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Available online freely at www.isisn.org Bioscience Research Print ISSN: 1811-9506 Online ISSN: 2218-3973 Journal by Innovative Scientific Information & Services Network RESEARCH ARTICLE BIOSCIENCE RESEARCH, 2020 17(2): 1511-1520. OPEN ACCESS Effect of aquatic plants (Duck Weed and Water Hyacinth) on physico-chemical and microbial activities of vermicompost Yasser Thabet A. Moustafa1, Tarek R. Elsayed2, Mohamad F. El-Dahshour3, Safwat A.A. Gomah1, Lixin Zhang4 and Nabil S. A. Mustafa5* 1Central Lab for Aquaculture Research (CLAR), Agricultural Research Center Egypt 2 Department of Microbiology, Faculty of Agriculture, Cairo University, Giza, Egypt 3 Fertilization Technology Dept., Agricultural and Biological Division Egypt 4 College of Life Sciences, Northwest A&F University, Yangling 712100, Shaanxi, China 5Pomology Dept, National Research Centre (NRC) Egypt *Correspondence: nabilhotline@yahoo.com Received 12-04-2020, Revised: 22-06-2020, Accepted: 26-06-2020 e-Published: 30-06-2020 Vermicompost is considered one of high-quality organic fertilizer forms. The aim of the current work + water hyacinth) and (cow dung + duckweed) at the Central Lab for aquaculture research (CLAR), Agricultural Research Center. The samples of these vermicompost types were delivered was to investigate the role of aquatic plants (i.e. water hyacinth and duckweed) in improving vermicompost quality. Different types of vermicompost were produced using (cow dung alone), (cow dung to determine bio-chemical parameters (i.e. nutrients, amino acids and growth promoters content) at the National Research Centre (NRC) as well as total bacteria and antibiotic resistant bacteria counts were compared among these different prepared vermicompost types using rt-PCR quantification of 16S rRNA genes and selective plating techniques respectively at faculty of agriculture, Cairo University. Furthermore, PCR detection of nifHgene was determined in total community DNA extract from studied different vermicompost types. The obtained results indicated that adding water hyacinth to cow dung during vermicomposting improved vermicompost studied parameters (dry matter, organic matter and both of nitrogen and phosphorus content, while adding duckweed to cow dung during vermicomposting increased potassium content in comparison with the other tested treatments. Moreover, vermicompost produced from mixture of (cow dung + water hyacinth) surpassed all tested treatments in amino acids and growth promoters content. Also, vermicompost produced from (cow dung + water hyacinth) mixture was characterized by higher bacterial populations, the abundance of diazotrophs and significantly lower population of antibiotic resistant bacteria compared to the (cow dung + duckweed) and control (cow dung alone) vermicompost samples. This study emphasizes that water hyacinth can be used as an enhancer additive component during vermicomposting. Keywords: Vermicompost quality, aquatic plants, water hyacinth, duckweed, physicochemical, growth promoters, amino acids content,diazotrophs. INTRODUCTION several problems were emerged with adverse As a consequence of the excessive use of impacts on the environment and consumer’s agrochemicals (mineral fertilizers and pesticides) health (i.e. depletion of soil fertility and microbial to maximize the productivity of various field crops, activity) (Rahman et al., 2017). Nowadays, more
Moustafa et al., Physico-chemical and microbial activities of vermicompost attention is focused on the utilization of organic irrigation, traffic, water quality, hydraulic and fertilizers in different forms for its positive impacts hydroelectric infrastructures (Hasanand on environment (i.e. restoration of soil fertility) and Chakrabarty 2009 & Hasan, and Chakrabarti, secure safe food for population. 2009). Several studies indicated that although, In Egypt a huge amount of agricultural wastes water hyacinth is one of the most noxious weeds (30-35 million tons) is produced annually (Abou in tropical and subtropical regions, many attempts Hussein and Sawan 2010). Conversion these were made to eliminate or control it. Harnessing wastes into compost by means of turned piles has its considerable productivity is considered as a resulted in a final product with poor physical and sustainable and possibly less expensive method chemical characteristics; thereby of control. Water hyacinth can be used as a green vermicomposting was nominated as an alternative dung, compost and mulch for soil improvement method of transforming these wastes into a because it has high nutritive value (high nitrogen valuable organic fertilizer. Vermicompost is content) (Yang Huazhu et al., 2001,Chu JianJun considered one of the organic fertilizer forms that et al., 2006 and Heuzé et al., 2015). got a lot of attention recently as a result of its In regard to duckweed, Reddy and environmentally friendly manner and several DeBusk(1985) reported that due to highly N merits that can be achieved by using this type of content (crude protein- 20-33%) of the small leaf organic fertilizers. Vermicompost is resulted from of duckweed, it is nominated for many purposes feeding earthworms on agricultural wastes. (i.e. animal feed and green dung). Later, Ahmad Besides, the interaction between earthworms and et al., (1990) indicated that there is a great microorganisms leads to degradation of organic potential to utilize duckweed as a complement to material whether cow dung, fish sludge or other mineral fertilizer in rice field that led to increase farm’s animals and crops wastes. Several studies plant height, straw and grain yield, N, P and K indicate that the vermicompost is rich in nutrients contents of rice plants and in available N, P and K (mainly nitrogen, potassium and phosphate), contents in soil. different growth promoters (i.e. IAA, gibberellins Also, several studies conducted on duckweed and cytokinines) (Edwads and Burrows,1988; as green dung and concluded that duckweed as Orozco et al., 1996; Tomati et al., 1988 green dung combined with chemical fertilizer ,Grappelliet al., 1987;Jeyabal and Kuppuswamy application provides an approach for increasing 2001 and Jouquet et al., 2010) and antimicrobials the rice yield without increasing inputs of N (Adhikary, 2012). Moreover, the applying of fertilizer and thereby provides a financially vermicompost raises the content of total attractive option for farmers to achieve antioxidants, carotenes, lycopene, carbohydrates, environmental integrity and ensure food security vitamin C, proteins, dry matter, iron and zinc in in rice production (Yuanlin et al., 2017). cultivated plants (Gutiérrez-Micely et al., 2007; The main goal of this study was to investigate Shankar et al., 2009; Sinha et al., 2011; Ghosh et the potentiality of using both water hyacinth and al., 2013). duckweed as raw material for vermicompost and However, many factors affect vermicompost their impact on the quality of the vermicompost quality, the main factor of these is the type of product. wastes material (i.e. cow dung, pig dung, fish sludge, or horse manure, and other crops wastes) MATERIALS AND METHODS (Bohlen, 2020). Moreover, mixing animal dungs (either. cow dung, fish sludge, pig dung or horse Preparing duckweed (DW) and water hyacinths dung) with crops residues (i.e banana leaves, (WH) for vermicomposting: sugarcane, duckweed and water hyacinth) as Duckweed (DW) was collected from the feeding materials for earthworms showed different drainage canals around the Central Laboratory for yield biomass and quality of produced Aquaculture Research (CLAR) and cultivated on vermicomposts (Dominguez, 2004 and Joshi et fish effluent ponds in a concrete pond. After two al., 2015; Sartaj et al., 2016). weeks, duckweed was harvested and subjected to At the same moment, water hyacinth is of a air-drying for 24 hours and then in an oven at major environmental concern in many countries. It 50C for another 24 hours to reach a constant quickly invades large water areas, due to its high weight. Thereafter, it was grinded and stored in rate of vegetative propagation, and forming dense plastic bags until used directly with fresh cow mats that obstructs waterways. It affects all water- dung to feed earthworm and produce based economic activities, including fishing, vermicompost. Bioscience Research, 2020 volume 17(2): 1511-1520 1512
Moustafa et al., Physico-chemical and microbial activities of vermicompost For water hyacinth (WH), only plant leaves Growth promoters Amino acid analysis: were collected from plants in the drainage canals To determine total free amino acids, the adjacent to the CLAR and subjected to drying in modified of ninhydrine colorimetric method that the oven at 50C for 48 hours to reach a constant described by (Rosein, 1957 and Selim et al., weight, after that it was grinded and stored in 1978) was used for this purpose. Growth plastic bags until used directly with fresh cow promoters in samples of vermicompost were dung to feed earthworm and produce estimated according to the method described by vermicompost. (Dobrev et al., 2005). Vermicompost production: Microbiological analysis of vermicompost Fresh cow dung was mixed with either dried samples duckweed or dried water hyacinth at a ratio of 2:3, Sampling and sample preparation respectively, and moistened to 60-70% in Five grams from vermicompost samples were styrofoam boxes with dimensions of 60× 40× 30 placed in sterile Stomacher bags and treated by a cm. After 24 h, three species of earthworm Stomacher 400 Circulator for 60 s at middle speed (Eisenia fetida; Perionyx excavatus and after adding 45 ml sterile 0.85% NaCl. The Lumbricus rubellus) were added to the media at a Stomacher blending step was repeated three rate of 50 g worm per 1000g media. For eight times and the microbial suspension was obtained. weeks the boxes were checked weekly and re- moistened and mixed until the vermicompost Estimation of total viable bacteria count matured. All boxes were kept indoor and the Tenfold serial dilution of the microbial temperature maintained between 20-25℃ during suspensions obtained with the protocol described the vermicompost maturation period. At harvest, above made with sterile 0.85% NaCl were plated vermicompost was checked manually on white onto plate count agar medium (PCA) for the surface plastic and the adult as well as pre-adult estimation of total viable counts, counts of colony earthworms were removed then the vermicompost forming units (CFU) were estimated after three was returned to the boxes again for one more days of incubation at 28°C and were calculated month. Later, the vermicompost was checked per gram vermicompost. The total antibiotic- again and all hatched earthworms were removed. resistant bacteria were estimated by planting the The harvested vermicompost was packed in same dilution onto PCA medium sublimated with plastic bags and sent for the analysis instantly. penicillin, ampicillin, erythromycin and tetracycline to final concentration of 20mg/L. Physiochemical analysis for vermicompost: Vermicompost samples were dried in a Total community DNA extraction from ventilated oven at 70 oC to a constant weight. vermicompost samples Samples were grinded in stainless steel mill with TC-DNA was extracted from 250 mg 0.5 mm sieve and kept in plastic containers for vermicompost of each treatment (three replicates chemical analysis. The samples (1 g of each each). D Neasy Power Soil kit was used for the sample) were dry-ashed in a muffle furnace at 450 extraction according to the manufacturer’s oC for 6 hours for determination ash and organic protocol. TC-DNA was diluted (1:5) using Tris- matter content. EDTA and stored at -20. The integrity and quality Macronutrients were extracted using the dry of extracted TC-DNA were confirmed using ashing digestion method (Chapman and Pratt, agarose gel electrophoresis and Nanodrop 2000 1978). Nitrogen was determined by using the spectrophotometer (Thermo Fisher Scientific). Kjeldahl method, the ash was dissolved in HCl (2N) and phosphorus was photometrical Quantification of total bacteria in TC-DNA determined in the digested solution using vanado- using 16S rRNA gene molybdate color reaction according to the method The total bacterial 16S rRNA gene copy described by Jackson (1973). Potassium was numbers were estimated in TC-DNA of compost measured in the digested suspension using the samples using the universal primers (Eub338 and Flame-photometer, (Eppendorof, DR Lang). Eub518) according to (Fierer et al., 2005). Organic matter content was determined according to Walkely and Black (1934). Bioscience Research, 2020 volume 17(2): 1511-1520 1513
Moustafa et al., Physico-chemical and microbial activities of vermicompost Table 1: Primers used in this study Target Primers Size Sequence Ta Reference gene used (bp) Eub338 ACTCCTACGGGAGGCAGCAG 16S rRNA 55°C 123 Fierer et al. 2005 Eub518 ATTACCGCGGCTGCTGG DVV ATIGCRAAICCICCRCAIACIACRTC nifH 53°C 454 Ando et al.2005 IGK3 GCIWTHTAYGGIAARGGIGGIATHGGIAA A real-time PCR detection system (Step One Plus vermicompost produced from cow dung alone Real-Time PCR System - Thermo Fisher recorded the significantly highest content of Ash Scientific) was used. Real time PCR was (51.6%), meanwhile vermicompost produced from performed with HOT FIREPol® EvaGreen® qPCR (cow dung + WH) and (cow dung + DW) came in Mix Plus (Solis BioDyne, Estonia) in a final the second rank without any significant volume of 20 µL. Real time PCR conditions were differences between both of them. as follow: Activation step for 12 min at 95°C Moreover, for C: N ratio , data in table 2 followed by 40 cycles of 95°C for 30s, 60°C for 1 showed that there are no markedly differences min, 72°C for 1 min and a final elongation step at found between tested treatments. However, data 72°C for 5 min. Primers sequences are listed in related to nitrogen content revealed that Table 1. vermicompost produced from (cow dung + WH) recoded the highest nitrogen content followed by PCR- based detection of genes encoding plant that produced from (cow dung + DW). The growth promoting related functions. vermicompost produced from cow dung The extracted TC-DNA was analyzed by PCR to individually was recorded the lowest value of amplify marker genes as biological indicator for nitrogen content. soil fertility such as nifH gene encoding the The same trend was observed in “P” content , dinitrogenasereductase. The nifH gene is the whereas the highest “P” content was recorded in biomarker most widely used to study the ecology vermicompost produced from (cow dung + WH) and evolution of nitrogen-fixing bacteria. Primers followed by (cow dung + DW) ,which did not differ sequences are listed in Table 1. significantly from the vermiompost from (cow dung alone). RESULTS AND DISCUSSION The “K” content showed different trend whereas the highest K content noticed in Physico-chemical parameters: (cowdung+ DW) followed by that of (cow dung Data in table (2) reveal that there is a relation alone), meanwhile vermicompost produced from between dry weight and humidity whereas (cow dung + WH) recoded the lowest content of vermicompost that produced from only cow dung “K”. without additive aquatic plants recoded higher These results can be attributed to releasing humidity. Although vermicompost produced by nutrients (N, P, K and other nutrients) from used mixing (cow dung + WH) recorded the lowest organic wastes for feeding earthworm. Ndegwa value of humidity it produced the higher value of and Thompson (2001) reported that the important dry matter than those produced from (cow dung + plant nutrients such as nitrogen, potassium, DW) or cow dung alone. These results indicated phosphorus, and calcium present in the feed that dry matter of vermicompost can be enhanced material are converted through microbial action by adding water hyacinth (7.53g) and duckweed into forms that are much more soluble and (7.33g) during vermicomposting. available to the plants than those in the parent In respect for organic matter, vermicompost substrate. Several studies supported these finding produced from (cow dung + WH) recorded the whereas they indicated that activities of significantly highest organic matter followed by endosymbiotic microbes and gut enzymes of that produced from (cow dung + DW) treatment. earthworm aid in transformation of ingested The significantly lowest organic matter observed organic matters into vermicompost constituting with vermicompost produced from (cow dung essential macronutrients such N, P, K in plant alone). available forms (Kaushik and Garg 2004and Chaulagain et al., 2017). Also, data concerning ash indicated that Bioscience Research, 2020 volume 17(2): 1511-1520 1514
Moustafa et al., Physico-chemical and microbial activities of vermicompost Table 2: shows different physico-chemical parameters as affected by adding duckweed or water hyacinth to the fresh cow dung. Fresh Dry Organic Humidity Treatments Weight Weight matter Ash C / N ratio N (%) P (%) K (%) % (g) (g) O.M (%) Cow dung (CD) 10 7.27c 27.34a 21.06 c 51.6a 11.65 a 1.05 c 0.40 b 2.05 b Cow dung + (WH) 10 7.53a 24.67c 28.49 a 46.84b 11.64 a 1.42 a 0.90 a 1.80 c Cow dung + (DW) 10 7.33b 26.67b 26.45 b 46.88b 11.62 a 1.32 b 0.41 b 2.12 a Means were represented as average of replicates. Different letters are express for significant differences while the same letters are non-significant at L.S.D. p>0.05. Whereas Duckweed:DW;water hyacinth:WH. Since 1972, earthworms are known as voracious nitric N (Cegarra et al. 1992). Orozco et al. (1996) feeders on organic wastes (whether animal also showed that in addition to increasing N wastes or crops residues). Earthworm used a availability in vermicompost, P, K, Ca, and Mg small portion of nutrients for their body growth, availability in the vermicompost are also greater they excrete a large part of these consumed than in the starting feed material. wastes in half digested form. The intestine of Supplementation cow dung with additives earthworms rich with a wide spectrum of material (agro-wastes such as banana wastes microorganisms, enzymes, hormones, etc. these saw dust) may lead to improving quality of half -digested substrate decompose rapidly and vermicompost, whereas Chaulagain et al., (2017) converted into vermicompost by microorganisms showed that high quality vermicompost containing within short time (Edwards and Lofty 1972). nitrogen, phosphorus, potassium and the greater Moreover, they indicated that about 5–10% of microbial population can be obtained from the ingested material is absorbed into the tissue for mixture of cow dung and banana wastes as earthworm’s growth and metabolic activity and compared to other mixtures (saw dust and leaf rest is excreted as vermicast. The vermicast is litter). mixed with mucus secretion of the gut wall, and According to what aforementioned, the associated microbes and transformed into nutrient status of vermicompost depends on vermicompost. inputs or substrates (the type of wastes and its In addition, Atiyeh et al., (2002) showed that content of nutrient) that offered for feeding the earthworms certainly fragment the organic earthworms. Physicochemical changes during the waste substrates increase rates of mineralization, degradation of organic matter (vermicomposting) rapidly converting the wastes into humus-like may be carried out through enzymatic digestion, substances. Another study by Suthar (2007) enrichment by minerals, which in turn depend on showed that earthworm processed waste material types of organic and inorganic materials, which contains higher concentration of exchangeable interpret differences in nutrients content in minerals due to enhanced microbial activity during vermicompost according to differing mixture cow the vermicomposting process, which consequently dung alone or supplemented with either duckweed enhances the rate of mineralization. Also, Rupani or water hyacinth. These findings supported with et al. (2013) reported that total nitrogen content in findings of (Kale 1998; Suthar 2007) who vermicomposts may be ranged quite widely from concluded that different nitrogen pattern and 0.1% to 4% or more depending on the organic mineralization activities depend on total amount of wastes used to feed earthworm. Lower K content nitrogen in the initial waste and on the earthworm in vermicompost is reported by Kale (1995) activity in the waste decomposition. (0.63%) in vermicompost produced from a mixture of cow dung + Banana leaves, although banana Amino acids and growth promoters content: waste considered rich in K content. Meanwhile, Vermicompost produced from (cow dung phosphorus content may be ranged from 0.1%- +WH) surpassed other treatments in amino acids 0.3% in vermicompost as reported by (Kale, content and growth promoters content (Table3). 1995). Whereas, vermicompost from (cow dung + WH) The studies on the effect of vermicomposting recoded (0.81mg/g dry weight) followed by on some components of organic waste showed vermicompost from (cow dung + DW) that that vermicompost enhances the degree of contained (0.54mg/g dry weight). Meanwhile, the polymerization of humic substances along with a vermicompost produced from (cow dung alone) decrease of ammonium N and an increase of recorded the significantly lowest content of amino Bioscience Research, 2020 volume 17(2): 1511-1520 1515
Moustafa et al., Physico-chemical and microbial activities of vermicompost acids. Table 3:shows the impact of adding aquatic plants (Duck weed and Water hyacinth) on vermicompost amino content and growth promoters. Amino acids Abscisic GA3 IAA Treatment (mg/g dry weight) acid (g/100g) (g/100g) (g/100g) Cow dung (CD) 0.27 c 0.33 c 1.08 b 0.04 b Cow dung+ Water Hyacinth (WH) 0.81 a 1.67 a 1.37 a 0.35 a Cow dung + Duckweed (DW) 0.54 b 0.37 b 0.55 c 0.06 b Means were represented as average of replicates. Different letters are express for significant differences while the same letters are non-significant at L.S.D. p>0.05 . Duckweed :DW; Water hyacinth :WH. medium were not significantly different between Regarding the growth promoters as presented different samples Fig(1). However, the CFU in table 3, vermicompost (cow dung + WH) counts determined for water hyacinth (WH)tended contained the highest amount of abscisc acid to be higher in total bacterial counts compared to (1.67g /100g) comparing to the other two other treatments (Log CFU g-1 = 9.98±0.14). treatments. Also, vermicompost (cow dung + DW) came in the second rank. Meanwhile, the 16S rRNA gene copy numbers vermicompost from cow dung alone produced the The average copy numbers of 16S rRNA lowest value for Abscisic acid. gene counts determined for water hyacinth (WH) In addition, vermicompost produced from (cow also tended to be higher in compared to other dung + WH) contained the highest value of GA3 treatments (Log 16S rRNA gene copies g-1 = (1.37 g /100g) followed by vermicompost from 10.25±0.06). cow dung alone , while, the vermicompost from (cow dung + DW) came in the last rank PCR- based detection of genes encoding plant significantly. growth promoting related functions. Finally, vermicompost produced from (cow The nifHgene encoding the nitrogenase dung + WH) had the highest value of IAA followed reductase indicating the presence of nitrogen by vermicompost from (cow dung + DW). fixing bacterial populations that was detected in While,the vermicompost from cow dung alone had total community DNA extracted from each the lowest content of IAA, although the differences compost samples. Our results showed relatively between vermicompost (cow dung + DW) and higher band intensity for nifHgene amplified from vermicompost from cow dung alone in IAA content WH TC-DNA followed by DW compared to the were not significant. cow dung control compost. These results are in consistence with Tajbakhsh et al. (2011) who indicated that Antibiotic resistant bacteria counts in different vermicompost is considered as an excellent vermicompost samples product since it has desirable esthetics, plant High bacterial populations were detected growth hormones, higher level of soil enzymes, resistant to different antibiotic such as penicillin, and greater microbial population, as tends to hold ampicillin, erythromycin and tetracycline (Table 4). more nutrients over a longer period without However, cow dung +WH characterized by adversely impacting the environment. significantly lower bacterial population bearing The plant growth regulators and other plant antibiotic resistant to ampicillin and erythromycin, growth influencing materials, that is, auxins, while individual CD and (CD + DW) showed cytokinins, humic substances, etc., produced by almost similar values. microorganisms have been reported in Satchell (1983) indicated that there were vermicompost by Atiyeh et al., (2002); Muscolo et changes in soil microbial populations as al. (1999). The humic materials extracted from consequences of vermicompost application. Few vermicomposts have been reported to produce reports deal with field trials involving the auxin-like cell growth and nitrate metabolism of application of vermicompost. Kale et al., (1992) carrots (Daucuscarota) (Muscolo et al.,1999). studied vermicompost in a rice paddy in India. Microbiological analysis: The CFU counts determined on PCA agar Bioscience Research, 2020 volume 17(2): 1511-1520 1516
Moustafa et al., Physico-chemical and microbial activities of vermicompost Figure 1: Total bacteria counts in different vermicompost samples determined using culture dependant methods (CFU counts) and in total community DNA (16S rRNA gene copies), the occurrence of nifH gene in TC-DNA (5 µl of the PCR products) is shown above the graph (three replicates for each compost type) Table 4: Antibiotic resistant bacteria counts in different vermicompost samples Sample Penicillin Ampicillin Erythromycin Tetracycline Cow dung(CD) 10.82±0.07 a 8.72±0.16 b 10.80±0.05 a 10.82±0.05a Cow dung +Water Hyacinth 10.81±0.04 a 7.82±0.48 c 9.07±0.026 b 10.81±0.08a (WH) Cow dung + Duck Weed (DW) 10.81±0.05 a 9.28±0.03 a 10.79±0.098 a 10.82±0.04a Means were represented as average of replicates. Different letters are express for significant differences while the same letters are non-significant at L.S.D. p>0.05. more deeply linked to the richer microbial Significant increases in the colonization of population in vermicompost (Tucker 2005). soil by microorganisms (including N-fixers, The quality of soil can be explored using Actinomycetes, spore formers, and Mycorrhizae) molecular detection of marker genes involved in occurred in the experimental plots compared to biogeochemical cycles (van Elsas & Costa, 2007) the control plots without added vermicompost. such as the plant growth promoting related Moreover, Subler et al., (1998) reported that functions as nifHgene encoding the nitrogenase vermicompost is rich in microbial diversity, reductase (Gaby and Buckley 2012) indicating the population, and activity .Also,Atiyeh et al.,(2002) presence of nitrogen fixing bacterial populations. showed that the earthworms certainly fragment However, the abundance of these marker genes the organic waste substrates stimulate enhanced is influenced by numerous factors such as plant microbial activity and increase rates of development stage, the content of organic matter. mineralization, rapidly converting the wastes into In the present study higher abundance of humus-like substances.Some microbial and microbial populations bearing nifH genes were enzyme activities are occurring within the gut of detected in WH compost samples (Fig. 1) which is the earthworm (Alter and Mitchell, 1992). characterized by higher Organic matter content. The research team at Ohio State University The importance of this study emerged from has demonstrated that it is not just because of the that plant nutrition through vermicomposts relatively high levels of nutrients and enables biotechnologically and energetically micronutrients within earthworm’s castings. The undemanding utilization of by-products or waste explanation of vermicompost’s influence may be products from a wide range of industrial and Bioscience Research, 2020 volume 17(2): 1511-1520 1517
Moustafa et al., Physico-chemical and microbial activities of vermicompost agricultural activities, which is one of the ways of the Environmental Issues in Egypt (A Case increasing soil fertility, the use of which has Study). Journal of Applied Sciences assumptions of applicability on each agricultural Research, 6(8): 1116-1124. land. AdhikaryS. (2012). Vermicompost, the story of organic gold: A Review, Agricultural CONCLUSION Sciences, 3(7), 905–917. The results suggesting that vermicompost is a https://doi.org/10.4236/as.2012.37110. promising organic fertilizer, where it has a Ahmad, Z. ; Hossain, N. S. ; Hussain, S. considerable growth promoters. Moreover, G. ; Khan, A. H.. (1990). Effect of duckweed vermicomposting is an effective mean to turn (Lemna minor) as complement to fertilizer wastes as well as aquatic plants into valuable nitrogen on the growth and yield of rice. products with economic value that protect the International Journal of Tropical environment and replenish soil fertility. Finally, Agriculture Vol.8 No.1 pp.72-79. adding aquatic plants to cow dung during Alter D, Mitchell A (1992) Use of vermicompost vermicomposting increasing nutrient contents, extract as an aluminum inhibitor in aqueous amino acids content and microbial population, solution. Commun Soil Sci Plant Anal particulraly vermicompost produced from (cow 23:231–240 dung + water hyacinth) which is characterized by Atiyeh RM, Lee Edwards CA, Arancon NQ, higher bio-chemical compostion and bacterial Metzger JD (2002) The influence of humic populations, and abundance of nitrogen fixing acids derived from earthworm-processed bacteria with lower population of antibiotic organic wastes on plant growth. resistant bacteria compared to the DW and BioresTechnol 84:7–14. Control compost samples. Bohlen P. J. (2002).Earthworms, Encyclopedia of Soil Science, Marcel Dekker. Inc. USA. CONFLICT OF INTEREST Cegarra J, Famandez FM, Tercero A, Roig A The authors declared that present study was (1992) Effects of vermicomposting of some performed in absence of any conflict of interest. components of organic wastes.Preliminary results.Mitteilungen-aus-dem- ACKNOWLEGEMENT hamburgischenzoologischen-museum-und- This research was accomplished through Institute 89:159–167 cooperation among the National Research Centre, Chapman, H.D. and Pratt, P.T. (1978).Methods of Central Laboratory for Aquaculture Research analysis for soils, plants and water.University (CLAR), Agricultural Research Centre (ARC) and of California, Dept. Agric. Sci., USA, 320 p. Dept. of Microbiology, Faculty of Agriculture, Cairo Chaulagain, A.;, B. Maharjan; R. Pathak; S. Piya; University. The authors would like to express their S. Chimoriya; I. S; D. P. Gauchan; J. gratitude for all members for their effort to Lamichhane.(2017).Effect of feeding accomplish this work and looking forward to materials on yield, quality of vermicompost, complete the remaining chain of this approach. multiplication and reproduction of eiseniafoetida. Journal of science, Copyrights: © 2020@ author (s). engineering and Technology Vol. 13, No. This is an open access article distributed under the II,,pp 15-25. terms of the Creative Commons Attribution License Chu JianJun; Ding Yi; ZhuangQiJia.(2006). (CC BY 4.0), which permits unrestricted use, Invasion and control of water hyacinth distribution, and reproduction in any medium, (Eichhorniacrassipes) in China. J. Zhejiang provided the original author(s) and source are Univ., 7 (8): 623-626. credited and that the original publication in this Dominguez J. (2004). State-of-the-art and new journal is cited, in accordance with accepted perspectives on vermicomposting research, Earthworm Ecology, C. A. Edwards (Ed.), academic practice. No use, distribution or CRC Press LLC, 2004, 401–424. reproduction is permitted which does not comply https://doi.org/10.1201/9781420039719.ch20 with these terms. Edwads, C.A. and I. Burrows. (1988). The potential of earthworms compots as plant REFERENCES growthmedia in Neuhauser, C. A. (Ed.), Abou Hussein S. D. and O. M. Sawa. (2010). The Earthworms in Environmetal and Waste Utilization of Agricultural Waste as One of Mangement. SPB Academic Publishing, The Bioscience Research, 2020 volume 17(2): 1511-1520 1518
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