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Pak. J. Weed Sci. Res. 11(3-4): 89 - 94, 2005 BIOHERBICIDAL EFFECTS OF TREE EXTRACTS ON SEED GERMINATION AND GROWTH OF CROPS AND WEEDS
Muhammad Azim Khan1, Khan Bahadar Marwat1,
ABSTRACTLaboratory based studies were undertaken during November/December, 2003 in Weed Research Laboratory, Department of Weed Science, NWFP Agricultural University, Peshawar, Pakistan to investigate the allelopathic potential of aqueous extracts of leaves of Prosopis juliflora and Eucalyptus camaldulensis and bark of Acacia nilotica. The concentrations studied included 150 g L-1 of each species. A check, tap water (0 g L-1) was also included for the comparison. The fresh green leaves of these trees were dried in shade and grinded. The powder of each species were soaked @ 150 g L-1 in water. The results showed that the germination percentage, seedling length (mm) and biomass yield (mg) plant-1 of Ipomoea sp., Asphodelus tenuifolius, Brassica campestris and Triticum aestivum were significantly affected by tree extracts as compared to control. Eucalyptus and Acacia had stimulatory effect on germination percentage of A. tenuifolius, while P. juliflora and E. camaldulensis had inhibitory effect on B. campestris. All extracts had inhibitory effects on seedling length of T. aestivum and B. campestris. Treatment means indicated that P. juliflora and E. camaldulensis are more allelopathic than Acacia. Effect of Acacia on the test species was statistically comparable with control, exhibiting its non-inhibitory role in the test species. Species means indicated that Ipomoea sp. and T. aestivum were less negatively affected than B. campestris and A. tenuifolius. Hence, P. juliflora and E. camaldulensis can be exploited as bioherbicides for sustainable weed management. Key words: Acacia, mesquite, wild onion, morning glory, allelopathy, inhibition. INTRODUCTIONAllelopathy is a chemical process that a plant uses to keep other plants out of its space. It is a natural and environment-friendly technique which may prove to be a unique tool for weed management and thereby increase crop yields. Chemicals with allelopathic potential are present in virtually all plants and in most tissues, including leaves, stems, flowers, roots, seeds and buds. Under appropriate conditions these chemicals may be released into the environment (generally the rhizosphere) in sufficient quantities to affect the neighbouring plants. Crop allelopathic interactions may provide weed control in the crops by various ways such as (a) use of phytotoxic crop residues as mulches and cover crops (b) use of allelopathic plants in crop rotations (c) crop mixtures and intercropping (d) germplasm selection (e) use of allelopathic crop water extracts. Phytotoxic mulches and cover crops, allelopathy may be utilized in weed management systems through the manipulation of allelopathic cover crop residues in annual and perennial cropping systems. The allelopathic crops may affect the germination of subsequent crops, therefore, those crops should be included which are tolerant. One potential technique of exploiting allelopathy in weed management is the transfer of allelopathic characteristics from wild types or unrelated plants into the commercial crop cultivars i.e. germplasm selection. If the new allelpathic character does not have undesirable effects, this technique could increase the ability of the crop to compete naturally against the weeds. Very few attempts have been made to enhance the weed suppressive potential of crop plants through conservation or non-traditional breeding programmes, even though this is a logical way to integrate the biorational approaches to pest control in the current production systems. The superior weed suppressing genotypes have been reported in cucumber, oat, rice, sunflower, soybean, sorghum, pearl millet and Brassica campestris (Ata and Jamil, 2001). These allelochemicals offer great potential for the pesticides because they are free from problems associated with the present pesticides. Therefore, allelochemicals are current area of research for the development of new herbicides. These could be used for weed control directly or their chemistry could be used to develop new herbicides. The water extracts of many crops e.g. sorghum, sunflower, B. campestris, E. camaldulensis and tobacco etc, contain a number of allelochemicals which are more effective and economical to control the weeds of many crops. In mature sorghum plants, nine water soluble allelochemicals have been identified which are phytotoxic to the growth of certain weeds. Several reports address the importance of allelopathic effect of various trees. E. camaldulensis, Prosopis juliflora, and Acacia nilotica, significantly affected seed germination and seedling growth of several crops and/or weed species (Velu et al. 1996; Dhawan and Gupta, 1996, Khan et al. 2004). Sundaramoorthy et al. (1995) concluded that P. juliflora significantly inhibited the seed germination in pearl millet. Ibrahim et al. (1999) reported that E. camaldulensis has allelopathic effect on crops. Keeping in view the importance of the allelopathic potential of some forest tree species, these experiments were conducted under the laboratory conditions with these objectives: a) to investigate allelopathic status of different forest trees. b) to quantify the response pf crop and weed seeds to different trees extracts.
MATERIALS AND METHODSLaboratory based experiments were conducted during November/December, 2003 in Weed Research Laboratory, Department of Weed Science, NWFP Agricultural University Peshawar, Pakistan, to investigate the bioherbicidal effects of tree extracts on seed germination and growth of crops and weeds. The experiments were laid out in completely randomized design. The experiment was repeated under the ambient conditions at room temperature around 22 + 2 0C. Fifteen seeds each of Triticum aestivum, Ipomoea spp., A. tenuifolius and B. campestris were placed in the petri dishes on blotting paper. The seeds of the test species were treated with fungicide Topsin-M 70 % @ 2 g kg-1 to avoid the fungal attack. The ground dry (in shade) leaves of P. juliflora and E. camaldulensis and ground bark of A. nilotica were soaked for 24 hours in tap water at room temperature. The concentrations of P. juliflora, E. camaldulensis and A. nilotica @ 150 g (ground powder in water) and 0 g L-1. Experiment was repeated with the same protocol in December 2003. Each treatment comprised of three pertri dishes planted to any one of the above stated 4 species. The given concentrations of extracts were applied to the respective treatments. Mere tap water was applied to the petri dishes of 0 g L-1. After 20 days, the data on seed germination percentage, seedling length (mm) and biomass yield seedling-1 (mg) were recorded during the course of studies. Combined analyses of the two experiments for each trait was run and the means were separated by Student Newmann Keul’s Multiple Range test by using MSTATC software (Steel and Torrie, 1980). RESULTS AND DISCUSSION Germination percentageAnalysis of the data showed that germination percentage of all the test species was significantly affected by various extracts and their interaction with the tested species (Table-1). Maximum (85%) germination in Ipomoea sp. was recorded under P. juliflora and Acacia while A. tenuifolius showed the least (6.67%) in P. juliflora and control treatments. Triticum and Brassica showed similar results. However, these values were statistically at par with the values of control. Table-1 shows that germination of B. campestris was significantly decreased by P. juliflora and E. camaldulensis. Minimum germination (30%) of B. campestris was recorded in P. juliflora and E. camaldulensis treatments as compared to 95 and 91.7 % in A. nilotica and control treatments, respectively. Treatment means showed that minimum germination was recorded in P. juliflora treated pots while maximum germination was recorded for Ipomoea sp., other species showed statistically similar results to extracts of trees. It can be concluded from the Table-that the effect of tree extracts on seed germination of Ipomoea sp. was stimulatory when compared with other species. Similar results have been reported by other scientists. Velu et al. (1996) reported the allelopathic effects of E. camaldulensis, P. juliflora and A. nilotica on legumes seeds. Al-Humaid and Warrag (1998) reported that germination percentage of Cynodon dactylon seeds decreased with increasing leaf extract concentration of P. juliflora. Putnam (1984) reported that E. camaldulensis species released volatile compounds such as benzoic, cinnamic and phenolic acids, which inhibit growth of crops and weeds growing near it. Prosopis juliflora reduced the germination percentage of gram and sorghum (Chellamuthu et al. 1997). Seedling length (mm) Analysis of the data showed that different extracts had significant effects on the seedling length of crops and weeds. Seedling length of Ipomoea sp. was significantly decreased by Eucalyptus while the rest of the tree extracts showed results that were comparable with the check. Similarly, the values for A. tenuifolius were statistically at par with each other in different extracts. In case of T. aestivum and Brassica, Prosopis and Eucalyptus showed inhibitory effect on the seedling length when compared with the control. Hence in these findings Prosopis and Eucalyptus showed inhibitory effect on crops. The treatments means showed that minimum (9.33 and 14.46 mm) seedling length was recorded in E. camaldulensis and P. juliflora treated treatments as compared to 33.08 mm in control treatment, thus P. juliflora and E. camaldulensis significantly decreased the seedling length of all the test species (Table-2). Analyzing the species means, the A. tenuifolius showed the minimum (11.29 mm) seedling length, while other species showed statistically similar results. It can be concluded from the results that Prosopis and Eucalyptus are the most harmful plants, inhibiting the crop seed germination and growth. These studies show similar results with Pawar and Chawan (1999) who reported that some forest trees including E. globolus reduced up-take of Ca, Zn and Mg in sorghum resulting in reduced growth. They further added that the E. globolus caused the greatest reduction in the absorption of Ca in sorghum. Schumann et al, (1995) reported that E. grandis water extracts significantly reduced weed establishment. Biomass yield (mg) plant-1 Table-3 depicts the biomass of different species as affected by different tree extracts. Maximum biomass (125 mg plant-1) of Ipomoea sp. was recorded in Acacia followed by control. In case of A. tenuifolius and T. aestivum, the values in all the treatments were comparable. Prosopis and Eucalyptus negatively affected Brassica where 14.5 and 10.33 mg plant-1 biomass, respectively was recorded in Prosopis and Eucalyptus as compared to 37.5 mg in control. It is evident from the treatment means that maximum biomass of 66.79 and 56.13 mg plant-1 was recorded in Acacia and control treatments as compared to the minimum in E. camaldulensis and P. juliflora treatments having the values 39.71 and 48.42 mg, respectively. The species means indicated that maximum biomass of 90 mg plant-1 was recorded for T.aestivum followed by 89.04 mg plant-1 by Ipomoea sp. Thus, it can be inferred from the data that Prosopis and Eucalyptus have consistent negative effect on the germination and growth of crops as well as weeds. It can be concluded from the results that T. aestivum has the competitive advantage over the weeds studied. Hence, T. aestivum can pove a better competitor if infested with these weeds. Pawar and Chawan (1999) reported that some forest trees including E. globolus reduced up-take of Ca, Zn and Mg in sorghum resulting in reduced growth. They further added that E. globolus caused the greatest reduction in the absorption of Ca in sorghum. Schumann et al. (1995) reported that E. grandis water extracts significantly reduced weed establishment. Noor et al. (1995) reported that Triticum aestivum showed inhibitory response to extracts of E.s camaldulensis. Table-1. Germination percentage of the test species
Table-2. Seedling length (mm) plant-1 of the test species
Table-3. Biomass yield (mg) plant-1 of the test species
CONCLUSIONS i. P. juliflora and E. camaldulensis have the potential to be used as bioherbicides in the future. ii. The plantation of E. camaldulensis in agro-forestry should be discouraged as there could be a risk of dissolved allelopathins in the irrigation water. iii. Further intensive studies are emphasized to explore the full knowledge of allelopathy in these trees so that we can get rid of huge import bills of herbicides. REFERENCES CITEDAl-Humaid, A.I. and M.O.A. Warrag 1998. Allelopathic effects of mesquite (Prosopis juliflora) foliage on seed germination and seedling growth of bermudagrass (Cynodon dactylon). J. Arid Environ. 38: 237-243. Ata, Z. and M. Jamil. 2001. Allelopathic suppression of weeds: a new field in need of attention. Daily Dawn, December 31, 2001. Chellamuthu, V., T.N. Balasusbramanian, A. Rajarajan and S.N. Palaniappan. 1997. Allelopathic influence of Prosopis juliflora on field crops. Allelopathy J. 4(2):291-302. Dhawan, S.R. and S.K. Gupta. 1996. Allelopathic potential of various leachate combinations towards SG and ESG of Parthenium hysterophorus Linn. World Weeds. 3(3-4): 135-144. Ibrahim, E.E., H.A. Mohamed and A.F. Mustafa. 1999. Allelopathic effects of Eucalyptus camaldulensis and Conocarpus plantations on germination and growth of two sorghum species. Sudan J. Agric. Res. 2: 9-14. Khan, M.A., K.B. Marwat and G. Hassan. 2004. Allelopathic potential of some multi purpose tree species (MPTS) on the wheat and some of its associated weeds. International J. Biol. & Biotech. 1(3): 275-278. Noor, M., U. Salam and M.A. Khan. 1995. Allelopathic effects of Prosopis juliflora. J. Arid Environ. 31 (1): 83-90. Pawar, K.B. and P.D. Chawan. 1999. Influence of leaf leachates of plant species on mineral nutrition of Sorghum bicolor L. Moench. Allelopathy J. 6:87-92. Putnam, A.R. 1984. Allelopathic chemicals. Can natural plant herbicides help control weeds. Weeds Today, 15: 6-8. Schumann, A.W., K.M. Little and N.S. Eccles. 1995. Suppression of seed germination and early seedling growth by plantation harvest residues. South African J. Plant and Soil 12: 170-172. Steel, R.G.D. and J.H. Torrie. 1980. Principles and procedures of statistics; a biological approach. 2nd Ed. McGraw Hill Book Co. New York. Sundaramoorthy, S., N. Kalra and D.D. Chawan. 1995. Allelopathy and Prosopis juliflora provenance Israel in semi-arid agroforestry systems. Indian J. Forest. 18(3): 214-220. Velu, G., P.S. Srinivasan, A.M. Ali and S.S. Narwal. 1996. Phytotoxic effect of tree crops on germination and radicle extension of legumes. Allelopathy 1: 299-302.
1 Department of Weed Science, NWFP Agricultural University Peshawar – Pakistan e-mail: ahmadzaipk@yahoo.com. 2 Department of Maths, Stats and Computer Science, NWFP Agricultural University, Peshawar – Pakistan. |
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