Next Article in Journal
Efficacy of Seed-Biopriming with Trichoderma spp. and Foliar Spraying of ZnO-Nanoparticles Induce Cherry Tomato Growth and Resistance to Fusarium Wilt Disease
Previous Article in Journal
Predicting the Responses of Functional Leaf Traits to Global Warming: An In Situ Temperature Manipulation Design Using Iris pumila L.
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Exploring the Impact of Salicylic Acid and Farmyard Manure on Soil Rhizospheric Properties and Cadmium Stress Alleviation in Maize (Zea mays L.)

1
Department of Agriculture, Government College University, Lahore 54000, Pakistan
2
Sustainable Development Study Center (SDSC), Government College University, Lahore 54000, Pakistan
3
Department of Agricultural Engineering, Khwaja Fareed University of Engineering and Information Technology, Rahim Yar Khan 64200, Pakistan
4
Department of Plant Production, College of Food and Agriculture Sciences, King Saud University, P.O. Box 2460, Riyadh 11451, Saudi Arabia
5
School of Biological Sciences, University of Reading, Reading RG6 6EX, UK
6
Department of Agronomy, University of Sargodha, Sargodha 40100, Pakistan
*
Authors to whom correspondence should be addressed.
Plants 2023, 12(17), 3115; https://doi.org/10.3390/plants12173115
Submission received: 27 June 2023 / Revised: 4 August 2023 / Accepted: 28 August 2023 / Published: 30 August 2023

Abstract

:
Cadmium (Cd) pollution is a growing environmental problem that negatively impacts plant growth and development, particularly in maize. In this research, the impact of farmyard manure (FYM) and salicylic acid (SA) on rhizospheric characteristics and the reduction of Cd stress in maize was examined at Government College (GC) University, Lahore, in 2022. The experiment was arranged with a randomized design, including three replications of 12 treatments (T1 = Control; T2 = Farmyard manure; T3 = Salicylic Acid; T4 = 100 mg/kg of soil Cd; T5 = 200 mg/kg of soil Cd; T6 = Farmyard manure + Salicylic acid; T7 = FYM + 100 mg/kg soil Cd; T8 = FYM + 200 mg/kg soil Cd; T9 = SA + 100 mg/kg soil Cd; T10 = SA + 200 mg/kg soil Cd; T11 = FYM + SA + 100 mg/kg soil Cd; T12 = FYM + SA + 200 mg/kg soil Cd). Results demonstrated that Cd stress negatively affected the maize plant and soil properties, but the application of SA and FYM was effective to mitigate the Cd stress up to a certain level. A reduction of 41.52%, 39.14%, and 39.94% in root length, length of the leaf, and crop growth rate was noticed, due to the Cd stress at 200 mg/kg soil, but this reduction was reduced to 18.83%, 10.35%, and 12.26%, respectively, when FYM and salicylic acid were applied as a combined application under the same stress level of Cd. The root biomass, leaf surface area, and length were all improved by SA and FYM, which enhanced the plant’s capacity to absorb nutrients and improve growth under Cd stress. In conclusion, the use of salicylic acid together with farm manure can be an effective approach to mitigate Cd stress in maize crops.

1. Introduction

Industrial and agricultural practices contribute to the accumulation of cadmium (Cd) in the soil. Plant growth and development are negatively impacted by Cd pollution, a serious environmental issue. Some of the physiological and biochemical alterations that plants undergo in response to Cd stress include a reduction in photosynthesis, increased oxidative stress, and a rebalancing of nutrients [1,2]. Zea mays L. is a staple grain crop, but its growth and productivity are severely affected by Cd stress. Therefore, it is essential to develop strategies to alleviate abiotic stress such heavy metals in maize and improve sustainable production in the agriculture sector [3,4]. In Pakistan, less maize is consumed directly by people, but its use in the feed and wet milling sectors is expanding far more quickly than anyone anticipated [5,6]. Cd-contaminated soils cannot provide the nutrients that maize requires from soil due to its high-nutrient requirements, which limits plant growth and prevents maize from reaching its maximum growth potential [7,8]. The absence of efficient production technologies and pest management methods, as well as moisture stress, low fertility, and poor cultural practices, are a few causes of the low yield [3].
Heavy metal pollution is going to increase on a dangerous level due to the escalating environmental crisis. Metropolitan areas of Pakistan are found to be contaminated with heavy metal pollution [9]. Industrial effluents contain chemicals and heavy metals that are released into water bodies without pretreatment. The groundwater, vegetation, and air have been found to be contaminated with heavy metals [10,11]. Acid rain, organic debris, and heavy metals are the main sources of soil contamination [12]. Heavy metals are particularly worrisome due to their non-degradability, high-toxicity, cumulative effects, and carcinogenicity. Heavy metals naturally occur in soil in trace levels, but their regional distribution poses problems owing to both natural and anthropogenic reasons [13,14].
Salicylic acid (SA) and farmyard manure (FYM) are potential candidates for alleviating Cd stress in plants. Salicylic acid (SA) plays a very important role in reducing metal stress such as Cr, Cd, and Cu [15]. Salicylic acid, at lower rates in plants, has the same effect as acclimatization and enhances the formation of antioxidants such as H2O2 [16]. Greater antioxidant enzyme production in plants can also improve plant growth under stress conditions [17]. Salicylic acid has the ability to mitigate a-biotic stress in crop plants by inducing positive physiological changes such as enhancing the water content in leaves, and improving nutrient uptake and the production of growth hormones [18]. SA is essential for the growth and development of plants. It can also reduce the harmful effects of Cd stress in a variety of plant species, including maize [8,14,19,20].
FYM is an organic supplement that can improve the soil’s physical, chemical, and biological qualities. FYM also provides nutrients and helps to improve the microbial activities in the soil that directly enhance the soil fertility level [21]. FYM application makes Cd less dangerous and helps plants to grow better under Cd stress [22]. FYM also enhances the organic matter contents, soil aeration, and nutrient availability in the soil [23]. Use of farmyard manure in crop production improves the soil structure, which creates a better environment for root growth. Farmyard manure also increases the soil’s ability to store water [21,24]. Farmyard manure aids in the growth of soil bacteria and their activities, which are critical for the easy availability of complex nutrients to plants [23].
Rhizospheric properties are crucial for plant growth and development. The rhizosphere is the soil region influenced by plant roots, which contains a complex microbial community that interacts with the plant [25]. Rhizospheric properties, such as soil pH, organic matter content, and microbial diversity, affect the availability of nutrients and the mobility of heavy metals in the soil. Therefore, improving the rhizospheric properties can enhance the plant’s tolerance to Cd stress [26]. Heavy metals in agricultural soils are a major environmental concern because of the longstanding toxicity and bioaccumulation of metals. Heavy metal toxicity can damage the beneficial microbes in the soil, creating water and soil pollution [27].
The high levels of Cd in maize crops slows down growth and photosynthetic activity, which lowers crop output [7]. To overcome these losses, a study is designed in which plant growth hormone “salicylic acid” and “farmyard manure” applications are used in the soil in maize crops. This study was planned with the objectives to examine the impact of SA and FYM on rhizospheric characteristics and to mitigate Cd stress in maize.

2. Materials and Methods

2.1. Crop Growth Conditions

A planned pot experiment was arranged at the Government College (GC) University Lahore to investigate the effect of farmyard manure and salicylic acid on cadmium-induced physiological damage in maize crops. The experiment was conducted with a complete randomized design (CRD), having three replications. The Punjab Seed Corporation-approved maize variety (MMRI Yellow) was used in the experiment. These seeds were planted in 2 kgs of pot soil and farmyard manure, in accordance with procedures. Salicylic acid was obtained from the university laboratory and FYM was obtained from the nearest livestock farm. Table 1 lists the characteristics of the loamy soil that was utilized for the experiment.
Maize seeds were sterilized with 70% ethanol for 2 min, followed by 5% sodium hypochlorite for 30 min, and then rinsed with distilled water before being sown and transplanted into pots. The planting was done on March 22, 2022. The pots received good irrigation and the required fertilizer dosage (120-80-60 NPK kg ha−1) was used.
The treatments applied in this experiment were as follows: T1 = control; T2 = Farmyard manure; T3 = Salicylic acid; T4 = 100 mg/kg of soil Cd; T5 = 200 mg/kg of soil Cd; T6 = Farmyard manure + Salicylic acid; T7 = FYM + 100 mg/kg soil Cd; T8 = FYM + 200 mg/kg soil Cd; T9 = SA + 100 mg/kg soil Cd; T10 = SA + 200 mg/kg soil Cd; T11 = FYM + SA + 100 mg/kg soil Cd; T12 = FYM + SA + 200 mg/kg soil Cd.

2.2. Measured Parameters

Crop physiological and growth-related parameters, such as plant height (cm), plant weight (g), leaf length (cm), number of leaves (n), chlorophyll content, and NPK uptake (%) of the maize crop was determined after 30 days of sowing. Chlorophyll contents were noticed by using the procedure described by Schagerl and Künzl [28]. The absorbance of the sample was measured at 663 and 645 nm, using a UV/visible spectrophotometer (Spectro scan 80D, Kyoto, Japan). Chlorophyll concentration a&b was determined by using the following equation and procedure, as described by Porra [29].
Ch. a (mg mL−1) = (11.64 × A663) − (2.16 × 645)
Ch. b (mg mL−1) = (−3.94 × A663) + (20.97 × A645)
To determine the relative water content (RWC) of a leaf, a 0.5 g leaf sample was kept in the dark in distilled water at 4 °C for 24 h. Subsequently, the samples were dried in an oven at 65 °C for 48 h to obtain the dry weight (in grams), which was measured and recorded. The calculation of RWC was carried out using the formula described by Barr and Weatherley [30]:
RWC (%) = [(FW − DW)/(TW − DW)] × 100.
Crop growth rate (CGR) was calculated as described by Hunt [31]:
CGR = (W2 − W1)/(t2 − t1)
Net assimilation rate (NAR) was calculated using a method reported by Hunt [26]:
TDM/LAD = NAR
where, LAD stands for leaf area duration, and TDM stands for total dry matter.
The method described by Smolander and Kitunen [32] was used to measure the dissolved organic nitrogen (DON) and carbon (DOC). In order to determine the nitrogen mineralization rate (NMIN), soil samples were taken before and after 10 days of incubation at 30 °C.

2.3. Statistical Analysis

Microsoft Excel 2019® and Statistic 8.1® were used to develop the aforementioned treatments using one-way ANOVA (Analysis of Variance) (Talhassee, USA’s Analytical Software). The dataset was compared using the least significant difference (LSD).

3. Results

3.1. Effect of Salicylic Acid (SA) and Farmyard Manure (FYM) on Root and Shoot Length of Maize Plant under Cd Stress

Data regarding root and shoot length of the maize plant were significantly affected by all studied treatments (Table 2). The highest root and shoot length (19.37 cm and 53.43 cm, respectively) was noticed in T6 when FYM and SA was applied without any Cd stress, followed by T2 (21.26 cm and 54.93 cm) when FYM was applied alone without Cd stress, and the lowest root and shoot length was noticed in T5 (11.33 cm and 44.13 cm) when Cd stress was at 200 mg/kg of soil.

3.2. Effect of SA and FYM on Plant Height of Maize under Cd Stress

Cadmium stress caused a significant reduction in maize plant height in all treatments carrying different concentrations of Cd stress. Application of farmyard manure (FYM) and salicylic acid (SA) significantly increased the plant height of maize crops. The highest plant height (77.68 cm) was observed in T6, indicating a 6% increase in growth when compared with the control, followed by T2 (76.19 cm), when FYM was applied alone without Cd stress, and the lowest plant height was noticed in T5 (55.46 cm), when Cd stress was at 200 mg/kg of soil. The application of farmyard manure mixed with salicylic acid, with Cd toxicity in the soil, significantly reduced the negative effect of Cd on the plant height of maize in all treatments (Table 2).

3.3. Effect of SA and FYM on Root, Shoot, and Plant Weight of Maize under Cd Stress

The root, shoot, and plant fresh weight were significantly affected by all studied treatments. The highest root, shoot, and plant fresh weight (10.95 g, 27.63 g, and 38.58 g) was noticed in T6, followed by T2 (10.27 g, 26.40 g, and 36.67 g), and the lowest results were noticed in T5 (3.42 g, 16.53 g, and 19.95 g). Greater decreases in root, shoot, and plant height were noticed when Cd toxicity increased. The highest plant dry weight (23.09 g) was noticed in T6 when FYM and SA were applied in combined form without any Cd stress, followed by T2 (22.38 g) when only FYM was applied without any Cd stress. The lowest plant dry weight (08.87 g) was observed in T5 when Cd stress was at 200 mg/kg of soil without FYM and SA (Table 3).

3.4. Effect of SA and FYM on Length and Number of Leaves of Maize under Cd Stress

Number of leaves and their length was significantly affected by the Cd toxicity and application of FYM and SA (Table 4). The greatest length of a leaf (17.82 cm) and number of leaves per maize plant (11.66) was noticed in T6 when there was no Cd toxicity and SA and FYM were applied in combined form, followed by T2 (16.54 cm and 10.66) when only FYM was applied, without any Cd toxicity, and the shortest length of the leaf and number of leaves was observed in T5 (08.92 cm and 1.66) when Cd toxicity was at 200 mg/kg of the soil without FYM and SA application.

3.5. Effect of SA and FYM on Chlorophyll Content of Maize under Cd Stress

The highest chlorophyll a&b (2.026 mg/g and 1.22 mg/g) was observed in T6 when SA and FYM were applied in combined form without Cd toxicity, followed by T2 (1.953 mg/g and 1.08 mg/g), when only FYM was applied, without any Cd toxicity, and the lowest chlorophyll a&b was observed in T5 (1.046 mg/g and 0.163 mg/g) when Cd toxicity was at 200 mg/kg of the soil, without FYM and SA application (Figure 1).

3.6. Effect of SA and FYM on NPK Uptake of Maize under Cd Stress

The application of farmyard manure and salicylic acid significantly increases the NPK uptake of maize and improves the plant growth conditions; thus, the average highest NPK uptake (%) was observed at T6. The NPK uptake of maize plants increased by 41%, 37%, and 32% (Figure 2). Cd stress caused a significant reduction in NPK uptake in maize plants in treatments that were carrying different concentrations of Cd alone, compared to T6 and other treatments that used Cd in combination with farm manure and salicylic acid. The lowest NPK uptake was observed at T5, carrying a concentration of 200 mg kg−1 of soil Cd, indicating a 90%, 84%, and 75% growth reduction, respectively.

3.7. Effect of SA and FYM on Crop Growth Rate (CGR) and Net Assimilation Rate (NAR) of Maize under Cd Stress

Crop growth rate is a crucial indicator because it shows how well a crop is using input materials and creating the photosynthates that the plant uses to produce an economic yield. It was found that T6 (farmyard manure and salicylic acid) had the highest crop growth rate (7.533 g/cm2/day), followed by T2 (7.323 g/cm2/day). Crop growth rate decreased under Cd stress. The lowest CGR was found in T5, followed by T4, with Cd 200 mg/kg and Cd 100 mg/kg, respectively. The highest NAR was noticed in T6 (6.20 g/cm2/day), followed by T2 (6.09 g/cm2/day), and the lowest NAR was observed in T5 (2.96 g/cm2/day) (Figure 3).

3.8. Effect of SA and FYM on Soil Organic Carbon (SOC), Dissolved Organic Nitrogen (DON), Dissolved Organic Carbon (DOC), Nitrogen Mineralization (NMIN), and Soil Respiration (SR) of Maize-Grown Soil under Cd Stress

The highest SOC (1.540 g/kg), DOC (143.8 g/kg), DON (20.643 g/kg), NMIN (72.853), and SR (25.627 g CO2/m2/day) was noticed in T6, when FYM and SA were applied in combined form, followed by F2 (SOC: 1.480 g/kg, DOC: 141.7 g/kg, DON: 19.463 g/kg, NMIN: 71.710, SR: 24.720 CO2/m2/day), when only FYM was applied, without any Cd stress, and the lowest results (SOC: 0.666 g/kg, DOC: 118.51 g/kg, DON: 9.620 g/kg, NMIN: 61.693, SR: 14.570 CO2/m2/day) were obtained in T5, when Cd stress was 200 mg/kg of soil (Table 5).

3.9. Effect of SA and FYM on Microbial Biomass Carbon (MBC), Phosphorus (MBP), and Nitrogen (MBN) of Maize-Grown Soil under Cd Stress

Data regarding the microbial biomass carbon (MBC), phosphorus (MBP), and nitrogen (MBN) show that Cd stress significantly reduces the results and that FYM application is more effective, as compared to SA, but the combined application of FYM with SA is more effective to control the negative effect of Cd toxicity (Figure 4). The highest MBC (390.49 µg g−1), MBN (298.64 µg g−1), and MBP (390.52 µg g−1) was noticed in T6 when FYM and SA were applied in combined form, followed by T2 (MBC: 380.48 µg g−1, MBN: 287.78 µg g−1, MBP: 380.27 µg g−1) when only FYM was applied, and the lowest results (MBC: 220.52 µg g−1, MBN: 201.28 µg g−1, MBP: 220.46 µg g−1) were observed in T5 when Cd stress was applied at 200 mg/kg of soil.

3.10. Effect of Farmyard Manure and Salicylic Acid on Soil pH, Mineral N, Bray P, and Exchangeable-K under Cadmium Stress Condition

Cd stress has negative effects on the soil chemical properties, but the combined application of FYM and SA is effective to control its negative impact. Soil pH, Mineral N, Bray P, and Exchangeable-K were significantly affected by all studied treatments (Table 6). The highest Soil pH (7.246), Mineral N (83.590 mg/kg), Bray P (7.846 mg/kg), and Exchangeable-K (173.58 mg/kg) was noticed in T6, followed by T2 (Soil pH: 7.136, Mineral N: 82.930 mg/kg, Bray P: 7.746 mg/kg, and Exchangeable-K: 172.52 mg/kg), and the lowest results were observed in T5 (Soil pH: 6.143, Mineral N: 68.397 mg/kg, Bray P: 6.446 mg/kg, and Exchangeable-K: 158.53 mg/kg).

4. Discussion

The use of farmyard manure combined with salicylic acid significantly improved and enhanced the vegetative growth of maize and mitigated the detrimental effect of Cd stress on maize growth. The findings highlight the beneficial properties of farmyard manure and salicylic acid in maize growth and development in environments where Cd contamination is a major problem, or even in the absence of Cd stress. Our findings are consistent with the previous studies of Sofy [33] and Bandyopadhyay [34] regarding the use of salicylic acids and farmyard manure in reducing the negative effects caused by heavy metals.
Salicylic acid can be used to diminish the negative effects of lead (Pb) toxicity on maize plants and to lessen oxidative damage [33]. According to Nasir et al. [35], applying salicylic acid, ascorbic acid, and farmyard manure significantly increased the amount of essential oils found in dragonhead by increasing the growth hormone levels in plants. In our investigation, the impacts of farmyard manure, alone, and in combination with salicylic acid, considerably improved many of the growth parameters of maize plants under a Cd-contaminated environment. The maize’s growth and yield characteristics were greatly enhanced compared to the control when FYM and SA were applied in combined form. Additionally, it was also noticed that the farmyard manure significantly enhanced the soil’s organic percentage. This increase in organic matter encourages the variety and growth of the microbial community in the soil’s rhizosphere [34,36]. Farmyard manure considerably boosted plant development indices while reducing the harmful impacts of Cd stress. Increase of root length density, root mass density, leaf area duration, and biomass help to increase nitrogen uptake, chlorophyll contents, and grain yield [34].
Salicylic acid application increased all growth features, including plant height, quantity, and area of green leaves, stem diameter, and dry weight of the stem, leaves, and entire plant. Tayyab et al. [37] found that foliar treatment of salicylic acid increased the growth parameters (plant height and dry weight) of maize seedlings under abiotic stress due to the increase of higher leaf area and growth hormone production. Zhang et al. [38] also found similar findings, such as that Cd stress lowers the root and plant height of maize in environments that suffer from soil contamination. However, using salicylic acid can enhance maize root and plant height growth under Cd stress [39]. Salicylic acid is shown to trigger the protective role from pathogens when its internal concentration is increased, which promotes a plant’s response, tolerance, and resistance to many ailments that damage plants [24]. Additionally, salicylic acid plays a variety of significant physiological tasks, including promoting protein synthesis, ion absorption, nutrition transfer, CO2 representation, ion absorption, blooming, and stomata movement [19]. Farmyard manure and salicylic acid applications were primarily responsible for this rise in plant height, shoot length, stem length, root length, and other physiological characteristics [34]. Providing macro- and micronutrients to plants, in the form of organic manures, helps to enhance the physical, chemical, and biological health of the soil [23]. Hayat et al. [40] concluded the same results for maize plant fresh and dry weight and reported that salicylic acid is found to enhance weight parameters more at a lower Cd stress level; at higher Cd stress levels, salicylic acid is found to be insufficient to mitigate the effect of Cd stress. FYM supplies vital nutrients, enhances soil structure, and lowers the amount of cadmium that is available in the soil [34]. When administered externally, salicylic acid stimulates the synthesis of antioxidants, controls hormones, and turns on defense mechanisms in maize [21,23,34]. These treatments work together to encourage root and shoot growth, which raises fresh and dry weights. Salicylic acid acts as a plant hormone that helps maize plants tolerate stress and activates defensive mechanisms [35,41]. Cd toxicity results in morphological parameter reductions and disturbances in the tissues of plants [42]. Cd stress decreases the cell division and photosynthesis in plants, which results in the reduction of root and shoot growth and plant height [43,44].
Photosynthetic characteristics are the major targets of cadmium’s harmful effects since they serve as major physiological indicators [45]. Similar outcomes for a reduction in the physiological characteristics of several plants caused by Cd stress have already been documented [46]. Cd toxicity in the soil causes harmful effects on plant cells and, ultimately, on chlorophyll, which results in Rubisco destruction and chlorophyll molecule disintegration [47]. Our results are also supported by the findings of many researchers who indicated that Cd reduced the root and shoot length which were enhanced by the application of salicylic acid [48,49,50]. Akhtar et al. [51] concluded similar results and indicated that high concentrations of Cd in agricultural soils resulted in the reduced growth of roots and shoots.
The amount of soil organic carbon (SOC) is increased by SA and FYM. FYM, an organic material, increases the soil’s carbon content, whereas SA encourages the growth of root biomass, which increases carbon sequestration [52,53]. Higher SOC levels are the result of these actions, which are crucial for soil fertility and the health of the entire ecosystem [54]. SA and FYM have a favorable impact on the soil’s dissolved organic carbon (DOC) and dissolved organic nitrogen (DON). The release of root exudates, rich in organic compounds, is induced by SA treatment, increasing the availability of DON and DOC [55]. Since FYM is a source of nitrogen, it helps to increase the level of dissolved organic nitrogen [23,33]. In the presence of cadmium stress, these variations in DON and DOC concentrations increase nutrient availability and stimulate microbial activity, resulting in improved soil fertility and nutrient cycling [33]. The release of mineral nitrogen from organic matter is boosted as a result of SA’s promotion of the synthesis of enzymes involved in nitrogen mineralization [55,56]. FYM serves as a substrate for microbial activity and furthers NMIN since it is rich in organic nitrogen [57]. Additionally, SA and FYM both contribute to increased soil respiration, indicating increased microbial activity and nutrient turnover, both of which are very effective for sustaining plant growth and soil health in the presence of cadmium stress [52,55,57].
SA and FYM can increase the soil’s microbial biomass [52,55,57]. SA stimulates root exudation by supplying a carbon-rich substrate that fosters microbial activity and growth [52]. FYM provides an ideal habitat for microorganisms to flourish because it is organic matter [33,55]. A higher number of microorganisms, which are essential for the cycling of nutrients and the health of the soil’s ecosystem, is shown by the increased microbial biomass carbon [58,59]. In order to increase the availability of phosphorus to soil microorganisms, SA treatment can improve the release of organic phosphorus compounds through root exudation and enzymatic activities [60]. For microbial growth, FYM contributes to the supply of organic nitrogen by creating a nitrogen-rich environment [28]. As a result, the microbial biomass’s phosphorus and nitrogen levels rise, showing that, under the influence of cadmium stress, nutrient availability and cycling have improved [33].
Farmyard manure is a rich source of nutrients and organic materials that can change the pH of soil [33]. When soil is exposed to Cd stress, organic matter from FYM decomposes, releasing organic acids that can help buffer the pH and keep the soil from becoming overly acidic [33,39,41]. By enhancing cation exchange capacity and improving soil structure, organic matter in FYM can also affect soil pH by minimizing the leaching of acidic chemicals [61]. Salicylic acid also indirectly affects soil pH by encouraging root development and the exudation of organic substances, which may also increase the soil’s ability to act as a buffer [62]. The mineralization of FYM’s organic nitrogen by soil bacteria results in the release of other forms of nitrogen, such as ammonium (NH4+) and nitrate (NO3-) [63]. This may make more nitrogen available for plant uptake when exposed to cadmium stress. Similar to this, salicylic acid may improve maize plants’ ability to absorb nitrogen by promoting root growth and nutrient uptake [62]. This would lead to a higher level of mineral nitrogen in the soil. Phosphorus is present in farmyard manure, and it can be gradually released through mineralization, leading to greater Bray P levels. Additionally, FYM’s organic matter helps plants gain and retain potassium from the soil [63]. Salicylic acid has the ability to increase nutrient uptake and raise nutrient usage efficiency, which may result in more phosphorus and potassium building up in the soil [62].

5. Conclusions

Cadmium (Cd) toxicity in the soil caused a significant decrease in maize crop growth and damaged the soil’s rhizospheric properties. The higher dose of Cd negatively affected maize crop growth and productivity. However, using salicylic acid (SA) and farmyard manure (FYM) resulted in effective results, in terms of improving maize crop growth and soil properties. Both SA and FYM mitigated Cd stress in maize crop with the surpass of combined application in most of the traits. Future research needs regarding the mechanisms involved in the application of salicylic acid on plants grown under different stress conditions include its fate in the environment and consequences for soil, plant, animal, and human health.

Author Contributions

Conceptualization, H.H.A. and N.S.; methodology, N.S.; software, N.S.; validation, A.R.; formal analysis, H.H.A.; investigation, N.S. and M.F.S.; resources, M.S.Z.; data curation, H.H.A., W.u.D.K. and K.J.A.; writing—original draft preparation, N.S.; writing—review and editing, M.S.Z.; W.u.D.K.; K.J.A. and M.F.S.; visualization, A.R.; supervision, H.H.A.; project administration, A.R. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by Researchers supporting project number (RSPD2023R751), King Saud University, Riyadh, Saudi Arabia.

Institutional Review Board Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

Researchers supporting project number (RSPD2023R751), King Saud University, Riyadh, Saudi Arabia is acknowledged.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Hassan, M.U.; Chattha, M.U.; Khan, I.; Chattha, M.B.; Aamer, M.; Nawaz, M.; Ali, A.; Ullah Khan, M.A.; Khan, T.A. Nickel toxicity in plants: Reasons, toxic effects, tolerance mechanisms, and remediation possibilities—A review. Environ. Sci. Pollut. Res. 2019, 26, 12673–12688. [Google Scholar] [CrossRef]
  2. Imran, K.; Seleiman, M.F.; Chattha, M.U.; Jalal, R.S.; Mahmood, F.; Hassan, F.A.; Izzet, W.; Alhammad, B.A.; Rana, R.; Hassan, M.U. Enhancing antioxidant defense system of mung bean with a salicylic acid exogenous application to mitigate cadmium toxicity. Not. Bot. Horti Agrobot. Cluj-Napoca 2021, 49, 12303. [Google Scholar]
  3. Seleiman, M.F.; Selim, S.; Jaakkola, S.; Mäkelä, P.S. Chemical composition and in vitro digestibility of whole-crop maize fertilized with synthetic fertilizer or digestate and harvested at two maturity stages in Boreal growing conditions. Agric. Food Sci. 2017, 26, 47–55. [Google Scholar] [CrossRef]
  4. Sang, L.; Zhu, G.; Xu, Y.; Sun, Z.; Zhang, Z.; Tong, H. Effects of Agricultural Large-And Medium-Sized Reservoirs on Hydrologic Processes in the Arid Shiyang River Basin, Northwest China. Water Resour. Res. 2023, 59, e2022WR033519. [Google Scholar] [CrossRef]
  5. PARC (Pakistan Agricultural Research Council). 2023. (n.d.). Home. Retrieved May 8. Available online: https://www.parc.gov.pk/ (accessed on 1 January 2023).
  6. FAO (Food and Agriculture Organization of the United Nations). 2023. (n.d.). FAO Country Profiles: Pakistan. Retrieved May 8. Available online: http://www.fao.org/countryprofiles/index/en/?iso3=PAK (accessed on 1 March 2020).
  7. Aslam, M.M.; Okal, E.J.; Waseem, M. Cadmium toxicity impacts plant growth and plant remediation strategies. Plant Growth Regul. 2023, 99, 397–412. [Google Scholar] [CrossRef]
  8. Wei, X.; Bai, X.; Wen, X.; Liu, L.; Xiong, J.; Yang, C. A large and overlooked Cd source in karst areas: The migration and origin of Cd during soil formation and erosion. Sci. Total Environ. 2023, 895, 165126. [Google Scholar] [CrossRef]
  9. Malik, R.N.; Husain, S.Z.; Nazir, I. Heavy metal contamination and accumulation in soil and wild plant species from industrial area of Islamabad, Pakistan. Pak. J. Bot. 2010, 42, 291–301. [Google Scholar]
  10. Ali, H.Q.; Yasir, M.U.; Farooq, A.; Khan, M.; Salman, M.; Waqar, M. Tanneries impact on groundwater quality: A case study of Kasur city in Pakistan. Environ. Monit. Assess. 2022, 194, 823. [Google Scholar] [CrossRef]
  11. Qiu, D.; Zhu, G.; Bhat, M.A.; Wang, L.; Liu, Y.; Sang, L.; Lin, X.; Zhang, W.; Sun, N. Water use strategy of nitraria tangutorum shrubs in ecological water delivery area of the lower inland river: Based on stable isotope data. J. Hydrol. 2023, 624, 129918. [Google Scholar] [CrossRef]
  12. Hayat, Q.; Hayat, S.; Irfan, M.; Ahmad, A. Effect of exogenous salicylic acid under changing environment: A review. Environ. Exp. Bot. 2010, 68, 14–25. [Google Scholar] [CrossRef]
  13. Rahman, Z.; Singh, V.P. The relative impact of toxic heavy metals (THMs) (arsenic (As), cadmium (Cd), chromium (Cr)(VI), mercury (Hg), and lead (Pb)) on the total environment: An overview. Environ. Monit. Assess. 2019, 191, 419. [Google Scholar] [CrossRef] [PubMed]
  14. Zhang, N.; Lu, D.; Sheng, H.; Xia, J.; Kan, P.; Yao, Z.; Chen, H.; Li, G.; Zhu, D.Z.; Liu, H. Constructed wetlands as hotspots of antibiotic resistance genes and pathogens: Evidence from metagenomic analysis in Chinese rural areas. J. Hazard. Mater. 2023, 447, 130778. [Google Scholar] [CrossRef] [PubMed]
  15. Noriega, G.; Caggiano, E.; Lecube, M.L.; Cruz, D.S.; Batlle, A.; Tomaro, M.; Balestrasse, K.B. The role of salicylic acid in the prevention of oxidative stress elicited by cadmium in soybean plants. BioMetals 2012, 25, 1155–1165. [Google Scholar] [CrossRef] [PubMed]
  16. Mateo, A.; Funck, D.; Mühlenbock, P.; Kular, B.; Mullineaux, P.M.; Karpiński, S. Controlled levels of salicylic acid are required for optimal photosynthesis and redox homeostasis. J. Exp. Bot. 2006, 57, 1795–1807. [Google Scholar] [CrossRef]
  17. Wang, L.; Li, X.; Gao, F.; Liu, Y.; Lang, S.; Wang, C.; Zhang, D. Effect of ultrasound combined with exogenous GABA treatment on polyphenolic metabolites and antioxidant activity of mung bean during germination. Ultrason. Sonochem. 2023, 94, 106311. [Google Scholar] [CrossRef]
  18. Hafez, E.H.; Seleiman, M.F. Response of barley quality traits, yield and antioxidant enzymes to water-stress and chemical inducers. Intern. J. Plant Prod. 2017, 11, 477–490. [Google Scholar]
  19. Metwally, A.; Finkemeier, I.; Georgi, M.; Dietz, K. Salicylic Acid Alleviates the Cadmium Toxicity in Barley Seedlings. Plant Phy. 2003, 132, 272–281. [Google Scholar] [CrossRef]
  20. Iqbal, N.; Fatma, M.; Gautam, H.; Sehar, Z.; Rasheed, F.; Khan, M.I.R.; Khan, N.A. Salicylic acid increases photosynthesis of drought-grown mustard plants effectively with sufficient N via regulation of ethylene, abscisic acid, and nitrogen-use efficiency. J. Plant Growth Regul. 2022, 41, 1966–1977. [Google Scholar] [CrossRef]
  21. Singh, T.B.; Ali, A.; Prasad, M.; Yadav, A.; Shrivastav, P.; Goyal, D.; Dantu, P.K. Role of Organic Fertilizers in Improving Soil Fertility. In Contaminants in Agriculture; Naeem, M., Ansari, A., Gill, S., Eds.; Springer: Cham, Switzerland, 2020. [Google Scholar] [CrossRef]
  22. Majeed, A.; Niaz, A.; Rizwan, M.; Imran, M.; Alsahli, A.A.; Alyemeni, M.N.; Ali, S. Effects of biochar, farm manure, and pressmud on mineral nutrients and cadmium availability to wheat (Triticum aestivum L.) in Cd-contaminated soil. Physiol. Plant. 2021, 173, 191–200. [Google Scholar] [CrossRef]
  23. Reddy, Y.R.; Reddy, G.H. Principle of Agronomy, 3rd ed.; Kalyani Publishers: Ludhiana, India, 2003; pp. 203–253. [Google Scholar]
  24. Kumar, V.; Singh, R.K.; Kumar, D.M. Effect of farm yard manure and Sulphur on production of Indian mustard: A review. J. Pharmacogn. Phytochem. 2019, 8, 2290–2294. [Google Scholar]
  25. Rizwan, M.; Ali, S.; Akbar, M.; Shakoor, M.B.; Mahmood, A.; Ishaque, W.; Hussain, A. Foliar application of aspartic acid lowers cadmium uptake and Cd-induced oxidative stress in rice under Cd stress. Environ. Sci. Pollut. Res. 2017, 24, 21938–21947. [Google Scholar] [CrossRef] [PubMed]
  26. Liu, S.; He, F.; Kuzyakov, Y.; Xiao, H.; Hoang, D.T.T.; Pu, S.; Razavi, B.S. Nutrients in the rhizosphere: A meta-analysis of content, availability, and influencing factors. Sci. Total Environ. 2022, 826, 153908. [Google Scholar] [CrossRef]
  27. Saxena, G.; Purchase, D.; Mulla, S.I.; Saratale, G.D.; Bharagava, R.N. Phytoremediation of Heavy Metal-Contaminated Sites: Eco-environmental Concerns, Field Studies, Sustainability Issues, and Future Prospects. In Reviews of Environmental Contamination and Toxicology; de Voogt, P., Ed.; Springer: Berlin/Heidelberg, Germany, 2019; p. 249. [Google Scholar] [CrossRef]
  28. Schagerl, M.; Künzl, G. Chlorophyll a extraction from freshwater algae—A reevaluation. Biologia 2007, 62, 270–275. [Google Scholar] [CrossRef]
  29. Porra, R.J.; Thompson, W.A.; Kriedemann, P.E. Determination of accurate extinction coefficients and simultaneous equations for assaying chlorophylls a and b extracted with four different solvents: Verification of the concentration of chlorophyll standards by atomic absorption spectroscopy. Biochim. Biophys. Acta 1989, 975, 384–394. [Google Scholar] [CrossRef]
  30. Barr, H.D.; Weatherley, P.E. A re-examination of the relative turgidity technique for estimating water deficit in leaves. Aust. J. Biol. Sci. 1962, 15, 413–428. [Google Scholar] [CrossRef]
  31. Hunt, R. Plant Growth Analysis; Arnold, E., Ed.; Institute of Terrestrial Ecology: Edinburgh, UK, 1978; pp. 26–38. [Google Scholar]
  32. Smolander, A.; Kitunen, V. Soil microbial activities and characteristics of dissolved organic C and N in relation to tree species. Soil Biol. Biochem. 2002, 34, 651–660. [Google Scholar] [CrossRef]
  33. Sofy, M.R.; Seleiman, M.F.; Alhammad, B.A.; Alharbi, B.M.; Mohamed, H.I. Minimizing adverse effects of Pb on maize plants by combined treatment with jasmonic and salicylic acids and proline. Agronomy 2020, 10, 699. [Google Scholar] [CrossRef]
  34. Bandyopadhyay, K.K.; Misra, A.K.; Ghosh, P.K.; Hati, K.M. Effect of integrated use of farmyard manure and chemical fertilizers on soil physical properties and productivity of soybean. Soil Tillage Res. 2010, 110, 115–125. [Google Scholar] [CrossRef]
  35. Nasiri, Y.; Zandi, H.; Morshedloo, M.R. Effect of salicylic acid and ascorbic acid on essential oil content and composition of dragonhead (Dracocephalum moldavica L.) under organic farming. J. Essent. Oil Bear. Pl. 2018, 21, 362–373. [Google Scholar] [CrossRef]
  36. Kashif, M.; Sang, Y.; Mo, S.; Rehman, S.U.; Khan, S.; Khan, M.R.; He, S.; Jiang, C. Deciphering the biodesulfurization pathway employing marine mangrove Bacillus aryabhattai strain NM1-A2 according to whole genome sequencing and transcriptome analyses. Genomics 2023, 115, 110635. [Google Scholar] [CrossRef]
  37. Tayyab, N.; Naz, R.; Yasmin, H.; Nosheen, A.; Keyani, R.; Sajjad, M.; Roberts, T.H. Combined seed and foliar pre-treatments with exogenous methyl jasmonate and salicylic acid mitigate drought-induced stress in maize. PLoS ONE 2020, 15, e0232269. [Google Scholar] [CrossRef]
  38. Zhang, Y.; Li, X. Salicylic acid: Biosynthesis, perception, and contributions to plant immunity. Curr. Opin. Plant Biol. 2019, 50, 29–36. [Google Scholar] [CrossRef]
  39. Fahad, S.; Hussain, S.; Matloob, A.; Khan, F.A.; Khaliq, A.; Saud, S.; Hassan, S.; Shan, D.; Khan, F.; Ullah, N.; et al. Phytohormones and plant responses to salinity stress: A review. Plant Growth Regul. 2015, 75, 391–404. [Google Scholar] [CrossRef]
  40. Hayat, S.; Khalique, G.; Wani, A.S.; Alyemeni, M.N.; Ahmad, A. Protection of growth in response to 28-homobrassinolide under the stress of cadmium and salinity in wheat. Int. J. Biol. Macromol. 2014, 64, 130–136. [Google Scholar] [CrossRef]
  41. Zaid, A.; Mohammad, F.; Fariduddin, Q. Plant growth regulators improve growth, photosynthesis, mineral nutrient and antioxidant system under cadmium stress in menthol mint (Mentha arvensis L.). Physiol. Mol. Biol. Plants. 2020, 26, 25–39. [Google Scholar] [CrossRef] [PubMed]
  42. El-Rasafi, T.; Oukarroum, A.; Haddioui, A.; Song, H.; Kwon, E.E.; Bolan, N.; Rinklebe, J. Cadmium stress in plants: A critical review of the effects, mechanisms, and tolerance strategies. Crit. Rev. Environ. Sci. Technol. 2022, 52, 675–726. [Google Scholar] [CrossRef]
  43. Farzadfar, S.; Zarinkamar, F. Morphological and anatomical responses of Matricaria chamomilla plants to cadmium and calcium. Adv. Environ. Biol. 2012, 6, 1603–1609. [Google Scholar]
  44. Ali, S.; Abbas, Z.; Seleiman, M.F.; Rizwan, M.; YAVAŞ, İ.; Alhammad, B.A.; Shami, A.; Hasanuzzaman, M.; Kalderis, D. Glycine betaine accumulation, significance and interests for heavy metal tolerance in plants. Plants 2020, 9, 896. [Google Scholar] [CrossRef]
  45. Haider, F.U.; Liqun, C.; Coulter, J.A.; Cheema, S.A.; Wu, J.; Zhang, R.; Wenjun, M.; Farooq, M. Cadmium toxicity in plants: Impacts and remediation strategies. Ecotoxicol. Environ. Saf. 2021, 211, 111887. [Google Scholar] [CrossRef]
  46. Krantev, A.; Yordanova, R.; Janda, T.; Szalai, G.; Popova, L. Treatment with salicylic acid decreases the effect of cadmium on photosynthesis in maize plants. J. Plant Physiol. 2008, 165, 920–931. [Google Scholar] [CrossRef]
  47. Chaffei, C.; Pageau, K.; Suzuki, A.; Gouia, H.; Ghorbel, M.H.; Masclaux-Daubresse, C. Cadmium toxicity induced changes in nitrogen management in Lycopersicon esculentum leading to a metabolic safeguard through an amino acid storage strategy. Plant Cell Physiol. 2004, 45, 1681–1693. [Google Scholar] [CrossRef]
  48. Rizwan, M.; Ali, S.; Abbas, T.; Zia-ur-Rehman, M.; Hannan, F.; Keller, C.; Al-Wabel, M.I.; Ok, Y.S. Cadmium minimization in wheat: A critical review. Ecotoxicol. Environ. Saf. 2016, 130, 45–53. [Google Scholar] [CrossRef] [PubMed]
  49. Seleiman, M.F.; Alotaibi, M.; Alhammad, B.; Alharbi, B.; Refay, Y.; Badawy, S. Effects of ZnO nanoparticles and biochar of rice straw and cow manure on characteristics of contaminated soil and sunflower productivity, oil quality, and heavy metals uptake. Agronomy 2020, 10, 790. [Google Scholar] [CrossRef]
  50. Pan, J.; Guan, M.; Xu, P.; Chen, M.; Cao, Z. Salicylic acid reduces cadmium (Cd) accumulation in rice (Oryza sativa L.) by regulating root cell wall composition via nitric oxide signaling. Sci. Total Environ. 2021, 797, 149202. [Google Scholar] [CrossRef] [PubMed]
  51. Akhtar, T.; Zia-ur-Rehman, M.; Naeem, A.; Nawaz, R.; Ali, S.; Murtaza, G.; Rizwan, M. Photosynthesis and growth response of maize (Zea mays L.) hybrids exposed to cadmium stress. Environ. Sci. Pollut. Res. 2017, 24, 5521–5529. [Google Scholar] [CrossRef] [PubMed]
  52. Li, W.; Wang, C.; Liu, H.; Wang, W.; Sun, R.; Li, M.; Shi, Y.; Zhu, D.; Du, W.; Ma, L.; et al. Fine root biomass and morphology in a temperate forest are influenced more by canopy water addition than by canopy nitrogen addition. Front. Ecol. Evol. 2023, 11, 1132248. [Google Scholar] [CrossRef]
  53. Zaheer, M.S.; Ali, H.H.; Iqbal, M.A.; Erinle, K.O.; Javed, T.; Iqbal, J.; Hashmi, M.I.U.; Mumtaz, M.Z.; Salama, E.A.A.; Kalaji, H.M.; et al. Cytokinin Production by Azospirillum brasilense Contributes to Increase in Growth, Yield, Antioxidant, and Physiological Systems of Wheat (Triticum aestivum L.). Front. Microbiol. 2022, 13, 886041. [Google Scholar] [CrossRef]
  54. Guo, Z.; Zhang, X.; Dungait, J.A.J.; Green, S.M.; Wen, X.; Quine, T.A. Contribution of soil microbial necromass to SOC stocks during vegetation recovery in a subtropical karst ecosystem. Sci. Total Environ. 2021, 761, 143945. [Google Scholar] [CrossRef]
  55. Meier, I.C.; Finzi, A.C.; Phillips, R.P. Root exudates increase N availability by stimulating microbial turnover of fast-cycling N pools. Soil Biol. Biochem. 2017, 106, 119–128. [Google Scholar] [CrossRef]
  56. Nie, S.; Mo, S.; Gao, T.; Yan, B.; Shen, P.; Kashif, M.; Zhang, Z.; Li, J.; Jiang, C. Coupling effects of nitrate reduction and sulfur oxidation in a subtropical marine mangrove ecosystem with Spartina alterniflora invasion. Sci. Total Environ. 2023, 862, 160930. [Google Scholar] [CrossRef]
  57. Tanaka, H.; Kyaw, K.M.; Toyota, K.; Motobayashi, T. Influence of application of rice straw, farmyard manure, and municipal biowastes on nitrogen fixation, soil microbial biomass N, and mineral N in a model paddy microcosm. Biol. Fertil. Soils. 2005, 42, 501–505. [Google Scholar] [CrossRef]
  58. Zhang, G.; Zhao, Z.; Yin, X.; Zhu, Y. Impacts of biochars on bacterial community shifts and biodegradation of antibiotics in an agricultural soil during short-term incubation. Sci. Total Environ. 2021, 771, 144751. [Google Scholar] [CrossRef]
  59. Zaheer, M.S.; Ali, H.H.; Erinle, K.O.; Wani, S.H.; Okon, O.G.; Nadeem, M.A.; Nawaz, M.; Bodlah, M.A.; Waqas, M.M.; Iqbal, J.; et al. Inoculation of Azospirillum brasilense and exogenous application of trans-zeatin riboside alleviates arsenic induced physiological damages in wheat (Triticum aestivum). Environ. Sci. Pollut. Res. 2022, 29, 33909–33919. [Google Scholar] [CrossRef]
  60. Zhao, Z.; Shi, X.; Shen, Z.; Gu, Y.; He, L.; Zhang, M.; Lu, N. Single-atom Fe nanozymes coupling with atomic clusters as superior oxidase mimics for ratiometric fluorescence detection. Chem. Eng. J. 2023, 469, 143923. [Google Scholar] [CrossRef]
  61. Saviozzi, A.; Biasci, A.; Riffaldi, R.; Levi-Minzi, R. Long-term effects of farmyard manure and sewage sludge on some soil biochemical characteristics. Biol. Fertil. Soils. 1999, 30, 100–106. [Google Scholar] [CrossRef]
  62. Joseph, B.; Jini, D.; Sujatha, S. Insight into the Role of Exogenous Salicylic Acid on Plants Grown under Salt Environment. Asian J. Crop Sci. 2020, 2, 226–235. [Google Scholar] [CrossRef]
  63. Moore, A.D.; Alva, A.K.; Collins, H.P.; Boydston, R.A. Mineralization of Nitrogen from Biofuel By-products and Animal Manures Amended to a Sandy Soil. Commun. Soil Sci. Plant Anal. 2010, 41, 1315–1326. [Google Scholar] [CrossRef]
Figure 1. Effect of salicylic acid and farmyard manure on chlorophyll a&b of maize plant. Different letters on the bar shows significant differences between treatments.
Figure 1. Effect of salicylic acid and farmyard manure on chlorophyll a&b of maize plant. Different letters on the bar shows significant differences between treatments.
Plants 12 03115 g001
Figure 2. Effect of salicylic acid and farmyard manure on NPK uptake (%) of maize plant. Different letters on the bar show significant differences between treatments.
Figure 2. Effect of salicylic acid and farmyard manure on NPK uptake (%) of maize plant. Different letters on the bar show significant differences between treatments.
Plants 12 03115 g002
Figure 3. Effect of farmyard manure and salicylic acid on crop growth rate (CGR) and net assimilation rate (NAR) under cadmium stress condition. Different letters on the bar show significant differences between treatments.
Figure 3. Effect of farmyard manure and salicylic acid on crop growth rate (CGR) and net assimilation rate (NAR) under cadmium stress condition. Different letters on the bar show significant differences between treatments.
Plants 12 03115 g003
Figure 4. Effect of farmyard manure and salicylic acid on microbial biomass carbon (MBC), phosphorus (MBP), and nitrogen (MBN) under cadmium stress condition. Different letters on the bar show significant differences between treatments.
Figure 4. Effect of farmyard manure and salicylic acid on microbial biomass carbon (MBC), phosphorus (MBP), and nitrogen (MBN) under cadmium stress condition. Different letters on the bar show significant differences between treatments.
Plants 12 03115 g004
Table 1. Characteristics of the experimental soil.
Table 1. Characteristics of the experimental soil.
Physiochemical Properties of SoilValues
Ph6.88
EC4.97 dSm−1
Organic matter4.93%
Moisture content19.01%
Concentration of nutrients
Potassium K44.49 mg L−1
Sodium Na25.01 mg L−1
Magnesium Mg22.30 mg L−1
Calcium Ca168.69 mg L−1
Soil composition percentage
Clay50%
Sand25%
Silt25%
Table 2. Effect of farmyard manure and salicylic acid on root and shoot length and plant height of maize under cadmium stress.
Table 2. Effect of farmyard manure and salicylic acid on root and shoot length and plant height of maize under cadmium stress.
TreatmentsRoot Length
(cm)
Shoot Length
(cm)
Plant Height
(cm)
T1 = Control19.37 d52.43 d71.81 d
T2 = Farmyard manure21.26 b54.93 b76.19 b
T3 = Salicylic acid20.73 c53.15 c73.88 c
T4 = Cadmium (100 mg/kg)12.43 k45.55 k57.98 k
T5 = Cadmium (200 mg/kg)11.33 l44.13 l55.46 l
T6 = Farmyard manure + Salicylic acid22.43 a55.25 a77.68 a
T7 = FYM + Cd (100 mg/kg)17.92 f50.74 f50.74 f
T8 = FYM + Cd (200 mg/kg)14.57 i47.15 i47.15 i
T9 = Salicylic acid + Cd (100 mg/kg)16.63 g49.22 g49.22 g
T10 = Salicylic acid + Cd (200 mg/kg)13.64 j46.64 j60.28 j
T11 = FYM + Salicylic acid + Cd (100 mg/kg)18.35 e51.28 e69.63 e
T12 = FYM + Salicylic acid + Cd (200 mg/kg)15.72 h48.23 h48.23 h
Means that do not have a common letter show significant differences at a 5% probability level.
Table 3. Effect of farmyard manure and salicylic acid on plant weight (g) of maize under cadmium stress.
Table 3. Effect of farmyard manure and salicylic acid on plant weight (g) of maize under cadmium stress.
TreatmentsRoot Fresh Weight (g)Shoot Fresh Weight (g)Plant Fresh Weight (g)Plant Dry Weight (g)
T1 = Control08.75 d24.43 d33.18 d19.26 d
T2 = Farmyard manure10.27 b26.40 b36.67 b22.38 b
T3 = Salicylic acid09.87 c25.26 c35.14 c21.08 c
T4 = Cadmium (100 mg/kg)03.95 k17.66 k21.61 k10.39 k
T5 = Cadmium (200 mg/kg)03.42 l16.53 l19.95 l08.87 l
T6 = Farmyard manure + Salicylic acid10.95 a27.63 a38.58 a23.09 a
T7 = FYM + Cd (100 mg/kg)06.73 f22.43 f29.16 f17.21 f
T8 = FYM + Cd (200 mg/kg)05.65 i19.56 i25.21 i13.12 i
T9 = Salicylic acid + Cd (100 mg/kg)06.45 g21.66 g28.12 g15.93 g
T10 = Salicylic acid + Cd (200 mg/kg)04.66 j18.26 j22.93 j12.10 j
T11 = FYM + Salicylic acid + Cd (100 mg/kg)07.84 e 23.73 e31.58 e18.38 e
T12 = FYM + Salicylic acid + Cd (200 mg/kg)06.14 h20.66 h26.80 h14.31 h
Means that do not have a common letter show significant differences at a 5% probability level.
Table 4. Effect of salicylic acid and farmyard manure on length of leaf (cm) and number of leaves (n) of maize.
Table 4. Effect of salicylic acid and farmyard manure on length of leaf (cm) and number of leaves (n) of maize.
TreatmentsLength of Leaf (cm)Number of Leaves (n)
T1 = Control14.65 d08.66 d
T2 = Farmyard manure16.54 b10.66 b
T3 = Salicylic acid15.94 c10.66 c
T4 = Cadmium (100 mg/kg)09.65 k01.66 k
T5 = Cadmium (200 mg/kg)08.92 l01.66 l
T6 = Farmyard manure + Salicylic acid17.82 a11.66 a
T7 = FYM + Cd (100 mg/kg)13.14 f06.66 f
T8 = FYM + Cd (200 mg/kg)10.46 i03.66 i
T9 = Salicylic acid + Cd (100 mg/kg)12.86 g05.66 g
T10 = Salicylic acid + Cd (200 mg/kg)10.12 j02.66 j
T11 = FYM + Salicylic acid + Cd (100 mg/kg)13.43 e07.66 e
T12 = FYM + Salicylic acid + Cd (200 mg/kg)13.14 h04.66 h
Means that do not have a common letter show significant differences at a 5% probability level.
Table 5. Farmyard manure and salicylic acid affect SOC, DOC, DON, NMIN, and SR under cadmium stress.
Table 5. Farmyard manure and salicylic acid affect SOC, DOC, DON, NMIN, and SR under cadmium stress.
TreatmentsSOC
(g kg−1)
DOC
(g kg−1)
DON
(g kg−1)
NMINSR
(g CO2/m2/day)
T1 = Control1.333 d137.6 d17.663 d69.740 d22.77 d
T2 = Farmyard manure1.480 b141.7 b19.463 b71.710 b24.72 b
T3 = Salicylic acid1.380 c140.7 c18.857 c70.77 c23.66 c
T4 = Cadmium (100 mg/kg)0.740 k120.3 k10.823 k62.287 k15.69 k
T5 = Cadmium (200 mg/kg)0.666 l118.5 l09.620 l61.693 l14.57 l
T6 = Farmyard manure + Salicylic acid1.540 a143.8 a20.643 a72.853 a25.62 a
T7 = FYM + Cd (100 mg/kg)1.220 f135.5 f15.857 f67.493 f20.37 f
T8 = FYM + Cd (200 mg/kg)0.933 i128.7 i12.500 i64.737 i17.62 i
T9 = Salicylic acid + Cd (100 mg/kg)1.180 g133.6 g14.773 g66.557 g19.52 g
T10 = Salicylic acid + Cd (200 mg/kg)0.856 j126.7 j11.407 j63.243 j16.53 j
T11 = FYM + Salicylic acid + Cd (100 mg/kg)1.280 e136.6 e16.467 e68.460 e21.61 e
T12 = FYM + Salicylic acid + Cd (200 mg/kg)1.080 h130.6 h13.827 h65.323 h18.52 h
Means that do not have a common letter show significant differences at a 5% probability level.
Table 6. Effect of farmyard manure and salicylic acid on Soil pH, Mineral N, Bray P, and Exchangeable-K under cadmium stress condition.
Table 6. Effect of farmyard manure and salicylic acid on Soil pH, Mineral N, Bray P, and Exchangeable-K under cadmium stress condition.
TreatmentsSoil pHMineral N
(mg kg−1)
Bray P
(mg kg−1)
Exchangeable-K
(mg kg−1)
T1 = Control6.960 d80.04 d7.526 d170.77 d
T2 = Farmyard manure7.136 b82.93 b7.746 b172.52 b
T3 = Salicylic acid7.026 c81.64 c7.640 c171.59 c
T4 = Cadmium (100 mg/kg)6.213 k69.49 k6.536 k159.23 k
T5 = Cadmium (200 mg/kg)6.143 l68.39 l6.446 l158.53 l
T6 = Farmyard manure + Salicylic acid7.246 a83.59 a7.846 a173.58 a
T7 = FYM + Cd (100 mg/kg)6.743 f78.79 f7.343 f168.53 f
T8 = FYM + Cd (200 mg/kg)6.436 i74.48 i6.960 i165.48 i
T9 = Salicylic acid + Cd (100 mg/kg)6.653 g77.60 g7.256 g167.84 g
T10 = Salicylic acid + Cd (200 mg/kg)6.340 j73.69 j6.853 j163.68 j
T11 = FYM + Salicylic acid + Cd (100 mg/kg)6.836 e79.55 e7.466 e169.75 e
T12 = FYM + Salicylic acid + Cd (200 mg/kg)6.563 h76.45 h7.153 h166.51 h
Means that do not have a common letter show significant differences at a 5% probability level.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Ali, H.H.; Shehzadi, N.; Zaheer, M.S.; Seleiman, M.F.; Aldhuwaib, K.J.; Din Khan, W.u.; Raza, A. Exploring the Impact of Salicylic Acid and Farmyard Manure on Soil Rhizospheric Properties and Cadmium Stress Alleviation in Maize (Zea mays L.). Plants 2023, 12, 3115. https://doi.org/10.3390/plants12173115

AMA Style

Ali HH, Shehzadi N, Zaheer MS, Seleiman MF, Aldhuwaib KJ, Din Khan Wu, Raza A. Exploring the Impact of Salicylic Acid and Farmyard Manure on Soil Rhizospheric Properties and Cadmium Stress Alleviation in Maize (Zea mays L.). Plants. 2023; 12(17):3115. https://doi.org/10.3390/plants12173115

Chicago/Turabian Style

Ali, Hafiz Haider, Nimra Shehzadi, Muhammad Saqlain Zaheer, Mahmoud F. Seleiman, Khalid J. Aldhuwaib, Waqas ud Din Khan, and Ali Raza. 2023. "Exploring the Impact of Salicylic Acid and Farmyard Manure on Soil Rhizospheric Properties and Cadmium Stress Alleviation in Maize (Zea mays L.)" Plants 12, no. 17: 3115. https://doi.org/10.3390/plants12173115

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop