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EFFECT OF BOKASHI BOTTOM ASH DOSAGES ON THE GROWTH OF VETIVER GRASS (Vetiveria

zizanioides) AND ITS LEAD CONTENT

NUNUNG SONDARI

Faculty of Agriculture of Winaya Mukti University Jalan Pahlawan No. 69 Bandung

e-mail : [email protected]

ABSTRACT

The experiment was conducted at a greenhouse of Agricultural Faculty of Winaya Mukti University Tanjungsari Sumedang, West Java, from May to October 2009. The objective of this research was to see the effect of the bokashi bottom ash application on the growth and of vertiver grass and its lead content. The experiment used the environmental design of Randomized Block Design (RBD) that consist of five treatments and is repeated five times. The factor was the bokashi bottom ash dosages ( 0,5,10, 15, and 20 t ha-1 ). The results show that the application of bokashi bottom ash affected the growth of vetiver grass, except shoot root ratio.

The dosage of 15 t ha-1 presented a good effect to the plant height, the number of leaves and tillers. The bokashi bottom ash with dosage of 20 t ha-1 wasthe best effect in absorbing lead applied to vetiver grass.

Keywords: bottom ash, bokashi bottom ash, heavy metal Pb, vetiver grass

INTRODUCTION

Bottom ash is a coarse fraction produced from the coal burning furnace. Although it is often called as dangerous and poisonous waste, the ash has its own benefit. In the United State of America and India, bottom ash has been used as an effi- cient material in agriculture which is utilized as ameliorant (a substance to make the marginal soils better) to cultivate various kinds of plants (Kumar et al., 2000). Capp and Engle (1987) suggested that the ash from residual coal burnt can be uti- lized as a soil ameliorant and it has been tested to subtropical plants such as oats, wheat, and barley at Virginia University ( Sondari and Arifin, 2000). The chemical substance in bottom ash is highly depended on coal source. Chemically, the bottom ash contains some nutrients, micro ele- ments, which are highly potential and are neces- sary for various kinds of plants to growth (Sondari, 2005).

In this research, bottom ash was used to support the growth of vertiver grass. Vertiver grass an im- portant plant to produce essensial oil which used widely in cosmetics industry (soap, toothpaste,

gredient / flavor enhancer, perfume industry, phar- maceutical industry and medicine, preservatives, and insecticides (Taryana, 2008 ). The vetiver grass comes from India, Southeast Asia and The Tropical Africa (Bertea and Comuso, 2002 in Hobir, et al., 2006) and now more than 100 countries use and plant vetiver grass, for the production of essential oils or as a plant holder and rehabilitation of soil erosion (Xiurong et al., 2003 in Hobir et al., 2006).

Although the vetiver grass is a tropical plant, the plant can also grow is an area that has temp. of 0- 45°C and average annual rainfall of 300-6000 mm (Hengchaovanich, 1996 in Carey, 2000). Vetiver grass is known to be tolerant to heavy metals such as copper, nickel, chromium, aluminum, cadmium and arsenic (Troung, 1999a in Carey, 2000). It is more tolerant to the heavy metals Pb which has been tested in the mining area (Shu et al., 1999 in Carey, 2000). Due to its tolerant nature to heavy metal, vertiver grass is used as an accumulator plant for contaminated land.

Bokashi is one of organic manure, composts, pro- duced by of organic substance fermentation us- ing EM (Effective Microorganism) technology

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ment and is not biodegradable. Its toxicity is not changed over time. Based on that fact, in this re- search, bokashi bottom ash was used to support the growth of vertiver grass and to know its re- sponse as accumulator plant of Pb.

METHODOLOGY

Materials used in this experiment were Vetiver grass (Vetivera zizanioides), andisol soil, bokashi bottom ash (bottom ash, chicken manure, rice husks, straw, bran, EM 4, sugar water, and wa- ter), urea (45% N), Super Poshpate SP-36 (36%

P2O5), KCl (Pottasium Chloride)(60% K2O), Fungisida Dithane M-45 80 WP and Furadan 3G Insecticide. The composition of bokashi bottom ash was analyzed at Agro Chemical Laboratory, Lembang.

The experiment used the environmental design of Randomized Block Design (RBD), consisting of 5 of dosage treatments (0, 5, 10, 15, and 20 t ha-1 of bokashi bottom ash) and was repeated in 5 times.

The data of plant height, number of leaves, num- ber of tiller, shoot root ratio, Pb content of plant, and level of heavy metal within plant, were ana- lyzed by the F test with 5% significant level and Duncan’s Multiple Range Test. Determination of heavy metals in plants employed HNO3 and HClO4

of dry ashing.

RESULTS AND DISCUSSION The Plant Height

Chemical analysis of bokashi bottom ash shows the MgO = 1,527 % ; CaO = 5,376 % ; K2O = 0,57

% ; Zn = 0,0058 % ; Cu = 0,0014 %, Fe total = 1,7078 %. Result of different treatment test is shown in Figure 1. It can be seen that the growth of vertiver grass without the application of bokashi bottom ash shows the lowest plant height. The

significantly different from control. The application of bokashi bottom ash up to 15 t ha-1 increased the plant height but it decreased when the dosage of 20 t ha-1 was added at the age of DAP 35. Prob- ably, this is related to the absorption of macro nutrients by the plants that has reached the opti- mum point, so the addition of organic substances did not give any effect to the plants.

The contribution of nutrients from bokashi bottom ash occurred because of decomposition and min- eralization. This is in a line with Sondari (2005) who found that the application of 10 t ha-1 bokashi bottom ash accompanied with 15 t ha-1 green manure increased the growth of hermada (Shorgum bicolor L. Moench), because it can improve the chemical and physical properties of utisols soil, improved CEC (Cation Exchange Capacity) from 14 c mol (+) kg -1 to 20 c mol (+) kg -1 and also improved the availability of other nutrients. It also decreased Al saturation, increased P absorption, so the plants can grow better.

The Number of Leaves

Result of different treatment test is shown in Fi- gure 2. There were significant differences of leave between control and other treatments at all obser- vation time. The growth of vertiver grass without the application of bokashi bottom ash gave the lowest number of leaves. Bokashi bottom ash can improve the physical, chemical, and biological properties of the soil. The role of bokashi bottom ash in improving the physical properties of the soil leads to the good soil’s porosity. The soil becomes loose and the roots can grow better. To absorb more effective elements as a result, it stimulates the plant growth, including the growth of leaves.

The Number of Tillers

Result of different treatment test to the number of tillers is shown in Figure 3. The number of tillers in vetiver grass was highly affected by the photo- synthesis process and nutrients. Bokashi bottom

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P lant H ei g h t (c m )

Bokashi Bottom Ash (t ha)

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0.0 5.0 10.0 15.0 20.0

0.0 10.0 20.0 30.0 40.0 50.0 60.0 70.0 80.0 90.0 100.0 110.0 120.0 130.0 140.0 150.0

-21 DAP = 34.7830 + 2.5374 X - 0.0898 X^2; R^2 = 0.7676 -35 DAP = 56.8740 + 2.8311 X - 0.1161 X^2; R^2 = 0.8232

-49 DAP = 65.978714 + 2.126714 X - 0.070286 X^2; R^2 = 0.8098 -63 DAP = 71.657429 + 3.059129 X - 0.096471 X^2; R^2 = 0.8199 -77 DAP = 85.918389 + 3.622881 X - 0.116759 X^2; R^2 = 0.8199 -91 DAP = 104.435571 + 3.824071 X - 0.139929 X^2; R^2 = 0.7919 -105 DAP = 110.634429 + 3.404429 X - 0.107171 X^2; R^2 = 0.8777

Figure 1. Effect of bokashi bottom ash on plant height

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N u m b e r o f Le av es p e r H il l (l e a f)

Bokashi Bottom Ash (t ha)

-1

0.0 5.0 10.0 15.0 20.0

0.0 10.0 20.0 30.0 40.0 50.0 60.0

-21 DAP = 5.662857 + 1.012857 X - 0.039143 X^2; R^2 = 0.8133 -35 DAP = 6.545714 + 1.484714 X - 0.059286 X^2; R^2 = 0.7671 -49 DAP = 10.665714 + 1.444714 X - 0.051286 X^2; R^2 = 0.7985 -63 DAP = 13.1300 + 2.1780 X - 0.0840 X^2; R^2 = 0.8116

-77 DAP = 17.621429 + 3.235429 X - 0.126571 X^2; R^2 = 0.8289 -91 DAP = 24.574286 + 3.500286 X - 0.133714 X^2; R^2 = 0.8411 -105 DAP = 29.5600 + 3.0710 X - 0.1090 X^2; R^2 = 0.8508 Y

Y Y Y Y Y Y

Figure 2. Effect of bokashi bottom ash on the number of leaves

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N u m b e r o f Le av es p e r H il l (l e a f)

Bokashi Bottom Ash (t ha)

-1

0.0 5.0 10.0 15.0 20.0

0.0 1.0 2.0 3.0 4.0 5.0 10.0

-21 DAP = 0.2400 + 0.1230 X - 0.0050 X^2; R^2 = 0.7664

-35 DAP = 0.342857 + 0.199857 X - 0.008143 X^2; R^2 = 0.7362 -49 DAP = 0.725714 + 0.233714 X - 0.010286 X^2; R^2 = 0.7557 -63 DAP = 1.14286 + 0.297286 X - 0.010714 X^2; R^2 = 0.8395 -77 DAP = 2.355714 + 0.359714 X - 0.012286 X^2; R^2 = 0.8538 -91 DAP = 2.881429 + 0.722429 X - 0.027571 X^2; R^2 = 0.8818 -105 DAP = 3.977143 + 0.733143 X - 0.028857 X^2; R^2 = 0.8975 Y

Y Y Y Y Y Y

6.0

7.0 8.0 9.0

Figure 3. Effect of bokashi bottom ash on the number of tillers

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Lead Content

Result of different treatment test to the Pb con- tent is shown in Figure 4. It can be seen that the application of bokashi bottom ash increases the lead content with liniar curve. This result supports the idea that the vetiver grass is an accumulator for Pb. Therefore, it can be used for land remediation polluted by Pb (Roechan et al., 2000).

other dosages (5, 10, 15, and 20 t ha-1). The ap- plication of bokashi bottom ash to the soil makes better physical properties of the soil. Observation on the ages from DAP 21 until 105 shows the in- crease curve regression at the beginning, then it in- crease sharply with the increase of bokashi dosage.

According to Hardjowigeno (2003), organic sub- stance makes soil processing easier. The aggre- gates formation of mineral grains causes loose condition, be able to store water, increase total porosity, decrease weight content of the soil so the soil can hold water longer. The application of bokashi bottom ash holds up the soil permeabil- ity, and water availability that result in increasing the number of tillers.

Shoot Root Ratio

Result of different treatment test to shoot root ra- tio is shown in Table 1.

Table 1. Effect of bokashi bottom ash dosage on shoot root ratio

Treatment

Shoot Root Ratio (t ha-1)

0 1,459 a

5 1,426 a

10 1,430 a

15 1,417 a

20 1,427 a

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CONCLUSIONS AND SUGGESTIONS Conclusion

The application of bokashi bottom ash affected the growth of vetiver grass. The dosage of 15 t ha-1 gave a good effect to the plant height, the number of leaves, and the number of tillers. Bokashi bot- tom ash with the highest dosage of 20 t ha-1 con- tributed to the greater absorption of Pb by vetiver grass as Pb hyperaccumulator.

Suggestion

To support the growth of vetiver grass, it is better use bokashi bottom ash at the dosage of 15 t ha-

1, however for reclamating the land polluted by Pb, it is recommended using bokashi bottom ash at the dosage of 20 t ha-1.

REFERENCES

Capp, J.P. and C. F. Engle. 1987 . Fly ash in agricul- ture. Morgantown coal research centre. Bureau of Mines Morgantown. WV. West Virginia Univer- sity

Carey, Edward F, ED. D. 2000. Using vetiver grass for erosion control and bio-engineering at mines. Indonesian Mining Journal, Vol. 6 Num- ber 3 October 2000. ISSN 0854-9931.

Hardjowigeno, S. 2003. Ilmu tanah. Akademika Pressindo. Jakarta

Hobir, Ma’Mun, Purwiyanti S, dan Suhirman S, 2006.

Pedoman pelaksanaan pengelolaan plasma nutfah akar wangi (Vetiveria zizanioides L.

Nash). Pusat Penelitian dan Pengembangan Perkebunan, Bogor.

Kumar, V., Zacharia. K.A and Goawarni G, 2000. Fly ash use in agriculture: issues and concerns.

news and views. http://tifac.org.in/news/

flyagrl.htm, accessed on 5 August 2003.

Ritapunto, 2008. Bokashi ekpress. Jurnalisme Publik (Citizen Journalism). http://WIKIMU.COM accesed on 16 March 2009.

Roechan, S., A.M. Kurniawansyah, and Emmyzar, 2000. Pemanfaatan akar wangi (Vetiveria zizanioides, L.) sebagai tanaman sarana rehabilitasi tanah tercemar logam berat lead and cadmium. Laporan Akhir Riset Unggulan Terpadu VI (1998-2000).

Sondari, N. and Arifin M., 2000. Prospect of fly ash and bottom ash utilization in Agricultural Sector.

Indonesian Mining Journal. Vol.6; No.3. Oct.2000.

ISSN: 0854-9931.Directorate General of Mines Ministry of Mines and Energy.

Sondari, N, 2005. Beberapa sifat fisika dan kimia tanah, konsentrasi hara, serta hasil hermada (Shorgum bicolor L Moench) akibat pemberian abu sisa bakaran batubara (ASBB) dan pupuk hijau pada Typic kanhapludults. Disertasi Pasca Sarjana UNPAD, Bandung.

Taryana, Y ,2008. Perkebunan: Akar Wangi. UNWIM, Sumedang.

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