Dergiler / Turkish Journal of Agriculture and Forestry / 2014 / Cilt: 38 - Sayı: 3

Effects of imazamox on soil carbon and nitrogen mineralization under Mediterranean climate

Sayfa
334–339
Yayın Tarihi
2014-05-18
DOI
—
🏛️Bu makalenin bibliyografik verileri ve tam metin bağlantısı DergiPark üzerinden sağlanmıştır.
DergiPark Kaydı ↗
✨

Yapay Zeka Hızlı Bakış & Çıkarımlar

AI Insight
⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

It may be concluded that the presence of imazamox in both soils was negatively affected by nitrate bacteria.

📌 3 Maddede Bu Makale

🎯
Amaç & Hipotez:Imazamox is an herbicide intensively used in the peanut fields of Turkey.
📊
Temel Bulgular & Veri:Carbon and nitrogen mineralizations were determined at 20 °C to evaluate the effects of the herbicide in soils humidified to 60% and 80% of field capacity (FC) over 45 days.
💡
Sonuç & Katkı:It may be concluded that the presence of imazamox in both soils was negatively affected by nitrate bacteria.
🔬Tür:Araştırma Makalesi
📍Kapsam:Genişletilmiş Akademik Örneklem
⚙️Değişkenler:Key words: Herbicide · humidity · microbial activity

Özet

Imazamox is an herbicide intensively used in the peanut fields of Turkey. Carbon and nitrogen mineralizations were determined at 20 °C to evaluate the effects of the herbicide in soils humidified to 60% and 80% of field capacity (FC) over 45 days. Three doses of this herbicide [recommended dose (RD, 10 mg kg-1), 2× RD, and 4× RD] were added to soils without any previous imazamox application (NI) and to peanut soils with previous applications of imazamox (I). Carbon mineralization, determined by CO2 respiration, at RD of I soil at 80% humidity was higher than that of the other herbicide doses at both 80% and 60% humidities. NO3-N contents (mg kg-1) of I and NI soil controls were significantly higher than with all herbicide doses at 80% and 60% of FC. Nitrate production decreased with increasing doses of herbicide and was significantly lower in I soil than NI soil at both humidity levels. It may be concluded that the presence of imazamox in both soils was negatively affected by nitrate bacteria.

Abstract

Imazamox is an herbicide intensively used in the peanut fields of Turkey. Carbon and nitrogen mineralizations were determined at 20 °C to evaluate the effects of the herbicide in soils humidified to 60% and 80% of field capacity (FC) over 45 days. Three doses of this herbicide [recommended dose (RD, 10 mg kg-1), 2× RD, and 4× RD] were added to soils without any previous imazamox application (NI) and to peanut soils with previous applications of imazamox (I). Carbon mineralization, determined by CO2 respiration, at RD of I soil at 80% humidity was higher than that of the other herbicide doses at both 80% and 60% humidities. NO3-N contents (mg kg-1) of I and NI soil controls were significantly higher than with all herbicide doses at 80% and 60% of FC. Nitrate production decreased with increasing doses of herbicide and was significantly lower in I soil than NI soil at both humidity levels. It may be concluded that the presence of imazamox in both soils was negatively affected by nitrate bacteria.

🔖

Bu Makaleye Atıf Yap

KIZILDAĞ, N., SAĞLIKER, H., CENKSEVEN, Ş., DARICI, H. C., KOÇAK, B. (2014). Effects of imazamox on soil carbon and nitrogen mineralization under Mediterranean climate. Turkish Journal of Agriculture and Forestry, Cilt: 38 - Sayı: 3, 334–339. https://ajindex.com/articles/180058

📄 Tam Metin PDF Okuyucu

📄

PDF görüntüleyici hazırlanıyor...

Kaynakça (14)

  1. Aka Sağlıker H (2009). Effects to soil carbon mineralization of the different doses of trifluralin at the different temperature conditions. Eur J Soil Biol 45: 473–777.
  2. Alexander M (1981). Biodegradation of chemicals of environmental concern. Science 211: 132–138.
  3. Allison LE, Moodie CD (1965). Carbonate. In: Black CA, editor. Methods of Soil Analysis. Amer. Madison, WI, USA: American Society of Agronomy, pp. 1379–1396.
  4. Benlot C (1977). Recherches sur les activites biochimiques dans les successions de sols derives de cendres volcaniques sous climat tropical humide (Zaire-Indonesie). Paris, France: ENS Lab de Zoologie (in French). Bouyoucos GS (1951). A recalibration of the hydrometer for making mechanical analysis of soil. Agron J 43: 434–438.
  5. Cervelli N, Nannipieri P, Sequi P (1978). Interactions between agrochemicals and soil enzymes. In: Burns RG, editor. Soil Enzymes. London, UK: Academic Press, pp. 251–280.
  6. Chen SK, Edwards CA, Subler S (2001). Effects of the fungicides benomyl, captan and chlorothalonil on soil microbial activity and nitrogen dynamics in laboratory incubations. Soil Biol Biochem 33: 1971–1980.
  7. Cook AM, Hutter R (1981). s-Triazines as nitrogen sources for bacteria. J Agric Food Chem 29: 1135–1143.
  8. Demiralay I (1993).
  9. Toprak Fiziksel Analizleri. Erzurum, Turkey: Atatürk Üniversitesi Ziraat Fakültesi (in Turkish). Duchaufour P (1970).
  10. Precis de Pedologie. Paris, France: Masson et C1e (in French). Edwards CA (1989). Impact of herbicides on soil ecosystems. Crit Rev Plant Sci 8: 221–253.
  11. Eser F, Aka Sağlıker H, Darıcı C (2007). The effects of glyphosate isopropylamine and trifluralin on the carbon mineralization of olive tree soils. Turk J Agric For 31: 297–302.
  12. Gökçeoğlu M (1979). Bazı bitki organlarındaki azot, fosfor ve potasyumun bir vejetasyon periyodundaki değişimi. Doğa Tarım ve Ormancılık 3: 192–199 (in Turkish). Haney RL, Senseman SA, Krutz LJ, Hons FM (2002). Soil carbon and nitrogen mineralization as affected by atrazine and glyphosate. Biol Fert Soils 35: 35–40.
  13. Hart MR, Brookes PC (1997). Soil microbial biomass and mineralisation of soil organic matter after 19 years of cumulative field applications of pesticides. Soil Biol Biochem 28: 1641–1649.
  14. Jackson ML (1958). Soil chemical analysis. Upper Saddle River, NJ, USA: Prentice Hall. Kara EE, Arli M, Uygur V (2004). Effects of the herbicide Topogard on soil respiration, nitrification and denitrification in potatocultivated soils differing in pH. Biol Fert Soils 39: 474–478. Klei