Introduction

Climate change is leading to increased incidences of flooding, resulting in significant crop losses in many parts of the world (Bailey-Serres et al. 2012; Arora 2019). Fruit growers in subtropical regions often experience a rainy summer season which can result in transient flooding. Peach production has expanded from temperate regions into these more flood-prone subtropical regions due to the success of subtropical stone fruit breeding programs. Peaches are typically grown on Prunus spp. rootstocks, which are mildly sensitive to flooding (Morales-Olmedo et al. 2021). However, the wide genetic diversity of this genus allows for varying levels of resistance/susceptibility, and thus there is a need for characterization of flood tolerance among peach rootstocks. Flooding reduces soil oxygen content which limits root respiration, ultimately hindering plant growth and production by blocking the translocation of nutrients between the aerial and below-ground portions of the plant (Morales-Olmedo et al. 2021). Both shoots and roots are affected by oxygen-deficient soil conditions (Araki et al. 2012), with roots affected first by these conditions. Although examining the response of roots to flooding is useful for assessing flooding stress, characterizing the early flooding response of the root system of perennial plants can prove difficult (Crocker et al. 2003) as much of the root system is often damaged very soon after flooding starts. Examining the responses of the above-ground portion of the plant to flooding, particularly concerning plant metabolism, can provide significant insights into the responses of plants to flooding.

Flooding significantly hinders plant growth and development (Schaffer et al. 1992), partially as a result of a shift from aerobic to anaerobic respiration in the roots, which reduces energy produced in the form of ATP. Additionally, anaerobic respiration in the roots can lead to production and translocation to the shoots of phytotoxic metabolites that can kill the plant (Schaffer et al. 1992). Flooding generally results in the generation of reactive oxygen species (ROS) that can exacerbate plant stress (Gries et al. 1990). Reactive oxygen species can destroy molecules including lipids, nucleic acids, and proteins which could hinder several physiological processes (Bandyopadhyay et al. 1999). In numerous fruit crop species including peach, stomatal conductance (gs) is adversely affected by flooding, which leads to a reduction in net CO2 assimilation (A) (Schaffer et al. 1992). In a study of flooding effects of peach scions on six different Prunus spp. rootstocks with either peach (Prunus persica (L.) Batsch) or plum (Prunus domestica.) parentage (peach: ‘Flordaguard’, ‘Guardian’, ‘Nemaguard’, ‘P-22’; plum: ‘R5064–5’, and ‘MP-29’), McGee et al. (2021) observed that gs on all but two rootstocks decreased as early as two days after trees were first flooded, and gs decreased in the remaining rootstocks within four to eight days of flooding. In that study, scions on rootstocks ‘R5064–5’ and ‘MP-29’ had the highest gs 2 to 6 days after the flooding began. The reduction in A in the flooded trees was likely linked to reduced intercellular CO2 concentrations (Ci) as a result of changes in stomatal aperture (Pezeshki 2001) because a simultaneous decrease in Ci and gs indicates that decreased A is due to stomatal factors (Ploetz and Schaffer 1989; Schaffer and Ploetz 1989). The decline in Ci results in adverse effects on the electron transport chain resulting in an upregulation of ROS (Mahajan and Tuteja 2005), which was also observed in the study of McGee et al. (2021). Morales-Olmedo et al. (2021) reported that Prunus rootstocks that retain their photosynthetic rates during flooding are deemed tolerant to flooding, suggesting that the ability of scions on flooded rootstocks ‘MP-29’ and ‘R5064–5’ to maintain higher A than the scions on flooded peach rootstocks observed by McGee et al. (2021) is an indication of their flood tolerance. In addition to stomatal limitations to A caused by flooding, flooding stress can result in biochemical limitations to A, such as reduced carboxylation efficiency (Morales-Olmedo et al. 2021). Morales-Olmedo et al. (2021) determined that responses to flooding in Prunus rootstocks included reduced A and gs, usually accompanied by reduced root growth. McGee et al. (2021) compared peach, plum, and plum x peach rootstocks, all grafted with the peach scion ‘UFSun’, a low-chill cultivar adapted for subtropical climates (Sarkhosh 2018), and determined that ‘UFSun’ on plum and/or plum x peach rootstocks is more tolerant of flooding than ‘UFSun’ on peach rootstocks. To the authors’ knowledge, the effects of flooding on carbon (C) and nitrogen (N) metabolism in Prunus rootstocks have not been elucidated.

Nitrogen is an essential element critical to plant growth and development, which requires energy and C skeletons to be assimilated into the leaf (Foyer et al. 1998). Thus, C metabolism is linked to N metabolism as they share energy supplied directly from photosynthetic electron transport, CO2 fixation, or from the respiration of fixed C, all of which depend on carbohydrates such as glucose, sucrose, and fructose (Huppe and Turpin 1994). Nitrogen is also linked to amino acid production and is involved in many complex metabolic interactions (Kusano et al. 2011). Measuring metabolite levels provides basic information about biological and physiological changes triggered by N status (Tschoep et al. 2009). Plant stress tolerance has been correlated with soluble sugar content, and may also be affected by N status, which is dependent upon soluble sugar content (Gao et al. 2018; Redillas et al. 2012; Tarkowski and Van den Ende 2015). Soluble sugars are utilized for respiration and other biological processes essential to plant growth and development, which are often depleted as a result of inhibition of physiological processes such as reduced A, or via the production of ROS. Flooding stress also results in the degradation of starch, especially when abscisic acid (ABA) is upregulated, as it further degrades starch (Thalmann and Santelia 2017). González et al. (2009) reported that in quinoa (Chenopodium quinoa Willd.), waterlogging resulted in higher leaf total soluble sugars compared to non-flooded conditions. Bailey-Serres and Voesenek (2008) indicated that flood-tolerant species exhibit higher nitrate reductase activity than species that are susceptible to flooding stress. Lamami et al. (2014) further supported this notion and reported that nitrate reduction regenerating NAD+ from NADH could be linked to the adaption of plants to low oxygen stress. Ren et al. (2017) reported that waterlogging of maize significantly reduced N uptake, translocation, and accumulation and decreased activity of enzymes involved in N metabolism. In that study, enzymatic activity related to N metabolism caused a reduction in photosynthetic capacity and dry matter accumulation, ultimately leading to reduced yield. Overall higher levels of N were considered beneficial during hypoxia stress. Kusano et al. (2011) reviewed the relationship between N content and C metabolism in rice, maize, and various dicots and concluded that nitrate levels were positively correlated with amino acid and organic acid levels and that carbohydrate levels were affected by N status. The effects of abiotic stress on C and N metabolism have been documented in several forest tree and tree fruit crops and generally follow similar trends among species. Ferner et al. (2012) reported that short-term flooding (5 days) did not change carbohydrate levels in beech (Fagus sylvatica L.) or oak (Quercus robur L.) trees, but long-term flooding (14 days) caused a two-fold increase in soluble sugars. They determined that changes in glucose and fructose contents are better indicators of flooding stress than sucrose because glucose and fructose levels increased whereas sucrose levels remained the same in both species after flooding. Root hypoxia reduced leaf nitrate content and dry matter production, but increased nitrate reductase activity in tomatoes (Solanum Lycopersicum L.) (Horchani and Aschi-Smiti 2010). The authors postulated that this response could indicate an adaptation of roots to transient hypoxia. McGee et al. (2021) reported a reduction in scion N content in leaves of P. persica L. cv. UFSun budded onto five of six Prunus rootstock genotypes tested. In that study, ‘MP-29’ was the only rootstock with leaf N levels of the scion unchanged after eight days of flooding. Although the researchers found the rootstocks to possess various levels of flood tolerance, it was unclear what could be causing the reduced A and nitrogen contents (McGee et al. 2021).

Flooding sensitivity of Prunus spp. is commonly associated with reduced gs and A, followed by a reduction in root and shoot growth (Morales-Olmedo et al. 2021). The Prunus rootstock, ‘Guardian’, has been determined to be very sensitive to flooding (Schaffer et al. 1992) and thus serves as a useful point of comparison for evaluating flooding sensitivity of other Prunus rootstocks. McGee et al. (2021) reported that A of peach scions on ‘MP-29’ and ‘R5064–5’ had higher A than scions on ‘Flordaguard’ after 4 and 6 days of flooding, but there were no differences among scions on six different Prunus rootstocks in the flooded treatment after 8 days. Stomatal conductance was reduced in scions on peach rootstocks under the flooded compared to the non-flooded treatment after two days, but in plum rootstocks this decrease was delayed until the fourth day of flooding (McGee et al. 2021). The less negative effect of flooding on A and gs in scions on plum rootstocks than peach rootstocks suggests greater transient flooding tolerance of scions on rootstocks ‘MP-29’ and ‘R5064–5’ than on peach rootstocks. It has been widely reported that plum-based rootstocks are more tolerant than peach-based rootstocks (Salvatierra et al. 2020).

In this study, we investigated the effects of flooding on carbohydrate contents, sucrose metabolism, and glycolysis, the accumulation of different forms of N, enzymatic activity related to N assimilation and metabolism, and how these changes could influence flooding tolerance. The objectives were to determine how the carbon and nitrogen metabolism of the P. persica scion cultivar UFSun on six Prunus rootstocks is affected by flooding and if these processes differ among tolerant and sensitive rootstocks. We hypothesized that the scion on flood-tolerant rootstocks would have higher leaf soluble sugar content, N contents, and enzymatic activity (enzymes related to sucrose metabolism, glycolysis, and N metabolism) than on flooding sensitive rootstocks.

Materials and methods

Experimental design and plant material

Prunus spp. rootstocks, each grafted with the P. persica cultivar ‘UFSun’ as the scion, were obtained from the United States Department of Agriculture, Agricultural Research Service (USDA-ARS) in Byron, Georgia, USA. Trees were one year old (from the time of grafting). The rootstocks used in this study were ‘Flordaguard’, ‘Nemaguard’, ‘Guardian’, ‘P-22’, ‘R5064–5’, and ‘MP-29’. ‘Flordaguard’. ‘Nemaguard’, and ‘Guardian’ are peach rootstocks that have been successfully released and are being used for commercial production in the southeastern USA, while ‘P-22’ is a peach rootstock resulting from a cross of ‘Guardian’ and ‘Flordaguard’ that is under consideration for release. ‘MP-29’ is an interspecific hybrid selected from a cross of Prunus umbellata and P. persica (Beckman et al. 2012). ‘R5064–5’ is a complex plum hybrid with no peach parentage; although the specific plum species are not known, it has been determined that neither parent was P. domestica (Thomas Beckman, USDA-ARS, personal communication). The levels of flooding tolerance for these rootstocks were previously determined by Schaffer et al. (1992) and McGee et al. (2021): ‘Flordaguard’ - very sensitive, ‘Guardian’ - very sensitive, ‘Nemaguard’ – sensitive, ‘P-22’ - sensitive, ‘R5064–5’ - tolerant, ‘MP-29’ - tolerant.

Trees were transplanted into 38-L polyester/polypropylene bags (247Garden, Montebello, CA, USA) containing a potting medium of 60% Jolly Gardner Pro-line c/25 mix (Old Castle Lawn and Garden, Atlanta, GA, USA) and 40% Griffis Lumber Garden Soil (Griffis Lumber and Sawmill, Gainesville, FL, USA). The experiment was conducted in a greenhouse at the University of Florida in Gainesville, Florida. The plants were divided into two treatments: 1) flooded and 2) non-flooded (control). Each treatment consisted of 5 single-tree replicates of each of the 5 rootstocks, for a total of 60 plants arranged in a complete block design. In the flooded treatment, the root system of each tree was submerged to 5 cm above the graft union by placing the tree and planting bag in a 75.7-L container filled with tap water. Each tree was flooded in a separate container. Trees in the control treatment were not flooded and irrigated for 5 min twice daily at a rate of 12.1 L/h via a microjet sprinkler system. After 8 days (>50% wilting of some flooded plants), trees and planting bags in the flooded treatment were removed from the larger container of tap water (unflooded).

Leaf sample collection

Leaf samples used for the biochemical analyses were collected from trees in the flooded and non-flooded treatments 8 days after treatments were initiated. Forty fully expanded mature leaves were collected from each tree. The leaves were randomly collected from all sides of the canopy of each tree and placed in a Ziploc® bag. Samples were immediately stored in a freezer at −80 °C until they were ready to be shipped overnight, in a Styrofoam cooler with dry ice, to the University of New Hampshire (Durham, NH, USA) for analyses.

Sugars, starch, and enzymatic activities

The method described by Jones et al. (1977) was used for the determination of glucose. The method of Buysse and Merckx (1993) was used for the determination of sucrose, fructose, and total soluble sugar (TSS) content, which was not limited to glucose, sucrose, and fructose and thus may reflect values higher than the total of these respective sugars. Enzymatic activity was determined in frozen leaf tissue (0.5 g) using the procedure described by Shahid et al. (2018). The Bradford (1976) assay was used for protein determination. Total acid invertase (AI) was estimated using a mixture (1 mL) comprised of a 0.2 mL extract of sodium acetate (0.1 M, pH 4.8) and sucrose (0.1 M). Neutral invertase (NI) was estimated using a mixture of dipotassium phosphate (0.1 M) with pH 7.2, sodium citrate (0.1 M), and sucrose (0.1 M) as described by Shahid et al. (2018). For the determination of AI/NI, 0.2 mL of enzyme extract was incubated for 40 min at 37 °C, the reaction was then stopped by adding dinitrosalicylic (1 mL), and the extract was boiled for 5 min. The absorbance of the reaction mixture was measured at 520 nm with a spectrophotometer (Thermo Fisher Scientific, Waltham, MA, USA). The AI or NI activities are expressed as the units of reducing sugars produced from sucrose per minute. Reducing sugars were determined using the method described by Buysse and Merckx (1993). Sucrose synthase (SS) and sucrose phosphate synthase (SPS) were extracted and quantified as described by Rufty and Huber (1983). The SPS activity for SS (Bird et al. 1974), SS activity for sucrose cleavage (Lowell et al. 1989), and fructokinase (Zrenner et al. 1995) were also determined. Hexokinase (HK), Pyruvate kinase (PK), and phosphofructokinase (PFK) were measured using commercial enzyme kits (Sigma-Aldrich, St. Louis, MO, USA).

Nitrate, nitrite, and ammonium content

Leaf tissue was boiled in distilled water (1:10 w/v) for 20 min then filtered through Whatman No. 1 filter paper to determine leaf nitrate (NO3), nitrite (NO2), and ammonium (NH4+) contents. Nitrate content was determined using the protocol of Cataldo et al. (1975), NO2 was assayed according to the methodology of Snell and Snell (1949), and NH4+ was estimated by the procedure of Molins-Legua et al. (2006). Reaction mixtures for N analysis were prepared following the protocol of Shahid et al. (2018).

Nitrogen assimilation enzymes

The protocol of Sym (1984) was used for the determination of nitrate reductase (NR) activity. Leaf tissue (0.5 g) was treated with phosphate buffer (pH 7.0), 0.5 mL of 0.02 M KNO3, 0.5 mL of sulphanilamide, and 0.5 mL of N-(1-naphthyl)-ethylene diamine dihydrochloride and then centrifuged at 4°C at 15,000 g. The activity was calculated as the amount of NO2 released g−1 FW h−1. The methods of Ramarao et al. (1983) were used to determine nitrite reductase activity (NiRA); the reaction mixture was created following the protocols of Shahid et al. (2018). Glutamine synthase (GS) activity was determined using the procedures of Lillo (1984). Frozen leaf tissue (0.5 g) was blended with Tris-hydrochloric acid (50 mM, pH 7.8), 15% glycerol, 2-mercaptoethanol (14 mM), ethylenediaminetetraacetic acid (1 mM) and triton x-100 (0.1%). The mixture was centrifuged for 20 min at 4°C at 15,000 g to produce an enzyme extract. The mixture was composed as described by Shahid et al. (2018). Glutamine-2-oxoglutarate aminotransferase (GOGAT) activity was estimated as described by Singh and Srivastava (1986). Leaf tissue (0.5 g) was blended in sodium phosphate buffer (0.2 M, pH 7.5) supplemented with thylenediaminetetraacetic acid (2 mM), potassium chloride (50 mM), 2-mercaptoethanol (0.1% v/v) and triton x-100 (0.1%), then centrifuged for 15 min at 4°C at 10,000 g. Procedures described by Singh and Srivastava (1983) were used to determine glutamate dehydrogenase (GDH) activity from 0.5 g of leaf tissue, ground in sodium phosphate buffer (0.5 M, pH 7.4), sucrose (0.4 M), and ethylenediaminetetraacetic acid (2 mM). Each variable was calculated in the following units GS (A540 g−1 FW h−1), GOGAT (1 μmol NADH oxidized h−1), and GDH (μmol NADH oxidized per hour).

Statistical analyses

A two-way analysis of variance (ANOVA) was used for all response variables to test for main effects and interactions between rootstock and flooding treatments. A one-way ANOVA and Waller-Duncan K-Ratio test were used to compare means among rootstocks and a non-paired T-test was used to compare means between flooding treatments. All data were analyzed with SAS Statistical Software (Version 9.4, SAS Institute, Cary, NC, USA).

Results

Enzymes for sucrose metabolism and glycolysis

The activity of AI was lower in the flooded treatment, whereas activities of NI, SS, and SPS were higher in the flooded treatment than in the non-flooded treatment for scions on all rootstocks (Fig. 1A, B, C, and D respectively). The largest treatment difference in AI activity (41% lower in flooded than non-flooded plants) was in scions on ‘Flordaguard’ (Fig. 1A), while the largest difference in activity of NI, SS, and SPS (300%, 214%, and 218% higher in flooded than non-flooded plants) was in scions on ‘MP-29’ (Fig. 1B, C, and D respectively). In the flooded treatment, scions on ‘MP-29’ and ‘R5064–5’ had the highest enzyme activities of AI, NI, SS, and SPS (except for scions on ‘P-22’) (Fig. 1A, B, C, and D respectively).

Fig. 1
figure 1

Effect of rootstock and flooding treatment on acid invertase (A), neutral invertase (B), sucrose synthase (C), and sucrose phosphate synthase (D) activities in leaves of Prunus persica cv. UFSun budded on Flordaguard, Guardian, MP-29, Nemaguard, P-22, and R5064-5 rootstocks. Different lowercase letters indicate significant differences among rootstocks in the non-flooded treatment, different uppercase letters indicate significant difference among rootstocks in the flooded treatment according to a Waller-Duncan K-Ratio Test (P < 0.05). Single (*) or double (**) asterisks indicate a significant difference at P < 0.05 or 0.01, respectively and ns indicates no significant difference between flooding treatments of each rootstock according to a non-paired T-test

Scions on rootstocks ‘MP-29’ and ‘R5064–5’responded differently to flooding in terms of FK and HK activities, then scions on the peach rootstocks (Fig. 2A  and B). Flooding reduced activities of these sugar sensing molecules in scions on peach rootstocks (25% to 38% lower in flooded than non-flooded plants) except for those on ‘P-22′ whose HK activity was unchanged (Fig. 2B). Flooded plants had lower activities of PK (13% to 59% lower in flooded than non-flooded plants) and PFK (4% to 31% lower in flooded than non-flooded plants) than non-flooded plants in scions on the peach rootstocks (Fig. 2C and D). In scions on ‘MP-29′ and ‘R5064–5′, PFK activity was unaffected by flooding (Fig. 2C), whereas PK activity was not significantly different between flooding treatments in scions on ‘R5064–5′ (Fig. 2D). Scions of flooded plants on ‘MP-29′ and ‘R5064–5′ had higher activities of FK (83% and 36% higher in flooded than non-flooded plants, respectively) and HK (17% and 9% higher in flooded than non-flooded plants, respectively) and the smallest differences in activities of PFK (4% and 10% lower in flooded than non-flooded plants, respectively) and PK (13% and 16% lower in flooded than non-flooded plants, respectively) than scions of non-flooded plants.

Fig. 2
figure 2

Effect of rootstock and flooding treatment on fructokinase (A), hexokinase (B), phosphofructokinase (C), and pyruvate kinase (D) activities in leaves of Prunus persica cv. UFSun budded on Flordaguard, Guardian, MP-29, Nemaguard, P-22, and R5064-5 rootstocks

Soluble sugars and starch

There were significantly higher contents of glucose, sucrose, fructose, and TSS (Fig. 3A, B, C, and E respectively) in scions in the flooded treatment compared to those in the non-flooded treatment, except for sucrose content in scions on ‘Flordaguard’, which was not affected by flooding (Fig. 3B). The largest changes in glucose, fructose, and sucrose content were in scions on ‘MP-29’ (119%, 110%, and 323% higher in flooded than non-flooded plants). Leaf starch content was higher in scions on all rootstocks in the non-flooded compared to the flooded treatment and the smallest differences were observed in scions on ‘MP-29’ (27% lower in flooded than non-flooded plants) (Fig. 3D). Total soluble sugars were higher in scions of flooded trees than non-flooded trees, and the largest differences occurred in scions on ‘MP-29’ and ‘R5064–5’ (375% and 281% higher in flooded than non-flooded plants) (Fig. 3E).

Fig. 3
figure 3

Effect of rootstock and flooding treatment on glucose (A), sucrose (B), fructose (C), starch (D), and total soluble sugars content (TSS) (E) in leaves of Prunus persica cv. UFSun budded on Flordaguard, Guardian, MP-29, Nemaguard, P-22, and R5064-5 rootstocks

Nitrate, nitrite, and ammonium content

Leaf nitrate content in the scions was lower in the flooded than non-flooded treatment for scions on all rootstocks except ‘MP-29’ and ‘R5064–5’ (Fig. 4A). Leaf nitrite content was also lower in the flooded than non-flooded treatment for scions on all rootstocks except ‘R5064–5’ (Fig. 4B), but ammonium content in the scions was higher in the flooded than non-flooded treatment on all rootstocks (Fig. 4C). Scions on ‘Flordaguard’ exhibited the largest difference in leaf NO3 content between treatments (87% lower in flooded than non-flooded plants) (Fig. 4A), while scions on ‘MP-29’ or ‘R5064–5’ exhibited no difference. Scions on ‘Flordaguard’ had the largest difference in NO2 content between treatments (32% lower in flooded than non-flooded plants) whereas scions on ‘R5064–5’ exhibited no differences (Fig. 4B). Scions on ‘Flordaguard’ and ‘P-22’ (which has ‘Flordaguard’ parentage) had the largest differences of the toxic compound NH4− between treatments (48% and 109% higher in flooded than non-flooded plants, respectively) compared to scions on the other rootstocks (Fig. 4C).

Fig. 4
figure 4

Effect of rootstock and flooding on nitrate (A), nitrite (B), and ammonium (C) content in leaves of Prunus persica cv. UFSun budded on Flordaguard, Guardian, MP-29, Nemaguard, P-22, and R5064-5 rootstocks

Enzymes for nitrogen metabolism

Scions on most peach rootstocks exhibited lower levels of enzyme activity of NR, NiR, GS, and GOGAT (Fig. 5A, B, C, and D respectively) in the flooded treatment than the non-flooded treatment, except for GDH activity which was higher in the flooded treatment (Fig. 5E). Activities of NR and GS were not different between the flooded and non-flooded treatments in scions on ‘Guardian’ (Fig. A and C, respectively). Activities of NR, NiR, GS, and GDH in scions on ‘MP-29’ did not differ between treatments (Fig. 5A,B,C, and E, respectively), whereas NiR, GS, or GDH activities in scions on ‘R5064–5’ did not differ between treatments (Fig. 5B,C, and E). Enzymatic activity of GOGAT was lower in scions on both plum rootstocks in the flooded treatment compared to the non-flooded treatment (Fig. 5D). Scions on ‘R5064–5’ had lower activity of NR in the flooded treatment than non-flooded treatment (Fig. 5A). The largest differences between NR, NiR, GS, and GOGAT (Fig. 5A, B, C, and D respectively) between the flooded and non-flooded treatments occurred in scions on ‘Flordagaurd’ (38%, 22%, 28%, and 22% lower in flooded than non-flooded plants, respectively) and ‘Nemagaurd’ (30%, 16%, 29%, and 26% lower in flooded than non-flooded plants). The largest treatment difference in GDH activity was seen in ‘Flordaguard (46% higher in flooded than non-flooded plants) (Fig. 5E).

Fig. 5
figure 5

Effect of rootstock on nitrate reductase (A), nitrite reductase (B), glutamine synthase (C), glutamate syn-thase (D), and glutamate dehydrogenase (E) activities in leaves of Prunus persica cv. UFSun budded on Flordaguard, Guardian, MP-29, Nemaguard, P-22, and R5064-5 rootstocks

Discussion

Carbon metabolism

The increases in leaf carbohydrate contents in scions on all flooded rootstocks suggests that sugar translocation to the root system was impaired, contrary to the response observed in wheat where glucose, sucrose, and fructose were lower in flooded than non-flooded plants (Huang and Johnson 1995). Similar to our observations of Prunus rootstocks, a few studies have shown that flooding reduced sugar translocation in the phloem of oak trees and castor oil plants, resulting in higher sugar content in flooded than non-flooded plants (Ferner et al. 2012; Peuke et al. 2015). A study of forest trees found that carbohydrate levels and efficient use of the glycolytic pathway are major aspects in determining tolerance to flooding (Kreuzwieser et al. 2004). Enzymatic activity associated with glycolysis, in the current study, indicated that rootstocks with plum parentage possess some genetic difference which allows for more efficient phosphorylation of sugars. Hexokinase and FK have been linked to the phosphorylation of glucose and fructose, and FK has been found to regulate starch synthesis (Granot et al. 2014). The activities in scions on peach rootstocks in the current study suggest that scions on peach rootstocks have diminished efficiency for phosphorylating glucose and fructose under flooded conditions, while glucose phosphorylation efficiency is improved for scions on rootstocks with plum parentage. This could explain why scions on flooded plum rootstocks have greater efficiency of the glycolytic pathway under flooding conditions than those on peach rootstocks. Ultimately, having more active HK and FK molecules increases the hexose pool and improves sucrose metabolism (Fukao and Bailey-Serres 2004; Salvatierra et al. 2020). However, with the low levels of enzymatic activity related to sucrose metabolism and glycolysis, the decrease of HK and FK activities, and the large negative differences in starch content in scions on peach rootstocks, it could be possible that increases in soluble sugars in scions on peach rootstocks are, at least partially, the result of starch degradation. Phosphofructokinase is another important enzyme in glycolysis as it is responsible for the conversion of fructose 6-bisphosphate and ATP to fructose 1,6-biphosphate and ADP (Granot et al. 2014). The activity of PFK in scions on plum rootstocks was unaffected by flooding, whereas PFK activity in scions on peach rootstocks was lower in the flooded than non-flooded treatment which could result in further reduced efficiency of the glycolytic pathway in scions on peach rootstocks. Furthermore, lower AI activity in flooded plants suggests a strain on the photosynthetic process, as AI is important for biological processes related to sucrose metabolism and hydrolysis for growth (Kulshrestha et al. 2013). Sucrose molecules are important for various metabolic activities and signaling pathways for different genes involved in photosynthesis (Rosa et al. 2009). Neutral invertase has similar activity and function as AI, but its functions are less well elucidated (Shen et al. 2018). The response of AI and NI in scions on peach rootstocks suggests that rootstocks with peach parentage are less efficient at sucrose metabolism than those with plum parentage. The activities of SS and SPS further support this idea as scions in the flooded treatment on peach rootstocks had lower SS and SPS activities compared to those on plum rootstocks. Sucrose synthase and SPS have similar roles in synthesizing sucrose. Santaniello et al. (2014) reported that corn and potato with lower SS activity exhibited more sensitivity to hypoxia stress compared to those with higher SS activity, which can be seen in the current study as scions on the more flood-sensitive peach rootstocks experienced lower SS activity in the flooded treatment than scions on plum rootstocks, causing them to synthesize and hydrolyze sucrose less efficiently than scions on plum rootstocks. Carbohydrate levels have been correlated with flooding tolerance; crops with limited carbohydrate availability only survived transient flooding (Fukao and Bailey-Serres 2004). Thus, the ability of scions on plum rootstocks to exhibit higher levels of carbohydrate may explain, at least in part, their greater degree of flood tolerance.

Nitrogen metabolism

Plant demand for N is closely associated with growth, and thus lower contents of nitrogen and less active enzymes related to nitrogen assimilation and metabolism are indicative of reduced growth. A study of popular trees (Populus x canescens) by Liu et al. (2015) found that NO3 uptake was reduced by hypoxia whereas NH4+ uptake was not. They also postulate that NO3 was preferentially assimilated by developing tissues to ensure growth and survival under hypoxic or waterlogged conditions. Horchani and Aschi-Smiti (2010) found that root hypoxia in tomato also reduced leaf NO3 content. Similar results were observed in the current study, though only scions on peach rootstocks exhibited reduced uptake of NO3 under flooded conditions, whereas plum rootstocks maintained similar levels of NO3 in both flooded and non-flooded treatments. Results of the current study agree with studies of coniferous species, where NH4+ uptake limited uptake of NO3 (Liu et al. 2015), whereas scions on peach rootstocks exhibited high levels of NH4+ and consequently lower levels of NO3 and those on plum rootstocks had low levels of NH4+ and high levels of NO3. Ammonium can be toxic to plants due to the depletion of carbon, damage to cellular structures, and disruption of a multitude of biological processes including photosynthesis (Bittsánszky et al. 2015). This would result in less growth of scions on peach rootstocks and exacerbated stress in these trees due to the elevated levels of NH4+, which could explain the greater sensitivity exhibited by scions on peach rootstocks.

Glutamate dehydrogenase is an important enzyme that links C and N metabolism (catalyzes the NADP+ linked deamination of glutamate to ammonia) and is used by cereal crops under low-oxygen stress to supply carbon (from amino acids) to the tricarboxylic acid cycle (Miflin and Habash 2002). Flooding resulted in an increase in GDH contents for all rootstocks except ‘MP-29’ and ‘R5064–5’ which suggests that scions on peach rootstocks are compensating for diminished carbon supply by cleaving carbon from amino acids, while those on plum rootstocks can continue producing carbohydrates during short-term flooding. Several studies have shown that reduced activity of enzymes involved in N metabolism is common in flood-sensitive plants during and after periods of hypoxia (Bailey-Serres and Voesenek 2008; Limami et al. 2014; Ren et al. 2017). Scions on plum rootstocks exhibited the smallest difference in NH4+ (slightly higher in the flooded compared to non-flooded trees), no differences in NO3-, and largely no differences in enzymatic activity related to N assimilation or metabolism between the flooded and non-flooded treatments, while N levels and enzymatic activity for scions on peach rootstocks were largely lower in the flooded than non-flooded treatments. This suggests that scions on rootstocks with plum parentage can maintain higher amounts of N and enzymatic activity related to N metabolism, ultimately being able to continue growth while under flooded conditions which contribute to their greater degree of flooding tolerance.

Conclusions

This study advances the understanding of how short-term flooding stress affects carbon and nitrogen metabolism of low-chill peach scions on various Prunus rootstocks. The results of the current study suggest that a low-chill peach cultivar when grown on plum and peach rootstocks respond similarly to flooding stress when examining carbon metabolism (except for HK and FK), while nitrogen metabolism in scions on peach is largely negatively affected (lower values in flooded treatment than non-flooded) and those on plum are mostly unaffected. The increased activities of HK and FK imply that the scions on plum rootstocks have more efficient phosphorylation of glucose and fructose than those on the peach rootstocks. This suggests that the hexose-phosphate pool is diminished in scions on peach rootstocks causing the metabolic pathways to be hexose limited, ultimately reducing the energy available for essential functions such as carbon assimilation, which is linked to N metabolism, which in turn is negatively affected. Thus, in flood-prone, subtropical areas where low-chill peach trees are planted, consideration should be given to replacing ‘Flordaguard’, the most common rootstock for low-chill peaches, with plum rootstocks such as ‘MP-29’ or another flood-tolerant rootstock.