Testing of Toxicity of Herbicides Formulated On Non-Target Organisms of Earthworms

Risvan Anwar; Stefanie Juveria; Sarina Sarina; Eka Suzanna; Djatmiko Djatmiko

doi:10.32663/ja.v20i1.2699

Authors

Risvan Anwar University of Prof. Dr. Hazairin, SH
Stefanie Juveria Program Studi Agroteknologi Fakultas PertanianUniversitas Prof. Dr. Hazairin, S.H. Bengkulu
Sarina Sarina Program Studi Agroteknologi Fakultas PertanianUniversitas Prof. Dr. Hazairin, S.H. Bengkulu
Eka Suzanna Program Studi Agroteknologi Fakultas PertanianUniversitas Prof. Dr. Hazairin, S.H. Bengkulu
Djatmiko Djatmiko Program Studi Akuakultur, Fakultas Pertanian, Universitas Prof. Dr. Hazairin, SH

DOI:

https://doi.org/10.32663/ja.v20i1.2699

Keywords:

environmentally friendly, herbicide, lethal concentration (LC50), formulation

Abstract

This study aims to determine the toxicity of the formulated herbicide concentration to non-target organisms (non-target) earthworms. The study was conducted from April to July 2021. The design used was a completely randomized design (CRD) with nine (9) herbicide concentrations (K) treatments, namely: K0 = control, K1 = 200 ppm concentration (0.2 ml/l water ), K2 = concentration of 400 ppm (0.4 ml/ l of water), K3 = concentration of 600 ppm (0.6 ml/ l of water), K4 = concentration of 800 ppm (0.8 ml/ l of water), K5 = concentration 1000 ppm (1.0 ml/ l of water), K6 = concentration of 1200 ppm (1.2 ml/ l of water), K7 = concentration of 1400 ppm (1.4 ml/ l of water), K8 = concentration of 1600 ppm (1, 6 ml/l water). Each treatment was repeated 3 times. The observed variables were mortality concentration 50 (LC50) for 96 hours, survival rate, mortality percentage and worm weight. This study concluded that the mortality concentration of 50 (LC50) for 96 hours from the formulated herbicide against earthworms was 600 ppm, while the 100% mortality occurred at the herbicide concentration of 1400 ppm. The lowest survival rate was found at a concentration of 1400 ppm, where at that concentration all the test worms died. Meanwhile, the highest survival rate after the herbicide was 200 ppm where the worm mortality was 20%. The higher the concentration of herbicide formulation given to earthworms, the higher the mortality rate and decrease in body weight.

References

Affandi, R dan Tang, UM. (2002). Fisiologi Hewan Air. Unri Press. Pekan Baru.
Anwar, R., Suzanna, E., & Djatmiko, D. (2019). Pengujian Efektifitas Herbisida Formulasi Unihaz yang Ramah Lingkungan dan Murah Dalam Mengendalikan Gulma Di Multi Lokasi (II). Bengkulu: Universitas Prof. Dr. Hazairin SH.
Anwar, R., Suzanna, E., & Djatmiko, D. (2021a). Pengujian Efektivitas Herbisida Formulasi Terhadap Gulma Di Multi Lokasi. Jurnal Agroqua: Media Informasi Agronomi Dan Budidaya Perairan, 19(2), 198–211. https://doi.org/10.32663/JA.V19I2.2226
Anwar, R., Suzanna, E., & Djatmiko, D. (2021b). Testing The Effectiveness Of Biological Herbicide In Coffee Plantations In Various Agro-ecological Conditions. Jurnal Agroqua: Media Informasi Agronomi Dan Budidaya Perairan, 19(1), 33–41. https://doi.org/10.32663/JA.V19I1.1799
Anwar, R., Suzanna, E., Djatmiko, D., Dwi Andika, W. S., & Gartiwo, D. M. T. (2019). Efektifitas herbisida formulasi pada gulma air di lahan rawa tadah hujan, rawa payau dan saluran drainase. Jurnal Agronomi Indonesia (Indonesian Journal of Agronomy), 47(2), 210–216. https://doi.org/10.24831/jai.v47i2.24136.
Edwards, C. A. (Ed.). (2004). Earthworm Ecology (2nd Edition). CRC Press, Boca Raton, Fl.
Effendie, M.I. (1997). Biologi Perikanan. Fakultas Perikanan IPB.Bogor.
Faradisha, N., S. Elystia Dan E. Yenie. (2015). Uji toksisitas akut effluent pengolahan Lindi TPA Muara Fajar terhadap ikan Mas (Cyprinus carpio L). JOM FTEKNIK, 2(2), 1-4.
Faqihhudin, M. D., Haryadi, & Purnamawati, H. (2014). Penggunaan Herbisida IPA-Glifosat terhadap Pertumbuhan, Hasil dan Residu pada Jagung. Ilmu Pertanian, 17(1), 1–12.
Garg, V. K., S.Chand, A. Chhillar, A. Yadav. (2005). Growth and reproduction of Eisenia foetida in various animal wastes during vermicomposting. Applied Ecology and Environmental Research, 3(2), 51-59.
Heath AG. 1987. Water Pollution and Fish Physiology. CRC Ress Inc. Florida
Ihsan, T., Edwin. T., Husni. N dan Rukmana. W. D. (2018). Uji toksisitas akut dalam penentuan LC50-96H insektisida Klorpirifos terhadap dua jenis ikan budidaya danau Kembar, Sumatera Barat. Jurnal Ilmu Lingkungan, 16(2), 98-103.
Kinasih, I., Kusumorini, A., & Komarudin, A. (2014). Pengaruh tiga jenis insektisida karbamat terhadap kematian dan bobot tubuh cacing Eisenia fetida. 8(1), 109–110.
Kurniawan, S., Kurniawati, Y., Sandri, D., & Fatimah. (2014). Efektifitas Air Kelapa Fermentasi Sebagai Larutan Penghemat Herbisida Komersil. Jurnal Teknologi Agro-Industri, 1(1), 19–23.
Sari, Y. K., Niswati, A., Arif, M. A. S., & Yusnaini, S. (2015). Pengaruh Sistem Olah Tanah dan Aplihasi Herbisida terhadap Populasi dan Biomassa Cacing Tanah pada Pertanaman Ubi Kayu (Manihot utilissima). Jurnal Agrotek Tropika, 3(3). https://doi.org/10.23960/JAT.V3I3.1980
Sodiq, M. (2000). Pengaruh Pestisida terhadap Organisme Tanah. Mapala, Vol. 2, pp. 20–22.
Supriadi, Sudiman, A., Jauhariya, E., & Rahayuningsih, S. (2012). Pengembangan Formulasi Herbisida Berbasis Asam Asetat Untuk Mengendalikan Gulma pada Tanaman Kelapa Sawit. Kementerian Pertanian, Badan Penelitian dan Pengembangan Pertanian.
Waren CE. (1971). Biologi and Water Pollution Central. W.D. Sunders. Co. Philadephia