Journals / Adnan Menderes Üniversitesi Ziraat Fakültesi Dergisi / 2018 / Cilt: 15 - Sayı: 1

The Effects of Treated and Untreated Oil Mill Wastewater on C and N-Dynamics of a Sandy Loam Soil

Kumlu Tın Bünyeli Bir Toprağın C ve N-Dinamiği Üzerine Ham ve Arıtılmış Zeytin Karasuyunun Etkileri

Pages
25–32
Publication Date
2022-10-11
DOI
—
🏛️Bibliographic metadata and full text access for this article are provided via DergiPark.
DergiPark Record ↗
✨

AI Summary & Key Takeaways

AI Insight
⚡ TL;DR(Too Long; Didn't Read)

These results showed that microbial biomass increased at 50 and 100 m3 ha-1 OMW rates but C-and N-dynamics of soil negatively were affected by 150 m3 ha-1 OMW applications.

📌 3 Key Takeaways

🎯
Objective & Hypothesis:Olive mill wastewater (OMW) is characterized by high pollutant load and phytotoxic levels of polyphenols, but also a high amount of organic compounds and plant mineral nutrients.
📊
Key Findings & Data:In this study, OMW treated with two different treatment processes (economic pre-treatment and advanced treatment process) and untreated OMW were applied to a sandy loam texture soil at the rates of 0, 50, 100, 150 m3 ha-1 and the changes in C-and N-dynamics of soil and some chemical properties were determined.
💡
Conclusion & Impact:These results showed that microbial biomass increased at 50 and 100 m3 ha-1 OMW rates but C-and N-dynamics of soil negatively were affected by 150 m3 ha-1 OMW applications.
🔬Design:Lab & Field Experiment
📍Scope:Comprehensive Sample
⚙️Variables:Domain Parameters

Abstract

Olive mill wastewater (OMW) is characterized by high pollutant load and phytotoxic levels of polyphenols, but also a high amount of organic compounds and plant mineral nutrients. For this reason, there is a potential to be used as a material improving soil after treated. In this study, OMW treated with two different treatment processes (economic pre-treatment and advanced treatment process) and untreated OMW were applied to a sandy loam texture soil at the rates of 0, 50, 100, 150 m3 ha-1 and the changes in C-and N-dynamics of soil and some chemical properties were determined. The experiment was carried out in total period of 90 days of incubation under laboratory conditions. Amendment with untreated and treated wastewaters increased the contents of total organic C (TOC), total N (TON), soluble- C (SOL-C), microbial biomass-C and N (MB-C and MB-N) and available P and K, but inorganic-N (INOR-N) pool decreased due to N-immobilization. The highest the ratios of MB-C/TOC, SOL-C/TOC and MB-N/TON were determined at the low OMW rates and the highest INOR-N/TON at the control and highest untreated OMW rate. These results showed that microbial biomass increased at 50 and 100 m3 ha-1 OMW rates but C-and N-dynamics of soil negatively were affected by 150 m3 ha-1 OMW applications. The fact that OMW that are minimized phenol and organic C load are applied to soils at not exceeding 100 m3 ha-1 rate may be considered to be a good strategy for recycling this waste.

Özet

Zeytin karasuyu, yüksek kirlilik yükü ve içerdiği polifenollerden dolayı fitotoksik etkilere sahip fakat bununla beraber organik bileşikler ve bitki besin elementleri yönünden de zengin bir atık su özelliğindedir. Bu nedenle belli düzeyde bir arıtımdan geçtikten sonra toprak ıslah maddesi olarak kullanılabilme potansiyeli bulunmaktadır. Bu çalışmada; zeytinyağı üretimi sırasında ortaya çıkan ham karasu ve iki farklı yöntem (ekonomik ön arıtma ve ileri arıtma tekniği) ile arıtılmış karasu kumlu tın bünyeli bir toprağa 50, 100 ve 150 m3 ha-1 dozlarında uygulanmış ve toprağın C ve N-dinamiği ile bazı kimyasal özelliklerinde meydana getirdiği değişimler incelenmiştir. Deneme laboratuvar koşullarında 90 günlük bir inkübasyon denemesi olarak yürütülmüştür. Gerek arıtılmış ve gerekse arıtılmamış zeytin karasu uygulamaları toprağın toplam organik-C (TOC), toplam N (TON), çözünebilir-C (ÇÖZ-C), mikrobiyal biyokütle-C ve-N (MB-C ve MB-N), alınabilir P ve K miktarlarını artırmış fakat N-immobilizasyonundan dolayı inorganik-N (İNOR-N) havuzunu küçültmüştür. En yüksek MB-C/TOC, ÇÖZ-C/TOC ve MB-N/TON oranları karasu uygulamalarının ilk dozlarında, en yüksek İNOR-N/TON oranları ise, kontrol ve en yüksek ham karasu uygulamalarında saptanmıştır. Bu sonuçlar karasuyun 50 ve 100 m3 ha-1 uygulamalarında topraktaki mikrobiyal biyokütlenin arttığını fakat 150 m3 ha-1 karasu uygulamasında topraktaki C ve N-dinamiğinin olumsuz etkilendiğini ortaya çıkarmıştır. Fenol ve organik C yükünün azaltıldığı arıtılmış karasuların100 m3 ha-1’ı geçmeyecek dozlardaki uygulamalarının bu atığın değerlendirilmesinde iyi bir geri dönüşüm stratejisi olabileceği düşünülmektedir.

🔖

Cite This Article

OKUR, N., BAYIZ, O. (2022). The Effects of Treated and Untreated Oil Mill Wastewater on C and N-Dynamics of a Sandy Loam Soil. Adnan Menderes Üniversitesi Ziraat Fakültesi Dergisi, Cilt: 15 - Sayı: 1, 25–32. https://ajindex.com/articles/429263

📄 Full Text PDF Viewer

📄

PDF görüntüleyici hazırlanıyor...

References (14)

  1. Anonim (1978) Torf für Gartenbau und Landwirtschaft (DIN 11542). Anonim (2015) Türkiye İstatistik Yıllığı. Türkiye İstatistik Kurumu Matbaası, Ankara.
  2. Belaqziz M, El-Abbassi A, Lakhal EK, Agrafioti E, Galanakis CM (2016) Agronomic Application of Olive Mill Wastewater: Effects on Maize Production and Soil Properties. Journal of Environmental Management 171:158-165.
  3. Bernal MP, Paredes C, Sanchez-Monedero MA, Cegarra J (1998) Maturity and Stability Parameters of Composts Prepared With a Wide Range of Organic Wastes. Bioresource Technology 63:91-99.
  4. Black C A (1965)
  5. Methods of Soil Analysis, Part 1-2.,
  6. American Society of Agronomy, Inc., Publisher.
  7. Madison Wisconsin. Böhme L, Böhme F (2006) Soil Microbiological and Biochemical Properties Affected by Plant Growth and Different Long-Term Fertilization. European Journal of Soil Biology 42:1-12.
  8. Bouyoucos GJ (1962) A Recalibration of the Hydrometer Method for Making Mechanical Analysis of the Soils. Agronomy Journal 4(9): 419-434.
  9. Bremner, JM (1965) Total Nitrogen. In: Black CA (ed), Methods of Soil Analysis. Part-2, American Society of Agronomy Inc, Publisher Madison, Wisconsin, 1149- 1178. Brunetti G, Senesi N, Plaza C (2007) Effects of Amendment With Treated and Untreated Olive Oil Mill Wastewaters on Soil Properties, Soil Humic Substances and Wheat Yield. Geoderma 138:144- 152. Demisie W, Liu Z, Zhang M (2014) Effect of Biochar on Carbon Fractions and Enzyme Activity of Red Soil. Catena 121:214-221.
  10. FAO (2016) Food and Agriculture Organization of the United Nations Statistics Division. Web: http://www.fao.org/faostat/en/#data/QD Erişim Tarihi: 27.04.2018.
  11. Gargouri K, Rouina BB, Mechichi T, Kallel M (2014) Effects of Olive Mill Wastewater on Soil Nutrients Availability. International Journal of Interdisciplinary and Multidisciplinary Studies (IJIMS) 2(1):175-183.
  12. Haynes RJ (2000) Labile Organic Matter as an Indicator of Organic Matter Quality in Arable and Pastoral Soils in New Zealand. Soil Biology & Biochemistry 32:211- 219. Hocaoğlu SM (2015) Zeytin Sektörü Atıklarının Yönetimi Projesi. Çevre ve Şehircilik Bakanlığı, Çevre Yönetimi Genel Müdürlüğü, Nihai Rapor, 335. Huang JY, Song, CC (2010) Effects of Land Use on Soil Water Soluble Organic C and Microbial Biomass C Concentration in the Sanjiang Plain in Northeast China. Acta Agriulturae Scandivanica Section B Soil Plant 60:182-188.
  13. Jackson ML (1967)
  14. Soil Chemical Analysis, Prentice Hall of India Private Limited, New Delhi. Jones DL, Willett, VB (2006) Exper