Journal Journal of Applied Horticulture, 19(3): 180-185, 2017 Appl Effects of soil moisture stress on chlorophyll sensor readings in Monarda and Veronica Bruce L. Dunn*, Megha Poudel, Mark Payton1, and Jessica Lilienthal Department of Horticulture and Landscape Architecture, Oklahoma State University, Stillwater OK 74078-6027, USA. 1 Department of Statistics, Oklahoma State University, Stillwater OK 74078-6027, USA. *E-mail:bruce.dunn@okstate.edu Abstract Different handheld nondestructive optical sensors have been developed for measuring leaf nitrogen status over time, but environmental factors like water status may affect readings and correlations with leaf nitrogen. Thus, a greenhouse study was conducted to evaluate the effect of different handheld optical sensors on determination of chlorophyll level under different irrigation regimes using tensiometers. In this study, Monarda spicata ‘Sunny Border Blue’ and Veronica didyma ‘Gardenview Scarlet’ were grown at 5, 10, and 15 centibars controlled irrigation soil moisture levels. Chlorophyll content meter (CCM) and atLEAF sensor measurements were taken from single mature leaves of 10 plants from each treatment. Measurements were taken from the leaf tip, blade, and base of a single leaf excluding mid rib. Both optical sensors were used for 14 days consecutively starting 65 days after planting. Similarly, foliar nitrogen analysis was conducted from a single plant per treatment for 14 consecutive days. For the same 14 days, total daily water output and rate of transpiration from each irrigation treatment were also determined. Sensor readings varied between the two sensors for both species. Sensor sampling location was also significant for both atLEAF and CCM. For atLEAF, readings were greater at the leaf blade for both species; whereas, CCM showed greater readings at the leaf blade in Veronica and at the leaf base and blade in Monarda. Similarly, water stress × day interaction was significant for atLEAF in both species, whereas no water stress × day interaction was found in CCM. The correlation between sensor location and leaf N was significant only for atLEAF at the leaf blade (r = 0.57) and base (r = 0.47) in Monarda. No correlation with leaf N for either species was observed for CCM, thus atLEAF would be recommended for nondestructive leaf nitrogen estimation. However, readings should be taken from the same location of the leaf to achieve consistent readings and to minimize error. Key words: atLEAF, CCM, tensiometer, leaf N Introduction Extensive periods of drought leads to water stress in a plant, which can alter photosynthesis, transpiration rate and respiration, along with other physiological processes within the plant (Zhao et al., 2013). Win et al. (2015) reported that all plants that were subjected to drought conditions had reduced biomass and leaf area. Brown and Pezeshki (2007) also showed that water stress caused the breakdown and inhibition of chloroplast activity. In addition to reduced physiological processes, water stress leads to the accumulation of harmful compounds in the cell, such as hydrogen peroxide, ultimately leading to pigment bleaching (Nikolaeva et al., 2010). The research also reported a 13 to 15% loss of chlorophyll content in wheat (Triticum aestivum L.) plants that were exposed to drought durations of 3, 5, or 7 days with plants showing a greater chlorophyll loss in the 5 and 7 day treatments. Thus, effective water management is crucial in commercial agriculture, since under and over irrigation reduces crop yield and quality. Irrigation efficiency is influenced by the method of irrigation, type of crops, and irrigation schedule. Thompson et al. (2007) stated that, inefficient management of drip irrigation without proper scheduling increases nitrogen (N) leaching and use of excess water than plants require. Soil volumetric water or soil matric potential can be measured through use of sensors, such as a tensiometer, to estimate available water in the soil. A tensiometer is useful for controlling time and duration of irrigation (Pardossi et al., 2009). The number of different matric potential (set-points) in a tensiometer helps in creating different water stress level according to plant requirement (Montesano et al., 2015). Sanchez et al. (1983) claimed that increasing water stress reduces the chlorophyll level in a plant up to 40%. Yet, water stress induced loss of chlorophyll did not affect leaf N content and rate of photosynthesis compared to nutrient induced chlorophyll loss. Nitrogen is a major structural element of the plastid chlorophyll (Basyouni and Dunn, 2013). Due to this close relation, chlorophyll meters are regularly used to make N fertilizer recommendations for crops (Murdock et al., 1997). Determination of plant N status through measurements of leaf chlorophyll is a common practice in plant science (Brito et al., 2011). Destructive methods of determining chlorophyll and N measurement, through use of organic solvents, are laborious, costly, and time consuming practices; however, nondestructive methods using handheld devices are widely used in the field to generate instant recommendations (Munoz-Huerta et al., 2013). The Soil Plant Analysis Development (SPAD) chlorophyll meter (Minolta Camera Company, Tokyo, Japan) was initially used in 1963 for leaf N estimation in rice (Oryza sativa L.), but has since been used on horticultural crops too (Wood et al., 1993). SPAD readings Journal of Applied Horticulture (www.horticultureresearch.net) Effects of soil moisture stress on chlorophyll sensor readings in Monarda and Veronica are calculated on the basis of transmission of red light at 650 nm and infrared light at 940 nm (Xiong et al., 2015). An alternative to SPAD is atLEAF, which is a newly developed sensor, and has shown a positive correlation with SPAD in terms of sensor readings and leaf chlorophyll content analyzed in the laboratory (Dunn and Goad, 2015; Basyouni et al., 2015; Basyouni et al., 2017). The atLEAF meter is based on the transmission of red light at 660 nm and far red light at 940 nm to estimate the chlorophyll content (Basyouni and Dunn, 2013). Another sensor, Chlorophyll Content Meter-200 (CCM-200) was developed to report a chlorophyll content index (CCI) of a leaf (Biber, 2007; Silla et al., 2010,) and the CCI calculated by CCM-200 was also strongly correlated with chlorophyll a content in leaves of three coastal wetland plant species (Biber, 2007). The CCM-200 uses a slightly varied form of red light (653 nm) and near-infrared (931 nm) light for its calculation of chlorophyll content (OptiSciences, 2014a). A number of factors including sensor data collection protocol, plant growth stage, and environmental factors can affect sensor readings. Loh et al. (2002) noted that leaf age, sampling time, nutrient interactions, and complex source-sink relationships can affect the ability to detect N. Basyouni et al. (2015) noted that plant water status may also affect sensor readings. The objective of this study was to evaluate if chlorophyll sensor readings are affected by soil moisture status. Materials and methods Plant material, growth conditions, and irrigation treatments: On 17 December 2014, rooted plugs of bee balm (Monarda spicata L. ‘Sunny Border Blue’) and Gypsyweed (Veronica didyma L. ‘Gardenview Scarlet’) in 72 cell trays were obtained from Park Seed (Greenwood, SC). Plugs were transplanted into 15.24 cm diameter and 1.35 L volume pots with about 0.35 kg 902 Metro-Mix media (Sun Gro Horticulture, Bellevue, WA) 12 day later. A single plant was placed in each pot and plants were grown in the Department of Horticulture and Landscape Architecture research greenhouses in Stillwater, OK under natural photoperiods. Temperature was set at 21°C/18°C day/night with a photosynthetic photon flux density (PPFD) range of 300 to 1200 μmol m-2 s-1 at 1200 HR. Plants received 200 mg L-1 20N-10P20K Jack’s Professional® General Purpose acidic fertilizer (J.R. Peters Inc., Allentown, PA) at each watering event. Pots were drip irrigated daily based on a tensiometer (IRROMETER, Riverside, CA) settings of 5, 10, or 15 centibars (cb) starting on 6 February 2015. atLEAF, CCM, transpiration, water usage, and leaf N concentration: Individual plants were scanned from the same 10 pots per treatment using an atLEAF (FT Green LLC, Wilmington, DE) and CCM-300 (Opti-Sciences, Inc., Hudson, NH) chlorophyll meters every day (total of 14 rating dates) in the afternoon starting on 23 February 2015. For each pot, three atLEAF and three CCM measurements were taken from one mature leaf from the tip, blade, and base of the leaf not including the midrib in the middle of the canopy. Foliar analysis consisted of collecting all leaves from a single plant per treatment for total leaf N per sampling treatment daily. Leaf samples were analyzed for total N content (g kg-1 DM) by the Soil, Water and Forage Analytical Laboratory (SWFAL) at Oklahoma State University, using a LECO TruSpec 181 Carbon and N Analyzer (LECO Corporation, St. Joseph, MI). Total daily water output from the irrigation was collected from each tensiometer treatment. A LI-1600 Steady State Porometer (LI-COR, Inc., Lincoln, NE) was utilized to collect transpiration rates from each plant. At the end of the study, data was collected on shoot weight (stems cut at media level) after drying for 2 days at 52.2°C from the same 10 plants used for sensor readings. All statistical analyses were conducted with SAS Version 9.4 (SAS Institute, Cary, NC) for each plant species separately. Analysis of variance methods were used to determine the effects of treatment. When measurements were taken over different days, a repeated measures model and planned comparisons of treatments for a given day were made. Correlation analyses of atLEAF, CCM, and transpiration readings with leaf N samples were also computed. In instances where interactions were insignificant, main effect means were reported and analyzed. Significance was set at the 0.05 level, except for correlation in which 0.001 and 0.0001 were also considered. Results Leaf senor location: For both V. ‘Gardenview Scarlet’ and M. ‘Sunny Border Blue’, no sensor leaf location interactions were observed; however, location as a main affect was significant (P < 0.0001) for both genera. Leaf blade atLEAF readings were greater than any other treatment for both V. ‘Gardenview Scarlet’ and M. ‘Sunny Border Blue’, followed by leaf base values, which were also different from leaf tip reading (Table 1). For V. ‘Gardenview Scarlet’, leaf base CCM values were greatest (Table 1). CCM readings taken from the leaf tip were the lowest, while CCM values for leaf blade were intermediate between leaf base and leaf tip values (Table 1). Leaf base and leaf blade had greater CCM values than the leaf tip for M. ‘Sunny Border Blue’ (Table 1). atLEAF and water stress: For both V. ‘Gardenview Scarlet’ and M. ‘Sunny Border Blue’, tensiometer × day were significant (P < 0.0001). At 8 days after start of the water stress treatments, V. ‘Gardenview Scarlet’ plants at 5 or 15 cb had a greater atLEAF value than plants at 10 cb (Table 2). At 14 days, plants watered at 10 and 15 cb had greater atLEAF values than 5 cb plants (Table 2). For M. ‘Sunny Border Blue’ at day 1, the 15 cb plants had a greater atLEAF value than 5 cb plants, but neither treatment was different from the 10 cb plants (Table 2). At day 2 the 15 cb M. ‘Sunny Border Blue’ plants had a greater atLEAF value than the 5 and 10 cb treatments; whereas, at 12 days plants watered at 5 cb had a greater atLEAF value than the 10 or 15 cb plants (Table 2). Table 1. Effect of optical sensor sampling location within a leaf of Monarda ‘Gardenview Scarlet’ and Veronica ‘Sunny Border Blue’ Genus Monarda Veronica Sensor leaf location atLEAF value (unitless) CCM-300 value (mg m-2) Tip 48.2c 445.9cz Blade 51.0a 472.3b Base 49.0b 477.4a Tip 54.6c 482.4b Blade 56.2a 529.4a Base 55.6b 524.3a Means (n = 10) within columns for each sensor reading followed by the same letter are not significantly different P < 0.05. z Journal of Applied Horticulture (www.horticultureresearch.net) 182 Effects of soil moisture stress on chlorophyll sensor readings in Monarda and Veronica Table 2. Optical sensor and transpirations rate readings for Monarda ‘Gardenview Scarlet’ and Veronica ‘Sunny Border Blue’ at different tensiometer settings over a 14 day period Day Tensiometer atLEAF value CCM-300 value Transpiration rate setting (unitless) (mg m-2) (μg cm-2 s-1) (centibars) Monarda Veronica Monarda Veronica Monarda Veronica 1 5 461.0az 3.3ay 47.7az 52.8bz 443.0bz 2.5ay 2 3 4 5 6 7 8 9 10 11 12 13 14 10 47.5a 55.2ab 389.1c 491.2a 3.8a 3.0a 15 50.0a 56.4a 425.0b 468.9ab 2.4a 2.9a 5 52.2a 57.4b 464.1a 487.8a 2.9a 4.3a 10 52.4a 57.2b 411.2b 414.8b 4.3a 3.0b 15 52.4a 60.3a 443.6a 416.5b 3.6a 3.2b 5 52.6a 57.1a 439.4a 491.8a 5.5b 6.0a 10 53.4a 57.9a 454.9a 493.3a 7.8a 6.1a 15 51.8a 55.9a 447.2a 486.4a 4.9b 6.0a 5 50.6a 55.1a 484.5ab 515.7a 4.5a 4.6a 10 52.4a 56.1a 494.6a 515.7a 3.9a 4.1a 15 51.9a 55.1a 468.6b 514.8a 4.2a 4.5a 5 50.1a 58.3a 523.6a 564.7b 1.5b 2.3a 10 50.8a 57.8a 497.6b 591.6ab 6.3a 2.6a 15 49.6a 58.1a 506.1ab 612.5a 1.4b 2.0a 5 49.8a 56.2a 479.2a 528.8a 2.9a 3.3a 10 50.3a 56.9a 460.2a 549.4a 1.8a 2.3a 15 50.0a 56.1a 467.9a 510.7a 1.5a 2.8a 5 49.6a 56.0a 460.2a 553.9a 4.8a 5.4a 10 51.1a 56.4a 469.3a 533.3ab 3.8a 3.2b 15 51.9a 54.6a 481.1a 510.5b 3.0a 2.9b 5 51.5a 56.6a 505.6a 552.6a 3.5a 4.5a 10 48.3b 55.5a 475.6b 527.3a 4.4a 3.1b 15 49.9ab 55.7a 489.0ab 543.6a 2.1a 3.7ab 5 47.9a 54.8a 450.8b 526.1a 4.0a 5.1a 10 48.3a 56.9a 453.7b 508.4a 5.2a 4.2a 15 47.7a 54.1a 498.4a 531.0a 4.2a 4.5a 5 46.0a 53.2a 548.4a 554.1a 2.2a 3.0a 10 46.9a 54.7a 513.3b 561.0a 2.3a 2.5a 15 47.3a 55.1a 527.5b 581.6a 1.5a 2.6a 5 48.2a 54.1a 450.6a 473.0b 3.5a 3.5a 10 48.5a 55.7a 469.2a 528.4a 2.1a 2.1b 15 47.3a 53.4a 444.4a 508.0a 2.8a 2.8ab 5 47.6a 56.1a 451.4a 495.7a 5.3a 4.1a 10 48.3a 53.6b 434.1a 502.5a 4.3a 4.2a 15 48.5a 52.6b 453.6a 503.0a 1.8b 2.6b 5 47.0a 52.0a 411.9a 457.8a 3.4a 4.4a 10 47.3a 54.0a 418.0a 471.5a 3.7a 4.9a 15 48.8a 52.3a 424.8a 448.7a 2.9a 4.2a 5 44.8b 52.3a 455.3b 499.6a 3.5a 3.5a 10 48.1a 54.3a 455.5b 513.3a 2.5a 4.1a 15 47.8a 54.3a 479.1a 523.1a 2.0a 3.0a Means (n = 30) within columns for each date followed by the same letter are not significantly different P < 0.05. y Means (n = 5) within columns for each date followed by the same letter are not significantly different P < 0.05. z CCM and water stress: For both V. ‘Gardenview Scarlet’ and M. ‘Sunny Border Blue’ no CCM leaf sensor location interactions occurred; however, water stress × day was significant (P < 0.0001). CCM values were greater for 5 cb V. ‘Gardenview Scarlet’ plants at 1 day. At 2 days, both 5 and 15 cb plants had greater CCM values than 10 cb plants. At 4 days, 10 cb V. ‘Gardenview Scarlet’ plants had a greater CCM value than 15 cb plants, but neither was different from 5 cb plants (Table 2). At 5 and 8 days, 5 cb V. ‘Gardenview Scarlet’ plants had a greater CCM value than 10 cb plants, but neither treatment was different from 15 cb plants (Table 2). CCM value was greatest at 15 cb for V. ‘Gardenview Scarlet’ plants at 9 and 14 days, while plants in the 5 and 10 cb treatments did not differ (Table 2). At 10 days, the 5 cb treatment was greater than both the 10 and 15 cb treatments, which were not different from each other (Table 2). For M. ‘Sunny Border Blue’ at 1 day, the 10 cb plants had a greater CCM value than plants grown at 5 cb though neither treatment was different from 15 cb plants. CCM was greatest for 5 cb M. ‘Sunny Border Blue’ plants at 2 days. At 5 days, M. ‘Sunny Border Blue’ plants grown at 15 cb had a greater CCM value than plants grown at 5 and 10 cb, but did not differ from the other two treatments. M. ‘Sunny Border Blue’ plants grown at 5 cb on 7 days had greater CCM values than plants grown at 15 cb, but neither treatment differed from the 10 cb treatments. Both 10 and 15 cb M. ‘Sunny Border Blue’ plants had greater CCM values than the 5 cb treatment at 11 days. Transpiration: No water stress × day interaction was found for V. ‘Gardenview Scarlet’ though both main effects were significant (P = 0.006) and (P < 0.0001), respectively. Transpiration rate was greater for 10 cb V. ‘Gardenview Scarlet’ plants at 3 and 5 days, while at 12 days plants grown at 5 and 10 cb had greater transpiration rates than 15 cb plants. For M. ‘Sunny Border Blue’ a significant (P = 0.019) water stress × day interaction was observed. M. ‘Sunny Border Blue’ plants had greater transpiration rates for 5 cb plants at 2 and 7 days, while on 8 and 11 days the 5 cb plants had a greater transpiration rate than 10 cb plants, but neither treatment differed from plants grown at 15 cb. For M. ‘Sunny Border Blue’, transpiration rates were greatest and did not differ for both 5 and 10 cb and were greater than 15 cb on day 12 (Table 2). Total daily water, leaf N, EC, and plant dry weight: No interactions were seen for total daily water use, leaf N, EC, or plant dry weight. Day main effects were significant for total daily water (P = 0.0136) and V. ‘Gardenview Scarlet’ leaf N (P = 0.0003). Total daily water use was greatest on 1 day, but did not differ from 3 d, which did not differ from 6, 8, 9, 10, 11, 12, 13, and 14 days (Table 3). Plants had the least amount of water at 4 d, but total water Journal of Applied Horticulture (www.horticultureresearch.net) Effects of soil moisture stress on chlorophyll sensor readings in Monarda and Veronica Table 3. Amount of water applied and leaf nitrogen (N) concentration collected for Monarda ‘Gardenview Scarlet’ and Veronica ‘Sunny Border Blue’ plants watered using a tensiometer Day Total daily water Monarda leaf N Veronica leaf N (mL) (g kg-1 DM)z (g kg-1 DM)z 1 2 3 4 5 6 7 8 9 10 11 12 13 14 90.3a 7.0cd 57.7ab 1.3d 7.7cd 27.7bcd 14.0cd 44.0bc 24.0bcd 25.7bcd 45.0bc 30.3bcd 28.7bcd 47.3bc 0.76ay ------x 0.71a -----0.69ab -----0.60cd -----0.63bc -----0.59cd -----0.55d ------ 0.64a -----0.61a -----0.63a -----0.62a -----0.61a -----0.63a -----0.59a ------ Sample included taking all leaves from a single plant. Means (n = 3) within genera followed by the same letter are not significantly different P < 0.05. xData not taken. z y Table 4. Pearson’s correlation coefficient matrix on measured leaf nitrogen (N), transpiration, and optical sensor parameters for Monarda and Veronica watered using a tensiometer Transpiration rate Monarda leaf N (g kg-1 DM)z Veronica leaf N (g kg-1 DM)z 0.109 -0.197 0.360 -0.222 atLEAF blade 0.574**y 0.056 atLEAF base 0.475* 0.083 CCM tip -0.157 0.021 CCM blade -0.165 0.066 CCM base -0.045 0.288 atLEAF tip Sample included taking all leaves from a single plant. For transpiration rate and all sensors (n = 21) and (n = 105), respectively. y P ≤ 0.05 (*), P ≤ 0.001 (**), or P ≤ 0.0001 (***). z Table 5. Pearson’s correlation coefficient matrix on measured optical sensor parameters for Monarda ‘Gardenview Scarlet’ and Veronica ‘Sunny Border Blue’ watered using a tensiometer. (n = 105) atLEAF blade atLEAF base CCM tip CCM blade CCM base 0.698*** 0.130 0.094 0.107 0.706*** 0.113 0.132 0.141 0.528 0.0819 0.106 0.825*** 0.737*** Monarda atLEAF tip 0.636*** z atLEAF blade atLEAF base CCM tip 0.850*** CCM blade Veronica atLEAF tip atLEAF blade atLEAF base 0.558*** 0.322** 0.431*** 0.465*** 0.333** 0.417*** 0.420*** 0.465*** 0.333** 0.217* 0.245* 0.260** 0.767*** 0.628*** CCM tip 0.695*** CCM blade P ≤ 0.05 (*), P ≤ 0.001 (**), or P ≤ 0.0001 (***). z 183 collected did not differ from 2, 5, 6, 7, 9, 10, 12, and 13 days (Table 3). For V. ‘Gardenview Scarlet’ leaf N was greatest at 1, 3, and 5 days, but 5 days did not differ from 9 days. The lowest leaf N concentration was found at 13 days, but did not differ from 7 and 11 days. No differences were observed for EC, which ranged from 0.4 mS cm-1 at 11 days to 3.1 mS cm-1 at 7 days for V. ‘Gardenview Scarlet’ and 0.9 mS cm-1 at 10 days to 2.68 mS cm-1 at 5 days for M. ‘Sunny Border Blue’ (data not shown). Similarly, no differences were observed in shoot dry weight of V. ‘Gardenview Scarlet’, which ranged from 5.1 g to 5.9 g in different soil moisture levels and 3.8 g to 4.6 g for M. ‘Sunny Border Blue’ (data not shown). Correlations: atLEAF readings from the leaf blade and base were correlated with leaf N for V. ‘Gardenview Scarlet’; however, no correlations were seen for transpiration rate and sensors with leaf N for M. ‘Sunny Border Blue’ (Table 4). Correlations among leaf sampling location within a senor was significant for both plants (Table 5). atLEAF and CCM sensors were not correlated for V. ‘Gardenview Scarlet’, but were correlated for M. ‘Sunny Border Blue’ (Table 5). Discussion Different readings were observed among the two optical sensors. Variation in readings occurred because the sensors work at different wavelengths, sampling areas, and compensation algorithms. atLEAF uses 660 nm and 940 nm wavelength of light to measure the transmittance of red and near infrared light through leaves (Basyouni and Dunn, 2013), while CCM operates in wavelength of 700 to 710 nm and 730 to 740 nm for red and near infrared wavelength, respectively (Opti-Sciences, 2014b). In both sensors, readings from the leaf tip, leaf blade, and leaf base were different for both V. ‘Gardenview Scarlet’ and M. ‘Sunny Border Blue’ (Table 1). atLEAF showed greater readings at the leaf blade for both species, whereas CCM showed greater readings at the leaf base in V. ‘Gardenview Scarlet’ and at the leaf blade and base in M. ‘Sunny Border Blue’. Bolhar-Nordenkampf and Grunweis (1987) suggested that the difference in chlorophyll content in different leaf locations has an anatomical relation. The additional layers of palisade and spongy parenchyma in veins and blade of leaves increases photosynthetic pigment chlorophyll in these areas. In contrast, the tip and base of a leaf has a lower chlorophyll concentration (Bolhar-Nordenkampf and Grunweis, 1987; Dunn and Goad, 2015; Ticha, 1985). Greater differences between readings were observed with the CCM meter in different water stress conditions than with the atLEAF sensor. Similar to this study where we observed no difference between water stress treatments for most days, others have reported no difference in atLEAF readings under different environmental conditions (Novichonok et al., 2016; Zhu et al., 2012). For most days, the readings of both sensors were different for both species in different water stress conditions, which could be because of the drought tolerant nature of V. ‘Gardenview Scarlet’ and M. ‘Sunny Border Blue’ (Gilman and Delvalle, 2014; Kessler, 2008), resulting in greater readings even if water-stressed. Upadhyaya (2005) also reported greater SPAD readings in peanut (Arachis hypogaea L.) in post-rainy season than during the rainy season. Journal of Applied Horticulture (www.horticultureresearch.net) 184 Effects of soil moisture stress on chlorophyll sensor readings in Monarda and Veronica In contrast, Yuan et al. (2016) reported decreasing chlorophyll content in tomato (Solanum lycopersicum L. cv. Jinfen 2) leaves with increasing water stress. In addition, differences between different water stress conditions were not observed in that study for chlorophyll sensor readings. Another reason for this might be the malfunction of a tensiometer because of cavitation, which will not allow the desired water stress level to be maintained (Tarantino and Mongiovi, 2001). Also, sensor-based leaf chlorophyll and leaf N estimation is highly influenced by environmental conditions including light, temperature, nutrients, and leaf characteristics like age of the leaf and location of the leaf (Minotta and Pinzauti, 1996; Xiong et al., 2015). In this study, there was a significant difference in rate of transpiration among the three tensiometer set points of 5, 10 and 15 cb. With increasing water stress, both V. ‘Gardenview Scarlet’ and M. ‘Sunny Border Blue’ showed a lower rate of transpiration. Both genera reduced the transpiration loss during the waterstressed condition. Increasing water stress forces plants to close stomata and reduce leaf area, which reduces transpiration (Akinci and Losel, 2012; Arve et al., 2011; Waister and Hudson, 1970). In addition, Hsiao (1973) claimed that besides water availability, temperature, light, humidity, and wind also effect transpiration. Total daily water input had a linear downward slope, which means rate of daily water input was decreasing with increasing plant age. Briggs and Shantz (1913) reported similar findings from the Von Seelhorst’s (1910) experiment on water requirement of lupin (Lupinus angustifolius L.). Climatic conditions highly influences the water requirement in plants. For example, a decrease in nutrient content in the substrate reduces the rate of dry matter accumulation with increasing plant age, which further increases water demand to maintain the balance, but would not be the case if additional nutrients are supplied. Water requirement is inversely proportional to rate of dry matter accumulation (Briggs and Shantz, 1913). Therefore, no conclusion is given for age of plant and water requirements. Leaf N concentration also decreased with increasing age in V. ‘Gardenview Scarlet’. The newly formed leaves contain high N content and with no additional N, leaf N decreases with increasing plant age (Hikosaka et al., 1994; Yang et al., 2014). In contrast, spinach (Spinacia oleracea L.) grown with high amount of N had shown greater leaf N and chlorophyll content with increasing plant age (Bottrill and Possingham, 1969). Correlation between atLEAF base and blade with V. ‘Gardenview Scarlet’ leaf N was observed. Dunn and Goad (2015) also observed a greater correlation between atLEAF tip and blade with leaf N in ornamental cabbage (Brassica oleracea var. capitata L.). None of the sensors showed correlation with leaf N for M. ‘Sunny Border Blue’. Use of SPAD in a study of 12 different cultivars of red maple (Acer rubrum L.) reported nonsignificant correlations between sensor readings and leaf N content (Sibley et al., 1996). Similarly, study of three different cultivars of peace lily (Spathiphyllum Schott) also found that SPAD readings and leaf N were not correlated (Wang et al., 2004). Xiong et al. (2015) states that the sensor readings are affected by environmental factor and leaf characteristics. Thus, cultivar specific calibration of sensors is essential for proper functioning of sensors. Although CCM did not show a correlation with leaf N in both plant species in our study, other studies found a positive correlation between CCM and leaf N (Cate and Perkins, 2003; Ghasemi et al., 2011) Based on the study, leaf sampling location affected the sensor readings. The readings were also affected by the leaf characteristics and type of sensor used. atLEAF and CCM values were not correlated. CCM readings were not correlated with leaf N, thus would not be recommended for use in determining leaf N, however, atLEAF showed correlation with leaf N even under various soil moisture conditions. No clear pattern was observed for greater or lower sensor values in different tensiometer settings; however, plant water status could affect sensor readings. This is similar with findings from Yuan et al. (2016), who reported that soil moisture status can affect leaf chlorophyll status of tomato. Differences may be more influenced by some outside factor like number of samples, time of sampling, or different water stress level. Zhang et al. (2011) reported a midday depression phenomenon that occurred in water-stressed oriental lily (Lilium L. cv. Sorbonne), but not in the control group, that reduced gas exchange around the plant. Plant water status can be difficult to determine when plants require more water because of limited water holding capacity of soilless mix (Fonteno et al., 1981; Karlovich and Fonteno, 1986). This problem can be solved through the use of a tensiometer by directly measuring the water availability in the substrate, but proper care and maintenance should be done for accurate functioning of the tensiometer. Although research is limited on conducting automated water management with a tensiometer, different set points help in maintaining different water regime according to plant needs (Montesano et al., 2015). Future research should look at tracking plants over the course of production, different species and even cultivars, increasing number of samples, optimum tensiometer set points for potted plants, and observing how environmental factors affect or interact with plant water status and sensor readings. Acknowledgements This work was supported by the USDA National Institute of Food and Agriculture, Hatch project and the Division of Agricultural Sciences and Natural Resources at Oklahoma State University. References Akinci, S. and D.M. Losel, 2012. 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