Abstract
Vermicomposting is a process in which earthworms are utilized to convert biodegradable organic waste into humus-like vermicast. Past work, mainly on vermicomposting of animal droppings, has shown that vermicompost is an excellent organic fertilizer and is also imbibed with pest-repellent properties. However, there is no clarity whether vermicomposts of organic wastes other than animal droppings are as plant-friendly as the manure-based vermicomposts are believed to be. It is also not clear as to whether the action of a vermicompost as a fertilizer depends on the species of plants being fertilized by it. This raises questions whether vermicomposts are beneficial (or harmful) at all levels of application or if there is a duality in their action which is a function of their rate of application. The present work is an attempt to seek answers to these questions. To that end, all hitherto published reports on the action of vermicomposts of different substrates on different species of plants have been assessed. The study reveals that, in general, vermicomposts of all animal/plant based organic wastes are highly potent fertilizers. They also possess some ability to repel plant pests. The factors that shape these properties have been assessed and the knowledge gaps that need to be bridged have been identified.
1. Introduction
For sustaining soil fertility and boost crop production, organic wastes such as cattle droppings, rejects from the kitchen, sewage sludge or anaerobically digested animal manure have been used in agriculture for a long time [1,2,3]. These substances provide nutrients and organic carbon to the soil, but not very efficiently [4]. Moreover, some of these substances can undergo anaerobic decomposition in the soil, and generate methane, which is a major global warming gas [5,6,7]. Vermicomposting is believed to offer a route by which organic waste can be stabilized to a significant extent, converting it into a finished fertilizer [8]. Similar ends can be achieved with composting but composting is an energy-intensive process and the fertilizer value of the composts is known to be inferior to that of vermicomposts [9,10,11,12].
Both composting and vermicomposting involve biological decomposition of organic waste to produce a stabilized organic fertilizer. However, vermicomposting is distinguished from all other pollution control processes, including composting, in that an animal—an earthworm—facilitates the microbial action on the waste. This occurs because the waste is exposed to certain bacteria and enzymes present in the earthworm gut which are not available during composting or other biological degradation processes and which bestow special attributes to a vermicompost (VC). During ingesting bits of waste, earthworms comminute them with their gizzards, thereby enhancing their surface area manifold and making them much more amenable to microbial and enzymatic action than they otherwise were [8]. As the masticated waste passes through an earthworm’s gut, it is acted upon by enzymes and microorganisms present in the gut to become extensively biodegraded [13,14,15,16]. The substrate also acquires some of the enzymes and microorganisms, as well as some of the hormones, present in the earthworm gut, as it is excreted by the earthworm in the form of vermicast. During this vermicomposting, 50 ± 10% of the organic carbon present in the parent substrate is mineralized and is emitted in the form of carbon dioxide. Due to this, the concentration of nitrogen, phosphorous, and other major, medium, and trace nutrients is enhanced in the VC relative to the parent substrate. The mineralization caused by the biodegradation also makes these nutrients more bioavailable than they were in the parent substrate.
However, even as several reports exist which have shown that VC stimulated seed germination [17,18,19], supported plant growth and enhanced the yield and the quality of fruits [20,21] of several plant species, there are also reports describing that VC either had no beneficial effect or had a detrimental effect [19,22,23,24,25]. Likewise, there are reports which show that VC can induce resistance in plants against pests and diseases [26,27,28,29] but it is not known whether the opposite effect also occurs.
This assessment of the state-of-the-art was performed to determine the balance of evidence for and against the virtues of VC. It is aimed to identify the different reasons advanced so far to explain the different types of impacts of VC as witnessed during different ways of VC application. Additionally, it is aimed to locate knowledge gaps that have to be filled up if we are to realize the true potential of VC as an organic fertilizer and biopesticide.
2. Methodology
We began by exploring all potential sources for material on the effect of VC derived from different substrates on different species of plants. All papers/reports available on Science Direct, Web of Science, and Google Scholar were considered. Abstracts from conferences, book reviews, editorials, letters, and news stories were excluded. The material was classified based on: (1) studies showing stimulatory effect at all levels of VC applications; (2) studies showing stimulatory effect depending on the concentrations of the VC applied; (3) studies showing no effect; and (4) studies showing inhibitory effect of VC application. The role of VC in inducing resistance in plants against pests and diseases was also assessed. The possible reasons for the differences in the nature of impacts of VC, as advanced by different authors, were then identified and classified.
When the study was initiated, we had aimed at a meta-analysis in which we would have tried to quantify cause–effect relationships, assess the weight of different influences, and carry out tests of significance. However, it was not possible because of great non-uniformity in the data that have been reported in the past. The effect of vermicomposts derived from different substrates has been assessed often in combination with other fertilizers on many different botanical species, with widely differing soils and container media, and irrigation with water of widely differing quality, under highly diverse agroclimatic conditions. This extent of variability made it impossible to quantify responses beyond computation of percentages under broad classifications.
3. State-of-the-Art
A total of 252 reports were located in primary literature. A summary is provided in Table 1, Table 2, Table 3 and Table 4. The bulk of these studies have been published during the last 10 years and more studies have been published during 2011–2015 than in any earily five-year span (Figure 1). These statistics reveal the world’s increasing interest in VC. The relative proportion of studies on VC derived from manure, phytomass, manure-phytomass blends, and substrates other than manure and phytomass are presented in Figure 2. As may be seen, there is predominance of studies which involve manure, either alone or in combination with phytomass. Studies on phytomass are less than 1/3 of all, even though by far much greater quantities of waste phytomass are generated in the world than of animal manure. The reasons for much lesser utilization of phytomass than animal manure for VC until now was explained by us recently [30].
Table 1.
Effect of vermicompost (VC) on seed germination.
Table 2.
Effect of vermicompost (VC) on growth and yield.
Table 3.
Effect of vermicomposts on soil.
Table 4.
Effect of vermicompost in suppressing plant disease and pests.
Figure 1.
Number of papers published on the effect of vermicompost (VC) on germination, growth, yield, disease control and soil health, during 1989–2017.

Figure 2.
Fractions of studies describing impact of vermicompost derived from manure
, phytomass
, manure-phytomass mixture
, other substrates
, and with no mention of source of VC
on (a) seed germination; (b) growth and yield, and (c) soil health.
, phytomass
, manure-phytomass mixture
, other substrates
, and with no mention of source of VC
on (a) seed germination; (b) growth and yield, and (c) soil health.
3.1. Effect of Vermicompost on Seed Germination
As shown in Table 1, seeds of several plant species have been used to evaluate the influence of VC on their germination. The findings present a mixed picture: in the majority of cases VC was found to promote germination but no effect or negative effect was also reported. The relative proportion of studies reporting different types of impacts of VC on seed germination is reflected in Figure 3a. Enhancement was reported in 40% of the studies while 37% reported stimulation up to certain VC concentrations and inhibition beyond those concentrations. In 9% of reports, only inhibition was shown, and 14% reported no impact. Thus, 77% of studies claimed that VC facilitates seed germination, at least up to certain levels of application.
Figure 3.
Relative fractions of studies on the effect of vermicompost on (a) seed germination; and (b) plant growth and yield:
no effect,
stimulation,
inhibition, and
stimulation at lower concentrations and inhibition at higher.
no effect,
stimulation,
inhibition, and
stimulation at lower concentrations and inhibition at higher.
The nature of the effect VC exerts seems to depend on plant species and VC concentration. Seed germination is essentially an internally regulated process, which is influenced mainly by the genotype of plants. However, external factors such as temperature, humidity, light period, soil moisture, and presence of certain chemical compounds can also alter this process through either promotion or inhibition [31,32]. All these factors are intertwined and are facilitated by signaling through multiple hormones that either promote or inhibit seed germination [33].
The first study reporting the duality in behavior of VC—increased germination success up to certain concentrations and inhibition at higher levels—was reported by Wilson and Carlile [34]. They found that duck waste VC in the range 2–8% increased the germination success of tomato (S. lycopersicum), lettuce (L. sativa), and pepper (Capsicum sp.), while 10–20% VC treatments reduced the germination success significantly. In a recent series of extensive investigations, Hussain et al. [35,36,37,38,39] found that VC derived from salvinia (Salvinia molesta), lantana (Lantana camara), parthenium (Parthenium hysterophorus), and ipomoea (Ipomoea carnea) enhanced the germination success of ladies finger, green gram and cucumber when used in the concentration range of 2–8% but hindered it at higher levels of application. The possible reasons for the dual behavior of VC, culled from reports in Table 1, are summarized below:
- (a)
- As mentioned in the Introduction, during vermicomposting, a substrate loses 50 ± 10% of its carbon in the form of emitted CO2 which is produced from worm-mediated aerobic biodegradation. On the other hand, nitrogen is not lost; rather some nitrogen gets added in the form of earthworm mucus. The combined effect is a reduction in the substrate mass with the consequent enhancement in the concentration of nitrate and ammonium in the vermicast relative to that in the substrate. All other nutrients also get enriched. As both nitrate and ammonium are efficient breakers of seed dormancy [40,41], their enrichment in VC makes the latter a facilitator of germination. Indeed, nitrate and ammonium are known to be especially effective when present together. Even though several attempts have been made to explain this individual and collective action of nitrate and ammonium on germination, no clear picture has emerged yet [42,43].
- (b)
- Breaking of seed dormancy is facilitated by several organic chemicals as well. Such compounds include relatively simple aliphatics, e.g., methanol, ethanol, acetone and ethyl ether; aromatics, e.g., phenol and hydroxyquinoline; and complex growth regulators, e.g., gibberellins and cytokines [44]. As VC is rich in organic chemicals [45,46,47,48], it is likely to contain one or more of these compounds which enhance germination success. It has already been shown that plant growth hormones that are present in VC facilitate seed germination [49,50].
- (c)
- Most of the chemicals which promote germination up to certain concentrations are known to inhibit it when present in higher concentration [50,51,52]. Chemical fertilizers also display this dichotomy—facilitating germination and growth up to certain levels of application and hindering the same at higher levels [53,54,55].
- (d)
- Elevated salinity, caused by the higher mineral content of VC, perhaps slows down water uptake by seeds, thereby inhibiting their germination and root elongation [56,57,58]. Neamatollahi et al. [59] suggested that salinity may also affect germination by facilitating intake of toxic ions, which may change certain enzymatic or hormonal activities in seeds to the detriment of seed germination [60].
3.2. Effect of Vermicompost on Plant Growth and Yield
The studies are summarized in Table 2. Of these, 84% of studies reported stimulation, 11% reported stimulation or inhibition based on the rate of application, 2% reported only inhibition and 3% reported no impact (Figure 3b). In other words, 95% of the studies showed that VC exerts a beneficial influence on plants, at least up to certain concentrations. This general surmise is significant, considering the great variability in the past studies in terms of plant species tested, types of soils and other container media used, and the manner of fertilization which ranged from exclusive use of a VC to the deployment of complex mixtures of VCs, chemical fertilizers, and other amendments. The reports also cover widely varying agroclimatic regions and agricultural practices.
Given the extent of coverage of various possibilities, and the very large fraction of the studies which indicate that VC exerts beneficial influence, it can be generalized that VCs are good organic fertilizers. However, a great deal of uncertainty exists on what levels of VC applications are beneficial for which stage of plant growth. It is also not totally clear as to how a VC exerts its beneficial impacts and why it begins harming the growth of plants beyond certain concentrations—even as a good deal of understanding of the possible factors does exist. It is almost certain that VC improves the nutrient content of the soil or the container media to which it is applied [61,62,63,64,65]. Several other reports also suggest that the increase in the growth and yield of plants is a result of the increased nutrient levels in the VC amended soil/media [66,67,68,69,70,71,72,73,74,75].
The improvement in the physical properties of soil caused by the VC application, discussed in the following section, may also be a factor supporting plant growth and fruit yield.
A VC carries rich and diverse microbial populations, particularly fungi and bacteria [76,77]. It has been suggested that this could result in the production of significant quantities of plant growth regulators such as indole acetic acid, gibberellins and cytokinins by microorganisms [78], besides an increase in the enzymatic activities. Hussain et al. [35,36,37,38,39] reported an increase in the microbial biomass carbon in soil amended with the VCs derived from L. camara, I. carnea, P. hysterophorus, and S. molesta. Pointing to the importance of the role of microorganisms, Arancon et al. [49] suggested that the enhanced plant growth in the VC amended media cannot be attributed entirely to the physical and chemical amelioration by the VC. They found that plant growth was better in the VC amended media, compared to the control media, even when all the nutrients equivalent to those contained in the VC were given to the plants growing in the control media [79]. They postulated that it was the plant growth hormones and humic acids in the VC that, in conjunction with better nutrient availability, exerted the beneficial effect. Canellas et al. [80] and Zandonadi et al. [81] reported that the humic substances extracted from earthworm’s compost were capable of inducing lateral root growth in maize plants by stimulation of the plasma membrane H+-ATPase activity, thus producing an effect similar to the one achieved by exogenous application of indole-3-acetic acid (IAA). Another perspective is the induction of lateral root initiation by VC-derived humic substances which has been related to the activation of the transcription of some auxin responsive genes [82]. The hypothesis of the auxin activity of the VC-based humic substances is reinforced by the presence of exchangeable auxin groups in their macrostructure [80].
The ability of VC to suppress plant pests and pathogens may also contribute to better growth and yield of the VC fertilized plants. This aspect is elaborated in Section 3.4.
3.3. Effect of Vermicompost on Soil Health
Several studies reported the positive impact of VC on soil health (Table 3). The possible ways by which VC is reported to improve soil health are:
- (1)
- Addition of VC to the soil elevates the organic matter content in the latter. The vermicast particles, which tend to slowly dissolve in water, contribute to an increase in the overall pore space and water holding capacity of the soil, with concomitant decrease in the soil’s bulk and particle density [17,34,83].
- (2)
- VC is known to contain high concentrations of plant-available nutrients such as nitrates, phosphates, exchangeable calcium and soluble potassium. These when supplemented to the soil enhance the nutrient content of the soil [84,85,86].
- (3)
- Earthworms excrete polysaccharides, proteins and other nitrogenous compounds creating resource heterogeneity that ultimately increases microbial diversity [45,46,47,48]. During the gut transit, the pore space between organic and mineral particles is altered and packing void is created in the deposited castings. The structural rearrangement of the organic matter in the intestine of the earthworm results in more fine pores and fewer macropores in the castings. This enhances the availability of both water and nutrients to microorganisms, thus enhancing the microbial population in the soil. This, in turn, increases the activity of beneficial enzymes, hormones and plant growth regulators in the VC, and hence in the soil.
3.4. Effect of Vermicompost on Pests and Disease
As can be seen in Table 4, several studies showed that VCs can suppress a wide range of microbial diseases, insect pests and plant parasitic nematodes. Szczech [87] and Szczech and Smolinska [88] reported significant reduction in the infection caused by Fusarium lycopersici and Phytophthora nicotianae in tomato grown in VC−amended soil. Arancon et al. [89] found that tomato, pepper and cabbage plants grown in VC amended media have significantly lesser infections caused by Myzus persicae, Pseudococcus spp. and Peiris brassicae. Yardim et al. [26] reported reduction in the Manduca quinquemaculata, Acalymma vittatum, and Diabotrica undecimpunctata infestations in the cucumber and tomato plants grown in pig manure VC. Several other reports also suggest that VC amendment significantly reduces pathogen attacks on plants [90,91,92,93,94,95,96].
Several studies have indicated that better nutrient availability and the presence of antimicrobial compounds such as flavonoids, phenolics and humic acids in the VC may have induced resistance to pathogens in the plants [27,97,98,99,100]. According to Cardoza [93], the resistance against the diseases and pests may be influenced more by the microbial flora than the chemical compounds in the VC [39]. This premise is supported by the studies of Ershehin et al. [91] and Szczech and Smolinska [88] who found that the autoclaved vermicasts were no longer effective in suppressing the plant pathogens. Gopalakrishnan et al. [101] reported that actinomycete isolates from vermicasts were found to be effective in the biocontrol of the fusarium wilt in chick pea (Cicer arietinum). Out of 137 tested isolates, 33 were reported to show an antagonistic potential against fusarium wilt and, hence, could help to control it in the C. arietinum plant.
4. A Summary of the Nature and Causes of Different Effects
The possible reasons for the beneficial effects of VCs are summarized as:
- (1)
- VCs have higher nutritional value than traditional composts. This is due not only to the increased mineralization but also greater degree of humification caused in them by the action of earthworms [21,102].
- (2)
- VCs contain higher concentrations of plant-available nutrients such as nitrates, phosphates, exchangeable calcium, soluble potassium, and trace metals. When a VC is supplemented in soil, it enhances the relative proportion of these micro, semi-micro, and macro nutrients, thereby promoting pant growth and yield [84,85,86,103,104].
- (3)
- VCs contain humus which plays an important role in regulating the retention and release of plant nutrients. Humus contains negatively charged components in large numbers and is thus capable of holding many cations. This gives a VC the ability to act as a slow release fertilizer [105,106].
- (4)
- VCs are rich in organic matter, which, when added to the soil, increases the soil’s porosity, aeration, and water-holding capacity, with concomitant reduction of soil’s bulk and particle density. The resulting overall improvement in the physical properties of the soil contributes significantly to better plant growth and yield [76,106,107,108].
- (5)
- VCs contain large and diverse microbial population, which produces plant growth regulators, enzymes, and hormones beneficial to the plant growth [77,109,110]. There is also production of cytokinins and auxins [78,111].
The possible reasons why VCs exert a negative effect when applied at higher-than-desirable concentrations can be summarized as:
- (1)
- As happens with germination, the growth of plants is adversely affected if nutrients are supplied in excess of the plant’s needs [35,112,113].
- (2)
- If VC application is excessive, the resulting salinity may also inhibit plant growth [114,115,116]. Elevated salinity slows down water uptake by the seeds, thereby inhibiting their germination and root elongation as well as subsequent plant growth [56,57,58,59,60].
- (3)
- High levels of active substances of both phenolic and humic nature may suppress plant growth [115,117]. Phenolic compounds are among the secondary metabolites implicated in plant allelopathy and affect the plants in the following ways:
- (a)
- They increase the permeability of cell membranes, causing the cell contents to spill out leading to increased lipid peroxidation. Consequently, the growth of cells slows down and causes the death of the plant tissues. In addition, excessive phenolic compounds interfere with the absorption of the nutrients by the plants, thereby restricting the growth of the plants.
- (b)
- They are also known to impede the elongation of roots, plant cell division, and disturb the cell ultra-structure. In this manner, they interfere with the normal growth and development of the entire plant.
- (c)
- They tend to weaken the oxygen absorption capacity of plants, causing hindrance in the respiratory process. In addition, phenolic compounds adversely affect photosynthesis by reducing the chlorophyll content of the leaves. Consequently, the rate of photosynthesis is slowed down. Patterson [118] reported that caffeic acid, coumaric acid, ferulic acid, cinnamic acid, and vanillic acid in the concentration range 10–30 µmol/L could significantly inhibit the growth of soybean (Glycine max). Photosynthetic products and chlorophyll content of G. max were also strongly reduced.
- (d)
- They enter the plants through the plant’s cell membrane and change the activity and function of certain enzymes. Rice [119] demonstrated that chlorogenic acid, caffeic acid and catechol can inhibit activities of phosphorylase, while cinnamic acid and its derivatives can inhibit the hydrolysis activities of ATPase.
- (e)
- Phenolic compounds can hinder, even stop, the physiological activity of plant hormones, in turn inhibiting the normal physiological processes in the plants. Hydroxyl benzoic acid, polyphenols, and other compounds have been shown to suppress the decomposition of indole acetic acid and gibberellin.
- (f)
- While some phenolics (i.e., ferulic acid and cinnamic acid) have been seen to inhibit protein synthesis [120], all phenolics have the potential to reduce integrity of DNA and RNA [121,122,123].
- (4)
- Elevated concentrations of heavy metals alongside the elevated salinity and nutrient contents may also be the cause of suppression of plant growth when excessive levels of VC are applied [17]. Heavy metals induce growth inhibition, structure damage, and a decline in physiological and biochemical activity when present above certain concentrations [122].
The possible reason why some authors found no impact of VC on plant growth and yield may be due to the use of such doses of VCs which may not have been sufficient to satisfy the nutrient demand of plant species studied, leading to no impact on growth and yield [124].
5. Summary and Conclusions
Extensive assessment of past studies on the effect of vermicompost (VC) on plants and soils was carried out. A summary of the 252 reports, located in primary literature, is presented. The reports reveal that, in general, VC is beneficial to germination, growth and yield of plants. It also improves the physical and chemical properties of soil vis-à-vis agriculture productivity. These effects are seen irrespective of whether the VC is derived from animal manure, phytomass, or manure-phytomass blends. The reports also reveal that, in general, VC may become detrimental if applied in concentrations far greater than the ones found beneficial. All possible reasons for this dual behavior of VC were culled from the reports and catalogued in the review. Future work should focus on determining the ranges of beneficial VC concentrations under typical soil–water plant–micrometeorological regimes.
Acknowledgments
Shahid A. Abbasi thanks the Council of Scientific and Industrial Research (CSIR), New Delhi, for the Emeritus Scientist grant (21(1034)/16/EMR-II).
Author Contributions
The collection of data was mainly done by NH and its reporting by SAA. The two authors shared the workload evenly in interpreting the data. Overall the contribution of the two authors is equivalent.
Conflicts of Interest
The authors declare no conflict of interest.
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