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Natural Farming: A Sustainable Alternative to Chemical Fertilizers for Marigold (Tagetes erecta cv. Siracole) Cultivation under Mid-Hills of Himalayan Region

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05 July 2024

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08 July 2024

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Abstract
Using desi-cow waste products like Jeevamrit, natural farming is widespread among farmers for improving soil biology and productivity. Jeevamrit enhances soil chemical and microbiological properties without needing large quantities of farmyard manure (FYM), as a sustainable farming practice with a reduced carbon footprint. Despite its traditional use, Jeevamrit faces criticism due to a lack of scientific evidence. This study investigated the comparative effect of Jeevamrit and chemical fertilizers on the growth and yield of marigold cv. Siracole. In this study mother block of marigold was raised for both summer and winter seasons. The cuttings were harvested from the mother block and then kept for rooting. The rooted cuttings were planted at monthly intervals and evaluated for flowering parameters and compared to those treated with RDF (30:20:20 N, P, and K g/m2). Soil supplied with Jeevamrit enhanced bacteria (26.33%), fungi (18.92%), and actinomycetes (31.21%) populations compared over the recommended dose of fertilizers (RDF) (i.e. N:P: K @ 30:20:20 g m-2). Jeevamrit-treated plants have marketable flower yield per square meter (3.98 %) and shelf life (9.93 %) compared to RDF. The study concludes that Jeevamrit @ 2 liter m-2 is a sustainable and effective alternative to traditional fertilizers for enhancing marigold production in the mid-hills of the Himalayan region, where natural farming is already accepted.
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Subject: Biology and Life Sciences  -   Horticulture

1. Introduction

Marigold (Tagetes erecta) flower cultivation is getting increasingly popular among farmers. Marigold, belonging to the family Asteraceae, is an important commercial loose flower grown for its highly decorative and long lasting flowers. The genus Tagetes consists of approximately 40–50 species and belongs to family Asteraceae (Composite). T. erecta is popularly known as ‘Aztec Marigold’ or ‘Cravo de defunto’, originally from Mexico and widely used as an ornamental plant, natural dye and source of bioactive products, especially lutein [1]. Moreover, its flowers are used as an ingredient in salads and as a natural food colorant, since it is one of the most popular edible flowers all over the world [2]. Flowers are also used in drugs and pharmaceutical products, processed food, confectionery and in the poultry industry; one of the most important effects of the plant is their use as very valuable intercrop for controlling plant parasitic nematodes and insecticidal activity [3]. The flowers of T. erecta have been used traditionally from ancient times and have been reported as helpful to treat stomachache and intestinal diseases and as tranquillizers and anthelmintic [4].
In marigold crop, the ‘Siracole’ variety, also known as ‘Laddu Gainda’, has gained popularity among farmers due to its distinct characteristics, such as uniform flower size and bushy foliage. This marigold cultivar, originally identified in Eastern India, has proven to be highly productive and holds a significant market demand, resulting in higher prices for farmers. The propagation of ‘Siracole’ primarily relies on herbaceous stem cuttings, which ensure the production of true-to-type plants. This method allows for efficient and effective cultivation of this valuable marigold variety. In the context of scientific research, it is crucial to explore the factors contributing to the success of ‘Siracole’ and to develop sustainable cultivation practices that optimize its potential for agricultural productivity and economic benefits. This cultivar is used for cultural and social occasions as loose flowers or as garlands [5].
Meeting the projected demand for healthy and sustainable food production is a crucial challenge. In fact, increasing crop productivity by mitigating climate change and preserving agro-ecosystems is one of the significant goals of sustainable agriculture [6]. However, meeting agricultural demand by intensive use of synthetic fertilizer and pesticides has led to land degradation and environmental pollution in several agro ecosystems which has had an adverse effect on humans, animals and aquatic ecosystems [7]. Sustainable agriculture has been identified as an alternative integrated approach that could be used to solve fundamental and applied issues related to production in an ecological way [8].
Natural organic formulations induce a multifold increase in microbial population and earthworm activity which enhances nutrient availability in soil, leads to strengthening the plants resistance mechanism and increases crop productivity [9,10,11]. Among natural farming formulations, Jeevamrit is recognized as pillar of natural farming system [12]. Jeevamrit application in the soil has the efficiency to improve soil fertility and plant development. The components used to prepare liquid organic fermented manures like Jeevamrit are easily available in farm viz. cow dung, urine, legume flour and jaggery. There is presence of essential macronutrients, micro nutrients, many vitamins, essential amino acids and beneficial microorganisms in these preparations [13,14] which helps in increasing yield.
The implementation of organic amendments like Jeevamrit in marigold cultivation is crucial due to its medicinal and culinary uses, as it helps minimize chemical residues within the plant. This eco-friendly practice promotes environmentally sustainable agriculture by reducing chemical inputs, fostering a balanced ecosystem and ultimately preserving natural resources while enhancing overall agricultural sustainability. Our research aims to explore the effectiveness of Jeevamrit in marigold cultivation, focusing on its impact on reducing chemical residues and contributing to a more sustainable agricultural system.

2. Materials and Methods

The investigation was carried out in the Department of Floriculture and Landscape Architecture, Experimental Research Farm, Dr YS Parmar University of Horticulture and Forestry, Nauni, Solan, Himachal Pradesh, India during summer and winter seasons of 2023–24. The Experimental farm of the department is located in the hilly regions of Western Himalayas at an altitude of 1276 m above mean sea level having latitude of 30° 52’02” N and longitude 70°11’30”E. About 75% of the region’s average rainfall (1115 mm) occurs during the monsoon, which runs from mid-June to mid-September. Fig. 1 displays the meteorological data collected during the experiment. The experiment was laid out in RBD factorial design comprising two fertilizer treatments (T1: Jeevamrit @ 2 liter m-2 at 15 days interval and T2: RDF (recommended doses of fertilizers) N:P:K @ 30:20:20 g m-2), three harvesting flushes (H1, H2 and H3) and two seasons (S-I: summer and S-II: winter). Before the start of the experiment, chemical characteristics of soil were assessed (Table 1). Farm yard manure (FYM) @ 5 kg m-2 was used in both the treatments at the time of field preparation. RDF (recommend does of fertilizers) comprising of fertilizers i.e., urea, single super phosphate (SSP) and muriate of potash (MOP) in desired quantities were incorporated to the soil at the time of field preparation in individual plots and split dosage of urea was applied; first half at the time of field preparation and the other half in two splits, first one month of transplanting and remaining after one month of first application (late vegetative stage/early flowering). The first application of Jeevamrit was started after 30 days of planting.
Rooted cuttings of three sequential harvests were planted on 15th March, 2nd April and 13th May in summer and on 28th August, 10th September and 27th September, 2023 for studying growth and flowering parameter. There were nine rooted cuttings planted in one meter square plot at a spacing of 30 × 30 cm.

Preparation of Jeevamrit

Jeevamrit was prepared by mixing 10 kg cow dung, 10 liter cow urine, 2 kg black jaggery, 2 kg pulse (blackchickpeas) flour and a handful of soil (100 g) as microbial inoculum, and the total volume was made up to 200 liters by adding water and stir the mixture twice a day, in a clockwise manner. On the fifth day, the solution was filtered, and the filtrate was used for soil drenching. Jeevamrit @ 2 liter m-2 was administered to the soil at 15 days interval. The first treatment was made on the 20th day after planting of cuttings, and the final two applications was made at fifteen days interval after the first treatment. The filtrate was applied in pure form in 1 m2 plots. The ingredients are shown in Figure 1.
Figure 1. Elements used for preparation of Jeevamrit.
Figure 1. Elements used for preparation of Jeevamrit.
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Figure 2. Metrological data during the study period.
Figure 2. Metrological data during the study period.
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Vegetative and Flowering Attributes

For every replication and treatment, nine plants were randomly selected and all the vegetative parameters (plant height and spread) and flowering parameters (days for bud formation, number of flowers per plant and duration of flowering) were noted from each harvesting flushes (H1-H3) at proper stage of data collection. At each replication and treatment, nine plants were randomly chosen, and all the vegetative and flowering characters were measured at each harvesting flush from H1 to H3. Plant attributes that were determined included; height and spread, days to bud initiation, number of flowers produced per plant and days to flowering.

Sample Collection and Measurement of Soil Chemical Properties

The soil samples were collected from each plot to a depth of 15 cm using soil auger before sowing and after harvesting of the crop. A composite sample was created by combining soil samples from several locations. The excess soil was quartered and 500 g saved for analysis. Mixed the remaining two quarters once again and the procedure was repeated until only 500 g of soil left. To prepare soil samples for chemical analysis, they were ground and passed through a 2 mm screen, and then placed in cotton bags to dry naturally. Soil pH and EC were estimated using a conductivity meter.

Soil Chemical Properties

Soil pH and EC were estimated using a conductivity metre [15]. Organic carbon content was estimated using the Walkley-Black method [16]. To obtain actual percentage of organic carbon by Walkley and Black method, organic carbon should be multiplied by a factor 100/77 i.e., 1.3 (77 % being the average recovery factor). To determine the available nitrogen (N) in the soil, the alkaline potassium permanganate method was employed [17]. Available P was determined using the alkaline potassium permanganate method [18]. Olsen’s method for available K was determined using the standard neutral ammonium acetate method [19].

Microbiological Properties of Soil

The microbiological properties of the soil were analyzed following the completion of the trial for each treatment. The quantification of viable microbes was carried out using the nutrient agar (NA) for bacterial count, potato dextrose agar medium (PDA) for fungal count, and Kenknight and Munaier’s medium (KNM) for actinomycetes count, using the standard spread plate technique with serial dilutions [20]. The population was measured in terms of colony-forming units (cfu) per gram of soil and the assessment of microbial biomass-C was done using the soil fumigation extraction method [21]:
M B C µ g g 1 s o i l = E C F E C U F K
Where, K = 0.25 ± 0.05 (factor which represents the efciency of extraction of microbial biomass carbon) EC (F) = Total amount of extractable carbon in fumigated soil samples. EC (UF)=Total amount of extractable carbon in unfumigated soil samples. Te 2,3,5-triphenyl tetrazolium chloride (TTC) reduction method was used to estimate the dehydrogenase activity in liquid formulations [22]. Te estimation of phosphatase activity was carried out using the procedure outlined by [23].

Plant N, P and K

Plant N, P and K was assessed by [24].
B i o m a s s ( k g / h a ) = W e i g h t   o f   d r y   p l a n t × 10 , 000 A r e a   c o v e r e d   b y   t h e   p l a n t × 1000
N u t r i e n t   U p t a k e ( k g / h a ) = B i o m a s s ( k g / h a ) × N u t r i e n t   c o n t e n t ( % ) 100

Chlorophyll Content

The leaf chlorophyll was estimated by using method given by [25]. The total chlorophyll content was calculated by using the formula:
T o t a l   c h l o r o p h y l l ( m g g g 1 ) = 20.2 A 645 + 8.02 A 663 a x 1000 x w x V
V - Volume of extract made
A - Length of light in cell (usually 1 cm)
W - Weight of sample
A645 - Absorbance at 645 nm
A663 - Absorbance at 663 nm

Carotenoid Content

The concentration of total carotenoids was compared using the standard curve [26]. The following formula was used to calculate the quantity of carotenoids:
T o t a l   c a r o t e n o i d s u g 100 g = C o n c e n t r a t i o n   f r o m   s t a n d a r d   c u r v e x   d i l u t i o n   f a c t o r   x   100 w t   o f   s a m p l e

Statistical Analysis

Field experiment was conducted having three replications with nine plants in each replications and was laid out in Randomized Complete Block Design (RBD). The analysis of variance using three-way ANOVA was conducted between treatments, growing seasons and planting dates. The data recorded during the experiment was statistically analyzed by using the Microsoft-Excel and SPSS.

3. Results

3.1. Effect of Seasons Nutritional Modules and Plants Raised from the Cuttings of Different Harvesting Flushes

The maximum plant height (124.66 cm), Plant spread (62.51 cm), chlorophyll content (2.52 mg/g), minimum number of days for flowering (53.67 days), minimum days taken for flowering (53.67 days), size of flower (11.00 cm) and marketable flower yield per square meter (8.00 kg) was obtained during summer season (S-I) as compared to winter season (Table 2 and Table 3). Whereas, the shelf life of flowers was observed more (5.76 days) during winter season due to low temperature during winters reduce ethylene production and slow down the senescence process.
Nutritional modules significantly promoted the chlorophyll content (2.28 mg/g), yield of marketable flower per square meter (7.29 kg) and shelf life (5.54 days) which was observed more from the plants which were supplied with Jeevamrit. The optimum nutrients are required for plant growth and development. However, there was no significant effect of treatments on plant height, plant spread, days taken for flowering and size of flowers. Plants raised from the cuttings of first harvesting flush (H1) exhibited maximum plant height (109.65 cm), chlorophyll content (2.41 mg/g), size of flower (8.86 cm), marketable flower yield per square meter (7.27 kg) and took minimum number of days for flowering (58.54 days), while the effect of harvesting flushes on plant spread was non significant.

3.2. Interaction Effect of Seasons and Plants Raised from the Cuttings of Different Harvesting Flushes

The interactions between seasons and harvesting flushes of cuttings revealed that the cuttings taken from H2 (i.e., plants raised from second harvesting flush) and planted during summer season resulted into maximum plant height (124.88 cm), size of flower (11.17 cm) and minimum number of days taken for flowering (53.18 days), whereas chlorophyll content of leaves (2.65 mg/g) and marketable flower yield per square meter (8.11 kg) was observed maximum from first harvesting flush of cuttings (H1) (Table 2 and Table 3). The maximum shelf life (6.12 days) was recorded during winter season (S-I) from the cuttings of third flush (H3) and the interaction effect of seasons and harvesting flushes on plant spread and marketable flower yield per square meter was non significant.

3.3. Interaction Effects of Seasons and Nutritional Modules

The interactions between seasons and nutritional modules indicates that the minimum number of days taken for flowering (53.46 days) and maximum marketable flower yield per square meter (8.19 kg) was recorded in nutritional modules T1 during summer season; whereas, the interaction effect on plant height, plant spread, chlorophyll content, size of flower and shelf life was found to be non significant.

3.4. Interaction Effect of Nutritional Modules and Plants Raised from the Cuttings of Different Harvesting Flushes

The interaction between nutritional modules and harvesting flushes revealed that maximum chlorophyll content (2.55 mg/g) was observed from the plants fed with Jeevamrit (T1) and the plants produced from first harvesting flush (H1); whereas, non significant effect was observed on plant height, plant spread, days taken for flowering and shelf life.

3.5. Interaction Effect of Seasons, Nutritional Modules and Plants Raised from the Cuttings of Different Harvesting Flushes

Data presented in Table 4 shows that the maximum chlorophyll content (2.68 mg/g) from the leaves of marigold was obtained during summer season (S-I), from the plants supplied with Jeevamrit (T1) from first harvesting flush of cuttings (H1); whereas, the flowers size was observed maximum (11.20 cm) from second harvesting flush (H2).
Non significant effect of nutritional modules and plants produced from different flushes of cuttings during two different seasons was observed on plant height, plant spread, chlorophyll content of leaves, days taken for flowering, marketable flower yield per square meter and shelf life of flowers.

3.6. Effect of Seasons, Nutritional Modules and Plants Raised from the Cuttings of Different Harvesting Flushes

Summer season enhanced the total carotenoids of flower (2.36 mg/g) and viable bacteria (18.27 × 105 cfu g-1), fungal (3.87 × 103 cfu g-1), actinomycetes (2.73 × 103 cfu g-1) in soil (Table 5); whereas, available N (300.39 kg/ha), P (61.57 kg/ha) and K (417.60 kg/ha) was obtained maximum during winter season (Table 6). Low temperatures during winter reduce plant metabolism, which in turn decreases nutrient uptake. This leads to a higher availability of nutrients such as nitrogen (N), phosphorus (P), and potassium (K) in the soil.
The available N (299.81 kg/ha), P (61.82 kg/ha) and K (419.80 kg/ha) in soil was reported higher under T2 (Table 6). Application of Jeevamrit enhanced the viable bacterial (18.46 × 105 cfu g-1), fungal (3.90 x 103 cfu g-1) and actinomycetes (2.82 x 103 cfu g-1) count (Table 5).
Soil collected from the plants, raised from cuttings of third harvested flush (H3) tends to have more viable bacterial (16.19 × 105 cfu g-1), fungal (3.90 × 103 cfu g-1) and actinomycetes (2.70 × 103 cfu g-1) count. In contrast, minimum fungal count (3.17 × 103 cfu g-1) was observed in H1. Available phosphorus (59.97 kg ha-1) was noted maximum under H1; whereas, the effect of harvesting flushes on available N and K in soil was found to be non significant.

3.7. Interaction Effect of Seasons and Plants Raised from the Cuttings of Different Harvesting Flushes

The cuttings planted during summer and taken from H2 (i.e., second harvesting flush) enhanced total carotenoids in flowers (2.53 mg/g), (Table 5). The significant effect on available nitrogen was observed which was maximum under H3 during winter season; whereas, the interaction effect was non significant on bacteria, fungus, actinomycetes, available P and K.

3.8. Interaction Effects of Seasons and Nutritional Modules

Total carotenoid content in flowers (2.48 mg/g) was significantly enhanced by application of Jeevamrit during summer season, while available nitrogen (306.74 kg ha-1) and potassium (423.90 kg ha-1) was observed maximum under T2 during winter season. The interaction effect was non significant on bacteria, fungus, actinomycetes and available P.

3.9. Interaction Effect of Treatments and Plants Raised from the Cuttings of Different Harvesting Flushes

The effect of treatments and harvesting flushes on total carotenoids, bacterial, fungal, actinomycetes count (Table 5) and available N, P, K (Table 6) was non significant.

3.10. Interaction Effect of Seasons, Nutritional Modules and Plants Raised from the Cuttings of Different Harvesting Flushes

The more carotenoid content (2.70) was observed (Table 7) in the flowers from those plants which were treated with Jeevamrit at second harvesting flush during summer (T1 × H2 × S-I). Non significant results were obtained on bacteria, fungus, actinomycetes and, available N, P, K.

3.11. Effect of Season Nutritional Modules and Plants Raised from the Cuttings of Different Harvesting Flushes

Cuttings planted during summer season (Table 8 and Table 9) resulted into more uptake of N (17.21 kg ha -1), P (9.32 kg ha -1) and K (14.71 kg ha -1) over winter season. Soil collected during Season-II (winter season) exhibited more organic carbon (1.01 %) over Season-II (0.87) i.e., summer season. As the higher temperature promotes microbial activity in soil resulting into release nutrients and make them in more available form to the plant.
Plants of marigold drenched with Jeevamrit enhanced the uptake of N (16.62 kg ha -1), P (6.87 kg ha -1) and K (13.19 kg ha -1) similar effect of Jeevamrit was observed on organic carbon (1.00 %) in soil. The minimum values of pH (6.27) and EC (0.41 dS m-2) was observed (Table 9) from the soil samples collected from the plots treated with Jeevamrit.
Higher uptake (Table 8) of N (15.92 kg ha -1), P (5.71 kg ha -1) and K (13.10 kg ha -1) by plant was noted under H1; whereas, lesser electrical conductivity (0.57 dS m-1) and more organic carbon (0.96 %) from the soil samples was observed under H2 (Table 9).

3.12. Interaction Effects of Seasons and Nutritional Modules

The interaction between season and nutritional modules (Table 8 and Table 9) revealed that the maximum N uptake (18.73 kg ha -1), P (9.32 kg ha -1), K (15.81 kg ha -1) and organic carbon (0.93 %) in soil samples was observed when plants were drenched with Jeevamrit (T1) during summer season (S-I).

3.13. Interaction Effect of Seasons and Plants Raised from the Cuttings of Different Harvesting Flushes

The interaction between season and harvesting flushes revealed that the maximum N (18.33 kg ha -1), P (8.80 kg ha -1) and K (15.15 kg ha -1) uptake of plant was observed from third harvesting flush of cuttings (H3) during summer season (Table 8). Interaction effect of nutritional modules and plants raised from the cuttings of different harvesting flushes on K uptake, pH, OC were found to be non significant.

3.14. Interaction Effect of Nutritional Modules and Plants Raised from the Cuttings of Different Harvesting Flushes

From Table 8 the maximum uptake of N (17.31 kg ha -1) and P (6.64 kg ha -1) was observed in interaction T1 × H1 whereas, the minimum electrical conductivity (0.40 %) of soil was observed from the samples collected from the plots which were supplied with Jeevamrit (T1) during second harvesting flush (H2).

3.15. Interaction Effect of Seasons, Nutritional Modules and Plants Raised from the Cuttings of Different Harvesting Flushes

Data presented in Table 10 shows the significant effect of seasons, nutritional modules and harvesting flushes on N (19.45 kg ha-1), P (11.09 kg ha-1) and K (16.34 kg ha-1) content of plant samples. The maximum N, P and K was observed from the plant samples collected from the plots supplied with Jeevamrit (T1), plants produced from third harvesting flush of cuttings (H3), during summer season (S-I).

4. Discussion

Data presented in Table 2, Table 3 and Table 4 shows that the marketable flower yield, plant spread and plant spread were equivalent in T1 (Jeevamrit @ 2 L/m²) and RDF (recommended dose of fertilizer N:P:K @ 30:20:20 g/m2) [27]. Observed that the application of organic manures in broccoli enhanced the soil properties, resulting into better nutrient absorption and more yield. Chandrakala et al. (2011) [28] suggested that organic fertilizers might increase nutrient availability in soil during the early stages of plant growth and release native soil nutrients at later stages. They attributed the increase the number of fruits per plant due to the presence of IAA, GA3 and other nutrients in fermented liquid manures like Jeevamrit, which improve the yield of plant [29]. Revealed that foliar application of organic manures with soil application stimulates growth regulator production in plant cells and resulted into enhanced plant growth. According to [30], yield depends on the morphology of the plant; including vegetative characteristics i.e., plant height, leaf area index, number of branches and leaves. They reported increased vigor in capsicum with the use of Jeevamrit, resulting in better distribution of nutrients to different plant parts, which ultimately increased yield.
Table 3 and Table 4 also shows that flowers harvested from plants which were treated with Jeevamrit had a longer shelf life compared to those treated with chemical fertilizers. Natural farming systems increases plant immunity and disease resistance, resulting in 50 % fewer mycotoxins in crops resulting into more shelf life [31].
In the present study on the marigold crop found that the application of Jeevamrit resulted in better foliage with dark green leaves, indicating higher chlorophyll content (Table 2 and Table 4). Application of Jeevamrit enhances photosynthate production and their translocation to vegetative buds and fruits [32]. Similarly, a study on sweet basil under NaCl-induced salt stress they concluded that plants supplied with Jeevamrit increases the chlorophyll ‘a’, ‘b’ and total carotenoids. These findings suggest that the organic liquid formulation i.e., Jeevamrit is effective in promoting optimum plant growth and development [33].
In Table 4, more plant height, plant spread, marketable flowers per square meter, flower size, and yield of marketable flowers per square meter are observed in summer plantings. More chlorophyll content was also observed in summer planted crop when supplied with Jeevamrit (Table 2 and Table 4). This can be attributed to increased vegetative growth in summer-planted crops, likely due to higher photosynthetic rates and carbon assimilation during the summer [34]. Nitrogen is crucial for the biosynthesis of proteins, chlorophyll and other organic compounds of plants, and it is a primary component of the energy molecules ATP and ADP [35]. Phosphorus affects photosynthesis, synthesis of protein and nucleic acid, membrane transport and cytoplasmic streaming. Potassium aids in osmotic and ionic regulation and activates enzymes involved in protein and carbohydrate metabolism. Similar results were reported by [36] on growth characteristics of soybean.
In Table 5 and Table 7, the total carotenoids were higher in flowers from plants treated with amendments from animal wastes (FYM + Jeevamrit) over those treated with chemical fertilizers. This is due to improved nutritional status of plant, more specifically the higher availability of nitrogen is an crucial part of carotenoids, chlorophyll molecules, amino acids, nucleic acids, phosphatides, alkaloids, enzymes, hormones and vitamins [37], experienced by the plants in the Jeevamrit treatment. More carotenoid content was observed during summer season due to the more sunlight and high temperature which enhances the biosynthesis resulting into increasing the carotenoid concentrations. Present study got support from the findings of [38].
Microbes present in the rhizosphere produce various metabolites, bioactive compounds, enzymes and phytohormones (i.e., cellulase, catalase, siderophores, indole acetic acid) which not only enhance the microbial community but also promote the plant growth and improve soil fertility [39,40]. Additionally, the secretion of enzymes, antibiotics and various organic compounds suppresses phytopathogens and neutralizes toxic compounds and microbes [40]. Diverse and rich microbes are crucial for maintaining soil bioavailability. Our study shows that Jeevamrit helps to improve the abundance and diversity of soil microflora (Table 5). The bacteria and fungi identified from the natural farming field exhibit strong plant-growth promoting properties, indicating their role in enhancing soil chemistry and biology. Our study also suggest that the plants supplied with organic amendments makes nutrients in more available form resulting into improved nutrient uptake of plant by plants [41].
The significantly highest available potassium (K) under T2 may be due to the acidifying action of FYM on applied K during decomposition, making more K available by reducing K fixation (Table 6). The higher available K content in the soil under T2 may be due to the fact that, with time, the K held in the interlayer spaces of minerals becomes mobile through the decomposition of applied FYM. Similar results were observed by [42] in potato and jute cultivation.
Natural farming has been reported to enhance soil microbial, physical and chemical properties [43,44,45,46,47], supporting our study [48]. Demonstrated that organic manure based products not only boost bacterial populations but also enhance nutrient uptake by plant. Proteobacteria and actinobacteria play crucial roles in nitrogen fixation, carbon recycling, disease and pathogen suppression, soil remediation, phosphate dissolution, and many other biological activities that directly or indirectly improve plant growth [49,50,51,52,53,54]. Our findings confirm that Jeevamrit application enhances bacterial abundance and boosts the soil ecosystem.
In Table 6, the increase in available nitrogen (N) in the FYM amended plot (T2) can be attributed to the accumulation of higher organic N due to the addition of more organic carbon to the soil [55]. This might be due to the residual effects of fertilizers and manures and the increase of inorganic N fractions in the soil due to biochemical degradation and mineralization. The addition of FYM with inorganic fertilizers under T2 would have acidified the soil by releasing H+ ions, thereby increasing phosphorus (P) availability [56].
From Table 8 and Table 10, the highest NPK content in the leaves of marigold plant with the incorporation of organic manure and Jeevamrit may be due to the proper nutrition of the crop and the enhanced efficiency of organic amendments. These findings align with those of [57] in onion.
Higher temperature extends the growing season of plant and enhances mineralization resulting into increase available nutrients to plants and increase the uptake [58]. Higher temperature promotes microbial activity in consequently release nutrients and make them more available and decrease nutrient restriction [59,60].
The increased levels of organic carbon (Table 9) might be attributed to a decrease in bulk density, likely due to the application of Jeevamrit [61]. Similar results were reported by Sharma & Chadak, who found that incorporating Jeevamrit and farmyard manure not only boosted the soil’s nutritional content but also influenced the composition of the microbial community, enhanced soil structure, water-holding capacity and soil organic carbon [62].

5. Conclusions

In summary, it can be concluded that the cuttings planted during the summer season enhanced plant height (124.66 cm), plant spread (62.51 cm), chlorophyll content (2.52 mg g-1), yield of marketable flower per square meter (8.00 kg), flower size (11.00 cm). Nutritional module T1 i.e., Jeevamrit @ 2 liter m-2 enhanced uptake of N (16.62 kg ha-1), P (6.87 kg ha-1), K (13.19 kg ha-1) by plant, resulting into higher yield of marketable flower per square meter (7.29 kg) over the recommended dose of fertilizers. The plants produced from the first flush of cuttings taken from the mother block effectively increased marketable flower yield per square meter (7.27 kg). From the present findings, it can be concluded that drench application of Jeevamrit @ 2 liter m-² at an interval of 15-day can be recommended as an alternative to chemical fertilizers for quality flower production in marigold cultivar ‘Siracole’.

Author Contributions

Conceptualization, B.K.; methodology, N.K. and B.K.; formal analysis, R.B., M.K., P.T. and A.H.S.; investigation, B.K. and S.B.; data curation, N.K. and S.B.; writing-original draft preparation, N.K., R.B., and M.K.; writing—review and editing, B.K., S.B, P.T.; visualization, B.K. and S.B.,; supervision, B.K. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding

Data Availability Statement

The data that support the findings of this study are available from https://www.mdpi.com/ethics. The data were analyzed and generated during the study and are available for public access.

Acknowledgments

We would like to express our gratitude to the people and organization that helped us finish this research.

Conflicts of Interest

The authors declare no conflicts of interest

References

  1. Pérez-Ortega, G.; Angeles-López, G.E.; Argueta-Villamar, A.; González-Trujano, M.E. Preclinical Evidence of the Anxiolytic and Sedative-like Activities of Tagetes Erecta L. Reinforces Its Ethnobotanical Approach. Biomed. Pharmacother. 2017, 93, 383–390. [Google Scholar] [CrossRef] [PubMed]
  2. Moliner, C.; Barros, L.; Dias, M.I.; López, V.; Langa, E.; Ferreira, I.C.F.R.; Gómez-Rincón, C. Edible Flowers of Tagetes Erecta L. as Functional Ingredients: Phenolic Composition, Antioxidant and Protective Effects on Caenorhabditis Elegans. Nutrients 2018, 10, 2002. [Google Scholar] [CrossRef] [PubMed]
  3. Bakshi, L.; Ghosh, R. Marigold biopesticide as an alternative to conventional chemical pesticides. Journal of Advanced Scientific Research 2022, 13, 26–33. [Google Scholar] [CrossRef]
  4. Meurer, M.; de Oliveira, B.M.M.; Cury, B.J.; Jerônimo, D.T.; Venzon, L.; França, T.C.S.; Mariott, M.; Silva-Nunes, R.; Santos, A.C.; Roman-Junior, W.A.; et al. Extract of Tagetes Erecta L., a Medicinal Plant Rich in Lutein, Promotes Gastric Healing and Reduces Ulcer Recurrence in Rodents. Journal of Ethnopharmacology 2022, 293, 115258. [Google Scholar] [CrossRef] [PubMed]
  5. Panda, S.; Grihalakshmi, K.; Barman, S.; Pramita Mishra, P. Production and marketing of marigold in Gajapati district, Odisha, India : challenges and opportunities. Plant Archives 2022, 22, 292–296. [Google Scholar] [CrossRef]
  6. Timsina, J. Can Organic Sources of Nutrients Increase Crop Yields to Meet Global Food Demand? Agronomy 2018, 8, 214. [Google Scholar] [CrossRef]
  7. Sr, D. Natural Farming: Eco-Friendly and Sustainable? Agrotechnology 2016, 05. [Google Scholar] [CrossRef]
  8. Lal, R. Soils and Sustainable Agriculture. A Review. Agronomy for Sustainable Development 2008, 28, 57–64. [Google Scholar] [CrossRef]
  9. Ray, P.; Lakshmanan, V.; Labbé, J.L.; Craven, K.D. Microbe to Microbiome: A Paradigm Shift in the Application of Microorganisms for Sustainable Agriculture. Frontiers in Microbiology 2020, 11. [Google Scholar] [CrossRef]
  10. Maduka, C.M.; Chukwuma Great, U. Comparative Analysis of the Effect of Some Organic Manure on Soil Microorganisms. Bionatura 2019, 4, 922–925. [Google Scholar] [CrossRef]
  11. Patel, J.S.; Kumar, G.; Bajpai, R.; Teli, B.; Rashid, M.; Sarma, B.K. PGPR Formulations and Application in the Management of Pulse Crop Health. In Biofertilizers; Elsevier, 2021, 239–251.
  12. Bharadwaj, K. Influence of ZBNF components on the growth and yield of Wheat in combination with FYM, Biofertilizer and Nitrogen. International Journal of Creative Research Thoughts 2021, 9, 2320–2882. [Google Scholar]
  13. Sreenivasa, M.N.; Naik, N.; Bhat, S.N. Beneficial traits of microbial isolates of organic liquid manures, P 223-224. In: Reddy MS Desai S Sayyed RZ Sarma YR Rao VK Reddy BC Reddy KRK Podile AR Kloepper JW (eds). Plant Growth Promotion by Rhizobacteria for Sustaianble Agriculture. Scientific publisher Jodhpur. India 2009. ISBN 9789387741096.
  14. C., S. Panchgavya: Boon to Organic Farming. IBDC Publishers, 2007; ISBN 8181891643.
  15. Jackson, M.L. Soil Chemical Analysis: Advanced Course : A Manual of Methods Useful for Instruction and Research in Soil Chemistry, Physical Chemistry of Soils, Soil Fertility, and Soil Genesis; UW-Madison Libraries Parallel Press, 2005; ISBN 1893311473.
  16. Walkley, A.; Black, I.A. An examination of the Degtjareff method for determining soil organic matter, and a proposed modification of the chromic acid titration method. Soil Science 1934, 37, 29–38. [Google Scholar] [CrossRef]
  17. Subbiah, B.V.; Asija, G.L. Rapid method for estimation of available nitrogen in soils, Current Science 1956, 25, 259–260. 25.
  18. Merwin, H.D.; Peech, M. Exchangeability of Soil Potassium in the Sand, Silt, and Clay Fractions as Influenced by the Nature of the Complementary Exchangeable Cation. Soil Science Society of America Journal 1951, 15, 125–128. [Google Scholar] [CrossRef]
  19. Olsen, S.R. , 1954. Estimation of available phosphorus in soils by extraction with sodium bicarbonate (No. 939). US Department of Agriculture.
  20. 16. Rao, N.S.S. 16. Rao, N.S.S. Soil Microorganisms and Plant Growth, 3: ISBN STANFORD, 3610. [Google Scholar]
  21. Vance, E.D.; Brookes, P.C.; Jenkinson, D.S. An Extraction Method for Measuring Soil Microbial Biomass C. Soil Biology and Biochemistry 1987, 19, 703–707. [Google Scholar] [CrossRef]
  22. 18. Casida, L.E., JR.; Klein, D.A.; Santoro, T. SOIL DEHYDROGENASE ACTIVITY. Soil Science 1964, 98, 371–376. [Google Scholar] [CrossRef]
  23. 19. Tabatabai, M.A.; Bremner, J.M. Use of P-Nitrophenyl Phosphate for Assay of Soil Phosphatase Activity. Soil Biology and Biochemistry 1969, 1, 301–307. [Google Scholar] [CrossRef]
  24. 20. Tandon, H.L.S.; Organisation, F.D. 20. Tandon, H.L.S.; Organisation, F.D. and C. Secondary and Micronutrient Recommendations for Soils and Crops: A Guidebook, 8185. [Google Scholar]
  25. Hiscox, J.D.; Israelstam, G.F. A Method for the Extraction of Chlorophyll from Leaf Tissue without Maceration. Canadian Journal of Botany 1979, 57, 1332–1334. [Google Scholar] [CrossRef]
  26. Ranganna, S. Hand Book of Analysis And Quality Control For Fruit And Vegetable Products; 2005; ISBN OCLC:770201996.
  27. Dash, S.K.; Sahu, G.S.; Das, S.; Sarkar, S.; Pathak, M. Effect of Integrated Nutrient Management on Yield, Yield Attributes and Economics of Broccoli. International Journal of Current Microbiology and Applied Sciences 2019, 8, 3254–3258. [Google Scholar] [CrossRef]
  28. Chandrakala, M. 2008. Effect of FYM and Fermented Liquid Manures on Yield and Quality of Chilli (Capsicum annuum L.), M.Sc. Thesis, Department of Soil Science and Agricultural Chemistry, University of Agricultural Sciences, Dharwad, Karnataka.
  29. Somasundaram, E. 2003. Evaluation of Organic Sources of Nutrients and Panchagavya Spray on the Growth and Productivity of Maize-Sunflower-Greengram System. Tamil Nadu Agricultural University, Coimbatore.
  30. Boraiah, B.; Devakumar, N.; Shubha, S.; Palanna, K.B. Effect of Panchagavya, Jeevamrutha and Cow Urine on Beneficial Microorganisms and Yield of Capsicum (Capsicum Annuum L. Var. Grossum). International Journal of Current Microbiology and Applied Sciences 2017, 6, 3226–3234. [Google Scholar] [CrossRef]
  31. Siddique, S.; Hamid, M.; Tariq, A.; Kazi, A.G. Organic Farming: The Return to Nature. In Improvement of Crops in the Era of Climatic Changes; Springer New York: New York, NY, 2014; pp. 249–281. [Google Scholar]
  32. Gangadhar, K.; Devakumar, N.; V. ; G, L. Growth, Yield and Quality Parameters of Chilli (Capsicum Annuum L.) as Influenced by Application of Different Organic Manures and Decomposers. International Journal of Chemical Studies 2020, 8, 473–482. [Google Scholar] [CrossRef]
  33. Singh, A.S.; Lal, E.P. Impact of organic liquid formulation, Jeevamrutha on photosynthetic pigments of Ocimum basilicum A L. (Sweet Basil) under NaCl induced salinity stress. Plant Archives 2019, 19, 1997–2001. [Google Scholar]
  34. Yu, J.-Y.; Chen, C.-M. Chlorophyll Fluorescence Parameter as a Tool in Selecting Heat-Tolerant Summer-Flowering Chrysanthemum (Dendranthema × grandiflorum). HortScience 2023, 58, 1603–1609. [Google Scholar] [CrossRef]
  35. Sarwar, M.; Patra, J.K.; Ali, A.; Maqbool, M.; Arshad, M.I. Effect of Compost and NPK Fertilizer on Improving Biochemical and Antioxidant Properties of Moringa Oleifera. South African Journal of Botany 2020, 129, 62–66. [Google Scholar] [CrossRef]
  36. Yadav, P.; Sharma, S.K.; Choudhary, R.; Jat, G.; Upadhayay, B.; Sisodia, S.S.; Athnere, S. Effect of different Natural Farming Practices on NPK and Chlorophyll Content of Cowpea (Vigna unguiculata L.) under Sub humid Southern plains of Rajasthan. In Biological Forum–An International Journal 2023, 15, 289–293. [Google Scholar]
  37. Libutti, A.; Trotta, V.; Rivelli, A. Biochar, Vermicompost, and Compost as Soil Organic Amendments: Influence on Growth Parameters, Nitrate and Chlorophyll Content of Swiss Chard (Beta Vulgaris L. Var. Cycla). Agronomy 2020, 10, 346. [Google Scholar] [CrossRef]
  38. de Azevedo, C.H.; Rodriguez-Amaya, D.B. Carotenoid Composition of Kale as Influenced by Maturity, Season and Minimal Processing. Journal of the Science of Food and Agriculture 2004, 85, 591–597. [Google Scholar] [CrossRef]
  39. Reinhold-Hurek, B.; Bünger, W.; Burbano, C.S.; Sabale, M.; Hurek, T. Roots Shaping Their Microbiome: Global Hotspots for Microbial Activity. Annual Review of Phytopathology 2015, 53, 403–424. [Google Scholar] [CrossRef] [PubMed]
  40. Yan, H.; Zhu, L.; Wang, Y.; Zhang, S.; Liu, P.; Dong, T.T.X.; Wu, Q.; Duan, J.-A. Comparative Metagenomics Analysis of the Rhizosphere Microbiota Influence on Radix Angelica Sinensis in Different Growth Soil Environments in China. Food Science and Technology 2021, 41, 775–784. [Google Scholar] [CrossRef]
  41. Gamage, A.; Gangahagedara, R.; Gamage, J.; Jayasinghe, N.; Kodikara, N.; Suraweera, P.; Merah, O. Role of Organic Farming for Achieving Sustainability in Agriculture. Farming System 2023, 1, 100005. [Google Scholar] [CrossRef]
  42. B. K. Mohapatra; S. MAm; M.R. Satapathy Integrated Nutrient Management in Potato (Solanum Tuberosum)-Jute (Corchorus Olitorius) Sequence. Indian Journal of Agronomy 2001, 53, 205–209. [Google Scholar] [CrossRef]
  43. Shang, L.; Wan, L.; Zhou, X.; Li, S.; Li, X. Effects of Organic Fertilizer on Soil Nutrient Status, Enzyme Activity, and Bacterial Community Diversity in Leymus Chinensis Steppe in Inner Mongolia, China. PLOS ONE 2020, 15, e0240559. [Google Scholar] [CrossRef] [PubMed]
  44. Sharma, N.; Kumar, J.; Abedin, Md.M.; Sahoo, D.; Pandey, A.; Rai, A.K.; Singh, S.P. Metagenomics Revealing Molecular Profiling of Community Structure and Metabolic Pathways in Natural Hot Springs of the Sikkim Himalaya. BMC Microbiology 2020, 20. [Google Scholar] [CrossRef] [PubMed]
  45. Wang, Q.; Jiang, X.; Guan, D.; Wei, D.; Zhao, B.; Ma, M.; Chen, S.; Li, L.; Cao, F.; Li, J. Long-Term Fertilization Changes Bacterial Diversity and Bacterial Communities in the Maize Rhizosphere of Chinese Mollisols. Applied Soil Ecology 2018, 125, 88–96. [Google Scholar] [CrossRef]
  46. Kopecky, J.; Kyselkova, M.; Omelka, M.; Cermak, L.; Novotna, J.; Grundmann, G.L.; Moënne-Loccoz, Y.; Sagova-Mareckova, M. Actinobacterial Community Dominated by a Distinct Clade in Acidic Soil of a Waterlogged Deciduous Forest. FEMS Microbiology Ecology 2011, 78, 386–394. [Google Scholar] [CrossRef] [PubMed]
  47. Bebber, D.P.; Richards, V.R. A Meta-Analysis of the Effect of Organic and Mineral Fertilizers on Soil Microbial Diversity. Applied Soil Ecology 2022, 175, 104450. [Google Scholar] [CrossRef]
  48. Hartmann, M.; Frey, B.; Mayer, J.; Mäder, P.; Widmer, F. Distinct Soil Microbial Diversity under Long-Term Organic and Conventional Farming. The ISME Journal 2014, 9, 1177–1194. [Google Scholar] [CrossRef] [PubMed]
  49. Maougal, R.T.; Kechid, M.; Ladjabi, C.; Djekoun, A. PGPR Characteristics of Rhizospheric Bacteria to Understand the Mechanisms of Faba Bean Growth. In Proceedings of the the 1st International Electronic Conference on Microbiology, MDPI: Basel Switzerland, January 11 2021. [Google Scholar]
  50. Kumar, R.; Kumar, S.; Yashavanth, B.S.; Meena, P.C.; Indoria, A.; Kundu, S.; Manjunath, M. Adoption of Natural Farming and Its Effect on Crop Yield and Farmers’ Livelihood in India; ICAR: New Delhi, India, 2020. [Google Scholar]
  51. Muenster, D. Performing Alternative Agriculture: Critique and Recuperation in Zero Budget Natural Farming, South India. Journal of Political Ecology 2018, 25. [Google Scholar] [CrossRef]
  52. Dinesh, R.; Anandaraj, M.; Kumar, A.; Bini, Y.K.; Subila, K.P.; Aravind, R. Isolation, Characterization, and Evaluation of Multi-Trait Plant Growth Promoting Rhizobacteria for Their Growth Promoting and Disease Suppressing Effects on Ginger. Microbiological Research 2015, 173, 34–43. [Google Scholar] [CrossRef] [PubMed]
  53. Sharma, S.B. Trend Setting Impacts of Organic Matter on Soil Physico-Chemical Properties in Traditional Vis -a- Vis Chemical-Based Amendment Practices. PLOS Sustainability and Transformation 2022, 1, e0000007. [Google Scholar] [CrossRef]
  54. Deluz, C.; Nussbaum, M.; Sauzet, O.; Gondret, K.; Boivin, P. Evaluation of the Potential for Soil Organic Carbon Content Monitoring With Farmers. Frontiers in Environmental Science 2020, 8. [Google Scholar] [CrossRef]
  55. Choudhary, M.; Panday, S.C.; Meena, V.S.; Singh, S.; Yadav, R.P.; Mahanta, D.; Mondal, T.; Mishra, P.K.; Bisht, J.K.; Pattanayak, A. Long-Term Effects of Organic Manure and Inorganic Fertilization on Sustainability and Chemical Soil Quality Indicators of Soybean-Wheat Cropping System in the Indian Mid-Himalayas. Agriculture, Ecosystems & Environment 2018, 257, 38–46. [Google Scholar] [CrossRef]
  56. Adnan, M.; Fahad, S.; Khan, I.A.; Saeed, M.; Ihsan, M.Z.; Saud, S.; Riaz, M.; Wang, D.; Wu, C. Integration of Poultry Manure and Phosphate Solubilizing Bacteria Improved Availability of Ca Bound P in Calcareous Soils. 3 Biotech 2019, 9. [Google Scholar] [CrossRef] [PubMed]
  57. Jayathilake, P.K.; Reddy, I.P.; Srihari, D.; Neeraja, R. Reddy, Effect of nutrient management on growth, yield and yield attributes on rabi onion (Allium cepa L.). Vegetable Science 2002, 29, 184–85. [Google Scholar]
  58. Arndal, M.F.; Merrild, M.P.; Michelsen, A.; Schmidt, I.K.; Mikkelsen, T.N.; Beier, C. Net Root Growth and Nutrient Acquisition in Response to Predicted Climate Change in Two Contrasting Heathland Species. Plant and Soil 2013, 369, 615–629. [Google Scholar] [CrossRef]
  59. Koller, E.K.; Phoenix, G.K. Seasonal Dynamics of Soil and Plant Nutrients at Three Environmentally Contrasting Sites along a Sub-Arctic Catchment Sequence. Polar Biology 2017, 40, 1821–1834. [Google Scholar] [CrossRef]
  60. Pilbeam, D.J. Breeding Crops for Improved Mineral Nutrition under Climate Change Conditions: Figure 1. Journal of Experimental Botany 2015, 66, 3511–3521. [Google Scholar] [CrossRef] [PubMed]
  61. Shraddha; Shukla, Y. R.; Thakur, K.; Vashishat, R.K.; Sharma, S.; Chandel, R.S.; Dhingra, S.; Alam, T.; Khargotra, R.; Jyoti, K. Impact of Fermented Organic Formulations Combined with Inorganic Fertilizers on Broccoli (Brassica Oleracea L. Var. Italica Plenck) Cv. Palam Samridhi. Heliyon 2023, 9, e20321. [Google Scholar] [CrossRef]
  62. 49. Sharma, R.; Chadak, S. Residual Soil Fertility, Nutrient Uptake, and Yield of Okra as Affected by Bioorganic Nutrient Sources. Communications in Soil Science and Plant Analysis 2022, 53, 2853–2866. [Google Scholar] [CrossRef]
Table 1. Initial soil characteristics.
Table 1. Initial soil characteristics.
Particular Season-I Season-II References
pH 7.86 6.92 [15]
EC 1.02 0.95 [15]
Organic Carbon (%) 0.78 0.91 [16]
Available N (kg/ha) 262.57 282.39 [17]
Available P (kg/ha) 52.56 57.52 [18]
Available K (kg/ha) 395.45 402.27 [19]
Table 2. Effect on plant height, plant spread, chlorophyll content and days taken for flowering.
Table 2. Effect on plant height, plant spread, chlorophyll content and days taken for flowering.
S-I S-II Mean T1 T2 Interactions CD SE
Plant height (cm)
H1 124.62 94.68 109.65 109.88 109.42 Seasons 0.86 0.29
H2 124.88 92.13 108.51 108.83 108.18 Nutritional modules NS 0.29
H3 124.47 90.70 107.58 107.77 107.40 Season × Nutritional modules NS 0.42
Mean 124.66 92.56 - Harvesting flushes 1.06 0.36
T1 124.96 92.70 108.90 Season × Harvesting flushes 1.49 0.51
T2 124.36 92.31 108.34 Nutritional modules × Harvesting flushes NS 0.51
Plant spread (cm)
H1 62.38 52.31 57.35 57.56 57.13 Seasons 1.65 0.56
H2 62.92 51.82 57.37 57.55 57.18 Nutritional modules NS 0.56
H3 62.23 48.47 55.35 55.52 55.18 Season × Nutritional modules NS 0.79
Mean 62.51 50.87 - Harvesting flushes NS 0.69
T1 62.72 51.03 56.88 Season × Harvesting flushes NS 0.97
T2 62.30 50.70 56.50 Nutritional modules × Harvesting flushes NS 0.97
Chlorophyll content of leaves (mg/g)
H1 2.65 2.17 2.41 2.55 2.27 Seasons 0.04 0.01
H2 2.54 1.78 2.16 2.21 2.10 Nutritional modules 0.04 0.01
H3 2.38 1.49 1.94 2.06 1.81 Season × Nutritional modules NS 0.02
Mean 2.52 1.81 - Harvesting flushes 0.05 0.02
T1 2.62 1.93 2.28 Season × Harvesting flushes 0.07 0.02
T2 2.42 1.70 2.06 Nutritional modules × Harvesting flushes 0.07 0.02
Days taken for flowering (days)
H1 54.22 62.87 58.54 58.45 58.63 Seasons 0.32 0.11
H2 53.18 65.65 59.42 59.42 59.42 Nutritional modules NS 0.11
H3 53.60 67.05 60.33 60.32 60.33 Season × Nutritional modules 0.46 0.16
Mean 53.67 65.19 - Harvesting flushes 0.39 0.13
T1 53.46 65.33 59.39 Season × Harvesting flushes 0.56 0.19
T2 53.88 65.04 59.46 Nutritional modules × Harvesting flushes NS 0.19
S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @30:20:20 g m-2, CD: critical difference, SE: standard error, NS: no-significant.
Table 3. Effect on size of flower, marketable flower yield per square meter and shelf life.
Table 3. Effect on size of flower, marketable flower yield per square meter and shelf life.
S-I S-II Mean T1 T2 Interactions CD SE
Size of flower (cm)
H1 10.97 6.76 8.86 8.90 8.82 Seasons 0.16 0.05
H2 11.17 5.69 8.43 8.47 8.39 Nutritional modules NS 0.05
H3 10.88 5.24 8.06 8.10 8.02 Season × Nutritional modules NS 0.08
Mean 11.00 5.89 Harvesting flushes 0.19 0.07
T1 11.04 5.94 8.49 Season × Harvesting flushes 0.27 0.09
T2 10.97 5.85 8.41 Nutritional modules × Harvesting flushes NS 0.09
Marketable flower yield m-1 (kg)
H1 8.11 6.42 7.27 7.41 7.13 Seasons 0.07 0.02
H2 8.10 6.28 7.19 7.28 7.10 Nutritional modules 0.07 0.02
H3 7.79 6.17 6.98 7.18 6.78 Season × Nutritional modules 0.10 0.03
Mean 8.00 6.29 - Harvesting flushes 0.08 0.03
T1 8.19 6.39 7.29 Season × Harvesting flushes NS 0.04
T2 7.81 6.19 7.00 Nutritional modules × Harvesting flushes 0.12 0.04
Shelf life (days)
H1 4.77 5.13 4.98 5.33 4.62 Seasons 0.21 0.07
H2 4.93 5.98 5.46 5.65 5.27 Nutritional modules 0.21 0.07
H3 4.62 6.12 5.37 5.65 5.08 Season × Nutritional modules NS 0.10
Mean 4.77 5.76 - Harvesting flushes 0.25 0.09
T1 5.02 6.07 5.54 Season × Harvesting flushes 0.36 0.12
T2 4.52 5.46 4.99 Nutritional modules × Harvesting flushes NS 0.12
S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @30:20:20 g m-2, CD: critical difference, SE: standard error, NS: non-significant.
Table 4. Three way table (seasons, treatments and harvesting flushes interactions).
Table 4. Three way table (seasons, treatments and harvesting flushes interactions).
Seasons
S-I S-II
T1 T2 T1 T2
Plant height (cm)
H1 124.87 124.37 94.90 94.47
H2 125.33 124.43 92.33 91.93
H3 124.67 124.27 90.87 90.53
CD 0.05 NS SE 0.72
Plant spread (cm)
H1 62.67 62.10 52.45 52.17
H2 63.10 62.73 52.00 51.63
H3 62.40 62.07 48.65 48.30
CD 0.05 NS SE 1.37
Chlorophyll content of leaves
H1 2.68 2.61 2.42 1.92
H2 2.62 2.45 1.80 1.75
H3 2.57 2.20 1.56 1.42
CD 0.05 0.10 SE 0.03
Days taken for flowering
H1 53.90 54.53 63.00 62.73
H2 53.03 53.33 65.80 65.50
H3 53.43 53.77 67.20 66.90
CD 0.05 NS SE 0.27
Size of flower (cm)
H1 11.00 10.93 6.80 6.71
H2 11.20 11.13 5.73 5.64
H3 10.92 10.85 5.28 5.19
CD 0.05 NS SE 0.13
Marketable flower yield m-1(kg)
H1 8.25 7.97 6.56 6.29
H2 8.24 7.96 6.33 6.23
H3 8.08 7.50 6.28 6.06
CD 0.05 NS SE 0.06
Shelf life (days)
H1 5.17 4.37 5.50 4.87
H2 5.07 4.80 6.23 5.73
H3 4.83 4.40 6.47 5.77
CD 0.05 NS SE 0.17
Kg: kilogram, cm: centimeters, S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @ 30:20:20 g m-2, CD: critical difference, SE: standard error, NS: non significant.
Table 5. Effect on total carotenoids, viable bacterial, fungal and actinomycetes.
Table 5. Effect on total carotenoids, viable bacterial, fungal and actinomycetes.
S-I S-II Mean T1 T2 Interactions CD SE
Total carotenoids (mg g-1)
H1 2.30 2.20 2.25 2.32 2.17 Seasons 0.04 0.01
H2 2.53 2.07 2.30 2.40 2.20 Nutritional modules 0.04 0.01
H3 2.25 1.80 2.02 2.10 1.95 Season × Nutritional modules 0.05 0.02
Mean 2.36 2.02 - Harvesting flushes 0.04 0.02
T1 2.48 2.07 2.28 Season × Harvesting flushes 0.06 0.02
T2 2.23 1.98 2.10 Nutritional modules × Harvesting flushes NS 0.02
Bacterial count (× 105 cfu g-1 Soil)
H1 17.97 13.65 15.81 18.17 13.44 Seasons 0.15 0.05
H2 18.38 13.82 16.10 18.58 13.63 Nutritional modules 0.15 0.05
H3 18.45 13.93 16.19 18.63 13.74 Season × Nutritional modules NS 0.07
Mean 18.27 13.80 - Harvesting flushes 0.18 0.06
T1 20.74 16.18 18.46 Season × Harvesting flushes NS 0.09
T2 15.79 11.42 13.60 Nutritional modules × Harvesting flushes NS 0.09
Fungal count (× 103 cfu g-1 Soil)
H1 3.54 2.79 3.17 3.57 2.77 Seasons 0.11 0.04
H2 3.80 3.05 3.43 3.83 3.03 Nutritional modules 0.11 0.04
H3 4.28 3.53 3.90 4.30 3.50 Season × Nutritional modules NS 0.05
Mean 3.87 3.12 - Harvesting flushes 0.14 0.05
T1 4.27 3.52 3.90 Season × Harvesting flushes NS 0.07
T2 3.47 2.72 3.10 Nutritional modules × Harvesting flushes NS 0.07
Actinomycetes count (× 103 cfu g-1 Soil)
H1 2.37 1.69 2.03 2.46 1.60 Seasons 0.08 0.03
H2 2.75 2.05 2.40 2.84 1.96 Nutritional modules 0.08 0.03
H3 3.06 2.35 2.70 3.15 2.26 Season × Nutritional modules NS 0.04
Mean 2.73 2.03 - Harvesting flushes 0.09 0.03
T1 3.16 2.47 2.82 Season × Harvesting flushes NS 0.05
T2 2.29 1.59 1.94 Nutritional modules × Harvesting flushes NS 0.05
cfu: colonies forming unit, mg: milligrams S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @30:20:20 g m-2, CD: critical difference, SE: standard error, NS: non significant.
Table 6. Effect on available N, P and K of soil.
Table 6. Effect on available N, P and K of soil.
S-I S-II Mean T1 T2 Interactions CD SE
N kg ha-1
H1 290.87 295.65 293.26 286.93 299.58 Seasons 0.82 0.28
H2 285.67 300.92 293.29 286.97 299.62 Nutritional modules 0.82 0.28
H3 283.20 304.62 293.91 287.58 300.23 Season × Nutritional modules 1.16 0.40
Mean 286.58 300.39 - Harvesting flushes NS 0.34
T1 280.28 294.04 287.16 Season × Harvesting flushes 1.42 0.49
T2 292.88 306.74 299.81 Nutritional modules × Harvesting flushes NS 0.49
P kg ha-1
H1 57.51 62.43 59.97 57.14 62.80 Seasons 0.79 0.27
H2 56.64 61.27 58.95 56.48 61.42 Nutritional modules 0.79 0.27
H3 55.41 61.00 58.20 55.17 61.23 Season × Nutritional modules NS 0.38
Mean 56.52 61.57 - Harvesting flushes 0.97 0.33
T1 53.92 58.61 56.27 Season × Harvesting flushes NS 0.47
T2 59.11 64.52 61.82 Nutritional modules × Harvesting flushes NS 0.47
K kg ha-1
H1 408.82 417.02 412.92 406.62 419.22 Seasons 5.00 1.70
H2 408.25 416.45 412.35 406.05 418.65 Nutritional modules 5.00 1.70
H3 411.12 419.32 415.22 408.92 421.52 Season × Nutritional modules 7.05 2.40
Mean 409.40 417.60 - Harvesting flushes NS 2.08
T1 403.10 411.30 407.20 Season × Harvesting flushes NS 2.95
T2 415.70 423.90 419.80 Nutritional modules × Harvesting flushes NS 2.95
Kg ha-1: kilogram per hectare, N: Nitrogen; P: Phosphorus; K: Potassium, S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @30:20:20 g m-2, CD: critical difference, SE: standard error, NS: non significant.
Table 7. Three way table (seasons, treatments and harvesting flushes interactions).
Table 7. Three way table (seasons, treatments and harvesting flushes interactions).
Seasons
Season-I Season-II
T1 T2 T1 T2
Total carotenoids (mg g-1)
H1 2.40 2.20 2.25 2.15
H2 2.70 2.35 2.10 2.04
H3 2.35 2.14 1.85 1.75
CD 0.05 0.02 SE 0.03
Bacteria count (× 105 cfu g-1)
H1 20.33 15.60 16.01 11.28
H2 20.93 15.83 16.23 11.42
H3 20.97 15.93 16.30 11.55
CD 0.05 NS SE 0.13
Fungal count (× 103 cfu g-1)
H1 3.94 3.14 3.19 2.39
H2 4.20 3.40 3.45 2.65
H3 4.68 3.88 3.93 3.13
CD 0.05 NS SE 0.09
Actinomycetes count (× 103 cfu g-1)
H1 2.80 1.94 2.12 1.26
H2 3.20 2.29 2.48 1.63
H3 3.49 2.63 2.81 1.89
CD 0.05 NS SE 0.06
N kg ha-1
H1 284.57 297.17 289.30 302.00
H2 279.37 291.97 294.57 307.27
H3 276.90 289.50 298.27 310.97
CD 0.05 NS SE 0.66
P kg ha-1
H1 54.69 60.32 59.59 65.27
H2 54.67 58.60 58.30 64.24
H3 52.39 58.42 57.96 64.04
CD 0.05 NS SE
P kg ha-1
H1 402.52 415.12 410.72 423.32
H2 401.95 414.55 410.15 422.75
H3 404.82 417.42 413.02 425.62
CD 0.05 NS SE 4.16
Kg ha-1: kilogram per hectare, N: Nitrogen; P: Phosphorus; K: Potassium, cfu: colonies forming uni, S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @30:20:20 g m-2, CD: critical difference, SE: standard error, NS: non-significant.
Table 8. Effect on N, P and K uptake.
Table 8. Effect on N, P and K uptake.
S-I S-II Mean T1 T2 CD 0.05 CD SE
N uptake (kg ha -1)
H1 16.07 15.77 15.92 17.31 14.52 Seasons 0.27 0.09
H2 17.25 14.39 15.82 16.72 14.92 Nutritional modules 0.27 0.09
H3 18.33 11.43 14.88 15.84 13.93 Season × Nutritional modules 0.38 0.13
Mean 17.21 13.86 - Harvesting flushes 0.33 0.11
T1 18.73 14.52 16.62 Season × Harvesting flushes 0.47 0.16
T2 15.70 13.21 14.46 Nutritional modules × Harvesting flushes 0.47 0.16
P uptake (kg ha -1)
H1 6.72 4.71 5.71 6.64 4.79 Seasons 0.10 0.03
H2 7.12 4.19 5.66 6.45 4.86 Nutritional modules 0.10 0.03
H3 8.80 3.61 6.20 7.52 4.89 Season × Nutritional modules 0.14 0.05
Mean 9.32 5.77 - Harvesting flushes 0.12 0.04
T1 9.32 4.42 6.87 Season × Harvesting flushes 0.17 0.06
T2 5.77 3.92 4.85 Nutritional modules × Harvesting flushes 0.02 0.06
K uptake (kg ha -1)
H1 14.27 11.94 13.10 14.13 12.08 Seasons 0.26 0.09
H2 14.71 10.22 12.47 13.32 11.61 Nutritional modules 0.26 0.09
H3 15.15 7.54 11.34 12.11 10.58 Season × Nutritional modules 0.36 0.12
Mean 14.71 9.90 - Harvesting flushes 0.31 0.11
T1 15.81 10.56 13.19 Season × Harvesting flushes 0.44 0.15
T2 13.61 9.23 11.42 Nutritional modules × Harvesting flushes NS 0.15
Kg ha-1: kilogram per hectare, N: Nitrogen; P: Phosphorus; K: Potassium, S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @30:20:20 g m-2, CD: critical difference, SE: standard error, NS: non significant.
Table 9. effect on pH, EC and OC of soil.
Table 9. effect on pH, EC and OC of soil.
S-I S-II Mean T1 T2 CD 0.05 CD SE
pH
H1 6.50 6.49 6.49 6.29 6.70 Seasons NS 0.01
H2 6.45 6.48 6.46 6.26 6.67 Nutritional modules 0.04 0.01
H3 6.46 6.49 6.47 6.26 6.69 Season × Nutritional modules NS 0.02
Mean 6.47 6.49 - Harvesting flushes NS 0.02
T1 6.28 6.26 6.27 Season × Harvesting flushes NS 0.03
T2 6.66 6.71 6.68 Nutritional modules × Harvesting flushes NS 0.04
EC (dS m-1)
H1 0.65 0.65 0.64 0.44 0.84 Seasons NS 0.02
H2 0.60 0.54 0.57 0.40 0.74 Nutritional modules 0.05 0.02
H3 0.61 0.54 0.58 0.41 0.75 Season × Nutritional modules NS 0.02
Mean 0.62 0.57 - Harvesting flushes 0.06 0.02
T1 0.43 0.40 0.41 Season × Harvesting flushes NS 0.03
T2 0.81 0.74 0.78 Nutritional modules × Harvesting flushes 0.02 0.03
OC (%)
H1 0.84 0.98 0.91 0.96 0.86 Seasons 0.02 0.01
H2 0.88 1.03 0.96 1.03 0.88 Nutritional modules 0.02 0.01
H3 0.88 1.02 0.95 1.01 0.89 Season × Nutritional modules 0.03 0.01
Mean 0.87 1.01 - Harvesting flushes 0.03 0.01
T1 0.93 1.07 1.00 Season × Harvesting flushes NS 0.01
T2 0.81 0.95 0.88 Nutritional modules × Harvesting flushes NS 0.01
pH: negative logarithm of H+ (concentration power of hydrogen), dS m-1: decisiemens per meter, EC: electrical conductivity, OC: A quantifiable part of soil organic matter is called soil organic carbon, S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @30:20:20 g m-2, CD: critical difference, SE: standard error, NS: non significant.
Table 10. Three way table (seasons, treatments and harvesting flushes interactions).
Table 10. Three way table (seasons, treatments and harvesting flushes interactions).
Seasons
Season-I Season-II
T1 T2 T1 T2
N uptake (kg ha -1)
H1 18.00 14.13 16.02 14.91
H2 18.72 15.77 14.72 14.06
H3 19.45 17.21 12.22 10.64
CD 0.05 0.67 SE 0.23
P uptake (kg ha -1)
H1 8.39 5.04 4.89 4.54
H2 8.47 5.77 4.42 3.96
H3 11.09 6.51 3.96 3.26
CD 0.05 0.24 SE 0.08
K uptake (kg ha -1)
H1 15.23 13.30 13.02 10.86
H2 15.84 13.57 10.80 9.64
H3 16.34 13.96 7.87 7.20
CD 0.05 0.63 SE 0.21
pH of soil
H1 6.29 6.70 6.29 6.69
H2 6.26 6.63 6.26 6.71
H3 6.28 6.63 6.24 6.74
CD 0.05 NS SE 0.04
EC (dS m-1) of soil
H1 0.44 0.85 0.44 0.83
H2 0.41 0.78 0.38 0.70
H3 0.43 0.78 0.38 0.71
CD 0.05 NS SE 0.04
OC (%)
H1 0.89 0.79 1.03 0.93
H2 0.96 0.81 1.10 0.95
H3 0.94 0.82 1.08 0.96
CD 0.05 NS SE 0.02
pH: negative logarithm of H+ (concentration power of hydrogen), dS m-1: decisiemens per meter, EC: electrical conductivity, OC: A quantifiable part of soil organic matter is called soil organic carbon, Kg ha-1: kilogram per hectare, N: Nitrogen; P: Phosphorus; K: Potassium, S-I: summer, S-II: winter, H1: first harvesting flushes, H2: second harvesting flushes, H3: third harvesting flushes T1: Jeevamrit @ 2 liter m-2, T2: RDF N:P:K @30:20:20 g m-2, CD: critical difference, SE: standard error, NS: non significant.
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