Salinity and Alkaline pH in Irrigation Water Affect Marigold Plants: II. Mineral Ion Relations

Authors:
Luis A. Valdez-Aguilar U.S. Department of Agriculture, Agricultural Research Service, U.S. Salinity Laboratory, 450 West Big Springs Road, Riverside, CA 92507

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Catherine M. Grieve U.S. Department of Agriculture, Agricultural Research Service, U.S. Salinity Laboratory, 450 West Big Springs Road, Riverside, CA 92507

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James Poss U.S. Department of Agriculture, Agricultural Research Service, U.S. Salinity Laboratory, 450 West Big Springs Road, Riverside, CA 92507

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Donald A. Layfield U.S. Department of Agriculture, Agricultural Research Service, U.S. Salinity Laboratory, 450 West Big Springs Road, Riverside, CA 92507

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Abstract

Scarcity of good-quality water for landscape irrigation is a major concern in arid and semiarid regions as a result of the competition with the urban population. Competing claims from urban, agricultural, environmental, and industrial groups leaves less water or water of lower quality for use in landscape maintenance. Although degraded waters, high in both salinity and alkaline pH, may challenge plant establishment and growth, these waters must be considered as valuable alternatives to the use of fresh water resources for landscape sites. The objective of the present study was to determine the effect of irrigation with saline water, with and without pH control, on the mineral ion relations of three marigold cultivars: Flagstaff, Yellow Climax, and French Vanilla. Treatments were five electrical conductivities of irrigation water (ECw): 2, 4, 6, 8, and 10 dS·m−1, and two pH levels: 6.4 and 7.8. Plants of ‘French Vanilla’ and flowering stems of ‘Flagstaff’ and ‘Yellow Climax’ were harvested at flower maturity. Leaves of the taller cultivars, Flagstaff and Yellow Climax, were collected separately from the main axis and from the lateral stems, whereas in ‘French Vanilla’, leaves were combined. Total sulfur, total phosphorus, Ca2+, Mg2+, Na+, K+, Cl, Fe2+, Zn2+, Cu2+, and Mn2+ concentrations in leaf and stem tissues were determined. The three marigold cultivars were strong Ca2+-accumulators and this response was more evident at the lower pH level. However, leaf Ca2+ tended to decrease as salinity increased despite a threefold increase in substrate Ca2+. Leaf Mg2+ increased as salinity increased and main stem leaves of the taller cultivars accumulated more Mg2+ than leaves on the lateral branches. The reverse was true for leaf K+; leaves on the lateral branches were stronger K+-accumulators than those on the main stem. Potassium concentrations in leaves of marigold irrigated with waters at pH 6.4 tended to decrease as ECw increased. Marigold seems to possess an efficient Na+ exclusion mechanism, which restricts Na+ accumulation in the leaves. Patterns of total phosphorus accumulation in leaf tissues were not consistent over the range of ECw treatments. Among the micronutrients, Fe2+ and Mn2+ tended to be partitioned to the younger rather than the older leaves. The decrease in marigold growth was associated with nutrient ion imbalance as demonstrated by the reduction in K+ concentration and the increase in Mg2+ and Cl in leaf tissue. Despite the reduction in growth, the aesthetic value of the cultivars was not detrimentally affected by application of saline waters with ECw values as high as 8 dS·m−1.

Water availability and quality are issues of major concern in reference to irrigation of urban landscapes resulting from the competition with a rapidly growing population that requires vast volumes of good-quality water (Kjelgren et al., 2000). Landscape irrigation accounts for 10% of total volume in the summer rainfall region of the United States, whereas in the arid western regions, irrigation of landscape accounts for nearly 50% (Kjelgren et al., 2000). One strategy for conservation of fresh water resources is the use of low-quality water for landscape irrigation. These degraded water resources may be saline and/or alkaline and also may contain specific ions that are toxic for plant growth (Reboll et al., 2000). Salinity, caused by Na+, Ca2+, Mg2+, Cl, and SO42−, together with alkalinity, resulting from HCO3 and CO32−, have direct toxic effects on plant physiology and/or affect plant growth through osmotic effects and loss of nutrient availability.

Marigold, one of the most important ornamental plants, is valued in landscape settings and also as cut flowers (Nau, 1997). In a companion paper (Valdez-Aguilar et al., 2009b), we described the effect of increasing irrigation water salinity and pH on growth and aesthetic value of three cultivars of marigold, ‘French Vanilla’ (Tagetes patula) and ‘Flagstaff’ and ‘Yellow Climax’ (both T. erecta). The results showed that marigold is sensitive to electrical conductivity of irrigation water (ECw) higher than 4 dS·m−1 and that growth reduction was greater when pH of irrigation water was 7.8 compared with 6.4. However, despite the growth reduction resulting from increasing salinity, plants were still of acceptable quality for landscape use even when ECw was as high as 8 dS·m−1. High irrigation water pH, however, caused a significant loss of aesthetic value. The objective of the present study was to investigate the relationship between the growth reduction detected in marigold as an effect of irrigation with saline water and high pH and ion accumulation to understand potential ion imbalances.

Materials and Methods

The experiment was conducted in a greenhouse at the U.S. Salinity Laboratory in Riverside, CA. Growth conditions and additional experimental details are provided in the companion paper (Valdez-Aguilar et al., 2009b). Three marigold cultivars, French Vanilla, Yellow Climax, and Flagstaff, were used for the present study. Treatments consisted of five ECw simulating the ionic composition of Colorado River water (Table 1) and were based on predictions of what long-term compositions would be on further concentration resulting from plant water extraction and evaporation (Suarez and Simunek, 1997). The ECw treatments were 2, 4, 6, 8, and 10 dS·m−1 and two pH levels: 6.4 (± 0.1) and 7.8 (± 0.2). Irrigation water was acidified by adding HNO3 until the target nitrogen concentration was reached and thereafter with H2SO4. Nutrient concentration of the irrigation solutions was maintained constant and was prepared as described in a companion paper (Valdez-Aguilar et al., 2009b). The higher pH was the normal pH of Riverside tap water. At harvest, average alkalinity was 0.47 ± 0.05 and 1.82 ± 0.09 meq·L−1 (mean ± se, n = 5) for solutions with pH 6.4 and 7.8, respectively.

Table 1.

Composition of salinizing salts in solutions used to irrigate marigold grown in greenhouse sand tanks.

Table 1.

Plants were irrigated twice daily for sufficient duration to completely saturate the sand. Solutions then drained to reservoirs below the tanks for reuse in the next irrigation. Calculations, accounting for maximum evapotranspiration, soil waterholding capacity, and intervals between irrigations, indicate that the salinity of the irrigation water (ECw) was essentially equivalent to the salinity of the sand water (ECsw). Based on a study of the soil–water dynamics in this river sand (Wang, 2002), ECsw is ≈2.2 times the EC of the saturated soil extract (ECe), the salinity parameter used to characterize salt tolerance in most studies (Ayers and Westcot, 1985). Our salinity treatments may be estimated as 0.91, 1.82. 2.73, 3.64, and 4.55 dS·m−1. Thus, the threshold ECw at which marigold cultivars exhibited acceptable growth, 8 dS·m−1, would be equivalent to an ECe of 3.64 dS·m−1 (Valdez-Aguilar et al., 2009b).

Plants were harvested when most of the flower heads were fully mature. Leaf samples from the main shoot (LMS) and from the lateral shoots (LLS) of ‘Flagstaff’ and ‘Yellow Climax’ were separated from the stems, whereas samples of ‘French Vanilla’ included both leaves from the main shoot plus from the lateral shoots. Leaves and stems were washed twice in deionized water, blotted dry, placed in paper bags, and oven-dried at 70 °C for 5 d. Once dried, the plant samples were ground to pass a 20-mesh screen. Total sulfur, total phosphorus, Ca2+, Mg2+, Na+, K+, Fe2+, Zn2+, Cu2+, and Mn2+ were analyzed on nitric-perchloric acid digests of the leaf and the stem tissues by inductively coupled plasma optical emission spectrometry. Chloride was analyzed on nitric–acetic acid extracts by coulometric–amperometric titration. The study was designed as a factorial experiment and set as a completely randomized design. Collected data and linear, quadratic, and cubic trends were analyzed by the analysis of variance procedure using SAS Version 8.2 (SAS Institute, Inc., 2001).

Results and Discussion

Calcium.

Increasing ECw and alkaline pH of irrigation water caused a general decrease in leaf Ca2+ concentration (Fig. 1). In the LLS of ‘Flagstaff’ and ‘Yellow Climax’, Ca2+ concentration was significantly affected by the pH of the irrigation water, but not by the pH × ECw interaction, whereas in the LMS, there was a significant pH × ECw interaction in both cultivars (Tables 2 and 3). The interaction in LMS was the result of the strong effect of pH resulting in higher Ca2+ concentrations when the substrate was acidic and ECw was lower than 6 dS·m−1. Increasing ECw resulted in a significant decrease of Ca2+ in ‘French Vanilla’ (Table 4) and a significant interaction resulting from the lack of response as ECw increased up to 6 dS·m−1 when pH was 6.4; Ca2+ decreased in a quadratic fashion in this cultivar when pH was 7.8 (Table 4; Fig. 1).

Table 2.

Significance of trends and the effect of electrical conductivity of irrigation water (ECw), pH, and pH × ECw interaction on ion concentration in leaves from the main shoot (LMS) and lateral shoots (LLS) of marigold Tagetes erecta ‘Flagstaff’.

Table 2.
Table 3.

Significance of trends and the effect of electrical conductivity of irrigation water (ECw), pH, and pH × ECw interaction on ion concentration in leaves from the main shoot (LMS) and lateral shoots (LLS) of marigold Tagetes erecta ‘Yellow Climax’.

Table 3.
Table 4.

Significance of trends and the effect of electrical conductivity of irrigation water (ECw), pH, and pH × ECw interaction on ion concentration in leaves of marigold Tagetes patula ‘French Vanilla’.

Table 4.
Fig. 1.
Fig. 1.

Calcium and magnesium concentration in leaves of marigold Tagetes patula ‘French Vanilla’ or in leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. For some measurements, se was smaller than the data point. Values are the means of three observations ± se.

Citation: HortScience horts 44, 6; 10.21273/HORTSCI.44.6.1726

Main shoot leaves of ‘Flagstaff’ and ‘Yellow Climax’ accumulated higher Ca2+ at pH 6.4 compared with the LLS (Fig. 1). However, Ca2+ concentration was significantly reduced when ECw rose to 8 or 10 dS·m−1. The decrease in Ca2+ uptake may be the result of external ionic interactions with high salinity or the displacement of Ca2+ in the plasma membrane of root cells at high Na+ concentration (Cramer et al., 1985). Reduced plant growth of the three marigold cultivars was observed even at ECw of 4 and 6 dS·m−1, as reported in the companion paper (Valdez-Aguilar et al., 2009b); this response may be related to the osmotic effect of increasing salinity because a decrease in Ca2+ concentration was not detected at these ECw levels. In addition, leaf dry weight (DW) production was significantly correlated with leaf Ca2+ content in all the three marigold cultivars (Table 5), suggesting that leaf Ca2+ accumulation was being regulated by growth.

Table 5.

Regression models for leaf content of Ca2+, K+ (mmol/plant), micronutrients (mg/plant), and leaf dry weight (Y), in grams, in three cultivars of marigold.z

Table 5.

Contrasting results concerning the effect of pH on Ca2+ accumulation have been reported. In the present experiment, Ca2+ concentration decreased only when ECw was 8 dS·m−1 or higher, but in the LLS of ‘Flagstaff’ and ‘Yellow Climax’, Ca2+ concentration was unaffected compared with control plants (Fig. 1). When plants were irrigated with water of alkaline pH, Ca2+ concentration decreased when ECw was 2 to 6 dS·m−1 in ‘Flagstaff’ and ‘Yellow Climax’ (or 4 to 6 dS·m−1 in ‘French Vanilla’); thus, high pH stress induced a lower Ca2+ uptake even at lower salinity. This is in contrast to a report presented by Islam et al. (1980), which indicated increased Ca2+ in shoots of several species when pH was increased up to 8.5. Calcium acquisition may have been suppressed under high salinity as a result of interactions with other ions in the external solution, resulting in lower Ca2+ activity, but the combination of high salinity and high pH may decrease Ca2+ activity at a greater extent as a result of the formation of calcium carbonates. When plants were exposed to the combination of alkaline pH and increasing ECw, the concentration of Ca2+ in the younger leaves was not markedly different from that of plants irrigated with water at pH 6.4.

Magnesium.

Magnesium concentration generally increased with increasing ECw in all three marigold cultivars (Fig. 1; Tables 24). In ‘Flagstaff’ and ‘Yellow Climax’, Mg2+ concentration was higher in the LMS than in LLS; however, the magnitude of the difference between leaf positions was larger when ECw was higher than 4 dS·m−1. The combination of pH and ECw treatments resulted in a significant interaction, which is explained by the different Mg2+ concentration resulting from the pH effect when plants were irrigated with nonsaline water (Fig. 1). In plants irrigated with acid water, a quadratic trend best described the increased Mg2+ concentration in response to higher ECw. However, when pH was 7.8, the response was linear for the LMS and cubic for the LLS (Tables 24).

The increase in Mg2+ concentration was probably the result of external Mg2+, increasing in concert with increasing ECw (Table 1). It is well established that Mg2+ competes with Ca2+ (Marschner, 1995) by decreasing the membrane sorption capacity even at a higher extent than Na+ (Yermiyahu et al., 1994). Because the activity of external Ca2+ may have been decreased at high ECw, the competition at membrane level between Ca2+ and Mg2+ might have been lower, leading to an increase in the selectivity of Mg2+ over Ca2+. Carvajal et al. (1999) reported that yield in hydroponically grown tomato was negatively correlated with increasing Mg2+ concentration in the external saline solutions, suggesting that the response was the result of nutrient imbalances because there was a clear Ca2+:Mg2+ interaction. In another study (Carvajal et al., 2000), this nutrient imbalance hypothesis was also supported because growth of tomato plants was partially restored under salinity treatments when the Ca2+:K+:Mg2+ ratio of the external solution was more balanced (10:12:3) than when it was higher in Ca2+ and K+ (4:6:1).

In general, alkaline pH of irrigation water was associated with an increase in Mg2+ concentration. The tendency to accumulate more leaf Mg2+ in plants irrigated with 2 dS·m−1 alkaline water, rather than under slightly acidic conditions, is in agreement with reports by Islam et al. (1980), who observed this response in the shoots of ginger, cassava, tomato, French bean, wheat, and maize. Increased acquisition of Mg2+ may also be related to the decreased competition with Ca2+ resulting from the formation of calcium carbonates under high pH and/or a decrease in the efficiency of the H+ pump at high H+ concentration in the external medium (Marschner, 1995).

Potassium.

In the LMS and LLS of ‘Flagstaff’ and ‘Yellow Climax’ as well as in the leaves of ‘French Vanilla’, concentration of K+ decreased when plants were irrigated with ECw 4 dS·m−1 or higher and acidic pH (Fig. 2; Tables 24). However, higher ECw values did not result in additional reduction in K+ concentration, explaining the cubic trends detected when pH was 6.4. The decrease in internal K+ concentration has been associated with a competition between external K+ and high external Na+ in saline solutions (Grattan and Grieve, 1999). The interaction of alkaline pH and increasing ECw was explained principally by the decrease in tissue K+ concentration when ECw was 2 dS·m−1 but pH increased from 6.4 to 7.8 (Fig. 2). In addition, in plants irrigated with acidic water pH, the effect of increasing ECw on K+ concentration was much higher than when irrigation water had alkaline pH.

Fig. 2.
Fig. 2.

Potassium and sodium concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

Citation: HortScience horts 44, 6; 10.21273/HORTSCI.44.6.1726

Potassium tissue concentration exhibited a negative linear correlation with internal Mg2+ when plants were irrigated with pH 6.4 water. In ‘French Vanilla’, the correlation was significant (r = −0.899***) as well as in the LLS of ‘Flagstaff’ (r = −0.876***) and ‘Yellow Climax’ (r = −0.921***) and in the LMS of ‘Flagstaff’ (r = −0.901***) and ‘Yellow Climax’ (r = −0.935***). However, when the solution pH was 7.8, the correlation was significant only for ‘Yellow Climax’ in the LLS and LMS (r = −0.650** and r = −0.568*, respectively). The negative correlation suggests an antagonism between K+ and Mg2+ as reported by Ding et al. (2006), Fageria (2001), Marschner (1995), and Troyanos et al. (2000). Results reported by Grunes et al. (1992) and Huang and Grunes (1992) suggest that translocation of Mg2+ is negatively correlated with a high root K+ concentration. Potassium content in LLS and LMS was positively correlated with leaf DW in all the three marigold cultivars (Table 5), indicating that the reduced growth may be an effect of impaired enzymatic activity or water relations in K+-deficient plants irrigated with high ECw water.

Potassium concentrations in LMS were below the deficiency level for most of the cultivated plants. At harvest time, the LMS in ‘Flagstaff’ and ‘Yellow Climax’ developed a marginal chlorosis when plants were irrigated with acidic water and increased ECw. According to Mills and Benton Jones (1991), a survey average K+ concentration in mature T. erecta plants grown in 36-cell packs was reported to be 560 mmol·kg−1 (2.19%), whereas in T. patula, it was between 714 and 737 mmol·kg−1 (2.79% to 2.88%). In LMS of ‘Flagstaff’ and ‘Yellow Climax’, K+ concentration was much lower than these levels when irrigated with high ECw (Fig. 2); thus, the marginal chlorosis observed on these leaves may be the result of a deficiency of K+. Compared with the mature leaves of control plants under high pH, K+ concentration was higher when plants were irrigated with 10 dS·m−1 water and yet, no deficiency symptoms were observed; this apparent contradiction may be the result of a concentration effect in K+ attributable to the reduced leaf growth under high ECw. The LLS did not exhibit symptoms of deficiency of K+, probably because K+ was retranslocated from the mature leaves to supply the developing leaves. However, the overall effect on aesthetic value was negligible because the mature leaves were hidden by the leaves of the lateral stems.

Sodium.

Leaf Na+ concentrations were much lower than expected (Fig. 2) because high Na+ concentrations in the nutrient solutions were used (Table 1). Increasing ECw or pH of irrigation water in ‘Flagstaff’ and ‘Yellow Climax’ had a nonsignificant effect on Na+ concentration (Tables 2 and 3); in ‘French Vanilla’, there was a significant but limited effect of water pH (Table 4). In general, Na+ concentrations in marigold were very low as compared with reports for other ornamentals irrigated with water of high salinity. Sodium in leaves of Limonium perezii (Carter et al., 2005a) and Celosia argentea (Carter et al., 2005b), for example, increased from 700 to 1400 mmol·kg−1 and from 200 to 500 mmol·kg−1, respectively, in response to increasing Na+ concentrations in saline irrigation waters. However, in our study, marigold concentration in foliar tissue ranged from 15 to 55 mmol·kg−1, suggesting that marigold possesses a mechanism that effectively restricts Na+ transport to the leaves. Leaf Na+ concentrations in the present experiment are in close agreement with the values reported by Jarecki et al. (2005) with levels of ≈44 to 130 mmol Na+/kg in shoots of marigold ‘Crackerjack’ irrigated with a half-strength Hoagland's solution containing 8.4 meq Na+/L. However, the authors reported root Na+ concentrations of ≈740 mmol·kg−1, indicating that Na+ was sequestered in the root. We also found evidence of limited partitioning of Na+ stem tissues, which was effective until ECw exceeded 6 dS·m−1 (Table 6).

Table 6.

Significance of trends and the effect of electrical conductivity of irrigation water (ECw), pH, and pH × ECw interaction on sodium and chloride concentration in stems of three cultivars of marigold.

Table 6.

Sodium exclusion capacity would explain the absence of correlation between leaf Na+ concentration and plant growth (data not shown), although it is important to consider that the energy the plants must have spent for the exclusion of Na+ may have negatively impacted growth. Our results are also in agreement with those reported by Huang and Cox (1988) who observed a slight (from 195 ppm in the control with ECw 1.3 dS·m−1 to 215 ppm in plants irrigated with ECw 7.9 dS·m−1 water) increase in leaf Na+ concentration of marigold plants cultivated in a peat-based medium and irrigated with increasing concentrations of a NaCl + CaCl2 mixture. Huang and Cox (1988) reported a 7.4 to 20.4 times higher Na+ concentration in the roots than in the shoot of marigold, suggesting a restricted translocation of Na+ under saline conditions.

High K+:Na+ ratios have been considered reliable markers for tolerance to salinity (Juan et al., 2005; Maathuis and Amtmann, 1999). Sodium exclusion in marigold may have increased the tolerance to salinity because K+ was not significantly affected when ECw increased from 4 to 10 dS·m−1 (Fig. 2); thus, a lower Na+ concentration combined with a less affected K+ may have resulted in a higher K+:Na+ ratio. In ‘Flagstaff’, the K+:Na+ ratio was 27.4 in the LLS of plants irrigated with water of ECw 2 dS·m−1, but increasing salinity to 4 dS·m−1 caused a decrease to 11.8. Nonetheless, the K+:Na+ ratio was not further decreased as salinity of irrigation water rose to 10 dS·m−1 and varied between 11.8 and 14.9 (data not shown), a considerably higher value than that reported for Matthiola incana (Grieve et al., 2006).

Phosphorus and sulfur.

EC and pH of irrigation water significantly affected total phosphorus (P) concentration in the three marigold cultivars (Tables 24), whereas the pH × ECw interaction was significant only for ‘French Vanilla’ (Table 4). Leaf total P of plants irrigated with acid water increased in a cubic trend when ECw increased up to 6 dS·m−1, but when ECw was higher than 8 dS·m−1, total P concentration decreased to the level of the control plants (Fig. 3). Total sulfur (S) exhibited similar responses as total P.

Fig. 3.
Fig. 3.

Total phosphorus and total sulfur concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

Citation: HortScience horts 44, 6; 10.21273/HORTSCI.44.6.1726

It has been proposed that P concentration increases in salinity studies performed in sand or solution cultures as a result of the higher P supply (Grattan and Grieve, 1999); however, our results contrast with other reports in which plants were grown under comparable conditions. Carter et al. (2005a, 2005b) reported a negative correlation between total P concentration and total S and Cl concentration when Limonium perezii and Celosia argentea plants were irrigated with water of similar composition to the one used in our study. Although Hu and Schmidhalter (2005) reported that competition between Cl and H2PO4 is unlikely, several reports indicate that Cl reduces P (Papadopoulos and Rendig, 1983) and SO42− uptake (Papadopoulos, 1987; Papadopoulos et al., 1985). Negative correlations between total P and total S and total P and Cl were also reported in Ranunculus asiaticus (Valdez-Aguilar et al., 2009a), suggesting some competition between P and S or Cl. In contrast, in the present study, a positive relationship between total P and total S concentration was found in all the three marigold cultivars when irrigation water pH was 6.4 (Fig. 3), but not with Cl (Fig. 4). The correlation coefficients between total P and total S concentration in ‘Flagstaff’ and ‘Yellow Climax’ were significant for the LMS (r = +0.621* and r = +0.577*, respectively) and for the LLS (r = +0.593* and r = +0.683**, respectively) and for ‘French Vanilla’ (r = +0.661**).

Fig. 4.
Fig. 4.

Chloride and zinc concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

Citation: HortScience horts 44, 6; 10.21273/HORTSCI.44.6.1726

Increasing the pH of irrigation water to 7.8 significantly increased total P concentration in the three marigold cultivars (Tables 24) compared with plants irrigated with water of pH 6.4 (Fig. 3). The higher pH treatment was responsible for an increase in total P in the LLS of ‘Flagstaff’ and ‘Yellow Climax’ of 112% and 55%, respectively, whereas in the LMS, the increase was 223% and 128%, respectively. In ‘French Vanilla’, the increase in total P was 50%. Alkaline pH combined with increasing ECw appears to invoke a synergistic effect because total P increased at a higher rate (Fig. 3). To a certain extent, this effect was unexpected because under alkaline conditions, the formation of calcium phosphates is higher, reducing availability of soluble P and reducing plant uptake and accumulation. However, total P accumulation [found by calculating total P content according to leaf dry weight (data not shown)] was not altered by pH, suggesting that pH of water increased total P concentration as salinity decreased plant growth. High alkalinity, however, decreased plant DW accumulation. Salinity also appears to affect total P concentration in the foliage through a decrease in plant growth. Total P in ‘Yellow Climax’ varied between 0.97 and 1.60 mg/plant and 1.06 and 1.66 mg/plant when irrigation water pH was 6.4 and 7.8, respectively.

Chloride.

Irrigation with saline water significantly increased Cl concentration in the three marigold cultivars (Tables 24; Fig. 4). The increase followed a linear trend and was significant when ECw was 4 dS·m−1 or higher. The linear trend suggests that Cl uptake was a function of external concentration, as also reported by Hajrasuliha (1980) in bean plants. Leaf position had no effect on Cl concentration in individual leaves along the main shoot axis and indicates that the anion is highly mobile. Ben-Gal and Shani (2002) reported similar trends in tomato. Leaf and stem Cl concentrations increased as irrigation water salinity increased. In our study, internal Cl and Mg2+ concentration were correlated; in general, increasing Mg2+ was positively correlated with increasing Cl, which probably is a mechanism for the maintenance of charge balance. In ‘Flagstaff’ irrigated with water of pH 6.4, in the LLS, the correlation was r = +0.817***, whereas in the LMS, it was r = +0.730**. In the LLS of ‘Yellow Climax’, the correlation was r = +0.894***, whereas in the LMS, the correlation was r = +0.773***. In ‘French Vanilla’, the correlation was r = +0.653**. Similar correlations were observed when the pH of the irrigation water was 7.8.

Healthy leaves of pistachio trees contain 112 to 225 mmol Cl/kg, whereas leaves containing 535 mmol·kg−1 exhibited severe marginal leaf scorching (Ashworth et al., 1985). Marigold exhibited a remarkable capacity to assimilate Cl, reaching concentrations close to 1500 mmol·kg−1. Because even the younger leaves contained high Cl levels, it is unlikely that Cl toxicity was responsible for the marginal chlorosis of the mature leaves mentioned previously. Salt-stressed tomato reportedly contained Cl concentrations in the range of 10 to 15 mmol·kg−1 in leaves, 8 to 10 mmol·kg−1 in stems, and 4 to 5 mmol·kg−1 in fruits (Ben-Gal and Shani, 2002). However, Pantalone et al. (1997) reported in susceptible soybean cultivars, leaf chlorosis was associated with Cl concentrations between 1507 and 2375 mmol·kg−1, whereas in tolerant cultivars, Cl ranged between 96 and 375 mmol·kg−1, probably as a result of an effective Cl exclusion mechanism. The Cl exclusion mechanism was not detected in marigold as demonstrated by the concentrations in the stems (Table 6), which were comparable or even lower than those of the leaves.

Micronutrients.

The effect of ECw and pH on the internal Zn2+ concentration in marigold ‘Flagstaff’ (Table 2) and ‘French Vanilla’ (Table 4) was significant, whereas in ‘Yellow Climax’, Zn2+ accumulation was only affected by solution pH (Table 3). In general, the response of leaf Zn2+ to increasing ECw was not consistent (Fig. 4); however, Zn2+ significantly decreased at a higher pH of irrigation water. Alkalinity is considered the major Zn2+ deficiency-causing factor in plants (Yang et al., 1993). Copper concentration was significantly affected by salinity of irrigation water in ‘Flagstaff’ and ‘Yellow Climax’ and by pH in all three marigold cultivars (Tables 24). As indicated for Zn2+, Cu2+ concentration in response to increasing ECw exhibited a nonconsistent pattern (Fig. 5); in general, the higher pH caused a significant decrease in Cu2+ content in LLS of ‘Yellow Climax’ and ‘French Vanilla’. The pH effect was also associated with a decrease in internal Cu2+ concentration in the LLS of the three marigold cultivars. Internal Mn2+ concentration tended to decrease with increasing ECw in plants of ‘Flagstaff’ and ‘Yellow Climax’ when pH was 6.4, but this response was only significant in ‘Yellow Climax’ (Tables 24). As indicated for Cu2+ and Zn2+, alkaline pH significantly reduced leaf Mn2+ concentration (Fig. 5). High irrigation water pH has been associated with decreased Fe2+ uptake and leaf chlorosis (Römheld, 2000). However, in the present study, internal Fe2+ concentration did not show a consistent trend with increasing salinity or pH of irrigation water (Fig. 6), perhaps as a result of the chelated Fe (Fe-DTPA) used in our nutrient solution.

Fig. 5.
Fig. 5.

Copper and manganese concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

Citation: HortScience horts 44, 6; 10.21273/HORTSCI.44.6.1726

Fig. 6.
Fig. 6.

Iron concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se and relationship between K+, Mg2+, and Cl concentration in the leaves of marigold ‘French Vanilla’ (•) or the leaves from the lateral shoots of ‘Flagstaff’ (⊙) and ‘Yellow Climax’ (▾) and the shoot dry weight produced at experiment termination.

Citation: HortScience horts 44, 6; 10.21273/HORTSCI.44.6.1726

In summary, increasing salinity appears to have little effect on micronutrient nutrition in marigold, a finding in agreement with reports by Eom et al. (2007) who found that NaCl salinity applied to six groundcover species had no effect on Fe2+ and Zn2+ accumulation, increased Mn2+ in Alchemilla mollis and Solidago cutleri, and decreased Cu2+ in Nepeta ×faassenii. However, in our study, a higher pH in irrigation water caused decreased leaf Zn2+, Cu2+, and Mn2+ concentrations, which ranged between 50% to 223%, 22% to 445%, and 46% to 67%, respectively. However, when micronutrient foliar content was calculated, a significant positive regression with leaf DW was detected (Table 5). No visual symptoms of micronutrient deficiencies were observed. Therefore, the positive correlation may be related to the lower growth rate resulting from the osmotic effects of salinity.

Plant growth, aesthetic value, and nutrient status.

The effect of increasing ECw and pH on plant shoot DW is reported in a companion paper (Valdez-Aguilar et al., 2009b). Internal K+ concentration and shoot DW production were positively correlated (Fig. 6), suggesting that the reduction in K+ resulting from higher salinity was associated with lower DW. On the other hand, a negative correlation between Mg2+ and shoot DW (Fig. 6) indicates that the increase in internal Mg2+ was associated with growth reduction. Similarly, shoot DW exhibited a quadratic decrease with internal Cl concentration (Fig. 6), corroborating that marigold, in common with other crops, is very sensitive to high Cl (Grattan and Grieve, 1999). Estañ et al. (2005) reported a negative correlation between leaf Cl concentration and yield of tomato plants grown at high NaCl concentrations, indicating that the most productive plants were those with the ability to regulate the transport of toxic ions. These correlations were not detected in marigold plants irrigated with water with pH 7.8. Martin and Koebner (1995) indicate that in bean plants grown under high salinity, Cl exerted a higher toxicity than Na+, reducing plant growth; this was explained by the increased influx of Cl resulting from the perturbation of Ca2+ homeostasis in the plasmalemma. The authors also reported that Mg2+ was phytotoxic under such conditions.

Although plant growth was significantly reduced as salinity increased in waters with pH 6.4, the aesthetic quality of these marigold cultivars was not compromised, making them valuable for landscape sites where degraded waters are used for irrigation. The overall health of the marigold species was undoubtedly the result of favorable ion balances and interactions within the plant, including the nonsignificant effect on Ca2+ in the LLS of ‘Flagstaff’ and ‘Yellow Climax’ (Fig. 1), the attenuation of Mg2+ accumulation (Fig. 1) or decrease in K+ (Fig. 2) when ECw was 4 dS·m−1 or higher, and the effects on total P concentration in response to increasing ECw (Fig. 3), and Na+ exclusion, which resulted in a low leaf Na+:K+ ratio and a high selectivity for K+.

Conclusions

Growth of marigold plants irrigated with water at pH 6.4 significantly decreased as ECw increased; however, the aesthetic value of the plants was not detrimentally affected. As suggested in a companion paper (Valdez-Aguilar et al., 2009b), growth reduction may be associated with the osmotic effects when plants were irrigated with solution of high ECw. The maintenance of a high ornamental value in flowering stems of the salt-stressed marigolds may have been associated with specific mineral ion relations such as the nonsignificant effect on Ca2+ in the LLS of ‘Flagstaff’ and ‘Yellow Climax’, the attenuation of Mg2+ accumulation, the plateau in K+ reduction when ECw was 4 dS·m−1 or higher, and the exclusion of Na+. Considering only the pH effect, it caused a severe reduction in landscape attributes of marigold, which was associated with a significant decrease in K+, Zn2+, and Cu2+ concentration and a significant increase in Mg2+.

Aesthetic factors for evaluating ornamental landscape plants include attractiveness, size, and health. In some cases, growth may be reduced as much as 50% as long as plant appearance remains acceptable. Maximum permissible salinity levels for plants grown in landscape sites are generally based on soil salinity [EC of the saturated soil paste (ECe)]. As a result of the soil–water dynamics of our sand tank system, the ECw of the irrigation waters is ≈2.2 times that of the ECe. The marigold cultivars retained aesthetic value and exhibited acceptable growth when ECw was as high as 8 dS·m−1 (equivalent ECe = 3.64 dS·m−1). Although many environmental and edaphic factors will influence the response of the marigold to salinity, the cultivars are recommended for moderately saline landscape settings.

Literature Cited

  • Ashworth, L.J., Gaona, S.A. & Surber, E. 1985 Nutritional diseases of pistachio trees: Potassium and phosphorus deficiencies and chloride and boron toxicities Phytopathology 75 1084 1091

    • Search Google Scholar
    • Export Citation
  • Ayers, R.S. & Westcot, D.W. 1985 Water quality for agriculture. FAO Irrigation and Drainage Paper 29 Rev. 1 Food and Agriculture Organization of the United Nations Rome, Italy

    • Search Google Scholar
    • Export Citation
  • Ben-Gal, A. & Shani, U. 2002 Yield, transpiration and growth of tomatoes under combined excess boron and salinity stress Plant Soil 247 211 221

  • Carter, C.T., Grieve, C.M. & Poss, J.A. 2005a Salinity effects on emergence, survival, and ion accumulation of Limonium perezii J. Plant Nutr. 28 1243 1257

    • Search Google Scholar
    • Export Citation
  • Carter, C.T., Grieve, C.M., Poss, J.A. & Suarez, D.L. 2005b Production and ion uptake of Celosia argentea irrigated with saline wastewaters Scientia Hort. 106 381 394

    • Search Google Scholar
    • Export Citation
  • Carvajal, M., Cerdá, A. & Martínez, V. 2000 Modification of the response of saline stressed tomato plants by the correction of cation disorders Plant Growth Regulat. 30 37 47

    • Search Google Scholar
    • Export Citation
  • Carvajal, M., Martínez, V. & Cerdá, A. 1999 Influence of magnesium and salinity on tomato plants grown in hydroponic culture J. Plant Nutr. 22 177 190

    • Search Google Scholar
    • Export Citation
  • Cramer, G.R., Läuchli, A. & Polito, V.S. 1985 Displacement of Ca2+ by Na+ from the plasmalemma of root cells Plant Physiol. 79 207 211

  • Ding, Y., Luoi, W. & Xu, G. 2006 Characterization of magnesium nutrition and interaction of magnesium and potassium in rice Ann. Appl. Biol. 149 111 123

    • Search Google Scholar
    • Export Citation
  • Eom, S.H., Setter, T.L., DiTommaso, A. & Weston, L.A. 2007 Differential growth response to salt stress among selected ornamentals J. Plant Nutr. 30 1109 1126

    • Search Google Scholar
    • Export Citation
  • Estañ, M.T., Martínez-Rodriguez, M.M., Perez-Alfocea, F., Flowers, T.J. & Bolarin, M.C. 2005 Grafting raises the salt tolerance of tomato through limiting the transport of sodium and chloride to the shoot J. Expt. Bot. 56 703 712

    • Search Google Scholar
    • Export Citation
  • Fageria, V.D. 2001 Nutrient interactions in crop plants J. Plant Nutr. 24 1269 1290

  • Grattan, S.R. & Grieve, C.M. 1999 Salinity–mineral nutrient relations in horticultural crops Scientia Hort. 78 127 157

  • Grieve, C.M., Poss, J.A. & Amrhein, C. 2006 Response of Matthiola incana to irrigation with saline wastewaters HortScience 41 119 123

  • Grunes, D.L., Huang, J.W., Smith, F.W., Joo, P.K. & Hewes, D.A. 1992 Potassium effects on minerals and organic-acids in 3 cool-season grasses J. Plant Nutr. 15 1007 1025

    • Search Google Scholar
    • Export Citation
  • Hajrasuliha, S. 1980 Accumulation and toxicity of chloride in bean plants Plant Soil 55 133 138

  • Hu, Y. & Schmidhalter, U. 2005 Drought and salinity: A comparison of their effects on mineral nutrition of plants J. Plant Nutr. Soil Sci. 168 541 549

    • Search Google Scholar
    • Export Citation
  • Huang, J.W. & Grunes, D.L. 1992 Effects of root temperature and nitrogen form in magnesium uptake and translocation by wheat seedlings J. Plant Nutr. 15 991 1005

    • Search Google Scholar
    • Export Citation
  • Huang, Z.T. & Cox, D.A. 1988 Salinity effects on annual bedding plants in a peat-perlite medium and solution culture J. Plant Nutr. 11 145 159

  • Islam, A.K.M.S., Edwards, D.G. & Asher, C.J. 1980 pH optima for crop growth Plant Soil 54 339 357

  • Jarecki, M.K., Chong, C. & Voroney, R.P. 2005 Evaluation of compost leachates for plant growth in hydroponic culture J. Plant Nutr. 28 651 667

  • Juan, M., Rivero, R.M., Romero, L. & Ruiz, J.M. 2005 Evaluation of some nutritional and biochemical indicators in selecting salt-resistant tomato cultivars Environ. Exp. Bot. 54 193 201

    • Search Google Scholar
    • Export Citation
  • Kjelgren, R., Rupp, L. & Kilgren, D. 2000 Water conservation in urban landscapes HortScience 35 1037 1040

  • Maathuis, F.J.M. & Amtmann, A. 1999 K+ nutrition and Na+ toxicity: The basis of cellular K+/Na+ ratios Ann. Bot. (Lond.) 84 123 133

  • Marschner, H. 1995 Mineral nutrition of higher plants 2nd Ed Academic Press San Diego, CA

  • Martin, P.K. & Koebner, R.M.D. 1995 Sodium and chloride ions contribute synergistically to salt toxicity in wheat Biol. Plant. 37 265 271

  • Mills, H.A. & Benton Jones J. Jr 1991 Plant analysis handbook II MicroMacro Publishing, Inc Athens, GA

  • Nau, J. 1997 Tagetes (marigold) 763 766 Ball V. Ball redbook Ball Publishing Batavia, IL

  • Pantalone, V.R., Kenworthy, W.J., Slaughter, L.H. & James, B.R. 1997 Chloride tolerance in soybean and perennial Glycine accessions Euphytica 97 235 239

  • Papadopoulos, I. 1987 Effects of residual soil salinity resulting from irrigation with sulphate waters on lettuce Plant Soil 97 171 177

  • Papadopoulos, I. & Rendig, V.V. 1983 Interactive effects of salinity and nitrogen on growth and yield of tomato plants Plant Soil 73 47 57

  • Papadopoulos, I., Rendig, V.V. & Broadbent, F.E. 1985 Growth, nutrition and water uptake of tomato plants divided roots growing in differentially salinised soil Agron. J. 75 676 700

    • Search Google Scholar
    • Export Citation
  • Reboll, V., Cerezo, M., Roig, A., Flors, V., Lapeña, L. & Garcia-Agustín, P. 2000 Influence of wastewater vs groundwater on young Citrus trees J. Sci. Food Agr. 80 1441 1496

    • Search Google Scholar
    • Export Citation
  • Römheld, V. 2000 The chlorosis paradox: Fe inactivation as a secondary event in chlorotic leaves of grapevine J. Plant Nutr. 23 1629 1643

  • SAS Institute, Inc 2001 SAS/STAT software changes and enhancements through release 8.0.2 SAS Institute Cary, NC

  • Suarez, D.L. & Simunek, J. 1997 UNSATCHEM: Unsaturated water and solute transport model with equilibrium and kinetic chemistry Soil Sci. Soc. Amer. J. 61 1633 1646

    • Search Google Scholar
    • Export Citation
  • Troyanos, Y.E., Hipps, N.A., Moorby, J. & Kingswell, G. 2000 The effects of external potassium and magnesium concentrations’ on the magnesium and potassium inflow rates and growth of micropropagated cherry rootstocks, ‘F.12/1’ (Prunus avium L.) and ‘Colt’ (Prunus avium L.) × Prunus pseudocerasus L.) Plant Soil 225 73 82

    • Search Google Scholar
    • Export Citation
  • Valdez-Aguilar, L.A., Grieve, C.M., Poss, J. & Mellano, M.A. 2009a Hypersensitivity of Ranunculus asiaticus to salinity and alkalinity in irrigation water in sand cultures HortScience 44 138 144

    • Search Google Scholar
    • Export Citation
  • Valdez-Aguilar, L.A., Grieve, C.M. & Poss, J. 2009b Salinity and alkaline pH in irrigation water affect marigold plants: I. Growth and shoot dry weight partitioning HortScience 44 1719 1725

    • Search Google Scholar
    • Export Citation
  • Wang, D. 2002 Dynamics of soil water and temperatures in above ground sand cultures used for screening plant salt tolerance Soil Sci. Soc. Amer. J. 66 1484 1491

    • Search Google Scholar
    • Export Citation
  • Yang, X., Römheld, V. & Marschner, H. 1993 Effect of bicarbonate and root zone temperature on uptake of Zn, Fe, Mn and Cu by different rice cultivars (Oryza sativa L.) grown in calcareous soil Plant Soil 155/156 441 444

    • Search Google Scholar
    • Export Citation
  • Yermiyahu, U., Nir, S., Ben-Hayyim, G. & Kafkafi, U. 1994 Quantitative competition of calcium with sodium or magnesium for sorption sites on plasma membrane vesicles of melon (Cucumus melo L.) root cells J. Membr. Biol. 138 55 63

    • Search Google Scholar
    • Export Citation
  • Fig. 1.

    Calcium and magnesium concentration in leaves of marigold Tagetes patula ‘French Vanilla’ or in leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. For some measurements, se was smaller than the data point. Values are the means of three observations ± se.

  • Fig. 2.

    Potassium and sodium concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

  • Fig. 3.

    Total phosphorus and total sulfur concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

  • Fig. 4.

    Chloride and zinc concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

  • Fig. 5.

    Copper and manganese concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

  • Fig. 6.

    Iron concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se and relationship between K+, Mg2+, and Cl concentration in the leaves of marigold ‘French Vanilla’ (•) or the leaves from the lateral shoots of ‘Flagstaff’ (⊙) and ‘Yellow Climax’ (▾) and the shoot dry weight produced at experiment termination.

  • Ashworth, L.J., Gaona, S.A. & Surber, E. 1985 Nutritional diseases of pistachio trees: Potassium and phosphorus deficiencies and chloride and boron toxicities Phytopathology 75 1084 1091

    • Search Google Scholar
    • Export Citation
  • Ayers, R.S. & Westcot, D.W. 1985 Water quality for agriculture. FAO Irrigation and Drainage Paper 29 Rev. 1 Food and Agriculture Organization of the United Nations Rome, Italy

    • Search Google Scholar
    • Export Citation
  • Ben-Gal, A. & Shani, U. 2002 Yield, transpiration and growth of tomatoes under combined excess boron and salinity stress Plant Soil 247 211 221

  • Carter, C.T., Grieve, C.M. & Poss, J.A. 2005a Salinity effects on emergence, survival, and ion accumulation of Limonium perezii J. Plant Nutr. 28 1243 1257

    • Search Google Scholar
    • Export Citation
  • Carter, C.T., Grieve, C.M., Poss, J.A. & Suarez, D.L. 2005b Production and ion uptake of Celosia argentea irrigated with saline wastewaters Scientia Hort. 106 381 394

    • Search Google Scholar
    • Export Citation
  • Carvajal, M., Cerdá, A. & Martínez, V. 2000 Modification of the response of saline stressed tomato plants by the correction of cation disorders Plant Growth Regulat. 30 37 47

    • Search Google Scholar
    • Export Citation
  • Carvajal, M., Martínez, V. & Cerdá, A. 1999 Influence of magnesium and salinity on tomato plants grown in hydroponic culture J. Plant Nutr. 22 177 190

    • Search Google Scholar
    • Export Citation
  • Cramer, G.R., Läuchli, A. & Polito, V.S. 1985 Displacement of Ca2+ by Na+ from the plasmalemma of root cells Plant Physiol. 79 207 211

  • Ding, Y., Luoi, W. & Xu, G. 2006 Characterization of magnesium nutrition and interaction of magnesium and potassium in rice Ann. Appl. Biol. 149 111 123

    • Search Google Scholar
    • Export Citation
  • Eom, S.H., Setter, T.L., DiTommaso, A. & Weston, L.A. 2007 Differential growth response to salt stress among selected ornamentals J. Plant Nutr. 30 1109 1126

    • Search Google Scholar
    • Export Citation
  • Estañ, M.T., Martínez-Rodriguez, M.M., Perez-Alfocea, F., Flowers, T.J. & Bolarin, M.C. 2005 Grafting raises the salt tolerance of tomato through limiting the transport of sodium and chloride to the shoot J. Expt. Bot. 56 703 712

    • Search Google Scholar
    • Export Citation
  • Fageria, V.D. 2001 Nutrient interactions in crop plants J. Plant Nutr. 24 1269 1290

  • Grattan, S.R. & Grieve, C.M. 1999 Salinity–mineral nutrient relations in horticultural crops Scientia Hort. 78 127 157

  • Grieve, C.M., Poss, J.A. & Amrhein, C. 2006 Response of Matthiola incana to irrigation with saline wastewaters HortScience 41 119 123

  • Grunes, D.L., Huang, J.W., Smith, F.W., Joo, P.K. & Hewes, D.A. 1992 Potassium effects on minerals and organic-acids in 3 cool-season grasses J. Plant Nutr. 15 1007 1025

    • Search Google Scholar
    • Export Citation
  • Hajrasuliha, S. 1980 Accumulation and toxicity of chloride in bean plants Plant Soil 55 133 138

  • Hu, Y. & Schmidhalter, U. 2005 Drought and salinity: A comparison of their effects on mineral nutrition of plants J. Plant Nutr. Soil Sci. 168 541 549

    • Search Google Scholar
    • Export Citation
  • Huang, J.W. & Grunes, D.L. 1992 Effects of root temperature and nitrogen form in magnesium uptake and translocation by wheat seedlings J. Plant Nutr. 15 991 1005

    • Search Google Scholar
    • Export Citation
  • Huang, Z.T. & Cox, D.A. 1988 Salinity effects on annual bedding plants in a peat-perlite medium and solution culture J. Plant Nutr. 11 145 159

  • Islam, A.K.M.S., Edwards, D.G. & Asher, C.J. 1980 pH optima for crop growth Plant Soil 54 339 357

  • Jarecki, M.K., Chong, C. & Voroney, R.P. 2005 Evaluation of compost leachates for plant growth in hydroponic culture J. Plant Nutr. 28 651 667

  • Juan, M., Rivero, R.M., Romero, L. & Ruiz, J.M. 2005 Evaluation of some nutritional and biochemical indicators in selecting salt-resistant tomato cultivars Environ. Exp. Bot. 54 193 201

    • Search Google Scholar
    • Export Citation
  • Kjelgren, R., Rupp, L. & Kilgren, D. 2000 Water conservation in urban landscapes HortScience 35 1037 1040

  • Maathuis, F.J.M. & Amtmann, A. 1999 K+ nutrition and Na+ toxicity: The basis of cellular K+/Na+ ratios Ann. Bot. (Lond.) 84 123 133

  • Marschner, H. 1995 Mineral nutrition of higher plants 2nd Ed Academic Press San Diego, CA

  • Martin, P.K. & Koebner, R.M.D. 1995 Sodium and chloride ions contribute synergistically to salt toxicity in wheat Biol. Plant. 37 265 271

  • Mills, H.A. & Benton Jones J. Jr 1991 Plant analysis handbook II MicroMacro Publishing, Inc Athens, GA

  • Nau, J. 1997 Tagetes (marigold) 763 766 Ball V. Ball redbook Ball Publishing Batavia, IL

  • Pantalone, V.R., Kenworthy, W.J., Slaughter, L.H. & James, B.R. 1997 Chloride tolerance in soybean and perennial Glycine accessions Euphytica 97 235 239

  • Papadopoulos, I. 1987 Effects of residual soil salinity resulting from irrigation with sulphate waters on lettuce Plant Soil 97 171 177

  • Papadopoulos, I. & Rendig, V.V. 1983 Interactive effects of salinity and nitrogen on growth and yield of tomato plants Plant Soil 73 47 57

  • Papadopoulos, I., Rendig, V.V. & Broadbent, F.E. 1985 Growth, nutrition and water uptake of tomato plants divided roots growing in differentially salinised soil Agron. J. 75 676 700

    • Search Google Scholar
    • Export Citation
  • Reboll, V., Cerezo, M., Roig, A., Flors, V., Lapeña, L. & Garcia-Agustín, P. 2000 Influence of wastewater vs groundwater on young Citrus trees J. Sci. Food Agr. 80 1441 1496

    • Search Google Scholar
    • Export Citation
  • Römheld, V. 2000 The chlorosis paradox: Fe inactivation as a secondary event in chlorotic leaves of grapevine J. Plant Nutr. 23 1629 1643

  • SAS Institute, Inc 2001 SAS/STAT software changes and enhancements through release 8.0.2 SAS Institute Cary, NC

  • Suarez, D.L. & Simunek, J. 1997 UNSATCHEM: Unsaturated water and solute transport model with equilibrium and kinetic chemistry Soil Sci. Soc. Amer. J. 61 1633 1646

    • Search Google Scholar
    • Export Citation
  • Troyanos, Y.E., Hipps, N.A., Moorby, J. & Kingswell, G. 2000 The effects of external potassium and magnesium concentrations’ on the magnesium and potassium inflow rates and growth of micropropagated cherry rootstocks, ‘F.12/1’ (Prunus avium L.) and ‘Colt’ (Prunus avium L.) × Prunus pseudocerasus L.) Plant Soil 225 73 82

    • Search Google Scholar
    • Export Citation
  • Valdez-Aguilar, L.A., Grieve, C.M., Poss, J. & Mellano, M.A. 2009a Hypersensitivity of Ranunculus asiaticus to salinity and alkalinity in irrigation water in sand cultures HortScience 44 138 144

    • Search Google Scholar
    • Export Citation
  • Valdez-Aguilar, L.A., Grieve, C.M. & Poss, J. 2009b Salinity and alkaline pH in irrigation water affect marigold plants: I. Growth and shoot dry weight partitioning HortScience 44 1719 1725

    • Search Google Scholar
    • Export Citation
  • Wang, D. 2002 Dynamics of soil water and temperatures in above ground sand cultures used for screening plant salt tolerance Soil Sci. Soc. Amer. J. 66 1484 1491

    • Search Google Scholar
    • Export Citation
  • Yang, X., Römheld, V. & Marschner, H. 1993 Effect of bicarbonate and root zone temperature on uptake of Zn, Fe, Mn and Cu by different rice cultivars (Oryza sativa L.) grown in calcareous soil Plant Soil 155/156 441 444

    • Search Google Scholar
    • Export Citation
  • Yermiyahu, U., Nir, S., Ben-Hayyim, G. & Kafkafi, U. 1994 Quantitative competition of calcium with sodium or magnesium for sorption sites on plasma membrane vesicles of melon (Cucumus melo L.) root cells J. Membr. Biol. 138 55 63

    • Search Google Scholar
    • Export Citation
Luis A. Valdez-Aguilar U.S. Department of Agriculture, Agricultural Research Service, U.S. Salinity Laboratory, 450 West Big Springs Road, Riverside, CA 92507

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Catherine M. Grieve U.S. Department of Agriculture, Agricultural Research Service, U.S. Salinity Laboratory, 450 West Big Springs Road, Riverside, CA 92507

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James Poss U.S. Department of Agriculture, Agricultural Research Service, U.S. Salinity Laboratory, 450 West Big Springs Road, Riverside, CA 92507

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Donald A. Layfield U.S. Department of Agriculture, Agricultural Research Service, U.S. Salinity Laboratory, 450 West Big Springs Road, Riverside, CA 92507

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Contributor Notes

Mention of company names or products is for the benefit of the reader and does not imply endorsements, guarantee, or preferential treatment by the USDA or its agents.

Current affiliation: Centro de Investigación en Química Aplicada, Blvd. Enrique Reyna Hermosillo 140, Saltillo, Coah, 25253 México.

To whom reprint requests should be addressed; e-mail lavaldez@ciqa.mx.

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  • Fig. 1.

    Calcium and magnesium concentration in leaves of marigold Tagetes patula ‘French Vanilla’ or in leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. For some measurements, se was smaller than the data point. Values are the means of three observations ± se.

  • Fig. 2.

    Potassium and sodium concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

  • Fig. 3.

    Total phosphorus and total sulfur concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

  • Fig. 4.

    Chloride and zinc concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

  • Fig. 5.

    Copper and manganese concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se.

  • Fig. 6.

    Iron concentration in the leaves of marigold Tagetes patula ‘French Vanilla’ or in the leaves from the main shoot (LMS) and from the lateral shoots (LLS) in Tagetes erecta ‘Flagstaff’ and ‘Yellow Climax’ irrigated with water with increasing electrical conductivity and two pH levels. Values are the means of three observations ± se and relationship between K+, Mg2+, and Cl concentration in the leaves of marigold ‘French Vanilla’ (•) or the leaves from the lateral shoots of ‘Flagstaff’ (⊙) and ‘Yellow Climax’ (▾) and the shoot dry weight produced at experiment termination.

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