Series: Materials Science and Engineering. 401(1): 012025. doi: 10.1088/1757-899X/ 401/1/012025.

  4. Chaudhary, C.S. and Rao, D.N. (1977). Study of some factors in plants controlling their susceptibility to SO2 pollution. Proceedings of the Indian National Science Academy, Part B. 46: 211-236.

  5. Chen, L., Liu, C., Zhang, L., Zou, R. and Zhang, Z. (2017). Variation in tree species ability to capture and retain airborne fine particulate matter (PM2.5). Scientific Reports. 7(1): 3206. doi: 10.1038/s41598-017-03360-1.

  6. Dittberner, H., Korte, A., Mettler-Altmann, T., Weber, A.P., Monroe, G. and De Meaux, J. (2018). Natural variation in stomata size contributes to the local adaptation of water-use efficiency in Arabidopsis thaliana. Molecular Ecology. 27(20): 4052-4065. doi: 10.1111/mec.14838.

  7. Domanda, C., Nuzzo, V., Montanaro, G., Failla, O. and Rustioni, L. (2023). Trichomes affect grapevine leaf optical properties and thermoregulation. Theoretical and Experimental Plant Physiology. 35(3): 299-308. doi: 10.1007/s40626- 023-00287-z.

  8. Durodola, T.A., Mudasiru, O.M., Idowu, D.A. and Umoren, O.D. (2025). Taxonomic implications of leaf epidermal anatomy in some members of genus Quisqualis L. and Guiera senegalensis J. F. Gmel. species. Species. 26: 1-8.

  9. Fambrini, M., Landi, M. and Pugliesi, C. (2021). Erinea in the ‘Ansonica’ grapevine cultivar: Trichome complement, histological effects and analysis of chlorophyll fluorescence in affected leaves. Vitis. 60(3): 101-108. doi: 10.5073/ vitis.2021.60.

  10. Farrokhirad, E., Rigillo, M., Köhler, M. and Perini, K. (2024). Optimising vertical greening systems for sustainability: An integrated design approach. International Journal of Sustainable Energy. 43(1): 2411831.

  11. Gago, P., Conejero, G., Martínez, M. C., Boso, S., This, P. and Verdeil, J.L. (2016). Microanatomy of leaf trichomes: Opportunities for improved ampelographic discrimination of grapevine (Vitis vinifera L.) cultivars. Australian Journal of Grape and Wine Research. 22(3): 494-503. doi: 10.1111/ajgw.12226.

  12. Hellebaut, A., Boisson, S. and Mahy, G. (2022). Do plant traits help to design green walls for urban air pollution control? A short review of scientific evidence and knowledge gaps. Environmental Science and Pollution Research. 29(54): 81210-81221.

  13. Jeong, N.R., Kim, J.H., Han, S.W., Kim, J.C. and Kim, W.Y. (2021). Assessment of the particulate matter reduction potential of climbing plants on green walls for air quality management. Journal of People, Plants and Environment. 24(4): 377- 387. doi: 10.11628/ksppe.2021.24.4.377.

  14. Jim, C.Y. (2015). Assessing growth performance and deficiency of climber species on tropical greenwalls. Landscape and Urban Planning. 137: 107-121. doi: 10.1016/j.landurbplan. 2015.01.001.

  15. Joshi, M., Kamble, S.P., Labhsetwar, N.K., Parwate, D.V. and Rayalu, S.S. (2009). Chlorophyll-based photocatalysts and their evaluation for methyl orange photoreduction. Journal of Photochemistry and Photobiology A: Chemistry. 204(2-3): 83-89. doi: 10.1016/j.jphotochem.2009.01.016.

  16. Keller, T. and Schwager, H. (1977). Air pollution and ascorbic acid. European Journal of Forest Pathology. 7(6): 338-350. doi: 10.1111/j.1439-0329.1977.tb00603.x.

  17. Köhler, M. (2008). Green facades-a view back and some visions. Urban Ecosystems. 11(4): 423-436. doi: 10.1007/s11252- 008-0063-x.

  18. Kumar, S., Dwivedi, S. K., Singh, S.S., Bhatt, B.P., Mehta, P., Elanchezhian, R. and Singh, O.N. (2014). Morpho-physiological traits associated with reproductive stage drought tolerance of rice (Oryza sativa L.) genotypes under rain-fed condition of eastern indo-gangetic plain. Indian Journal of Plant Physiology. 19(2): 87-93. doi: 10.1007/s40502- 014-0075-x.

  19. Larcher, W. (2003). Physiological Plant Ecology: Ecophysiology and Stress Physiology of Functional Groups. Springer Science and Business Media.

  20. Leyser, O. (2009). The control of shoot branching: An example of plant information processing. Plant, Cell and Environment. 32(6): 694-703. doi: 10.1111/j.1365-3040.2009.01930.x.

  21. Padmavathi, P., Cherukuri, J. and Reddy, M.A. (2013). Impact of air pollution on crops in the vicinity of a power plant: A case study. International Journal of Engineering Research and Technology. 2(12): 3641-3651.

  22. Pandey, A.K., Pandey, M. and Tripathi, B.D. (2016). Assessment of air pollution tolerance index of some plants to develop vertical gardens near street canyons of a polluted tropical city. Ecotoxicology and Environmental Safety. 134: 358-364. doi: 10.1016/j.ecoenv.2015.08.028.

  23. Pavlović, D., Nikolić, B., Đurović, S., Waisi, H., Anđelković, A. and Marisavljević, D. (2014). Chlorophyll as a measure of plant health: Agroecological aspects. Pesticidi i Fitomedicina. 29(1): 21-34. doi: 10.2298/PIF1401021P.

  24. Perini, K., Bazzocchi, F., Croci, L., Magliocco, A. and Cattaneo, E. (2017). The use of vertical greening systems to reduce the energy demand for air conditioning: Field monitoring in mediterranean climate. Energy and Buildings. 143: 35-42. doi: 10.1016/j.enbuild.2017.03.036.

  25. Perini, K., Ottelé, M., Fraaij, A.L.A., Haas, E.M. and Raiteri, R. (2011). Vertical greening systems and the effect on air flow and temperature on the building envelope. Building and Environment. 46(11): 2287-2294. doi: 10.1016/j.buildenv. 2011.05.009.

  26. Prasad, B.J. and Rao, D.N. (1982). Relative sensitivity of a metropolitan plant species to SO2 and O3 pollution. Environmental Pollution (Series A). 29(1): 57-70.

  27. Ramírez-Soto, M., Márquez-Godoy, J.N., Cota-Barreras, C.I., Gutiérrez- Gutiérrez, O.G., Pérez-Álvarez, J.G. and Acosta-Gallegos, J.A. (2026). Morphological analysis of stomata of Cicer arietinum L. Legume Research. 49(5): 798-805. doi: 10.18805/LRF-907.

  28. Satish, K., Muniswamy, S., Girish, G., Kulkarni, V., Diwan, J.R., Geeta, S.N., Pandey, S. and Singh, I.P. (2023). Pod trichome characterisation using foldscope, morphological characterization and genetic diversity among indigenous collections of pigeonpea [Cajanus cajan (L.) Millsp.]. Legume Research. 46(8): 1013-1019. doi: 10.18805/LR-4423.

  29. Sethupathy, D., Sarathchandran, R. and Rana, D.P. (2025). Exploring the efficiency of indirect green façades with native plants to lower rising façade temperatures: A way to improve urban living in tropical regions. Journal of Urban Regeneration and Renewal. 18(3): 288-312.

  30. Seyyednejad, S.M., Motamedi, H. and Lordifard, P. (2017). Biochemical changes of Conocarpus erectus (Combretaceae) in response to gas refinery air pollution as an air pollution indicator. Pollution. 3(2): 185-190. doi: 10.7508/pj.2017. 02.002.

  31. Shrestha, S., Baral, B., Dhital, N.B. and Yang, H.H. (2021). Assessing air pollution tolerance of plant species in vegetation traffic barriers in Kathmandu Valley, Nepal. Sustainable Environment Research. 31(1): 3. doi: 10.1186/s42834- 020-00076-2.

  32. Singh, S.K. and Rao, D.N. (1983). Evaluation of the plants for their tolerance to air pollution. Proceedings of the Symposium on Air Pollution Control. 1: 218-224.

  33. Werker, E. (2000). Trichome diversity and development. Annals of Botany. 85(Suppl. A). doi: 10.1016/S0065-2296(00)31005-9.

  34. Winner, W.E. (1981). The Effect of SO2 on Photosynthesis and Stomatal Behavior of Mediterranean-Climate Shrubs and Trees. In Components of Productivity of Mediterranean- Climate Regions: Basic and Applied Aspects. Proceedings of the International Symposium on Photosynthesis, Primary Production and Biomass Utilization in Mediterranean- Type Ecosystems, Kassandra, Greece (pp. 91-103).

Indirect Green Facades: Exploring the Efficiency of Ornamental Climbers

S
S. Dariqul Hameed1
S
S. Anandhi1,*
C
C. Kanimozhi1
P
P. Chandrasekaran2
1Department of Floriculture and Landscape Architecture, SRM College of Agricultural Sciences, SRM Institute of Science and Technology, Baburayanpettai, Chengalpattu-603 201, Tamil Nadu, India.
2Department of Basic Sciences, SRM College of Agricultural Sciences, SRM Institute of Science and Technology, Baburayanpettai, Chengalpattu-603 201, Tamil Nadu, India.

Background: Urban air pollution and environmental stress can be mitigated by vertical greening systems (VGS), where indirect green facades enhance thermal regulation, air quality, biodiversity and psychological well-being. However, comprehensive screening of ornamental climbers for their morphological, physiological, biochemical and anatomical suitability to indirect green facades is lacking. This study aimed to assess these traits to determine climbers’ potential resistance to air pollution and growth performance on indirect green facades.

Methods: Twelve ornamental climbers were screened for indirect green facade adaptation using randomized block design with 3 replications on a 7 ft × 5 ft iron-framed structure. Frame coverage, stem girth, branches per plant, leaves per branch, leaf area, stomatal density, trichome density, total chlorophyll, ascorbic acid, leaf pH, relative water content and air pollution tolerance index (APTI) were recorded at 180 days after planting.

Result: Clitoria ternatea, Basella alba, Passiflora edulis, Ipomoea purpurea, Thunbergia grandiflora, Antigonon leptopus, Jacquemontia pentanthos and Dolichandra unguis-cati recorded 100% frame coverage, while maximum stem girth occurred in Basella alba (3.16 cm). Ipomoea purpurea (18.68) and Antigonon leptopus (18.21) recorded the highest APTI values (tolerant category), followed by Passiflora edulis (17.80, moderately tolerant); remaining climbers fell in the intermediate category. Abaxial stomatal density was highest in Dolichandra unguis-cati (61.00 mm²) and abaxial trichome density was highest in Clitoria ternatea (92.00 mm²). Ipomoea purpurea, Antigonon leptopus and Passiflora edulis evergreen, simple leaved and fast covering emerged as the most suitable climbers for indirect green facades.

Ornamental climbers are frequently favored in urban environments, a preference stemming from their swift growth, visual appeal and capacity to acclimate to diverse environmental factors. On the other hand, there are significant variations among climbing plant species in terms of growth rate, branching patterns, leaf size, canopy density and area coverage. These features have a direct impact on the effectiveness of shade and the degree to which wall temperatures are lowered. Climbing plants are better at concealing sunlight and enhancing thermal performance because they have denser leaves and grow more quickly in both height and width (Köhler, 2008). Despite the growing prevalence of ornamental climbing plants in green facade systems, a comprehensive assessment of their efficacy in controlled environments is lacking. Instead than focusing on the unique performance characteristics of certain species, current research emphasizes the overall advantages of vertical greenery. Even with vertical greening systems becoming more common, the process behind choosing which plants to use hasn’t really caught up. Farrokhirad et al. (2024) point out that most existing design frameworks skip over a proper species-selection step altogether, defaulting instead to generic approaches that treat all climbers as roughly interchangeable. That assumption doesn’t hold up well in practice. Sethupathy et al., (2025) found that even common, easily available ornamental climbers can vary quite a bit in how well they actually cool a building. This is exactly the gap the present study sets out to close, through a systematic, multi-parameter comparison of ornamental climbing species for indirect green facade use. Therefore, an assessment of decorative climbers is essential to find species that, when incorporated into indirect green facades, demonstrate quick establishment, ideal coverage and improved cooling benefits (Perini et al., 2011). The purpose of this study is to evaluate specific decorative climbing plants’ compatibility and performance for indirect green facade systems. The assessment will concentrate on foliar density, coverage extent, branching frequency and essential growth features. As a result, the findings of this study will help choose the best climbing plants, supporting sustainable urban landscaping techniques and improving building thermal management.
At SRM College of Agricultural Sciences, Chengalpattu, an experiment was carried out to assess ornamental climbers appropriate for indirect green façades during the year 2025-26. The location lies between latitudes 12°23′19.7"N and longitudes 79°44′37.4"E, with an average elevation of 50 m and a relative humidity of 50-70%. The region’s average temperature varied between 23°C and 38°C. An iron frame construction with supporting poles on both sides and a frame height of seven feet and width of five feet was used for the experiment (Fig 1). The experiment was laid out in a randomaized block design (RBD) with three replications. The treatment involves twelve ornamental climbers viz., T1-Butterfly pea (Clitoria ternatea L.), T2-Malabar spinach (Basella alba L.), T3-Passion fruit (Passiflora edulis Sims.), T4-Garlic vine (Mansoa alliacea (Lam.) A.H.Gentry),T5-Morning glory [Ipomoea tricolor (L.) Roth], T6-Blue Trumpet Vine [Thunbergia grandiflora (Roxb. ex Rottler) Roxb], T7-Rangoon creeper [Quisqualis indica (L.) DeFilipps], T8-Coral vine (Antigonon leptopus Hook. and Arn.), T9-Skyblue clustervine [Jacquemontia pentanthos (Jacq.) G.Don.], T10-Rock trumpet [Mandevilla splendens (Hook.f.) woodson], T11-ornamental Grape vine (Vitis vinifera L.), T12-Cat’sclaw vine (Dolichandra unguis-cati). The observations were recorded on the botanical (habit, evergreen or deciduous and leaf type), morphological (frame coverage, stem girth, number of branches/plant and number of leaf per branch, leaf area), anatomical (stomatal density and trichome density), biochemical (chlorophyll content, ascorbic acid, leaf pH), physiological (relative water content, APTI value) characteristics. The Air Pollution Tolerance Index was calculated following the method of Singh and Rao (1983). 



Where,
A = Ascorbic acid content (mg/g).
T= Total chlorophyll content (mg/g).
P= Leaf extract pH.
R= Relative water content (%) of the leaf sample.

Fig 1: Dimensions of the Iron frame designed for this experiment.


       
ANOVA was performed on the collected data using statistical software RStudio in accordance with the design. The F-test was used to determine whether there were significant changes between treatments and CD was used to compare means at the 5% level.
Botanical characteristics
 
Among the ornamental climbers studied, Clitoria ternatea, Basella alba, Antigonon leptopus, Jacquemontia pentanthos are herbaceous perennial, Passiflora edulis, Mansoa alliacea, Thunbergia grandiflora, Quisqualis indica, Vitis vinifera, Dolichandra unguis-cati are woody perennials, while Ipomoea purpurea is a herbaceous annual climber. Ipomoea purpurea and Vitis vinifera are deciduous in nature while all the other species are evergreen. The leaf type of Clitoria ternatea, Mansoa alliacea and Dolichandra unguis-cati are compound while all the other species should bears simple leaf (Table 1).

Table 1: Botanical characteristics of ornamental climbers.


 
Morphological parameters
 
All the morphological parameters showed significant difference among the treatments (Table 2). At 180 days of planting, Clitoria ternatea, Basella alba, Passiflora edulis, Ipomoea purpurea, Thunbergia grandiflora, Antigonon leptopus, Jacquemontia pentanthos, Dolichandra unguis-cati species covered 100.00% of the installed iron frame, while Vitis vinifera covered 75.00%, Mansoa alliacea covered 50.00% and Quisqualis indica and Mandevilla splendens covered only 25.00% of the frame. The maximum stem girth was recorded in T2 (3.16 cm), followed by T3 (2.90 cm), whereas the minimum was found in T10 (1.80 cm). The number of branches per plant was highest in T5 (47.00), followed by T1 (33.96), whereas the lowest was recorded in T10 (1.00). The highest number of leaves per branch was observed in T5 (62.00), followed by T3 and T4 (47.00), while the lowest was recorded in T11 (5.00).

Table 2: Morphological and anatomical characteristics of ornamental climbers.


 
Physiological and biochemical characteristics
 
To examine the possible role of physiological and biochemical components influencing air pollution tolerance index were analysed and presented in Table 3. Ascorbic acid content was significantly varied across the 11 species that were studied and it ranges from 14.01 to 6.94 mg/g FW across the species. Ipomoea purpurea (14.01 mg/g FW) followed by Passiflora edulis (13.99 mg/g FW) and Antigonon leptopus (13.99 mg/g FW) recorded the highest ascorbic acid compared to species like Thunbergia grandiflora which recorded the least ascorbic acid of 6.94 mg/g FW. It is observed that all the ornamental climbers exhibited a leaf pH towards acidic side from 4.57 to 6.24. Plants like Mansoa alliacea recorded the highest pH among them i.e., 6.24 pH, followed by Basella alba and Thunbergia grandiflora with the pH of 5.94, while Mandevilla recorded the lowest pH of 4.57. The relative water content (RWC) varied from 84.75 % to 65.70 % across the studied species. The relative water content was high in some of the species like Thunbergia grandiflora (84.75%), Passiflora edulis (83.23%), Basella alba (82.45%), Vitis vinifera (82.62%) and Dolichandra unguis-cati (82.05%) and low in Mandevilla splendens (65.70%). Among the studied species total chlorophyll content was found to be highest (1.51 mg/g FW) in Clitoria ternatea and Antigonon leptopus, followed by Ipomoea purpurea (1.28 mg/g FW). The climbers like Basella alba showed the lowest total chlorophyll content (0.36 mg/g FW).

Table 3: Biochemical, physiological characteristics and the APTI value of ornamental climbers.


 
Air pollution tolerance index (APTI) value
 
The APTI value estimated using the four biochemical parameters in plant leaves namely, RWC, total chlorophyll content, leaf pH and ascorbic acid value, can be used as a predictor of air quality.
       
In the present study, Ipomoea purpurea and Antigonon leptopus recorded the APTI of 18.68 and 18.21 respectively coming under tolerant category, followed by Passiflora edulis (17.80) being moderately tolerant. All the other species falls in intermediate category of APTI response with the values ranging from 10.95 to 13.73.
 
Anatomical characteristics
 
The leaf stomatal density was higher on the abaxial surface in the species studied ranging from 61.00 mm2 in Dolichandra unguis-cati to 26.66 mm2  in Basella alba (Table 2). Stomata was absent on the adaxial leaf surface in other species. Basella albarecorded the maximum stomatal density (67.33 mm2) on the adaxial leaf surface, while Ipomoea purpurearecorded the minimum stomatal density (5.66 mm²). Clitoria ternatea, Passiflora edulis, Thunbergia grandiflora, Quisqualis indica and Antigonon leptopus bears trichomes on both abaxial and adaxial leaf surface. Jacquemontia pentanthos bears trichomes only on the adaxial surface while Vitis vinifera bears only on the abaxial surface. The trichome density on the adaxial surface was highest in Passiflora edulis (69.66 mm2), followed by Clitoria ternatea (41.00 mm2). The trichome density on the abaxial surface was highest in Clitoria ternatea (92.00 mm2), followed by Antigonon leptopus (62.33 mm2).
       
Climbing plants have a lot of potential for urban vertical greening since they use unique vertical growth processes. The suitability of ornamental climbers for use in indirect green façades has been tested using an inexpensive iron-framed indirect green façade construction. In green facade systems, frame coverage that influences climbers’ capacity to spread also enhances shade effectiveness and helps control the microclimate. In the present study, Clitoria ternatea, Basella alba, Passiflora edulis, Ipomoea purpurea, Thunbergia grandiflora, Antigonon leptopus, Jacquemontia pentanthos, Dolichandra unguis-cati exhibited faster growth and covered the frame at 180 days of planting (Fig 2). Azhar et al., (2018) revealed similar results regarding frame coverage by Anemopaegma chamberlaynii, Antigonon leptopus and Quisqualis indica. Because of the pattern of foliage coverage, Vitis vinifera, Mansoa alliacea, Quisqualis indica and Mandevilla splendens displayed slow frame coverage. According to Azhar et al., (2018), Quisqualis indicafoliage pattern cascades downward and the stem climbs twinning vertically over the supporting structure with less leaf coverage before reaching the highest point of the structure. These findings are consistent with the current study.

Fig 2: Plant coverage on the iron frame


       
Climbing plants’ canopy expansion and productivity are significantly influenced by their stem girth, number of branches per plant and leaf output, which indicates the plants’ capacity for photosynthetic processes.In the present study, Passiflora edulis, Ipomoea purpurea, Antigonon leptopus, Thunbergia grandiflora and Jacquemontia pentanthos showed higher values for stem girth, number of branches and number of leaves per plant. These species are evergreen and bears simple leaf. According to earlier research, shoot branching is crucial in defining the overall performance and architecture of plants (Leyser, 2009). Perini et al., (2017) found that dense foliage development in climbers enhances thermal regulation and environmental performance of green facade systems, which is corresponding to the current findings on big leaf area in Vitis vinifera and Thunbergia grandiflora. Better photosynthesis and growth are supported by increased branching, which also increases light interception and plant spread. In general, plants with more leaves have more photosynthetic surface area. Additionally, it helps to increase the density of the canopy. Increased leaf numbers improve photosynthetic capability and growth performance, according to research by Larcher (2003). Antigonon leptopus had the lowest number of leaves per plant and the highest number of branches in the current study. This is in accordance with Azhar et al. (2018). The leaf has a tendency to expand quickly before experiencing rapid withering and death. As a result, the leaf has a shorter lifespan, which is thought to be caused by the fast rate of photosynthetic absorption, particularly in tropical plants.
       
The water in the plant tissue can be determined using Relative Water Content (RWC). According to Seyyednejad et al., (2017), a significant amount of water in plant tissue aids in preserving its physiological equilibrium under stressful circumstances. The relative water content was highest in Basella alba, Passiflora edulis, Thunbergia grandiflora, Quisqualis indica, Vitis vinifera and Dolichandra unguis-cati ranging from 84.75% to 82.05%. Relative water content, which indicates the water balance and cellular stability of plant tissues, is one of the key physiological activities used to assess plant tolerance to atmospheric contaminants, according to a similar study published by. The plant species’ resistance to stress is increased by high RWC (Kumar et al., 2014).  According to Joshi et al. (2009) and Pavlović et al. (2014), total chlorophyll is regarded as a measure of photosynthetic activity, growth and biomass productivity. Clitoria ternatea and Antigonon leptopus had the greatest total chlorophyll content (1.51 mg/g FW) in the current investigation. The result illustrates how plants’ physiological health and photosynthetic efficiency differ. Environmental stressors like air pollution can lower the content of chlorophyll by damaging the architecture of chloroplasts and interfering with the synthesis of pigments.The outcome is similar to that of who discovered that plants exposed to external pollutants frequently exhibit chlorophyll degradation.  Higher leaf pH values were recorded by Mansoa alliacea, Basella alba and Thunbergia grandiflora, indicating their greater resistance to air contaminants. Early research by Chaudhary and Rao (1977) found that leaf pH plays a major influence in influencing a plant’s sensitivity to air contaminants. An essential antioxidant molecule in plant defense mechanisms against oxidative stress is ascorbic acid. Because ascorbic acid protects cellular components and photosynthetic pigments from oxidative damage, plants with higher ascorbic acid contents are more resilient to contaminants. Increased ascorbic acid concentration enhances plant resilience to air contaminants, a conclusion corroborated by Keller and Schwager (1977).
       
APTI is an effective method for green belt development, according to studies done by different academics. Plants’ degree of tolerance to air pollutants is assessed using the Air Pollution Tolerance Index (APTI). When the APTI value is ≤11, the plant is sensitive; when it is 12-16, it is intermediate; and when it is ≥17, it is tolerant of air pollution (Padmavathi et al., 2013; Shrestha et al., 2021). Higher APTI values in the current study indicate that Ipomoea purpurea (18.68) and Antigonon leptopus (18.21) are typically thought to be tolerant of contaminated settings. In a similar vein, earlier research by showed that plants with higher APTI values have better physiological defense mechanisms and are appropriate for planting in metropolitan areas that are contaminated.This result is consistent with that of Pandey et al., (2016), who found that Ipomoea palmata, Thunbergia grandiflora, C. splendens, A. elegans, Q. indica, Petria volubilis and Antigonon leptopus had the highest APTI values and were excellent choices for green façade. Additionally, Ipomoea purpurea had the highest APTI value in the current study, which is in line with finding that deciduous species have high APTI. Additionally, Quisqualis indica (12.35 ATPI value) in this study indicated an intermediate response, that corresponds to Jim (2015) findings. Similar APTI based screening was conducted by Akilan and Nandhakumar (2016) in Vellore district, Tamil Nadu, where plant species growing in industrial and transportation-heavy zones consistently recorded higher APTI values than those from less polluted college farm sites, reinforcing the reliability of ascorbic acid, chlorophyll, leaf pH and relative water content as robust biochemical indicators for species screening.
       
In general, plants with dense stomata use water more efficiently and have higher stomatal conductance. On the other hand, because stomatal conductance and transpiration are reduced, a drop in stomatal density may result in a conservative use of water (Dittberner et al., 2018). In the present study, the Dolichandra unguis-cati followed by Quisqualis indica and Passiflora edulisrecorded higher values for stomatal density per mm2. Hypostomatic leaves were observed in Thunbergia grandiflora, Quisqualis indica, Antigonon leptopus, Jacquemontia pentanthos, Mandevilla splendens, Vitis vinifera, Dolichandra unguis-cati, Passiflora edulis, Mansoa alliacea. Because stomata are the main entrance point for gaseous contaminants into leaves, related research by Winner (1981) demonstrates that stomatal features have a substantial impact on plant exposure to air pollutants. The results of Durodola et al. (2025) are in line with the stomatal density of Quisqualis indica in the current investigation. This trade off pattern between structural traits is consistent with findings by Ramírez-Soto et al. (2026), who reported a significant negative correlation between stomatal area and trichome density on both leaf surfaces in Kabuli chickpea cultivars, suggesting that species investing more in trichome development tend to develop smaller, more conservative stomata as part of an adaptive water-use strategy.
       
Increased trichome density may improve plants’ ability to fend off contaminants. The quantity of particulate matter adsorbed on the leaf surface is correlated with the number of trichomes on the leaf surface (Chen et al., 2017). Clitoria ternatea, Passiflora edulis, Thunbergia grandiflora, Quisqualis indica, Antigonon leptopus, Jacquemontia pentanthosbears trichomes on the both the abaxial and adaxial surface of the leaf which is one of the selection criteria for pollution control. In the present study, the ultrastructure of the trichomes in Vitis vinifera was explored with transmission electron microscopy. On the abaxial surface, the ribbon trichomes are twisted, greatly elongated possessing erect and prostrate trichomes, the prostrate type completely covered the erect form (Fig 3). Domanda et al. (2023); Fambrini et al. (2021) and Gago et al. (2016) have reported similar findings regarding the existence of prostrate and erect trichomes. According to earlier research, trichomes serve as protective structures that lessen environmental harm and increase a plant’s resistance to external stress (Werker, 2000). According to Jeong et al., (2021) and Hellebaut et al. (2022), trichomes on the leaf surface exhibit the highest level of particulate matter reduction. This investigation likewise produced comparable results. This protective function of trichome density aligns with the findings of Satish et al., (2023), who demonstrated in pigeonpea that genotypes with higher pod trichome density and length experienced significantly reduced pest damage, indicating that dense trichome coverage functions as a physical barrier against external stressors, whether biotic pests or airborne particulate matter.

Fig 3: Scanning electron microscopic (SEM) images of trichomes present in the ornamental climbers.

This study indicated that ornamental climbers exhibit a wide range of morphological, physiological, biochemical and anatomical traits that affect their adaptation to green façades. Ipomoea purpurea, Antigonon leptopus and Passiflora edulis are among the climbers that are most suited for indirect green façades.
The authors declare no conflicts of interest regarding this manuscript.

  1. Akilan, M. and Nandhakumar, S. (2016). Air pollution tolerance index of selected plants in industrial and urban areas of Vellore district. Agricultural Science Digest. 36(1): 66-68. doi: 10.18805/asd.v35i1.9315.

  2. Arnon, D.I. (1949). Copper enzymes in isolated chloroplasts: Polyphenoloxidase in Beta vulgaris. Plant Physiology. 24(1): 1-15.

  3. Azhar, M.S.M.K., Shahidan, M.F., Jamil, M. and Mohd, Z.M. F. (2018). Percentage coverage of tropical climbing plants of green facade. IOP Conference Series: Materials Science and Engineering. 401(1): 012025. doi: 10.1088/1757-899X/ 401/1/012025.

  4. Chaudhary, C.S. and Rao, D.N. (1977). Study of some factors in plants controlling their susceptibility to SO2 pollution. Proceedings of the Indian National Science Academy, Part B. 46: 211-236.

  5. Chen, L., Liu, C., Zhang, L., Zou, R. and Zhang, Z. (2017). Variation in tree species ability to capture and retain airborne fine particulate matter (PM2.5). Scientific Reports. 7(1): 3206. doi: 10.1038/s41598-017-03360-1.

  6. Dittberner, H., Korte, A., Mettler-Altmann, T., Weber, A.P., Monroe, G. and De Meaux, J. (2018). Natural variation in stomata size contributes to the local adaptation of water-use efficiency in Arabidopsis thaliana. Molecular Ecology. 27(20): 4052-4065. doi: 10.1111/mec.14838.

  7. Domanda, C., Nuzzo, V., Montanaro, G., Failla, O. and Rustioni, L. (2023). Trichomes affect grapevine leaf optical properties and thermoregulation. Theoretical and Experimental Plant Physiology. 35(3): 299-308. doi: 10.1007/s40626- 023-00287-z.

  8. Durodola, T.A., Mudasiru, O.M., Idowu, D.A. and Umoren, O.D. (2025). Taxonomic implications of leaf epidermal anatomy in some members of genus Quisqualis L. and Guiera senegalensis J. F. Gmel. species. Species. 26: 1-8.

  9. Fambrini, M., Landi, M. and Pugliesi, C. (2021). Erinea in the ‘Ansonica’ grapevine cultivar: Trichome complement, histological effects and analysis of chlorophyll fluorescence in affected leaves. Vitis. 60(3): 101-108. doi: 10.5073/ vitis.2021.60.

  10. Farrokhirad, E., Rigillo, M., Köhler, M. and Perini, K. (2024). Optimising vertical greening systems for sustainability: An integrated design approach. International Journal of Sustainable Energy. 43(1): 2411831.

  11. Gago, P., Conejero, G., Martínez, M. C., Boso, S., This, P. and Verdeil, J.L. (2016). Microanatomy of leaf trichomes: Opportunities for improved ampelographic discrimination of grapevine (Vitis vinifera L.) cultivars. Australian Journal of Grape and Wine Research. 22(3): 494-503. doi: 10.1111/ajgw.12226.

  12. Hellebaut, A., Boisson, S. and Mahy, G. (2022). Do plant traits help to design green walls for urban air pollution control? A short review of scientific evidence and knowledge gaps. Environmental Science and Pollution Research. 29(54): 81210-81221.

  13. Jeong, N.R., Kim, J.H., Han, S.W., Kim, J.C. and Kim, W.Y. (2021). Assessment of the particulate matter reduction potential of climbing plants on green walls for air quality management. Journal of People, Plants and Environment. 24(4): 377- 387. doi: 10.11628/ksppe.2021.24.4.377.

  14. Jim, C.Y. (2015). Assessing growth performance and deficiency of climber species on tropical greenwalls. Landscape and Urban Planning. 137: 107-121. doi: 10.1016/j.landurbplan. 2015.01.001.

  15. Joshi, M., Kamble, S.P., Labhsetwar, N.K., Parwate, D.V. and Rayalu, S.S. (2009). Chlorophyll-based photocatalysts and their evaluation for methyl orange photoreduction. Journal of Photochemistry and Photobiology A: Chemistry. 204(2-3): 83-89. doi: 10.1016/j.jphotochem.2009.01.016.

  16. Keller, T. and Schwager, H. (1977). Air pollution and ascorbic acid. European Journal of Forest Pathology. 7(6): 338-350. doi: 10.1111/j.1439-0329.1977.tb00603.x.

  17. Köhler, M. (2008). Green facades-a view back and some visions. Urban Ecosystems. 11(4): 423-436. doi: 10.1007/s11252- 008-0063-x.

  18. Kumar, S., Dwivedi, S. K., Singh, S.S., Bhatt, B.P., Mehta, P., Elanchezhian, R. and Singh, O.N. (2014). Morpho-physiological traits associated with reproductive stage drought tolerance of rice (Oryza sativa L.) genotypes under rain-fed condition of eastern indo-gangetic plain. Indian Journal of Plant Physiology. 19(2): 87-93. doi: 10.1007/s40502- 014-0075-x.

  19. Larcher, W. (2003). Physiological Plant Ecology: Ecophysiology and Stress Physiology of Functional Groups. Springer Science and Business Media.

  20. Leyser, O. (2009). The control of shoot branching: An example of plant information processing. Plant, Cell and Environment. 32(6): 694-703. doi: 10.1111/j.1365-3040.2009.01930.x.

  21. Padmavathi, P., Cherukuri, J. and Reddy, M.A. (2013). Impact of air pollution on crops in the vicinity of a power plant: A case study. International Journal of Engineering Research and Technology. 2(12): 3641-3651.

  22. Pandey, A.K., Pandey, M. and Tripathi, B.D. (2016). Assessment of air pollution tolerance index of some plants to develop vertical gardens near street canyons of a polluted tropical city. Ecotoxicology and Environmental Safety. 134: 358-364. doi: 10.1016/j.ecoenv.2015.08.028.

  23. Pavlović, D., Nikolić, B., Đurović, S., Waisi, H., Anđelković, A. and Marisavljević, D. (2014). Chlorophyll as a measure of plant health: Agroecological aspects. Pesticidi i Fitomedicina. 29(1): 21-34. doi: 10.2298/PIF1401021P.

  24. Perini, K., Bazzocchi, F., Croci, L., Magliocco, A. and Cattaneo, E. (2017). The use of vertical greening systems to reduce the energy demand for air conditioning: Field monitoring in mediterranean climate. Energy and Buildings. 143: 35-42. doi: 10.1016/j.enbuild.2017.03.036.

  25. Perini, K., Ottelé, M., Fraaij, A.L.A., Haas, E.M. and Raiteri, R. (2011). Vertical greening systems and the effect on air flow and temperature on the building envelope. Building and Environment. 46(11): 2287-2294. doi: 10.1016/j.buildenv. 2011.05.009.

  26. Prasad, B.J. and Rao, D.N. (1982). Relative sensitivity of a metropolitan plant species to SO2 and O3 pollution. Environmental Pollution (Series A). 29(1): 57-70.

  27. Ramírez-Soto, M., Márquez-Godoy, J.N., Cota-Barreras, C.I., Gutiérrez- Gutiérrez, O.G., Pérez-Álvarez, J.G. and Acosta-Gallegos, J.A. (2026). Morphological analysis of stomata of Cicer arietinum L. Legume Research. 49(5): 798-805. doi: 10.18805/LRF-907.

  28. Satish, K., Muniswamy, S., Girish, G., Kulkarni, V., Diwan, J.R., Geeta, S.N., Pandey, S. and Singh, I.P. (2023). Pod trichome characterisation using foldscope, morphological characterization and genetic diversity among indigenous collections of pigeonpea [Cajanus cajan (L.) Millsp.]. Legume Research. 46(8): 1013-1019. doi: 10.18805/LR-4423.

  29. Sethupathy, D., Sarathchandran, R. and Rana, D.P. (2025). Exploring the efficiency of indirect green façades with native plants to lower rising façade temperatures: A way to improve urban living in tropical regions. Journal of Urban Regeneration and Renewal. 18(3): 288-312.

  30. Seyyednejad, S.M., Motamedi, H. and Lordifard, P. (2017). Biochemical changes of Conocarpus erectus (Combretaceae) in response to gas refinery air pollution as an air pollution indicator. Pollution. 3(2): 185-190. doi: 10.7508/pj.2017. 02.002.

  31. Shrestha, S., Baral, B., Dhital, N.B. and Yang, H.H. (2021). Assessing air pollution tolerance of plant species in vegetation traffic barriers in Kathmandu Valley, Nepal. Sustainable Environment Research. 31(1): 3. doi: 10.1186/s42834- 020-00076-2.

  32. Singh, S.K. and Rao, D.N. (1983). Evaluation of the plants for their tolerance to air pollution. Proceedings of the Symposium on Air Pollution Control. 1: 218-224.

  33. Werker, E. (2000). Trichome diversity and development. Annals of Botany. 85(Suppl. A). doi: 10.1016/S0065-2296(00)31005-9.

  34. Winner, W.E. (1981). The Effect of SO2 on Photosynthesis and Stomatal Behavior of Mediterranean-Climate Shrubs and Trees. In Components of Productivity of Mediterranean- Climate Regions: Basic and Applied Aspects. Proceedings of the International Symposium on Photosynthesis, Primary Production and Biomass Utilization in Mediterranean- Type Ecosystems, Kassandra, Greece (pp. 91-103).
In this Article
Published In
Indian Journal of Agricultural Research

Editorial Board

View all (0)