Research Article Volume 6 Issue 1
1Botany Department, Faculty of Agriculture, Fayoum University, Fayoum, Egypt
2Horticulture Department, Faculty of Agriculture, Fayoum University, Fayoum, Egypt
Correspondence: Mohamed A Seif El-Yazel, Botany Department, Faculty of Agriculture, Fayoum University, Fayoum
Received: February 15, 2022 | Published: February 24, 2022
Citation: El-Yazel MAS, EI-Shewy AA, Matter FMA. Impact of water logging condition on seedling of five timber tree species. Horticult Int J. 2022;6(1):37-45. DOI: 10.15406/hij.2022.06.00240
Under natural conditions, plants are frequently exposed to transient or permanent soil waterlogging. Flooding of the soil with water with poor drainage drastically influences the soil physico-chemical properties, most notably soil oxidation-reduction potential, pH and O2 level. Thus, conditions of hypoxia or anoxia are commonly encountered by plant root systems. These O2 restrictive conditions dramatically have an effect on plant growth, development and survival. One in every of the simplest characterized plant responses to soil waterlogging is that the metabolic switch from aerobic respiration to anaerobic fermentation. In this study the effects of waterlogged were examined on seedling growth, metabolic, physiological and morphological responses of five species of timber trees (Casuarina cunninghamiana, C. glauca, Eucalyptus rostrata, Cupressus sempevirens and E. citrodora). The results indicated a wide variation among these timber tree species in their response to water logging. Casuarina cunninghamiana and C. glauca were more tolerant to waterlogging than the other species, followed by Eucalyptus rostrata then Cupres sussempevirens. E. citrodora was the least tolerant waterlogging species.
Waterlogging treatment decreased the seedling growth and the leaf contents from carbohydrates, total and free phenols, chlorophylls and carotenoids as well as N, P and K contents in the leaves. On the other hand, waterlogging treatment increased both epinastic leaf angles, contents of total indoles, total free amino acids, chloride, sodium, calcium and magnesium in the leaves. Moreover, total free amino acids, total indoles, carbohydrates, total and free phenols contents were also increased in stems and roots of waterlogged seedlings.
Stress tolerant tree also called resistance or susceptible stress tree is one type of tree mechanism to respond in stress conditions.1 The reaction involved changes whether it inhibits or stimulates tree growth either in hormone, structure or physiological changes. As known, woody trees were the best selections in tolerating stress resulting by planted in high risky areas such as along highway. Subsequently, these urban tree areas were facing with critical environment stress every day. One of common stress was waterlogging stress occurred when excessive water is supplied to the trees.2,3
Waterlogging does not necessarily occur only when the soil is inundated. Soil waterlogging has long been identified as a major abiotic stress and the constraints it imposes on roots have marked effects on plant growth and development. When such events take place in the spring, they can greatly reduce seed germination and seedling establishment. Thus, soil waterlogging is an important factor affecting the growth, development and survival of numerous plant species, not only in natural ecosystems but also in agricultural and horticultural systems.4,5 Waterlogging occurs when water fills a critical proportion of the soil air spaces, depending on the plant species of plant involved. During waterlogging, inhibition of root respiration and subsequent to the root tissue has been suggested as cause of flooding stress.6 As water saturates the soil, air spaces are filled, leading to the modification of several soilphysico-chemical characteristics.7,8 The first event that takes place is in fact the increased presence of H2O: soil water saturation characterises flooding. Nevertheless, the mechanisms which trigger a plant response are often presumed by-products of root zone flooding (i.e. changes in soil redox and pH; a decline in O2 level…). Alternatively, toxic effects of the production of anaerobic respiration have been suggested as a mechanism of root damage in both herbaceous and tree species.9,10 The 02 diffusion system from the aerial parts to the roots is limited and varies in mesophytes depending on waterlogging tolerance.11-13 Adventitious root formation and increasing root porosity are however a temporary feature to case or help recover from waterlogging damage.14,15
Plant species differ in tolerance to root zone waterlogging.16-18 and these differences are important for selecting plants adapted to these conditions.19 The existence of genetic variability for waterlogging tolerance is known19,20 and screening plants for increased tolerance to waterlogging was reported.19,21
The purpose of this study was to evaluate the relative waterlogging tolerance of some timber seedling tree species. Also, to examine the effects of waterlogging on growth, elemental contents, and endogenous hormones in seedlings of some timber tree species.
The present investigation was carried out in two successive seasons of 1999 and 2000 on seedlings of five timber trees species (Casuarina cunninghamiana, C. glauca, Eucalyptus rostrata, E. citrodora and Cupres sussempervirens).
Seeds of each timber tree species were germinated in sand in the greenhouse. After germination, newly emerged seedlings with the first two leaves were chosen and transferred into washed sand in plastic containers of 30 cm diameter at the base, 50 cm at the top and 30 cm deep. The plants were irrigated with a dilute nutrient solution,22 until starting the waterlogging treatment, where the seedlings were grown for 6 months. The plants were then selected for uniformity on the basis of plant length within each cultivar. Plants were grown in containers, each contained 20 plants.
Waterlogging was initiated by closing the drainage system of plastic containers and adding tap water to the containers. Water was maintained about 5 cm above the sand level through the experimental period. Non waterlogged plants were served as control and irrigated and drained daily.
More details on the experimental technique are described elsewhere.23
Time of appearance of waterlogging symptoms and percentage of survived seedlings were recorded and the affected seedlings were daily removed.
Samples were taken from waterlogging seedlings as well as from the control (freely drainage) for growth measurements. The seedlings were separated to roots and shoots. The root system was washed to be free from sand. Fresh weight of roots and tops was recorded.
Leaves or phylloclades (casuarinaspieces), stems and roots samples were collected for determination of potassium, sodium24 chloride,25 nitrogen,26 phosphorus,27 calcium, magnesium,28 total indols29 and the modification of Selim et al,30 freephenols,31 total phenols,32 total carbohydrates33 total sugars,31 and total free amino acids.34 Moreover chlorophyll and caroteniods were determined in leaves/phylloclade according to Welburn and Lichtenthaler.35
The values presented in the tables are based on the means of the two seasons.
The experimental design for all studied treatments was the complete randomized block design with three replicates and data were statistically analyzed according to the method of Duncan.36 Data were subjected to an analysis of variance. Significant differences among means were determined using least significant differences (p < 0.05) comparison.
Symptoms of waterlogging injury on the seedlings were chlorosis and abscission of leaves, in addition to wilting of leaves and shoot, which are considered the main indicators for plant damage.
Survival
A great variability existed among the timber tree species in their tolerance to waterlogging (Table 1). The time required for each population to reach certain level of survival differed from specie to another. The survival percentage declined as a function of time of waterlogging treatment.
Species |
Time needed to reach levels of survival (days) |
|||
|
Survival % |
|
|
|
|
2000 |
|
1999 |
|
50% |
80% |
50% |
80% |
|
E. rostrata |
54 |
45 |
45 |
38 |
E. citrodora |
27 |
23 |
11 |
4 |
C. cunninghamiana |
172 |
140 |
168 |
130 |
C. glauca |
168 |
125 |
160 |
122 |
C. sempervirens |
32 |
31 |
18 |
15 |
LSD0.05 |
2.9 |
3.9 |
2.1 |
3.5 |
Table 1 Times (days) at which percentage of seedlings reached specified levels of survival during waterlogging treatment mean of the two seasons, 1999-2000
It can be noticed that E. rostrata appeared to be least tolerant species to waterlogging; however, C. cunningharniana was the most waterlogging tolerant species. The relative tolerance had been found in an ascending order as Casuarina cunninghamiana, C. glauca, Eucalyptus rostrata, Cupres sussempervirens and E. citrodora. Variation between species and strains in their tolerant to waterloging had been reported.6,16 Plant tolerance may be adapted to the reduced oxygen levels by either reducing their demand for oxygen by metabolic change or by increasing oxygen supply to root through the modification of root anatomy.8,37-40 The extent of injury is dependent on the duration of oxygen deficiency and can range from stoppage of growth to death of plants.4,41
Seedling growth
The waterlogging treatment decreased seedling growth in terms of fresh weight (Table 2) of all timber tree species under this study, compared with un-waterlogging control. The reduction in growth was associated with the tolerant to waterlogging. The lowest reduction in seedling growth 3.1% and 7.9% for root and shoot respectively was found for the most tolerant species (C. cunningharniana) which showed the least effect by water logging. However, the great reduction in growth (67.6% and 51%for root and shoot, respectively was found in the seedlings of the least waterlogging tolerant (E. cetrodora).
Species |
Seedlings weight (g) |
Growth reduction % |
|
|
Control |
Waterlogged |
|
Shoots |
|||
E. rostrata |
1.96 |
2.92 |
32.9 |
E. citrodora |
1.52 |
3.1 |
51 |
E. cunninghamiana |
1.16 |
1.26 |
7.9 |
E. glauca |
1.51 |
1.64 |
7.9 |
E. sempervirens |
0.54 |
0.98 |
44.9 |
LSD0.05 |
0.42 |
0.19 |
|
Roots |
|||
E. rostrata |
0.94 |
1.66 |
43.4 |
E. citrodora |
0.6 |
1.58 |
67.6 |
E. cunninghamiana |
0.94 |
0.97 |
3.1 |
E. glauca |
1.19 |
1.26 |
3.6 |
E. sempervirens |
0.27 |
0.67 |
59.7 |
LSD0.05 |
0.16 |
0.11 |
|
Table 2 Effect of water logging on seedlings growth (measured as fresh weight when 50% survival was reached) of five timber tree species (mean of the two seasons, 1999-2000)
Similar growth reduction was found in citrus,16 olive,18 Birch rootstocks17 and in other tree species.3-5,10 Such decrease in growth can by oxygen deficiency could be possibly due to reduction of photosynthesis.4,42 and nutrient uptake by active absorption.43 In this connection, Parent et al.2 reported that, adaptations to waterlogging include morphological changes which comprise the formation of hypertrophied lenticels, the initiation of adventitious roots and/or the development of aerenchyma. Our knowledge of the basic adaptive mechanisms of plants to soil waterlogging has benefited from large scale genomic and proteomic approaches, however, the diversity of the adaptive responses involved underlines the difficulty when studying this stress.
Leaf angle (epinasty)
Waterlogging increased leaf epinasty (Table 3). The epinastic movement of the leaves has been caused by more rapid expansion of cell on the upper side of the petiole compared to the cell on the lower side.44 It is known that ethylene will induced epinasty even at very low concentration,41 thus waterlogged plants have similarly appeared to the plants which have been gassed with ethylene.44 In this respect, Irfan et al., (2010) reported that other plant response to waterlogging is to produce ethylene, which signals various adaptive functions to plant survival, such as increased number of adventitious roots, and formation of aerenchyma in such environment. Different apple genotypes present variable response to hypoxia due to genetic variability. The main responses in apple rootstocks to waterlogging are reduction of new adventitious root growth, leaf senescence and reduced dry weight accumulation.45
Species |
Leaf or phylloclade angle (degree) |
|
|
|
% of control |
Waterlogged |
Control |
E. rostrata |
166.6 |
55 |
33 |
E. citrodora |
181.3 |
58 |
32 |
E. cunninghamiana |
140 |
28 |
20 |
E. glauca |
154.2 |
37 |
24 |
E. sempervirens |
182.4 |
62 |
34 |
LSD0.05 |
|
3.8 |
2.1 |
Table 3 Effect of waterlogging on leaf/phylloclade epinasty of some timber tree species (mean of the two seasons, 1999-2000)
Various studies have established that the ethylene levels in waterlogged plants exceeded those of the control plants.46 The ethylene production and epinasty were observed in shoots under anaerobic conditions, this is true when the root of tomato plants growing in nutrient solution were made anaerobic, increased ethylene production and epinasty were observed in the shoot.47 Auxin and ethylene concentration increased in waterlogged plants.23,41
However, the effect of waterlogging on epinastic leaf angle differed with specie (Table 3). Seedling of C.cunninghamiana which was the most tolerant species to waterlogging had the lowest effect of waterlogging on epinastic leaf angle, However epinastic leaf angle of E. citrodora, the least waterlogging tolerance was the most influenced by waterlogging. Accordingly’, the waterlogging tolerance of Casuarina species have been linked with their ability to minimize ethanol production by the maintenance of low respiration rates and the production of other non-toxic and proportion such as oxygen transport from the shoot to the root.38
Sodium, chloride, calcium and magnesium
Waterlogging increased the concentration of Na+, Cl-, Ca++ and Mg++ in the leaves, stems and roots of all timber tree species under this study (Table 4). This increase of both Na+ and Cl- that occurred with waterlogging were the result of increase in the uptake of Na+ and Cl-.48 The more tolerant Casuarina species (C.cunninghamiana and, C. glauca) as shown in Table 1, had the lowest increases of both Na+ and Cl-. Oncontrary the least tolerant specie E. citrodora had the highest increases of Na+ and Cl-.
Species |
Sodium % |
|
|
|
|
|
|
Roots |
|
Stems |
|
Leaves or phylloclade |
|
Waterlogged |
Control |
Waterlogged |
Control |
Waterlogged |
Control |
|
E. rostrata |
0.69 |
0.39 |
0.59 |
0.29 |
0.45 |
0.4 |
E. citrodora |
0.75 |
0.42 |
0.7 |
0.3 |
0.51 |
0.43 |
E. cunninghamiana |
0.64 |
0.44 |
0.66 |
0.49 |
0.57 |
0.54 |
E. glauca |
0.68 |
0.39 |
0.69 |
0.43 |
0.55 |
0.51 |
E. sempervirens |
0.79 |
0.52 |
0.68 |
0.2 |
0.61 |
0.55 |
LSD0.05 |
0.1 |
0.12 |
0.1 |
0.13 |
0.08 |
0.1 |
Chloride % |
||||||
E. rostrata |
1.18 |
0.98 |
0.72 |
0.59 |
0.25 |
0.18 |
E. citrodora |
1.19 |
0.86 |
0.65 |
0.47 |
0.27 |
0.18 |
E. cunninghamiana |
1.2 |
0.74 |
0.59 |
0.53 |
0.17 |
0.16 |
E. glauca |
1.15 |
0.78 |
0.58 |
0.54 |
0.17 |
0.15 |
E. sempervirens |
0.88 |
0.17 |
0.23 |
0.18 |
0.28 |
0.19 |
LSD0.05 |
0.19 |
0.06 |
0.08 |
0.08 |
0.08 |
N.S. |
Calcium % |
||||||
E. rostrata |
0.51 |
0.35 |
0.53 |
0.63 |
0.98 |
0.53 |
E. citrodora |
0.52 |
0.39 |
0.61 |
0.59 |
0.91 |
0.66 |
E. cunninghamiana |
0.41 |
0.23 |
0.61 |
0.27 |
0.57 |
0.53 |
E. glauca |
0.39 |
0.24 |
0.55 |
0.34 |
0.61 |
0.57 |
E. sempervirens |
0.53 |
0.53 |
0.63 |
0.67 |
0.87 |
0.63 |
LSD0.05 |
0.06 |
0.08 |
0.06 |
0.07 |
0.06 |
0.09 |
Magnesium % |
||||||
E. rostrata |
0.65 |
0.61 |
0.51 |
0.45 |
0.69 |
0.39 |
E. citrodora |
0.68 |
0.59 |
0.56 |
0.51 |
0.66 |
0.42 |
E. cunninghamiana |
0.95 |
0.61 |
0.76 |
0.21 |
0.53 |
0.51 |
E. glauca |
0.86 |
0.67 |
0.66 |
0.33 |
0.51 |
0.57 |
E. sempervirens |
0.51 |
0.43 |
0.29 |
0.27 |
0.59 |
0.15 |
LSD0.05 |
0.1 |
0.09 |
0.09 |
0.07 |
0.09 |
0.09 |
Table 4 Effect of waterlogging on sodium, chloride, calcium and magnesium concentration in seedling parts of some timber tree species (mean of the two seasons, 1999-2000)
This increment in both Na and Cl were correlated with the reduction in root and shoot growth (Table 2). The higher tolerance species to waterlogging had the lower reduction in die growth of shoots and roots as well as the lower increase in both Na+ and Cl- concentration. These results possibility indicate that waterlogging increases the potential salt toxicity.
In this respect Gadallah49 indicated that waterlogging and salinity together increased Na+ Ca++and Cl- accumulation in shoot tissues and decreased the stability of leaf membranes to dehydration.
Nitrogen, phosphorus and potassium
The waterlogging treatment decreased the concentration of N, P and K in the leaves, stem and roots of the studied all timber tree species (Table 5). In this respect Pearson et al.50 Nasr et al.51 reported that the waterlogging treatment had no influence on N, P and K concentrations in different plant parts. A reduction in mineral uptake in waterlogged plants might be attributed to the dieback of the absorbing roots during flooding. This causes a declining content of nutrients in plants with increased age. In addition, possible decrease in 02 in the soil with increasing waterlogging may have reduced the uptake of N, P and K by the plants.
Species |
Roots |
Stems |
|
|
Leaves or phylloclade |
|
|
Waterlogged |
Control |
Waterlogged |
Control |
Waterlogged |
Control |
Nitrogen % |
||||||
E. rostrata |
1.2 |
1.4 |
1 |
1.1 |
1.9 |
1.9 |
E. citrodora |
1.3 |
1.4 |
1.2 |
1.3 |
1.8 |
1.9 |
E. cunninghamiana |
1.2 |
1.3 |
1 |
1.1 |
1.6 |
1.6 |
E. glauca |
1.2 |
1.3 |
1.1 |
1.2 |
1.7 |
1.8 |
E. sempervirens |
1.1 |
1.2 |
1.1 |
1.3 |
2 |
2.1 |
LSD0.05 |
N.S. |
N.S. |
N.S. |
N.S. |
N.S. |
N.S. |
Phosphorus % |
||||||
E. rostrata |
0.03 |
0.05 |
0.03 |
0.05 |
0.18 |
0.27 |
E. citrodora |
0.05 |
0.07 |
0.06 |
0.09 |
0.19 |
0.24 |
E. cunninghamiana |
0.08 |
0.1 |
0.1 |
0.13 |
0.2 |
0.31 |
E. glauca |
0.09 |
0.09 |
0.1 |
0.1 |
0.22 |
0.32 |
E. sempervirens |
0.31 |
0.15 |
0.08 |
0.15 |
0.25 |
0.26 |
LSD0.05 |
0.06 |
N.S. |
N.S. |
N.S. |
N.S. |
N.S. |
Potassium % |
||||||
E. rostrata |
0.41 |
0.44 |
41 |
0.44 |
0.67 |
1.44 |
E. citrodora |
0.43 |
0.47 |
0.45 |
0.48 |
0.7 |
1.38 |
E. cunninghamiana |
0.42 |
0.44 |
0.51 |
0.54 |
0.79 |
1.1 |
E. glauca |
0.43 |
0.46 |
0.52 |
0.56 |
0.75 |
1.12 |
E. sempervirens |
0.55 |
0.66 |
0.71 |
0.74 |
0.78 |
1.44 |
LSD0.05 |
0.05 |
0.12 |
0.09 |
0.08 |
0.03 |
0.16 |
Table 5 Effect of waterlogging on the concentration of nitrogen, phosphorus and potassium in seedling parts of some timber tree species (mean of the two seasons, 1999-2000)
Also, Gadallah49 reported that die waterlogging was the dominant factor affecting K+ content.
Total free amino acids
Data in Table 6 show that leaves or phylloclade of waterlogged seedlings of timber trees contained more free amino acids than un-waterlogged seedlings. The same trend also was noted with both stems and roots of waterlogged seedlings. From the same Table 6 it could be nosed that both survived of E. rostrata and E. citrodora contained the highest values of total free amino acids in their leaves, stems and roots. Moreover, the two species have higher sensitivity to waterlogging treatment (Table 1). This result may explain that amino acids increased in tissue of survived seedlings.
Species |
Total free amino acid as mg/g D.W. |
|
|
|
||
Roots |
|
Stems |
|
Leaves or phylloclade |
||
Waterlogged |
Control |
Waterlogged |
Control |
Waterlogged |
Control |
|
E. rostrata |
5.91 |
3.08 |
5.26 |
2.87 |
12.41 |
11.86 |
E. citrodora |
6.05 |
3.33 |
5.66 |
3.01 |
12.99 |
11.25 |
E. cunninghamiana |
5.52 |
2.93 |
4.39 |
2.26 |
8.52 |
8.16 |
E. glauca |
5.88 |
3.02 |
3.99 |
2.33 |
9.95 |
8.15 |
E. sempervirens |
5.39 |
3.43 |
4.39 |
2.26 |
9.4 |
9.28 |
LSD0.05 |
0.12 |
0.11 |
0.14 |
0.31 |
1.08 |
1.17 |
Table 6 Effect of waterlogging on the concentration of total free amino acid in seedling parts of some timber tree species (mean of the two seasons, 1999-2000)
In this respect Slatyer52 reported that the increase in total free amino acids may be due to the interruption of protein synthes and proteolysis which occurs in plants under stress. Bradford and Young53 noted that ethylene release from many plant species in response to flooding due to amino acid (1-aminocyclo-propan-1-carboxylic acid (ACC)), the intermediate precursor of ethylene. Moreover, Parent et al,2 reported that, most proteins induced during hypoxic conditions are enzymes involved in the establishment of this fermentative pathway. Because the plant cells need to keep a continuous ATP supply, the use of alternative electron acceptors and/or alternative pathways may be key elements of survival under soil waterlogging.
Total and free phenols
The waterlogging treatment Table 7 decreased the total and free phenols in the leaves or phylloclade of all timber tree compared with the control. In this connection Leopold54 classified the phenols compounds as growth inhibitors. Moreover, Kefeli and Kutacek,55 suggested that, plant phenols may be divided into three groups, promotive, Inhibitors and inactive.
Species |
Roots |
|
Stems |
|
Leaves or phylloclade |
|
|
Waterlogged |
Control |
Waterlogged |
Control |
Waterlogged |
Control |
|
Total phenols mg/g D.W. |
|
|
|
|
|
E. rostrata |
62.05 |
38.92 |
61.83 |
19.99 |
52.6 |
61.49 |
E. citrodora |
55.15 |
35.15 |
56.1 |
23.2 |
43.15 |
59.2 |
E. cunninghamiana |
58.53 |
29.02 |
60.86 |
29.02 |
57.77 |
84.56 |
E. glauca |
59.1 |
33.15 |
55.1 |
33.2 |
52.2 |
81.13 |
E. sempervirens |
49.4 |
27.89 |
27.26 |
20.79 |
31.44 |
38.68 |
LSD0.05 |
2.45 |
2.5 |
3.5 |
2.23 |
2.23 |
2.58 |
Free phenols as mg/g D.W. |
||||||
E. rostrata |
40.09 |
32.59 |
16.06 |
9.52 |
26.83 |
35.26 |
E. citrodora |
30.25 |
20.2 |
18.25 |
8.25 |
33.15 |
41.15 |
E. cunninghamiana |
33.89 |
24.02 |
21.5 |
9.08 |
39.23 |
57.52 |
E. glauca |
29.15 |
19.11 |
19.25 |
11.12 |
39.2 |
49.13 |
E. sempervirens |
34.6 |
11.83 |
23.68 |
8.52 |
15.39 |
16.05 |
LSD0.05 |
2.45 |
3.05 |
2.19 |
1.4 |
2.69 |
3.54 |
Table 7 Effect of waterlogging on total phenols and free phenols concentration in seedling parts of some timber tree species (mean of the two seasons, 1999-2000)
On the other hand, the total and free phenols in both stems and roots of all timber tree species were increased compared with the control. This increasing effect may be attributed to that phenolic compounds constitute a part of cellular solutes and provide a reducing environment that could be an adaptive mechanism for scavenging oxygen free radicals during stress.
Total indoles
The leaves or phylloclade, stem and roots of waterlogged seedlings of timber trees contained high values of total indoles (IAA) compared with non-waterlogged seedlings.
Yamamoto and Kozlowski56 on Acer negundo seedlings indicated that auxin accumulation at or above the flooding are essential for AR initiation and development. However, apparent auxin effects actually might be mediated by ethylene (C2H4) action, since auxin accumulation stimulates C2H4 biosynthesis.
Steven et al57 suggested that auxin was accumulated at or above the flood line of tomatoplant. They added that auxin is essential for the initiation of adventitious root primordial (ARP).
Total soluble sugars and carbohydrates
A progressive reduction in both sugar and total carbohydrate contents (Table 9) were observed in seedling leaves of timber trees as a result of waterlogging treatments. Such reduction in growth which caused by oxygen deficiency due to waterlogging could be possibly due to reduction of photosynthes, Loustalat42 and nutrient uptake by active absorption roots.43
Species |
Total indols as mg/g D.W. |
|
|
|
|
|
Roots |
|
Stems |
|
Leaves or phylloclade |
||
|
Waterlogged |
Control |
Waterlogged |
Control |
Waterlogged |
Control |
E. rostrata |
0.636 |
0.589 |
0.59 |
0.311 |
1.571 |
0.534 |
E. citrodora |
0.713 |
0.666 |
0.62 |
0.34 |
1.34 |
0.571 |
E. cunninghamiana |
0.809 |
0.319 |
1.333 |
1.114 |
1.135 |
0.637 |
E. glauca |
0.73 |
0.455 |
1.389 |
1.202 |
1.95 |
0.84 |
E. sempervirens |
1.597 |
0.743 |
0.957 |
0.889 |
1.49 |
0.9 |
LSD0.05 |
0.1 |
0.02 |
0.28 |
0.11 |
0.27 |
0.08 |
Table 8 Effect of waterlogging on total indols concentration in seedling parts of some timber tree species. (mean of the two seasons, 1999-2000)
Species |
Roots |
|
Stems |
|
Leaves or phylloclade |
|
|
Waterlogged |
Control |
Waterlogged |
Control |
Waterlogged |
Control |
Total soluble sugars as mg/g D.W. |
||||||
E. rostrata |
23.44 |
9.21 |
15.97 |
8.6 |
15.84 |
37.36 |
E. citrodora |
29.17 |
19.11 |
17.15 |
9.2 |
19.2 |
36.37 |
E. cunninghamiana |
40.03 |
16.66 |
32.39 |
18.33 |
17.33 |
26.39 |
E. glauca |
35.15 |
18.99 |
36.11 |
19.99 |
19.2 |
29.5 |
E. sempervirens |
24.98 |
16.86 |
23.41 |
7.59 |
18.3 |
31.75 |
LSD0.05 |
3.6 |
2.75 |
3.8 |
3.2 |
2.53 |
2.81 |
Total soluble carbohydrates as mg/g D.W. |
||||||
E. rostrata |
56.65 |
18.51 |
21.99 |
11.45 |
51.9 |
56.38 |
E. citrodora |
45.2 |
25.11 |
24.14 |
13.44 |
50.09 |
54.11 |
E. cunninghamiana |
63.33 |
30.1 |
67.5 |
19 |
50.08 |
60.85 |
E. glauca |
44.1 |
32.11 |
51.1 |
22.5 |
48.14 |
55.2 |
E. sempervirens |
41.85 |
22.8 |
50.68 |
17.25 |
23.36 |
50.9 |
LSD0.05 |
3.54 |
2.68 |
5.92 |
1.79 |
2.44 |
1.29 |
Table 9 Effect of waterlogging on total soluble sugars and total carbohydrates concentration in seedling parts of some timber tree species (mean of the two seasons, 1999-2000)
The plant response may also include a reduction in stomatal conductance and photosynthesis, as well as root hydraulic conductivity. These physiological modifications may in turn affect carbohydrate reserves and translocation. In fact, efficient use of carbohydrates may discriminate between tolerant and intolerant species.2
On the other hand, total soluble sugars and total carbohydrates in both stem and roots of all timber tree species were increased compared with the control. Blake and Reid58 compared three species of Eucalyptus, and found that ethylene production was high in the flood-tolerant species in response to flooding, and that the ethylene caused tissue hypertrophy (opening channels for air movement to the roots) and basal stem thickening.
Chlorophyll content
Data in Table 10 showed a progressive reduction in chlorophyll A, B and carotenoids contents in leaves of timber trees grown under waterlogging condition.
Species |
Carotenoid |
|
Chlorophyll as mg/g F.W. |
|
|
|
|
|
|
A |
|
B |
|
|
Waterlogged |
Control |
Waterlogged |
Control |
Waterlogged |
Control |
E. rostrata |
0.852 |
1.295 |
1.377 |
2.001 |
0.763 |
1.268 |
E. citrodora |
0.703 |
1.402 |
1.23 |
1.8 |
0.624 |
1.074 |
E. cunninghamiana |
0.123 |
0.686 |
0.546 |
1.072 |
0.077 |
0.577 |
E. glauca |
0.24 |
0.84 |
0.67 |
1.24 |
0.13 |
0.72 |
E. sempervirens |
0.347 |
0.692 |
1.077 |
1.319 |
0.47 |
0.815 |
LSD0.05 |
0.11 |
0.08 |
0.14 |
0.11 |
0.08 |
0.15 |
Table 10 Effect of waterlogging on chlorophyll content in the leaves/phylloclade of some timber tree species (mean of the two seasons, 1999-2000)
Gadalla49 and our results indicated that waterlogging increased the concentration of Na and Cl in leaves. This increase of both Na and Cl were the result of increase in the uptake of Na and Cl.48 Moreover, Muller and Santarius59 reported that NaCl accumulated in the leaf cells and affected lipid-synthesizing enzymes such as galactosyltransferase and cylase which are attached to the chloroplast envelop.
From the results of this study, it could be noticed that, plants that can withstand waterlogging are characterized by the following:
It is clear from this study that there are wide variations among these timber tree species in their response to waterlogging. Casuarinacunninghamiana and C. glauca were more tolerant to waterlogging than the other species, followed by Eucalyptus rostrata then Cupressussempevirens. E. citrodora was the least tolerant waterlogging species.
In general, it is recommended that, under areas where water table is high, especially in the newly reclaimed lands that needs to plant timber trees as a fences, to plant Casuarina plants, as they can tolerate high water table which causes suffocation of plant roots, and consequently death of plants.
None.
The author declares there is no conflict of interest.
©2022 El-Yazel, et al. This is an open access article distributed under the terms of the, which permits unrestricted use, distribution, and build upon your work non-commercially.