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Simulated Seawater Flooding Reduces the Growth of Ten Vegetables

Excessive salinity in soil and irrigation water in combination with waterlogging in coastal regions can significantly reduce the productivity ofmany agricultural crops. To evaluate the plant growth responses to simulated seawater (SSW) flooding, seedlings of 10 vegetables (broccoli, chinese cabbage, chinese greens, cucumber, eggplant, kale, radish, ‘Red Crunchy’ radish, spinach, and tomato) were flooded with SSW at electrical conductivity (EC) of 44.0 ± 1.3 dS·m or tap water at EC of 0.8 ± 0.1 dS·m for 24 hours and grown subsequently for 2 weeks in a greenhouse. Chinese greens and cucumber plants died shortly after flooding with SSW, whereas other vegetables exhibited various degrees of visible salt damage. Chinese cabbage suffered the strongest reduction, whereas spinach, tomato, and eggplant exhibited the least decrease in dry weight (DW) due to SSW flooding in comparison with their perspective control. Two weeks after flooding treatment with SSW, net photosynthetic rate of broccoli, kale, spinach, and tomato was reduced by 43% to 67%, transpiration rate by 35% to 66%, and stomatal conductance (gS) by 51% to 82%. In summary, spinach, eggplant, and tomato were the most tolerant, whereas chinese cabbage, chinese greens, and cucumber were the least tolerant to SSW flooding. Crop production in coastal areas is threatened by seawater intrusion, which increases soil salinity. Seawater intrusion will become a more prominent concern as sea level continues to rise with global climate change and overuse of groundwater. According to Stoner (1988), about 40,000 ha of arable lands are lost every year due to salinity and waterlogging. Excessive salinity in soil and irrigation water in combination with waterlogging can significantly reduce the productivity of many agricultural crops, especially those vegetables that are sensitive to salinity. Salinity is one of the major abiotic stresses that threaten agricultural production. Increasing salinity in soil and irrigation water usually leads to a buildup in sodium (Na) and chloride (Cl) content and imposes water deficit detrimental to plants (Yamaguchi and Blumwald, 2005). Adverse effects associated with salinity include plant growth reduction, leaf burning, decreased photosynthesis, and potentially death (Munns and Tester, 2008). Salt tolerance varies among plant species or even cultivars within species. Akinci et al. (2004) observed that growth and development of eggplant cultivars at the germination and seedling stages were negatively affected by increasing NaCl from 50 mM to 150 mM, and ‘Kemer’ was more tolerant than ‘Pala’ and ‘Aydin Siyahi’. Furthermore, salt tolerance is frequently different from one growth stage to another. Sugar beet and tomato plants are more sensitive to salinity during germination and early growth, but moderately to highly salt tolerant at maturity (Ungar, 1996). The response of eggplant cultivars Kemer, Pala, and Aydin Siyahi to salinity varied also with plant growth stage with salt tolerance increasing as later growth stages progressed (Akinci et al., 2004). Flooding is another major abiotic stress significantly impacting crop growth and productivity. An estimated $500–$600 million in agricultural production was lost due to flooding in eastern Australia in 2010–11, especially the production of cotton, fruit, grain sorghum, vegetables, andwinter crops (ABARES, 2011). In general, flooding damages vegetables by reducing oxygen in the root zone, which inhibits aerobic processes. Flooding restricts respiration and gaseous exchange, ceases growth processes, reduces yields, or even leads to death and decay of crop plants (Visser et al., 2003). Johnson (2011) reported that most vegetable crops can recover if the flooding or waterlogging duration is less than 48 h. Longer flood periods will lead to root death and lower chances of recovery. Most vegetables are highly sensitive to flooding and genetic variation is high. Tomato ‘LA1579’ genotype is flooding sensitive, whereas genotype ‘CLN2498E’ and ‘CA4’ show high tolerance to flooding (Ezin et al., 2010). Some plants have developed a mechanism that allows them to exclude salts from their shoots or tolerate accumulated salts in their tissue (Munns and Tester, 2008). However, the mechanism to exclude salts from shoots will break down and roots become ‘‘leaky’’ to salts because waterlogging makes plant roots oxygen deficient and thus decreases their production of energy (Qureshi and BarrettLennard, 1998). Barrett-Lennard (1986) observed that waterlogging and salinity interactively allow large and rapid accumulation of Na and Cl in plant shoots. Na content in wheat leaves continuously increased with salt and waterlogged treatment (Ibrahim et al., 2007). Salt-waterlogged treatment also greatly reduced grain DW and number per plant in Triticum aestivum (wheat) ‘Pirsabak’, ‘Inqlab91’, ‘SARC-6’, and ‘HD-2320’ (Ibrahim et al., 2007). In addition, there is substantial evidence that waterlogging under salt conditions increases leaf senescence. The combination of waterlogging and salinity (8.7 dS·m NaCl) increased the numbers of senescenced leaves, but did not affect the rate of production of new leaves of squash (Cucurbita pepo) that grew in sand irrigation (Huang et al., 1995a, 1995b). Little information is available on the tolerance of many vegetables at early stages of development to seawater flooding. The purpose of this study was to evaluate the plant growth responses of 10 common vegetable crops to SSW flooding for 24 h in a greenhouse. Gas exchange rates and leaf Na, potassium (K), calcium (Ca), and Cl accumulation of selected vegetables were also determined. Materials and Methods Plant materials. On 8 Jan. 2014, seeds of 10 vegetables [eggplant ‘Amadeo’ hybrid (Solanum melongena), broccoli ‘Packman’ hybrid (Brassica oleracea), kale ‘Winterbor’ hybrid (Brassica oleracea), chinese cabbage ‘Kaboko’ (Brassica campestris), tomato ‘Mega Bite’ hybrid (Solanum lycopersicum), spinach ‘Palco’ hybrid (Spinacia oleracea), cucumber ‘Spring Swallow’ hybrid (Cucumis sativus), radish (Raphanus sativus) (Geo. W. Park Seed Co., Inc., Greenwood, SC), radish ‘Red Crunchy’ hybrid (Abbott & Cobb, Inc., Feasterville, PA), chinese greens (Brassica rapa; Seedway, Inc., Hall, NY)] were sown at a depth of 0.5 cm in a germination insert (13.5 cm · 13.5 cm · 4.5 cm) filled with Metro-Mix 360 (Sun Gro Horticulture, Bellevue,WA). Flats were placed under intermittent mist with reverse osmosis (RO) water and the misting frequency was controlled by a timer (Phytotronics Inc., Earthcity, MO) set at 20 s Received for publication 14 Jan. 2015. Accepted for publication 9 Mar. 2015. This work was supported by the USDA National Institute of Food and Agriculture, Hatch Project TEX090450, and Texas A&M AgriLife Research. To whom reprint requests should be addressed; e-mail gniu@ag.tamu.edu. 694 HORTSCIENCE VOL. 50(5) MAY 2015 per hour. One week later, seedlings emerged, and theyweremoved out of themist bench and placed on greenhouse bench. Seedlings were watered with nutrient solution with an EC of 1.6 ± 0.3 dS·m. The nutrient solution was prepared by adding 0.72 g·L 15 N–2.2 P– 12.5 K (Peters 15-5-15, Marysville, OH) to tap water. On 21 Jan., seedlings were transplanted into 4-inch pots (8.5 cm · 8.5 cm · 8.0 cm), one plant per pot, filled with Metro-Mix 360 and were watered with nutrient solution until treatments were initiated. Treatments. On 6 Feb., 4 weeks after sowing, flats with 10 vegetable species were placed (flooded) in a tub for 24 h with SSW or with tap water (tap water flooding control). There were 12 seedlings per species, 12 plants per flat, 30 flats in total. The EC for SSW and tap water was 44.0 ± 1.3 dS·m and 0.8 ± 0.1 dS·m, respectively. The flooding completely immersed the growing medium but leaves were not in contact with SSW or tap water. Another group of seedlings were not immersed and served as no flooding control. The SSW was prepared by adding 35 g of NaCl (Fisher Scientific, Waltham, MA) to 1 kg of tap water (Wikipedia, The Free Encyclopedia, 2014). All flooded seedlings were moved out of the tub 24 h later. The substrate EC was determined by using pour-through protocol (Cavins et al., 2008) and measured using an EC meter (Model B173; Horiba, Ltd., Japan). The substrate EC was 4.1 ± 1.1 dS·m, 2.5 ± 0.5 dS·m, and 43.0 ± 4.7 dS·m for control without flooding, tap water flooding, and SSW flooding, respectively, measured the day after SSW treatment. All seedlings were placed on greenhouse benches and grown subsequently for another 2 weeks. Plants were irrigated with nutrient solution whenever the substrate surface started to dry (a total of three times during the 2-week period). Temperature in the greenhouse wasmaintained at 25.7 ± 8.1 C during the day and 13.4 ± 4.5 C at night. The daily light integral photosynthetically active radiation (PAR) was 12.3 ± 2.2 mol·m·d. The substrate final ECs, determined using saturated paste extract (Gavlak et al., 1994; USDA Staff, 1954), were 3.1 ± 0.2 dS·m, 2.4 ± 0.2 dS·m, and 7.3 ± 0.7 dS·m, respectively, for control without flooding, tap water flooding, and SSW flooding. Growth data.At the end of the experiment (2 weeks after flooding treatment), visual foliar salt damage of every plant (leaf edge burn, necrosis, or discoloration) was rated on a score of 0 to 5, where 0 = dead, 1 = severe (over 90%), 2 = moderate (50% to 90%), 3 = slight (<50%), 4 = good quality with minimal foliar damage, and 5 = excellent with no visible foliar damage. Plant height was recorded from the pot rim to the top growth point, or leaf apex of the longest leaf. The shoots of all plants were severed at the substrate surface, and fresh weight was recorded immediately. Leaf area of all plants was determined using LI-3100C area meter (LI-COR Biosciences, Lincoln, NE). Shoot DW was determined after shoots were ovendried at 65 C to constant weight. Gas exchange and SPAD reading. Gas exchange and relative chlorophyll content were measured for broccoli ‘Packman’ hybrid, eggplant ‘Amadeo’ hydrid, kale ‘Winterbor’ hybrid, spinach ‘Palco’ hybrid, and tomato ‘Mega Bite’ hybrid. Gas exchange and relative chlorophyll content were not measured for other species because the plants were dead or almost dead by the end of the experiment. Leaf net photosynthesis (Pn), transpiration (E), and gS of five plants per species per treatment were measured 1 d before growth data were taken using a CIRAS-2 portable photosynthesis system (PP Systems, Amesbury, MA) with an automatic universal PLC6 broad leaf cuvette. Fully expanded healthy leaves were chosen for measurements. The environmental conditions in the cuvette were set at leaf temperature of 25 C, photosynthetic photon flux (PPF) of 1000 mmol·m·s, and CO2 concentration of 375 mmol·mol. Data were recorded when the environmental conditions and gas exchange parameters in the cuvette became stable. These measurements were taken on a sunny day between 10:00 AM and 2:00 PM, and the plants were well watered to avoid water stress. Leaf greenness or relative chlorophyll content of five plants per species per treatment was measured using a handheld SPAD chlorophyll meter (Minolta Camera Co., Osaka, Japan) 1 d before harvest. For each plant, five healthy and fully expanded leaves were chosen for measuring the relative chlorophyll content (SPAD) readings. Ion analysis. Five leaf samples per treatment per species were randomly selected for mineral analysis. Plants in the control treatment and SSW flooding treatment were chosen for mineral analysis. Dried tissue samples were ground to pass a 40-mesh screen with a stainless Wiley mill (Thomas Scientific, Swedesboro, NJ). Plant tissues were digested using environmental protection agency method 3051 with 1 mL nitric acid and 4 mL hydrogen peroxide using a microwave acceleration reaction system (CEM Corporation; Mathews, NC) for determining alkaline earth metals (Na, K, Ca). The plant tissues were extracted with 2% acetic acid (EM Science, Gibbstown, NJ) for determining anions (Cl) using methods described by Gavlak et al. (1994). Na, K, and Ca in the digested samples were analyzed by inductively coupled plasma-optical emission spectrometry (Perkin-Elmer Optima 4300 DV; Perkin-Elmer, Shelton, CT). Cl was determined by M926 Chloride Analyser (Cole Parmer Instrument Company, Vernon Hills, IL). Experimental design and statistical analysis. The experiment followed a splitplot design with flood treatment as the main plot and species as subplot with 12 replications. All data were analyzed as a two-way analysis of variance (ANOVA) using PROC GLM. Because all growth, gas exchange, and mineral element data of plants in the control treatment were not significantly different from those of plants flooded with tap water, they were pooled for further analysis. For each species, Student’s t tests between treatments were conducted within species. Relative height for each plant in the SSW treatment was calculated as follows: Relative heightð%Þ = Height in SSW treatment Averaged height in control

Crop production in coastal areas is threatened by seawater intrusion, which increases soil salinity. Seawater intrusion will become a more prominent concern as sea level continues to rise with global climate change and overuse of groundwater. According to Stoner (1988), about 40,000 ha of arable lands are lost every year due to salinity and waterlogging. Excessive salinity in soil and irrigation water in combination with waterlogging can significantly reduce the productivity of many agricultural crops, especially those vegetables that are sensitive to salinity.
Salinity is one of the major abiotic stresses that threaten agricultural production. Increasing salinity in soil and irrigation water usually leads to a buildup in sodium (Na) and chloride (Cl) content and imposes water deficit detrimental to plants (Yamaguchi and Blumwald, 2005). Adverse effects associated with salinity include plant growth reduction, leaf burning, decreased photosynthesis, and potentially death (Munns and Tester, 2008). Salt tolerance varies among plant species or even cultivars within species. Akinci et al. (2004) observed that growth and development of eggplant cultivars at the germination and seedling stages were negatively affected by increasing NaCl from 50 mM to 150 mM, and 'Kemer' was more tolerant than 'Pala' and 'Aydin Siyahi'. Furthermore, salt tolerance is frequently different from one growth stage to another. Sugar beet and tomato plants are more sensitive to salinity during germination and early growth, but moderately to highly salt tolerant at maturity (Ungar, 1996). The response of eggplant cultivars Kemer, Pala, and Aydin Siyahi to salinity varied also with plant growth stage with salt tolerance increasing as later growth stages progressed (Akinci et al., 2004).
Flooding is another major abiotic stress significantly impacting crop growth and productivity. An estimated $500-$600 million in agricultural production was lost due to flooding in eastern Australia in 2010-11, especially the production of cotton, fruit, grain sorghum, vegetables, and winter crops (ABARES, 2011). In general, flooding damages vegetables by reducing oxygen in the root zone, which inhibits aerobic processes. Flooding restricts respiration and gaseous exchange, ceases growth processes, reduces yields, or even leads to death and decay of crop plants (Visser et al., 2003). Johnson (2011) reported that most vegetable crops can recover if the flooding or waterlogging duration is less than 48 h. Longer flood periods will lead to root death and lower chances of recovery. Most vegetables are highly sensitive to flooding and genetic variation is high. Tomato 'LA1579' genotype is flooding sensitive, whereas genotype 'CLN2498E' and 'CA4' show high tolerance to flooding (Ezin et al., 2010).
Some plants have developed a mechanism that allows them to exclude salts from their shoots or tolerate accumulated salts in their tissue (Munns and Tester, 2008). However, the mechanism to exclude salts from shoots will break down and roots become ''leaky'' to salts because waterlogging makes plant roots oxygen deficient and thus decreases their production of energy (Qureshi and Barrett-Lennard, 1998). Barrett-Lennard (1986) observed that waterlogging and salinity interactively allow large and rapid accumulation of Na and Cl in plant shoots. Na content in wheat leaves continuously increased with salt and waterlogged treatment (Ibrahim et al., 2007).
Salt-waterlogged treatment also greatly reduced grain DW and number per plant in Triticum aestivum (wheat) 'Pirsabak', 'Inqlab-91', 'SARC-6', and 'HD-2320' (Ibrahim et al., 2007). In addition, there is substantial evidence that waterlogging under salt conditions increases leaf senescence. The combination of waterlogging and salinity (8.7 dS · m -1 NaCl) increased the numbers of senescenced leaves, but did not affect the rate of production of new leaves of squash (Cucurbita pepo) that grew in sand irrigation (Huang et al., 1995a(Huang et al., , 1995b. Little information is available on the tolerance of many vegetables at early stages of development to seawater flooding. The purpose of this study was to evaluate the plant growth responses of 10 common vegetable crops to SSW flooding for 24 h in a greenhouse. Gas exchange rates and leaf Na, potassium (K), calcium (Ca), and Cl accumulation of selected vegetables were also determined.  Hall, NY)] were sown at a depth of 0.5 cm in a germination insert (13.5 cm · 13.5 cm · 4.5 cm) filled with Metro-Mix 360 (Sun Gro Horticulture, Bellevue, WA). Flats were placed under intermittent mist with reverse osmosis (RO) water and the misting frequency was controlled by a timer (Phytotronics Inc., Earthcity, MO) set at 20 s per hour. One week later, seedlings emerged, and they were moved out of the mist bench and placed on greenhouse bench. Seedlings were watered with nutrient solution with an EC of 1.6 ± 0.3 dS · m -1 . The nutrient solution was prepared by adding 0.72 g · L -1 15 N-2.2 P-12.5 K (Peters 15-5-15, Marysville, OH) to tap water. On 21 Jan., seedlings were transplanted into 4-inch pots (8.5 cm · 8.5 cm · 8.0 cm), one plant per pot, filled with Metro-Mix 360 and were watered with nutrient solution until treatments were initiated.

Materials and Methods
Treatments. On 6 Feb., 4 weeks after sowing, flats with 10 vegetable species were placed (flooded) in a tub for 24 h with SSW or with tap water (tap water flooding control). There were 12 seedlings per species, 12 plants per flat, 30 flats in total. The EC for SSW and tap water was 44.0 ± 1.3 dS · m -1 and 0.8 ± 0.1 dS · m -1 , respectively. The flooding completely immersed the growing medium but leaves were not in contact with SSW or tap water. Another group of seedlings were not immersed and served as no flooding control. The SSW was prepared by adding 35 g of NaCl (Fisher Scientific, Waltham, MA) to 1 kg of tap water (Wikipedia, The Free Encyclopedia, 2014). All flooded seedlings were moved out of the tub 24 h later. The substrate EC was determined by using pour-through protocol (Cavins et al., 2008) and measured using an EC meter (Model B-173; Horiba, Ltd., Japan). The substrate EC was 4.1 ± 1.1 dS · m -1 , 2.5 ± 0.5 dS · m -1 , and 43.0 ± 4.7 dS · m -1 for control without flooding, tap water flooding, and SSW flooding, respectively, measured the day after SSW treatment. All seedlings were placed on greenhouse benches and grown subsequently for another 2 weeks. Plants were irrigated with nutrient solution whenever the substrate surface started to dry (a total of three times during the 2-week period). Temperature in the greenhouse was maintained at 25.7 ± 8.1°C during the day and 13.4 ± 4.5°C at night. The daily light integral photosynthetically active radiation (PAR) was 12.3 ± 2.2 mol · m -2 · d -1 . The substrate final ECs, determined using saturated paste extract (Gavlak et al., 1994;USDA Staff, 1954), were 3.1 ± 0.2 dS · m -1 , 2.4 ± 0.2 dS · m -1 , and 7.3 ± 0.7 dS · m -1 , respectively, for control without flooding, tap water flooding, and SSW flooding.
Growth data. At the end of the experiment (2 weeks after flooding treatment), visual foliar salt damage of every plant (leaf edge burn, necrosis, or discoloration) was rated on a score of 0 to 5, where 0 = dead, 1 = severe (over 90%), 2 = moderate (50% to 90%), 3 = slight (<50%), 4 = good quality with minimal foliar damage, and 5 = excellent with no visible foliar damage. Plant height was recorded from the pot rim to the top growth point, or leaf apex of the longest leaf. The shoots of all plants were severed at the substrate surface, and fresh weight was recorded immediately. Leaf area of all plants was determined using LI-3100C area meter (LI-COR Ò Biosciences, Lincoln, NE). Shoot DW was determined after shoots were ovendried at 65°C to constant weight.
Gas exchange and SPAD reading. Gas exchange and relative chlorophyll content were measured for broccoli 'Packman' hybrid, eggplant 'Amadeo' hydrid, kale 'Winterbor' hybrid, spinach 'Palco' hybrid, and tomato 'Mega Bite' hybrid. Gas exchange and relative chlorophyll content were not measured for other species because the plants were dead or almost dead by the end of the experiment. Leaf net photosynthesis (P n ), transpiration (E), and g S of five plants per species per treatment were measured 1 d before growth data were taken using a CIRAS-2 portable photosynthesis system (PP Systems, Amesbury, MA) with an automatic universal PLC6 broad leaf cuvette. Fully expanded healthy leaves were chosen for measurements. The environmental conditions in the cuvette were set at leaf temperature of 25°C, photosynthetic photon flux (PPF) of 1000 mmol · m -2 · s -1 , and CO 2 concentration of 375 mmol · mol -1 . Data were recorded when the environmental conditions and gas exchange parameters in the cuvette became stable. These measurements were taken on a sunny day between 10:00 AM and 2:00 PM, and the plants were well watered to avoid water stress.
Leaf greenness or relative chlorophyll content of five plants per species per treatment was measured using a handheld SPAD chlorophyll meter (Minolta Camera Co., Osaka, Japan) 1 d before harvest. For each plant, five healthy and fully expanded leaves were chosen for measuring the relative chlorophyll content (SPAD) readings.
Ion analysis. Five leaf samples per treatment per species were randomly selected for mineral analysis. Plants in the control treatment and SSW flooding treatment were chosen for mineral analysis. Dried tissue samples were ground to pass a 40-mesh screen with a stainless Wiley mill (Thomas Scientific, Swedesboro, NJ). Plant tissues were digested using environmental protection agency method 3051 with 1 mL nitric acid and 4 mL hydrogen peroxide using a microwave acceleration reaction system (CEM Corporation; Mathews, NC) for determining alkaline earth metals (Na, K, Ca). The plant tissues were extracted with 2% acetic acid (EM Science, Gibbstown, NJ) for determining anions (Cl) using methods described by Gavlak et al. (1994). Na, K, and Ca in the digested samples were analyzed by inductively coupled plasma-optical emission spectrometry (Perkin-Elmer Optima 4300 DV; Perkin-Elmer, Shelton, CT). Cl was determined by M926 Chloride Analyser (Cole Parmer Instrument Company, Vernon Hills, IL).
Experimental design and statistical analysis. The experiment followed a splitplot design with flood treatment as the main plot and species as subplot with 12 replications. All data were analyzed as a two-way analysis of variance (ANOVA) using PROC GLM. Because all growth, gas exchange, and mineral element data of plants in the control treatment were not significantly different from those of plants flooded with tap water, they were pooled for further analysis. For each species, Student's t tests between treatments were conducted within species. Relative height for each plant in the SSW treatment was calculated as follows: Relative heightð%Þ = Height in SSW treatment Averaged height in control · 100% Similarly, relative percent for leaf count, leaf area, fresh weight, DW, and gas exchange, SPAD were calculated. Relative reduction values were also used for ANOVA analysis. Mean separation among species were conducted using Tukey's honest significant difference. All statistical analyses were performed using SAS (Version 9.1.3; SAS Institute Inc., Cary, NC).

Results and Discussion
Plant growth. As mentioned earlier, data from the tap water flooding control and the control without flooding were pooled in data analysis because no statistical differences in growth or physiological parameters were found between these two control groups. In other words, the 24-h flooding with tap water did not have a negative impact on the growth of vegetables in the subsequent 2 weeks. Therefore, results of SSW treatment were compared with those of the pooled control.
There were interactions between treatment and vegetable type for plant height, leaf count, leaf area, fresh weight, DW, and visual score (P < 0.0001). Chinese greens and cucumber flooded with SSW died at the end of experiment or 2 weeks after flooding. Therefore, their growth data were not collected. Visual scores of all plants flooded with SSW were significantly lower than those in the control treatment (Table 1). Broccoli, kale, and tomato plants flooded with SSW had minimal foliar damage with visual score of 4.8, 4.6, and 4.0, respectively. Eggplant and spinach plants had slight foliar damage with visual scores of 3.9 and 3.5, respectively. Radish and chinese cabbage plants had moderate foliar damage with visual score of 2.2 and 1.8, respectively, whereas 'Red Crunchy' radish exhibited over 90% foliar damage with visual score of 0.6.
Plants flooded with SSW were shorter than those in the control treatment (Table  2). Compared with the control plants, the height of chinese cabbage and kale plants flooded with SSW was reduced by 63.4% and 55.7%, respectively, whereas that of eggplant, radish, spinach, and tomato plants decreased by 26.8% to 37.7%. All vegetables except spinach flooded with SSW had reduced number of leaves than those in the control treatment. The number of leaves in 'Red Crunchy' radish and chinese cabbage plants were reduced by 77.0% and 59.2%, respectively. The relative reductions in number of leaves for eggplant, spinach, and tomato plants flooded with SSW were 16.5% to 18.4%, whereas those of broccoli, kale, and radish were 45.0% to 46.8%. Plants flooded with SSW had smaller leaf area than those in the control treatment (Table 2). Compared with plants in the control treatment, leaf area of chinese cabbage plants reduced the most (88.4%), whereas that of spinach plants decreased the least (46.7%). Other vegetables had 60.7% to 81.7% smaller leaf area than those in the control treatment. Foliar damage and reduced leaf number and area are undesirable for the production and marketability of leafy vegetables such as chinese cabbage, kale, and spinach. The reduction in leaf number and area would reduce the assimilation of carbohydrates, resulting in poorer quality of vegetables.
Salinity and waterlogging negatively impact the productivity of many agricultural crops (Visser et al., 2003). Plants flooded with SSW produced less fresh and DW compared with those in the control (Table  3). All tested vegetables had 40.5% to 87.2% loss in fresh weight and 48.3% to 77.7% loss in DW. Chinese greens and cucumber plants died when they were flooded with SSW. Chinese cabbage had a loss of 87.2% in fresh weight and 72.9% in DW. These results indicate that chinese cabbage, chinese greens, and cucumber are very sensitive to SSW flooding. In a previous report, chinese cabbage was placed in the moderately salt sensitive category based on the fact that the yield of mature plants was reduced about 10% per dS · m -1 (Maas, 1986). The different growth stages of chinese cabbage plants may attribute to the discrepancy as plant salt tolerance is dependent on growth stages (Akinci et al., 2004;Chartzoulakis and Klapaki, 2000). Spinach, eggplant, and tomato had the least reduction in fresh weight (40.5% to 59.6%) and DW (48.3% to 60.9%), suggesting they were more tolerant than other tested vegetables to SSW flooding. In previous reports, eggplant and tomato were considered to be sensitive to moderately sensitive vegetables with 50% yield loss of eggplant at 8.5 dS · m -1 soil salinity (Savvas and Lenz, 1996;Shalhevet et al., 1983) and 50% yield loss of tomato at salinity level of 5.0 dS · m -1 (Ciobanu and Sumalan, 2009). For fruit crops like eggplant, salt tolerance in vegetative and reproductive stages could differ significantly. € Unl€ ukara et al. (2010) reported that threshold salinity levels were 1.5 and 6.7 dS m -1 for fruit and vegetative growth, indicating that fruit yield is more sensitive to salinity than vegetative growth in eggplant. Spinach is a moderately salt sensitive leaf vegetable with a tolerance threshold EC of 2.0 dS · m -1 (Shannon and Grieve, 1999). The fresh weight and DW of broccoli, kale, radish, and 'Red Crunchy' radish were decreased by 68.2% to 81.5% and 65.7% to 69.4%, respectively. These data indicated that they were moderately tolerant to SSW flooding among tested vegetables. Radish is a salt sensitive crop. Root yield of radish declined 13% per dS · m -1 when salinity exceeded a threshold of 1.3 dS · m -1 (Shannon and Grieve, 1999). Earlier studies indicated that broccoli is a moderately salt sensitive crop with a calculated threshold EC of the saturated paste of 2.8 dS · m -1 (Bernstein et al., 1974;Shannon and Grieve, 1999). However, L opez-Berenguer et al. (2008) observed that broccoli was moderately tolerant to salinity. The discrepancy is probably due to the different criteria of classification.
Gas exchange and SPAD. Interactions between treatment and type of vegetables on P n , E, g S , and SPAD were significant, indicating different responses to SSW flooding among types of vegetables (P < 0.001). Flooding with SSW significantly decreased P n , E, and g S of broccoli, kale, spinach, and tomato plants, but not eggplant (Table 4). The P n values of broccoli, kale, spinach, and tomato plants flooded with SSW were reduced by 42.8%, 42.5%, 67.3%, and 45.6% than the control, respectively. The transpiration rates of broccoli, kale, spinach, and tomato plants flooded with SSW were Table 2. Effect of flooding with simulated seawater (SSW) on the growth of 10 vegetables. Height, leaf count, and leaf area were recorded at the end of experiment.
Relative reduction (%) in height, leaf count, and leaf area were calculated as percent of control. .9 a 160.0 b 60.7 BC z For each species, means with same lowercase letters are not significantly different between treatments by Students's t test at P < 0.05. y Means with same uppercase letters within column are not significantly different among vegetables by Tukey's honest significant difference test at P < 0.05. x Data were not collected due to plant death. Table 3. Effect of flooding with simulated seawater (SSW) on the growth of 10 vegetables. Fresh weight (g) and dry weight (g) were recorded at the end of experiment. Relative reduction (%) in fresh weight and dry weight were calculated as percent of control. 25.5 a 9.6 b 59.6 CD 2.2 a 0.9 b 55.0 BC z For each species, means with same lowercase letters are not significantly different between treatments by Students's t test at P < 0.05. y Means with same uppercase letters within column are not significantly different among vegetables by Tukey's honest significant difference test at P < 0.05. x Data were not collected due to plant death. decreased by 47.1%, 35.2%, 65.5%, and 40.3%, respectively, compared with the control. The g S was reduced for broccoli, kale, spinach, and tomato plants flooded with SSW by 81.6%, 51.4%, 76.8%, and 58.1%, respectively, compared with those in the control treatment. Flooding with SSW considerably affected the SPAD values of broccoli and spinach plants, but not eggplant, kale, tomato plants. Broccoli and spinach plants that were flooded with SSW had SPAD readings of 14.0% and 19.4% lesser than those in the control. Although previous studies by other researchers did not report the impact of salinity on these vegetables, gas exchange rates are reduced by salinity stress in other vegetable and agronomic crops (Niu et al., 2010;Sun et al., 2013).

Species
Ion analysis. Leaf concentrations of Na, Cl, K, and Ca were significantly different among the types of vegetables and between SSW flooding and control treatments, and the interactive effects were also significant (Table 5). SSW flooding significantly increased leaf Na and Cl concentration of all tested vegetables (Table 3). Leaf Na and Cl concentration of all plants flooded with SSW increased by 253% to 769% and 260% to 583% compared with those in the control treatment, respectively. Leaf Na concentration of spinach and tomato plants flooded with SSW increased the most with up to nine times higher than those in the control treatment. They also had the least loss of fresh weight (47% to 63%) and DW (50% to 58%). However, leaf Na concentration of broccoli, radish, and 'Red Crunchy' radish plants that were flooded with SSW increased the least with only about three times higher than those in the control treatment. Leaf Cl concentration of broccoli, spinach, and tomato plants flooded with SSW increased the most up to seven times higher than those in the control treatment, whereas that of chinese cabbage and radish increased the least by only four times higher than those in the control treatment.
Na or Cl exclusion and tolerance of tissue to accumulated Na or Cl are two mechanisms of plant adaptation to salinity (Munns and Tester, 2008). However, the mechanism to exclude salts from shoots will break down and the roots become ''leaky'' to salts under flooded condition (Qureshi and Barrett-Lennard, 1998). In this study, Na and Cl ions accumulated rapidly in the leaves of 10 vegetables after they were flooded with SSW for 24 h. The leaf Na and Cl concentrations are significantly higher than those reported previously in ornamental chili peppers irrigated with salt solution of EC of 4.1 and 8.1 dS · m -1 (Niu et al., 2012). Most plants reported previously accumulated much less Na than Cl (Niu et al., 2010(Niu et al., , 2012Qureshi and Barrett-Lennard, 1998). However, in our study, less Na accumulated than Cl in the leaf tissue of all analyzed vegetables. SSW flooding might inhibit the capability of roots to screen out salt elements (Qureshi and Barrett-Lennard, 1998). The magnitude of increase in the leaf concentrations of Na and Cl varied with the types of vegetables. Leaf Na and Cl concentration of spinach and tomato plants increased the most when they were flooded with SSW. Tolerance to high Na and Cl, thus, attributed to the salt tolerance of spinach and tomato plants.
Salinity can directly affect nutrient uptake, such as Na reducing K uptake (Akinci et al., 2004;Grattan and Grieve, 1999). In our study, leaf K concentrations of broccoli, chinese cabbage, eggplant, kale, spinach, and tomato decreased significantly when they were flooded with SSW (Table 5). Compared with plants in the control treatment, leaf K concentration in broccoli, chinese cabbage, eggplant, kale, spinach, and tomato decreased by 22.5%, 19.7%, 31.7%, 31.1%, 24.7%, and 43.8%, respectively. The leaf K concentrations in radish and 'Red Crunchy' radish were statistically similar between treatments. Potassium plays a critical role in the turgor pressure-driven solute transport in the xylem and water balance of plants (Marschner, 1995). It is essential for plants to maintain adequate K levels to survive saline conditions. All these results demonstrated that K might be preferentially acquired and transported against a strong Na concentration gradient (Grattan and Grieve, 1999).
Salinity dominated by Na salts also reduces Ca availability, transport, and mobility to growing regions of the plant (Grattan and Grieve, 1999). Leaf Ca concentrations of broccoli, kale, radish, and 'Red Crunchy' radish decreased by 33.6%, 30.2%, 59.8%, and 26.0%, respectively, when they were flooded with SSW. This might be caused by depressed uptake of Ca from the substrate due to ion interactions, precipitation, and increases in ionic strength (Grattan and Grieve, 1999). The leaf Ca concentrations in other tested vegetables were statistically similar between treatments. Calcium plays an important role in preserving plant membrane integrity, stabilizing cell wall structures, and regulating cell wall enzyme activities (Marschner, 1995;Rengel, 1992). The decreased Ca availability induced by salinity would lead to severe calcium-deficiency disorders of economically important crops and further increase economic losses of vegetable production.
In conclusion, spinach, eggplant, and tomato were more tolerant to SSW flooding Table 4. Effect of flooding with simulated seawater (SSW) on the leaf net photosynthesis (P n ), transpiration (E), stomatal conductance (g S ), and relative chlorophyll content (SPAD) of five vegetables. Relative reduction (%) in P n , E, g S , SPAD were calculated as percent of control. Chinese cabbage, chinese greens, cucumber, radish, and 'Red Crunchy' radish plants were not measured due to plant death or unhealthy. 2 AB z For each species, means with same lowercase letters are not significantly different between treatments by Students's t test at P < 0.05. y Means with same uppercase letters within column are not significantly different among vegetables by Tukey's honest significant difference test at P < 0.05.  114.6 a z For each species, means followed with same lowercase letters within each column are not significantly different between treatments by Students's t test at P < 0.05. than other tested vegetables, whereas chinese cabbage, chinese greens, and cucumber were the least tolerant. Simulated seawater flooding significantly increased leaf Na and Cl concentration of all tested vegetables, but decreased leaf K concentrations in broccoli, chinese cabbage, eggplant, kale, spinach, and tomato and Ca concentrations in broccoli, kale, radish, and 'Red Crunchy' radish.
In coastal areas with intermittent seawater intrusion, crop production should consider using salt-tolerant vegetables such as spinach, eggplant, and tomato to minimize damage to the vegetables.