『Abstract
Transformations of phosphate (Pi) in different soil fractions
were tracked using the stable isotopic composition of oxygen in
phosphate (δ18OP) and Pi concentrations.
Clay soil from Israel was treated with either reclaimed waste
water (secondary, low grade) or with fresh water amended with
a chemical fertilizer of a known isotopic signature. Changes of
δ18OP and Pi within different
soil fractions, during a month of incubation, elucidate biogeochemical
processes in the soil, revealing the biological and the chemical
transformation impacting the various P pools. O in the soil solution
is affected primarily by enzymatic activity that yields isotopic
equilibrium with the water molecules in the soil solution. The
dissolved P interacts rapidly with the loosely bound P (extracted
by bicarbonate). The oxides and mineral P fractions (extracted
by NaOH and HCl, respectively), which are considered as relatively
stable pools of P, also exhibited isotopic alterations in the
first two weeks after P application, likely related to the activity
of microbial populations associated with soil surfaces. Specifically,
isotopic deletion which could result from organic P mineralization
was followed by isotopic enrichment which could result from preferential
biological uptake of depleted P from the mineralized pool. Similar
transformations were observed in both soils although transformations
related to biological activity were more pronounced inn the soil
treated with reclaimed waste water compared to the fertilizer
treated soil.
Keywords: Phosphate; Soil fractionation; Oxygen isotopes; Reclaimed
waste water 』
1. Introduction
2.Materials and methods
2.1. Experimental design
2.2. Soil samples used in the experiment
2.3. The ‘irrigation event’
2.4. Soil incubation and sampling
2.5. Soil sequential extraction and preparation of samples for
isotopic analysis
2.6. P concentration determination
2.7. Mass-spectroscopy analysis
2.8. Calculations isotopic mass balance of soil P fractions
3. Results
3.1. Concentration and isotopic composition of soil P prior
to the experiment and following the ‘irrigation event’
3.2. Isotopic mass balance calculations
4. Discussion
4.1. Water extractable and most labile Pi-DDI extraction
4.2. Loosely bound Pi-Bicarbonate extraction
4.3. Fixed Pi by oxides and minerals - NaOH and HCl extraction
4.4. A unifying model
5. Conclusions
Acknowledgment
References