Identification of Chlorophyll Fluorescence Parameters for Evaluating Drought Stress in Garden Plants

Article information

J. People Plants Environ. 2025;28(5):601-613
Publication date (electronic) : 2025 October 31
doi : https://doi.org/10.11628/ksppe.2025.28.5.601
1Doctoral Student, Dept. of Plant Resources and Landscape Architecture, Hankyong National University, Anseong-si 17579, Republic of Korea
2Professor, School of Plant Resources and Landscape Architecture, Hankyong National University, Anseong-si 17579, Republic of Korea
3Chief, Institute of Ecological Phytochemistry, Hankyong National University, Anseong-si 17579, Republic of Korea
4Master’s Student, School of Plant Resources and Landscape Architecture, Hankyong National University, Anseong-si 17579, Republic of Korea
5Senior Reseacher, Institute of Ecological Phytochemistry, Hankyong National University, Anseong-si 17579, Republic of Korea
*Corresponding author: Sung Yung Yoo, lsn136@hknu.ac.kr, https://orcid.org/0000-0002-7889-3924
Co-First authorSeong Ju Lee, leesj9691@naver.com, https://orcid.org/0009-0009-1811-2506
Co-First authorTae Wan Kim, taewkim@hknu.ac.kr, https://orcid.org/0000-0002-1742-1982
This work was supported by the Firefly Research Support Project of the Academic Scholarship Promotion Foundation at Hankyong National University.
Received 2025 July 31; Revised 2025 September 11; Accepted 2025 September 24.

Abstract

Background and objective

This study aimed to analyze chlorophyll fluorescence responses to drought stress in ten garden plant species and to identify effective parameters for evaluating drought stress.

Methods

The study took place from July to August 2023 in a greenhouse at Hankyong National University in Anseong, Gyeonggi-do, South Korea, to evaluate drought stress responses in ten garden plant species. After growing the plants under well-watered conditions under a drip irrigation system for 20 days, irrigation was withheld to induce drought stress. Chlorophyll fluorescence responses were measured at five-day intervals to define different drought stages.

Results

During the control period, the plants exhibited the highest maximum chlorophyll fluorescence, indicating efficient electron transport from PSII to PSI. However, maximum fluorescence decreased progressively following drought stress treatment. To identify key photophysiological indicators for evaluating drought stress in garden plants, species-specific JIP-test parameters were calculated and analyzed using Pearson’s correlation analysis with soil moisture content. Parameters reflecting energy flux per leaf area showed significant positive correlations across all species. Based on these correlations, a principal component analysis (PCA) was performed, which suggested that 11 parameters were associated with drought stress. To assess the importance of each variable, a multiple linear regression model was constructed. The model showed high predictive reliability, although some multicollinearity among independent variables was observed. After excluding mutual influences and evaluating the relative contributions of each variable, five chlorophyll fluorescence parameters—TRo/CS, ABS/CS, RC/CS, ET2o/CS, and RE1o/CS—were proposed as effective indicators for assessing drought stress in garden plants.

Conclusion

The five chlorophyll fluorescence parameters—TRo/CS, ABS/CS, RC/CS, ET2o/CS, and RE1o/CS—proposed in this study demonstrated the potential to serve as universally applicable indicators for assessing drought stress across various garden plant species. Their practical utility as evaluation metrics could be further strengthened through future studies incorporating species-specific sensitivity analyses or different planting conditions.

Introduction

The growing popularity of gardening as both an activity and a lifestyle has broadened the scope of the gardening industry, prompting policy initiatives to promote gardening culture and support industry development through enhanced garden infrastructure (2nd Garden Promotion Basic Plan (2021~2025), 2021). Moreover, rising national income levels have increased public interest in garden plants and invigorated urban gardening culture (Choi et al., 2017). As green spaces that can be established even in limited areas, urban gardens contribute to urban biodiversity and play a role in addressing various environmental challenges (Mo, 2021).

Over 70% of Korea’s annual precipitation occurs between June and August, resulting in a prolonged dry period from October through May. Urban areas experience chronic dryness due to the prevalence of impervious surfaces, such as asphalt, as well as energy consumption from vehicles and heating systems (Kim et al., 2014). Moreover, abiotic stress on plants is expected to intensify as climate change accelerates the frequency and severity of extreme weather events. Reduced precipitation, which leads to soil moisture deficiency, is the most critical environmental factor limiting plant growth (Araus, 2002; Fedoroff et al., 2010). Under optimal growth conditions, plants can improve light energy use efficiency and enhance productivity through photosynthesis. However, exposure to abiotic stresses—such as excessive light, temperature extremes, or deficiencies in water and nutrients—can cause significant damage to the photosynthetic system (Pereira, 2016; Zhu, 2016). Water deficiency, in particular, is widely recognized as a key environmental factor limiting photosynthetic activity. It disrupts turgor pressure, thereby inhibiting leaf expansion and stem elongation, and often induces stomatal closure or leaf abscission to minimize water loss (Kim et al., 2020; Lee et al., 2014). Furthermore, plants exposed to drought stress are known to accumulate reactive oxygen species (ROS), which trigger the activation of various antioxidant defense mechanisms. These include increased activities of enzymes such as superoxide dismutase (SOD), catalase (CAT), and ascorbate peroxidase (APX), as well as elevated proline accumulation to mitigate oxidative stress (Foyer et al., 1994; Heuer, 2010; Mittler, 2002). However, under severe drought conditions, photosynthesis is significantly inhibited, osmotic regulation is disrupted, and major metabolic dysfunctions may occur, ultimately leading to substantial physiological damage (Frary, 2015). As such, drought stress inhibits photosynthetic activity by inducing stomatal closure, reducing water use efficiency, and causing imbalances in photochemical reactions and electron transport. Consequently, chlorophyll fluorescence analysis (or chlorophyll fluorescence transients) can be employed as an effective tool for diagnosing stress responses in crops (Strasser et al., 2000).

Chlorophyll fluorescence is a phenomenon observed when chlorophyll molecules are exposed to light of specific wavelengths and intensities. After a period of dark adaptation—typically ranging from 15 minutes to 1 hour—excited chlorophyll molecules return to their ground state (Kautsky and Hirsch, 1931; Strasser, 1978). This process is characterized by the OJIP fluorescence transient, also known as the Kautsky effect, OJIP curve, fluorescence induction or fluorescence decay. In this transient, the O step (origin) represents the initial fluorescence level immediately after dark adaptation; the J step (jump) corresponds to the first inflection step where minimal fluorescence change occurs; the I step (intermediate) indicates an intermediate fluorescence level; and the P step (peak) reflects the maximum fluorescence intensity (Govindje, 1995). Furthermore, the JIP-test—a set of fluorescence parameters that quantitatively analyzes the Kautsky effect —is widely employed to investigate the relationship between chlorophyll fluorescence parameters and abiotic stress conditions (Stirbet and Govindjee, 2011).

Ham et al. (2018) reported that drought stress in nursery seedlings of tomato and cucumber can be diagnosed using six chlorophyll fluorescence parameters—Fv/Fm, DIo/RC, ET2o/RC, RE1o/RC, PI_ABS, and PI_total ABS—through chlorophyll fluorescence analysis (Ham et al., 2018). Kim et al. (2020) assessed water stress in Cnidium officinale Makino using Fv/Fm, Rfd_Lss, and NPQ_Lss, while Yoo et al. (2013) analyzed the photochemical responses of red pepper (Capsicum annuum L.) via the OJIP test, introducing PI_ABS and the drought factor index (DFI) (Kim et al., 2020; Yoo et al., 2013). Additionally, Liu et al. (2018) investigated the response of the photosynthetic electron transport chain (ETC) in maize under varying levels of drought stress, revealing that under moderate drought stress, the photochemical activity of photosystem II (PSII) declined while photosystem I (PSI) remained unaffected; however, under severe drought stress, the entire ETC was inhibited, indicating that PSII is more sensitive to drought stress than PSI (Liu et al., 2018).

Therefore, this study aimed to analyze chlorophyll fluorescence responses in ten garden plant species to identify universal photophysiological indicators applicable to drought stress assessment across species.

Research Methods

Experimental materials and drought stress treatment

This study was conducted from July to August 2023 in a greenhouse at the Hankyung National University Affiliated Farm, located in Anseong, Gyeonggi Province, South Korea (37°00′42″N, 127°19′12″E). Ten species of garden plants were obtained from The K Flower (Yongin-si, Gyeonggi-do) and planted in experimental pots (143 × 143 × 160 mm): Polygonatum odoratum var. pluriflorum (Miq.) Ohwi, Carex maculata Boott, Pachysandra terminalis Siebold and Zucc., Hosta longipes (Franch. and Sav.) Matsum., Lilium lancifolium Thunb., Allium dumebuchum H.J. Choi, Iris sanguinea Donn ex Hornem., Sedum take-simense Nakai, Aster spathulifolius Maxim., and Mukdenia rossii (Oliv.) Koidz. The pots were filled with silty loam soil. To minimize the influence of increased soil moisture through ground contact, all pots were placed in triplicate on pallets (Fig. 1A). Angled drip spikes were also installed in each pot to deliver a consistent daily amount of water via drip irrigation. After a 15-day acclimatization period, the plants were cultivated under normal watering conditions for 5 days, which served as the control period (Control). Following this, irrigation was suspended to induce drought stress (Fig. 1B). Drought severity was evaluated in four stages ( DS 1 t o DS 4 ) at 5 -day intervals. Throughout the experiment, ambient temperature was recorded hourly using a data logger (testo 174 H, Testo Saveris GmbH, Baden-Württemberg, Germany) to monitor environmental conditions. Additionally, four pots were randomly selected, and their soil moisture content was measured using a WaterScout SM 100 soil moisture sensor (Spectrum Technologies, Inc., Aurora, IL 60504, USA). A data logger (WatchDog 1000 Series Watermark Irrigation Stations, Spectrum Technologies, Inc., Aurora, IL 60504, USA) was used to record the data. Soil moisture content was determined using the calibration formula embedded in the soil moisture sensor.

Fig. 1

Field setup and drought stress treatments: (A) Field plot; (B) Examples of plants under drought stress.

Chlorophyll fluorescence measurement

Chlorophyll fluorescence was measured on fully expanded leaves (the upper third and fourth leaves) using a chlorophyll fluorescence meter (FP-100, Photon System Instruments, Czech Republic). Three plants were measured in duplicate for each treatment, and measurements were conducted across five drought stress stages (Control, DS 1, DS 2, DS 3, and DS 4). Prior to measurement, the selected leaves were dark-adapted for 30 minutes using leaf clips to ensure that all PSII reaction centers were open and that energy had returned to the ground state. Fluorescence measurements were then performed in OJIP mode, targeting a 4 mm² leaf area with saturating light at an intensity of 2,400 μmol m−2 s−1 (Ayyaz et al., 2020).

The minimal fluorescence (Fo) is measured at 50 μs, when all PSII reaction centers are open. Then, the fluorescence passes through the J step (2 ms) and the I step (30 ms), reaching the P step within 1 second, during which all PSII reaction centers are closed and the maximum fluorescence (Fm) is attained. This sequence is well-documented in chlorophyll fluorescence kinetics studies of photosystem II (Strasser et al., 2000). In this study, chlorophyll fluorescence data for each species were comparatively analyzed across drought stress stages based on their respective O-J-I-P responses. Chlorophyll fluorescence parameters were derived using the JIP-test (Stirbet and Govindjee, 2011; Table 1).

Formulas and glossary of terms used in the JIP-Test for analyzing OJIP fluorescence transients (Stirbet and Govindjee, 2011)

Statistical analysis

All statistical analyses in this study were performed using the R software (R Core Team, 2021). Chlorophyll fluorescence parameters estimated at each drought stress stage of garden plants were analyzed using Pearson correlation analysis and principal component analysis (PCA).

Variable importance assessment

Based on the above analyses, an evaluation of variable importance was conducted to identify suitable photophysiological indicators for effectively assessing the drought stress responses of garden plants. Using 546 data points with missing values excluded, a multiple linear regression model was constructed. To minimize the influence of differences in measurement units among chlorophyll fluorescence parameters, z-score normalization was applied. The explanatory power of the model was assessed using the coefficient of determination (R2) and the adjusted coefficient of determination (Adjusted R2). Predictive accuracy was evaluated using the root mean square error (RMSE) and mean absolute error (MAE) (Equations 14). In addition, the model’s performance was compared with that of a baseline model based on the simple mean, to verify its predictive superiority. To address potential multi-collinearity among predictor variables, a relative weights analysis was conducted following the method proposed by Johnson (2000). Through this procedure, key photo-physiological indicators suitable for assessing drought stress in garden plants were derived.

(1) Multiple R-squared (R2)=1-Σ(yi-y^)2Σ(yi-y¯)2
(2) Adjusted R2=1-(1-R2)(N-1)N-p-1
(3) Root Mean Square Error (RMSE)=1NΣ(yi-y^i)2
(4) Mean Absolute Error (MAE)=1NΣ|(yi-y^l)|

(yi: observed data, ŷl: predicted data, : mean of observed data, N: total number of samples, p: number of independent variables)

Results and Discussion

Environmental monitoring

Environmental monitoring was performed at one-hour intervals to measure air temperature and soil moisture content inside the greenhouse (Fig. 2). During the cultivation period, the daily mean air temperature ranged from a minimum of 22.3 °C at 28 days after treatment (DAT) to a maximum of 39.9 °C at 6 DAT, with an overall average of 31.6 °C. The daily mean soil moisture content under normal cultivation conditions (Control) was 26.9%. However, it declined sharply immediately after the onset of the drought stress treatment (DS 1).

Fig. 2

Microclimatic conditions and soil moisture content in the greenhouse after transplantation: (A) Daily average temperature (℃); (B) Daily average soil moisture content (%).

Chlorophyll fluorescence (OJIP) analysis across drought stress stages

In general, each phase of the chlorophyll fluorescence transient reflects specific processes occurring in the PSII reaction center: the O-J phase corresponds to the reduction of quinone A (QA), the J-I phase indicates the reduction and reoxidation of QA, and the I-P phase represents the rapid reduction of the plastoquinone (PQ) pool (Stirbet et al., 1998). A comparative analysis of chlorophyll fluorescence in garden plants across different drought stress stages revealed that, in all species, Control exhibited the highest fluorescence intensity up to the maximum fluorescence (Fp), indicating efficient electron transport from PSII to PSI. After the onset of drought stress, Fp gradually declined ( Fig. 3 ). At the DS 1 s tage, Fp decreased by a minimum of 6.9% in Hosta longipes (Franch. and Sav.) Matsum and a maximum of 29.4% in Carex maculata Boott. At the DS 2 stage, the reduction ranged from 25.2% in Iris sanguinea Donn ex Hornem to 51.8% in Sedum takesimense Nakai. At the DS 3 stage, Fp had decreased by a minimum of 52.0% in Mukdenia rossii (Oliv.) Koidz and a maximum of 88.5% in Carex maculata Boott. At the DS 4 stage, reductions ranged from 59.2% in Hosta longipes (Franch. and Sav.) Matsum to 95.1% in Carex maculata Boott. In this study, at the DS 4 stage, seven out of ten species exhibited more than a 70% reduction in Fp compared to Control, with the exceptions being Hosta longipes (Franch. and Sav.), Mukdenia rossii ( Oliv.) Koidz, and Lilium lancifolium Thunb. Notably, Carex maculata Boott showed a reduction exceeding 90%, indicating severe inhibition of electron transport. Under drought stress, plants commonly respond by closing their stomata to conserve water, which in turn limits CO2 availability. This limitation delays the reduction and reoxidation of QA, leads to inactivation of reaction centers (RCs), and impairs the overall function of PSII (Baker, 2008; Lee, 2018; Shanker et al., 2022; Yan et al., 2024). Additionally, the reduced rate of QA reoxidation suppresses electron transport and inactivates the oxygen- evolving complex (OEC). These disruptions promote the accumulation of reactive oxygen species (ROS), further impairing the early stages of the photosynthetic electron transport chain. As a result, water-splitting activity ceases, and electron flow to the RC is interrupted (Asada, 1999; Cifre et al., 2005; Lidon and Henriques, 1993; Strasser et al., 2000; Strasser et al., 2004). Consequently, inhibition of electron acceptor activity under drought stress results in QA accumulation (O-J phase), suppression and stagnation of electron transfer from QA to quinone B (QB) (J-I phase), and limited electron transport from QB to the plastoquinone (PQ) pool (I-P phase) (Kalaji et al., 2017; Shu et al., 2024; Tóth et al., 2007). In this study, following drought stress treatment, Carex maculata Boott, Iris sanguinea Donn ex Hornem, and Aster spathulifolius Maxim exhibited a transient increase in chlorophyll fluorescence during the O-J phase at the DS 2 stage, which was subsequently suppressed. This suppression was accompanied by a marked decline in fluorescence during the J-I and I-P phases, resulting in chlorophyll fluorescence induction curves (OJIP curves) that progressively shifted toward a more linear profile. These results suggest that the initial rise in the O-J phase, followed by reductions in the J-I and I-P phases under drought conditions, reflects rapid photochemical damage to OEC and QA. This impairs the recovery mechanisms of the photosynthetic system, leading to a more gradual slope in the OJIP curves of these garden plants (Ham et al., 2018; Lee et al., 2014; Oukarroum et al., 2007).

Fig. 3

Changes in chlorophyll fluorescence intensity in the ten garden plant species under drought stress: (A) Polygonatum odoratum var. pluriflorum (Miq.) Ohwi; (B) Carex maculata Boott; (C) Pachysandra terminalis Siebold and Zucc; (D) Hosta longipes (Franch. and Sav.) Matsum; (E) Lilium lancifolium Thunb; (F) Allium dumebuchum H.J. Choi; (G) Iris sanguinea Donn ex Hornem; (H) Sedum takesimense Nakai; (I) Aster spathulifolius Maxim; (J) Mukdenia rossii (Oliv.) Koidz.

Identification of key photophysiological indicators for drought stress assessment

The flow of energy in plants typically begins when light energy absorbed by chlorophyll is transferred through the antenna complex to the oxygen-evolving complex (OEC), ultimately exciting the reaction center (RC). Once excited, the RC releases an electron to pheophytin, which then reduces the primary electron acceptor, quinone A (QA). The electron is subsequently transferred to quinone B (QB), during which QA is re-oxidized and QB is reduced to plastoquinone (PQ) by accepting protons from the stroma. The PQ pool then mediates electron transfer to plastocyanin (PC) via the cytochrome b6f complex, undergoing a redox cycle. During this process, protons are translocated into the thylakoid lumen. These resulting proton gradient is subsequently utilized in the synthesis of adenosine triphosphate (ATP) and nicotinamide adenine dinucleotide phosphate (NADPH) (Frary, 2015; Johnson, 2025).

To identify key photophysiological indicators for assessing drought stress in garden plants, species-specific chlorophyll fluorescence parameters derived from the JIP-test) were calculated and subjected to Pearson correlation analysis against soil water content (Fig. 4). The analysis revealed that five parameters—the number of active reaction centers per cross-sectional area (RC/CS), which reflects changes in energy flux per unit leaf area; light energy absorption per cross-sectional area (ABS/CS); trapped excitation energy per cross-sectional area (TRo/CS); and two electron transport-related parameters (ET2o/CS and RE1o/CS)—were consistently and positively correlated with soil moisture across all species, with most correlation coefficients exceeding 0.8 (Eom et al., 2024; Oh and Koh, 2013; Shin, 2022). In addition, the maximum quantum yield of PSII (Fv/Fm) and the performance indices associated with energy conversion efficiency in the electron transport chain (PI_ABS and PI_total ABS) have previously been reported to decline under drought stress. Consistent with these findings, this study also observed significant correlations in seven or more plant species, indicating similar physiological trends (Guo et al., 2022; Jia et al., 2020; Rathod, 2011; Wang et al., 2025). In contrast, five parameters representing energy flux per PSII reaction center—including ABS/RC, DIo/RC, ET2o/RC, RE1o/RC, and TRo/RC—showed weak correlations with soil moisture, suggesting that they are less suitable as indicators for evaluating drought stress in garden plants.

Fig. 4

Heatmap of correlations between soil moisture content and JIP-Test parameters in ten garden plants. Asterisks denote statistically significant differences (* p < .05, ** p < .01, *** p < .001).

A principal component analysis (PCA) was performed using 11 photophysiological parameters—Fv/Fm, RC/ABS, PI_ABS, PI_total ABS, DF_total ABS, RC/CS, ABS/CS, TRo/CS, ET2o/CS, DIo/CS, and RE1o/CS—to identify common indicators for assessing drought stress in ten garden plant species. The PCA results showed that PC1 (69.3%) and PC2 (16.4%) explained a total of 85.7% of the variance, and the distribution exhibited a trend of shifting from the negative to the positive direction along PC1 in response to soil moisture levels (Fig. 5). PC1 was characterized by strong negative loadings (< −0.25) for all parameters except DIo/CS, which instead exhibited the highest positive loading (0.65) on PC2. These findings indicate that all parameters included in the analysis are associated with drought stress responses in garden plants (Table 2).

Fig. 5

PCA biplot of JIP-Test parameters colored by soil moisture levels.

Loadings of variables on principal components 1 and 2 in the PCA

Based on the results of the Pearson correlation analysis and PCA, a multiple linear regression model was developed to evaluate the relative importance of the variables. The model achieved an R2 of 0.8 or higher, with both RMSE and MAE reduced to less than half of those observed in the baseline model, indicating high predictive reliability (Table 3). However, multicollinearity was identified among certain independent variables. To minimize inter-variable influence and accurately determine the relative contribution of each, Johnson’s (2000) relative weights analysis was applied, and the results were visualized in Fig. 6. Among the eleven parameters, TRo/CS exhibited the greatest explanatory power for drought stress in garden plants, accounting for 15.1% of the total R2. This was followed by ABS/CS (14.8%), RC/CS (14.5%), ET2o/CS (13.5%), and RE1o/CS (11.9%). Collectively, these top five parameters explained over 70% of the total R2. These findings suggest that the five chlorophyll fluorescence parameters—TRo/CS, ABS/CS, RC/CS, ET2o/CS, and RE1o/CS—can serve as effective indicators for evaluating drought stress responses in garden plants. In contrast, DF_total ABS accounted for only 1.4% of the R2, while RC/ABS (4.5%) and PI_total ABS (4.7%) also demonstrated relatively low contributions.

Evaluation metrics for the multiple linear regression model

Fig. 6

Relative weights analysis for identifying key JIP-test parameters for assessing drought stress in garden plants.

In this study, five proposed chlorophyll fluorescence parameters were identified as potential indices for assessing drought stress in garden plants composed of various species. However, since these indicators are derived from mean values, certain parameter values may be biased, and species-specific characteristics could be partially obscured. Nevertheless, integrated analyses based on the mean values of extensive datasets collected from diverse species confirmed the potential to establish common indicators applicable across multiple species. Furthermore, as plants exhibit species-dependent variation in factors affecting soil moisture—such as leaf area, canopy coverage, and transpiration rate—future studies that incorporate species-specific sensitivity analyses or account for different planting conditions, while accounting for soil moisture variation, are expected to enhance the practical applicability of these indices as assessment tools.

Conclusion

This study was conducted from July to August 2023 in a greenhouse at the Hankyung National University Affiliated Farm in Anseong, Gyeonggi Province, South Korea, using ten garden plant species as experimental subjects. The plants during the control period (Control) were maintained under normal cultivation conditions via drip irrigation, after which irrigation was withheld to induce drought stress. The drought treatment was applied in five-day intervals, during which chlorophyll fluorescence responses were analyzed. The analysis showed that Control exhibited the highest values of maximum chlorophyll fluorescence, while these values progressively decreased with continued drought stress. To identify key photophysiological indicators for evaluating drought stress in garden plants, species-specific chlorophyll fluorescence parameters were calculated using the JIP-test. Pearson correlation analysis and Principal Component Analysis (PCA) were then performed with respect to soil moisture content. The results demonstrated that eleven parameters—Fv/Fm, RC/ABS, PI_ABS, PI_total ABS, DF_total ABS, RC/CS, ABS/CS, TRo/CS, ET2o/CS, DIo/CS, and RE1o/CS—were associated with drought stress responses in garden plants. Based on these findings, a multiple linear regression model was constructed to assess the relative importance of the variables, demonstrating high predictive reliability. However, multicollinearity was detected among certain independent variables. After excluding inter-variable influence and determining individual contributions, five chlorophyll fluorescence parameters—TRo/CS, ABS/CS, RC/CS, ET2o/CS, and RE1o/CS—were proposed as effective indices for assessing drought stress responses in garden plants. As the analyses in this study were conducted using mean values, certain parameter estimates may have been biased, and species-specific characteristics may have been partially obscured. Nevertheless, this research is significant in that an integrated analysis of extensive data collected from multiple species enabled the identification of common indicators applicable to drought stress assessment in garden plants. Future studies are expected to further improve the practical applicability of the proposed indicators by incorporating sensitivity analyses that consider species-specific factors affecting soil moisture content—such as leaf area, canopy coverage, and transpiration rate—as well as through validation under diverse planting conditions.

References

Araus J.L.. 2002;Plant breeding and drought in C3 cereals: What should we breed for? Annals of Botany 89(7):925–940. https://doi.org/10.1093/aob/mcf049.
Asada K.. 1999;The water-water cycle in chlopoplasts: Scavenging of active oxygens and dissipation of excess photons. Annual Review of Plant Physiology and Plant Molecular Biology 50(1):601–639. https://doi.org/10.1146/annurev.arplant.50.1.601.
Ayyaz A., Amir M., Umer S., Iqbal M., Bano H., Gul H.S., Noor Y., kanwal A., khalid A., Javed M., Athar H.R., Zafar Z.U., Farooq M.A.. 2020;Melatonin induced changes in photosynthetic efficiency as probed by OJIP associated with improved chromium stress tolerance in canola (Brassica napus L.). Heliyon 6(7):e04364. https://doi.org/10.1016/j.heliyon.2020.e04364.
Baker N.R.. 2008;Chlorophyll fluorescence: A probe of photosynthesis in vivo. Annual Review of Plant Biology 59(1):89–113. https://doi.org/10.1146/annurev.arplant.59.032607.092759.
Choi W.K., Jin H.Y., Song J.H.. 2017;Analysis of users recognition on wildflowers as gardening plants. Journal of Korea Society for Plants People and Environment 20(1):81–93. https://doi.org/10.11628/ksppe.2017.20.1.081.
Cifre J., Bota J., Escalona J.M., Medrano H., Flexas J.. 2005;Physiological tools for irrigation scheduling in grapevine (Vitis vinifera L.) Agriculture. Ecosystems andamp; Environment 106(2–3):159–170. https://doi.org/10.1016/j.agee.2004.10.005.
Eom T.S., Jang S.Y., Hwang Y.B., Yoo S.Y., Kang S.K., Park J.S., Kim T.W.. 2024;Chlorophyll fluorescence analysis for the assessment of high temperature stress in citrus during the coloration period. Journal of Environmental Science International 33(9):613–623. https://doi.org/10.5322/jesi.2024.33.9.613.
Fedoroff N.V., Battisti D.S., Beachy R.N., Cooper P.J.M., Fischhoff D.A., Hodges C.N., Knauf V.C., Lobell D., Mazur B.J., Molden D., Reynolds M.P., Ronald P.C., Rosegrant M.W., Sanchez P.A., Vonshak A., Zhu J.K.. 2010;Radically Rethinking Agriculture for the 21st Century. Science 327(5967):833–834. https://doi.org/10.1126/science.1186834.
Foyer C.H., DescourviÈRes P., Kunert K.J.. 1994;Protection against oxygen radicals: an important defence mechanism studied in transgenic plants. Plant, Cell andamp; Environment 17(5):507–523. https://doi.org/10.1111/j.1365-3040.1994.tb00146.x.
Frary A.. 2015. Plant physiology and development plant physiology and development In : Taiz Lincoln, Zeiger Eduardo, Moller Ian Max, Murphy Angus, eds. 2014. (looseleaf). Sinauer Associates Inc. Sunderland, MA: Rhodora 117(971)p. 397–399. https://doi.org/10.3119/0035-4902-117.971.397.
Govindje e. 1995;Sixty-three years since kautsky: Chlorophyll a fluorescence. Functional Plant Biology 22(2):131. https://doi.org/10.1071/pp9950131.
Guo C., Liu L., Sun H., Wang N., Zhang K., Zhang Y., Zhu J., Li A., Bai Z., Liu X., Dong H., Li C.. 2022;Predicting Fv/Fm and evaluating cotton drought tolerance using hyperspectral and 1D-CNN. Frontiers in plant science :13. https://doi.org/10.3389/fpls.2022.1007150.
Ham H.D., Kim T.S., Lee M.H., Park K.B., An J.-H., Kang D.H., Kim T.W.. 2018;The assessment of photochemical index of nursery seedlings of cucumber and tomato under drought stress. Environmental Biology Research 36(4):479–487. https://doi.org/10.11626/kjeb.2018.36.4.479.
Heuer B.. 2010. Role of proline in plant response to drought and salinity. Books in Soils, Plants, and the Environment p. 213–238. CRC Press.
Jia Y., Xiao W., Ye Y., Wang X., Liu X., Wang G., Li G., Wang Y.. 2020;Response of photosynthetic performance to drought duration and re-watering in maize. Agronomy 10(4):533. https://doi.org/10.3390/agronomy10040533.
Johnson J.W.. 2000;A heuristic Mmthod for estimating the relative weight of predictor variables in multiple regression. Multivariate Behavioral Research 35(1):1–19. https://doi.org/10.1207/s15327906mbr3501_1.
Johnson M.P.. 2025;Structure, regulation and assembly of the photosynthetic electron transport chain. Nature Reviews Molecular Cell Biology 26(9):667–690. https://doi.org/10.1038/s41580-025-00847-y.
Kalaji H.M., Schansker G., Brestic M., Bussotti F., Calatayud A., Ferroni L., Goltsev V., Guidi L., Jajoo A., Li P., Losciale P., Mishra V.K., Misra A.N., Nebauer S.G., Pancaldi S., Penella C., Pollastrini M., Suresh K., Tambussi E., Bąba W.. 2017;Frequently asked questions about chlorophyll fluorescence, the sequel. Photosynthesis Research 132(1):13–66. https://doi.org/10.1007/s11120-016-0318-y.
Kautsky H., Hirsch A.. 1931;Neue versuche zur kohlensäureassimilation. Die Naturwissenschaften 19(48):964–964. https://doi.org/10.1007/bf01516164.
Kim J.S., Jung M.I., Han S.W., Jang H.K.. 2014;Assessment of drought-resistant of garden plant for greening city. Society for People, Plants, and Environment
Kim K.S., Seo Y.J., Kim D.C., Nam H.H., Lee B.Y., Kim J.H.. 2020;Effect of soil water and shading treatment on chlorophyll fluorescence parameters and photosynthetic capacity in cnidium officinale makino. Korean Journal of Medicinal Crop Science 28(6):412–420. https://doi.org/10.7783/kjmcs.2020.28.6.412.
Lee K.C.. 2018;Changes in photosynthetic performance and water relation parameters in the seedlings of Korean dendropanax subjected to drought stress. Korean Journal of Medicinal Crop Science 26(2):181–187. https://doi.org/10.7783/kjmcs.2018.26.2.181.
Lee K.C., Kim S.H., Park W.G., Kim Y.S.. 2014;Effects of drought stress on photosynthetic capacity and photosystem II activity in oplopanax elatus. Korean Journal of Medicinal Crop Science 22(1):38–45. https://doi.org/10.7783/kjmcs.2014.22.1.38.
Lidon F.C., Henriques F.S.. 1993;Oxygen metabolism in higher plant chloroplasts [Journal article]. Photosynthetica 29(2):249–279.
Liu J., Guo Y.Y., Bai Y.W., Camberato J.J., Xue J.Q., Zhang R.H.. 2018;Effects of drought stress on the photosynthesis in maize. Russian Journal of Plant Physiology 65(6):849–856. https://doi.org/10.1134/s1021443718060092.
Mittler R.. 2002;Oxidative stress, antioxidants and stress tolerance. Trends in Plant Science 7(9):405–410. https://doi.org/10.1016/s1360-1385(02)02312-9.
Mo Y.. 2021;Review of ecosystem services assessment methods in urban garden. Journal of The Korean Insitute of Urban Design 7(1):61.
Oh S., Koh S.C.. 2013;Chlorophyll a fluorescence response to mercury stress in the freshwater microalga chlorella vulgaris. Journal of Environmental Science International 22(6):705–715. https://doi.org/10.5322/jesi.2013.22.6.705.
Oukarroum A., Madidi S.E., Schansker G., Strasser R.J.. 2007;Probing the responses of barley cultivars (Hordeum vulgare L.) by chlorophyll a fluorescence OLKJIP under drought stress and re-watering. Environmental and Experimental Botany 60(3):438–446. https://doi.org/10.1016/j.envexpbot.2007.01.002.
Pereira A.. 2016;Plant abiotic stress challenges from the changing environment. Frontiers in Plant Science :7. https://doi.org/10.3389/fpls.2016.01123.
R Core Team. 2021;R : A language and environment for statistical computing. (Version 4.1.2)
Rathod D.P.. 2011;Chlorophyll a fluorescence determines the drought resistance capabilities in two varieties of mycorrhized and non-mycorrhized Glycine max Linn. African Journal of Microbiology Research 5(24)https://doi.org/10.5897/ajmr11.737.
Shanker A.K., Amirineni S., Bhanu D., Yadav S.K., Jyothilakshmi N., Vanaja M., Singh J., Sarkar B., Maheswari M., Singh V.K.. 2022;High-resolution dissection of photosystem II electron transport reveals differential response to water deficit and heat stress in isolation and combination in pearl millet [Pennisetum glaucum (L.) R. Br.]. Frontiers in Plant Science :13. https://doi.org/10.3389/fpls.2022.892676.
Shin Y.K.. 2022. Evaluation of abiotic stress tolerance in vegetable plug seedlings using non-destructive chlorophyll fluorescence analysis. Domestic doctoral dissertation Jeonbuk National University; Jeonju, Korea:
Shu P., Gong Y., Du X., Han Y., Jin S., Wang Z., Qian P., Li X.. 2024;Effects of simulated acid rain on photosynthesis in pinus massoniana and cunninghamia lanceolata in terms of prompt fluorescence, delayed fluorescence, and modulated reflection at 820 nm. Plants 13(5):622. https://doi.org/10.3390/plants13050622.
Stirbet A., Govindjee . 2011;On the relation between the Kautsky effect (chlorophyll a fluorescence induction) and Photosystem II: Basics and applications of the OJIP fluorescence transient. Journal of Photochemistry and Photobiology B: Biology 104(1–2):236–257. https://doi.org/10.1016/j.jphotobiol.2010.12.010.
Stirbet A., Govindjee , Strasser B.J., Strasser R.J.. 1998;Chlorophylla fluorescence induction in higher plants: modelling and numerical simulation. Journal of Theoretical Biology 193(1):131–151. https://doi.org/10.1006/jtbi.1998.0692.
Strasser R.. 1978;The grouping model of plant photosynthesis. Chloroplast Development :513–542.
Strasser R.J., Srivastava A., Tsimilli-Michael M.. 2000;The fluorescence transient as a tool to characterize and screen photosynthetic samples. Probing Photosynthesis: Mechanisms, Regulation and Adaptation :445–483.
Strasser R.J., Tsimilli-Michael M., Srivastava A.. 2004. Analysis of the chlorophyll a fluorescence transient. advances in photosynthesis and respiration p. 321–362. Springer. Netherlands:
Tóth S.Z., Schansker G., Strasser R.J.. 2007;A non-invasive assay of the plastoquinone pool redox state based on the OJIP-transient. Photosynthesis Research 93(1–3)https://doi.org/10.1007/s11120-007-9179-8.
Wang R., Qin X., Pan H., Li D., Xiao X., Jin Y., Wang Y., Liang H.. 2025;Assessing the effects of drought stress on photosynthetic performance and physiological resistance in camphor seedling leaves. PLoS One 20(1):e0313316. https://doi.org/10.1371/journal.pone.0313316.
Yan W., Lu Y., Guo L., Liu Y., Li M., Zhang B., Zhang B., Zhang L., Qin D., Huo J.. 2024;Effects of drought stress on photosynthesis and chlorophyll fluorescence in blue honeysuckle. Plants 13(15):2115. https://doi.org/10.3390/plants13152115.
Yoo S.-Y., Lee Y.-H., Park S.-H., Choi K.-M., Park J.-Y., Kim A.R., Hwang S.-M., Lee M.-J., Ko T.-S., Kim T.-W.. 2013;Photochemical response analysis on drought stress for red pepper (Capsiumannuum L.). Korean Journal of Soil Science and Fertilizer 46(6):659–664. https://doi.org/10.7745/kjssf.2013.46.6.659.
Zhu J.-K.. 2016;Abiotic stress signaling and responses in plants. Cell 167(2):313–324. https://doi.org/10.1016/j.cell.2016.08.029.

Article information Continued

Fig. 1

Field setup and drought stress treatments: (A) Field plot; (B) Examples of plants under drought stress.

Fig. 2

Microclimatic conditions and soil moisture content in the greenhouse after transplantation: (A) Daily average temperature (℃); (B) Daily average soil moisture content (%).

Fig. 3

Changes in chlorophyll fluorescence intensity in the ten garden plant species under drought stress: (A) Polygonatum odoratum var. pluriflorum (Miq.) Ohwi; (B) Carex maculata Boott; (C) Pachysandra terminalis Siebold and Zucc; (D) Hosta longipes (Franch. and Sav.) Matsum; (E) Lilium lancifolium Thunb; (F) Allium dumebuchum H.J. Choi; (G) Iris sanguinea Donn ex Hornem; (H) Sedum takesimense Nakai; (I) Aster spathulifolius Maxim; (J) Mukdenia rossii (Oliv.) Koidz.

Fig. 4

Heatmap of correlations between soil moisture content and JIP-Test parameters in ten garden plants. Asterisks denote statistically significant differences (* p < .05, ** p < .01, *** p < .001).

Fig. 5

PCA biplot of JIP-Test parameters colored by soil moisture levels.

Fig. 6

Relative weights analysis for identifying key JIP-test parameters for assessing drought stress in garden plants.

Table 1

Formulas and glossary of terms used in the JIP-Test for analyzing OJIP fluorescence transients (Stirbet and Govindjee, 2011)

Parameter Descriptions
Fv/FM = 1 − FO/FM Maximum quantum yield of primary PSII photochemistry
ABS/RC=MO(1/VJ)(1/ϕPO) Absorption flux per RC
TRO/RC=MO(1/VJ) Trapped energy flux per RC (at t = 0)
ET2O/RC=(MO/VJ)(1-VJ) Electron transport flux from QA to QB per RC (at t = 0)
RE1O/RC=(MO/VJ)(1-VI) Electron transport flux until PSI acceptors per RC (at t = 0)
DIO/RC=(ABS/RC)-(TRO/RC) Disipated energy flux per RC (at t = 0)
RC/CSx = ϕPo(VJ/MO)(ABS/CSx) Density of RCs (QA-reducing PS II reaction centers)
ABS/CSx Absorption flux per CS ‘x’ can be ‘Chl’, 0 or ‘M’
TRO/CSxPo (ABS/CSx) Trapped energy flux per CS (at t = 0)
ET2O/CSxEo (ABS/CSx) Electron transport flux per CS (at t = 0)
RE1O/CSx = ϕRE1o (ABS/CSx) Electron transport flux until PSI acceptors per CS (at t = 0)
DI0/CSx = (ABS/CSx)(TR O /CSx) Disipated energy flux per CS (at t = 0)
DF=log(PI) Driving force on absorption basis
PIABS=RCABSϕPO1-ϕPOψO1-ψO Performance index for energy conservation from photons absorbed by PSII antenna, to the reduction of QB
PITotalABS=PIABS[δRE1O/(1-δRE1O)] Performance index for energy conservation from photons absorbed by PSII antenna, until the reduction of PSI acceptors

Table 2

Loadings of variables on principal components 1 and 2 in the PCA

PC1 PC2


Parameter Positive Parameter Negative Parameter Positive Parameter Negative
RC/CS −0.347 DIo/CS 0.647 PI_total ABS −0.411
ET2o/CS −0.347 ABS/CS 0.350 RC/ABS −0.320
RE1o/CS −0.343 TRo/CS 0.225 PI_ABS −0.254
TRo/CS −0.337 RE1o/CS 0.132 DF total ABS −0.149
Fv/Fm −0.328 ET2o/CS 0.122 Fv/Fm −0.099
ABS/CS −0.318 RC/CS 0.087
RC/ABS −0.305
PI_ABS −0.302
PI_total ABS −0.259
DF total ABS −0.251
DIo/CS −0.071

Table 3

Evaluation metrics for the multiple linear regression model

Metric Model value Baseline value
R2z 0.815 -
Adjusted R2y 0.755 -
RMSEx 0.430 0.999
MAEw 0.345 0.942
z

R2: Multiple R-squared.

y

Adjusted R2: Adjusted R-squared.

x

RMSE: Root Mean Square Error.

w

MAE: Mean Absolute Error.