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Geoderma
journal homepage: www.elsevier.com/locate/geoderma
Biochars mediated degradation, leaching and bioavailability of
pyrazosulfuron-ethyl in a sandy loam soil
Suman Manna, Neera Singh
⁎
Division of Agricultural Chemicals, ICAR-Indian Agricultural Research Institute, New Delhi 110 012, India
ARTICLE INFO
Handling Editor: A.B. McBratney
Keywords:
Rice and wheat straw biochars
Soil amendment
Herbicide fate
Mobility
ABSTRACT
Burning of crop residues after harvest is a quick, cheap and an easy way to manage the large quantities of
agricultural biomass for timely preparation of the field for next crop. Conversion of the crop harvest residues into
biochars and incorporating them back in the same field can address the issue of land clearing, waste utilization
and nutrient conservation but, any amendment to the soil changes its physico-chemical characteristics and can
affect the fate of soil applied herbicides. The present study reports the effect of low (400 °C) and high (600 °C)
temperature wheat (WBC) and rice (RBC) straw biochar's amendment on leaching, degradation and bioavail-
ability of pyrazosulfuron-ethyl (PYRAZO) in a sandy loam soil. The PYRAZO was poorly retained in the control
soil column where 78% of the soil-applied herbicide leached out of the control soil column. Biochars addition
(0.02 and 0.05 g kg
-1
) significantly reduced the PYRAZO leaching by affecting herbicide's breakthrough time
and its maximum concentration in leachate.
The biochars reduced PYRAZO degradation, both in the flooded and the nonflooded soils; but, effect was
more pronounced in the nonflooded soils. The effect of biochars on PYRAZO's leaching and degradation was the
function of the nature of feedstock, biochar production temperature and its dose. The high temperature biochars
were more effective in reducing the leaching and degradation of PYRAZO than the low temperature biochars and
the rice biochars were better than the wheat biochars. The bioavailability of PYRAZO was assayed by its effect on
mustard seedlings and results suggested that low temperature biochars, even at 0.05 g kg
-1
level, had no ne-
gative effect on herbicide efficacy. However, high temperature biochars significantly reduced the herbicide
bioavailability and higher concentration of PYRAZO was required for the desired effect. These findings are
relevant in assaying the fate of PYRAZO in the biochar amended soils.
1. Introduction
Pyrazosulfuron-ethyl (ethyl-5-(4,6-dimethoxypyrimidin-2-ylcarba-
moylsulfamoyl)-1-methylpyrazole-4-carboxylate) (PYRAZO) belongs to
the sulfonylurea group of herbicides. PYRAZO is recommended for the
selective control of pre-emergent and early post-emergent grassy and
broad leaved weeds in direct seeded and transplanted rice (Mathew
et al., 2013). PYRAZO is weakly acidic in nature (pKa - 3.7) and has
lower aqueous solubility (14.5 mg L
-1
) than its other counterparts
metsulfuron-methyl (pKa - 3.3, K
OW
– 0.018; aqueous solubility –
2.79 g L
-1
) and sulfosulfuron (pKa - 3.5, K
OW
– 0.17; aqueous solubility
– 1.63 g L
-1
), which are highly soluble in water, have low octanol
water partition coefficient and are poorly sorbed, especially in alkaline
soils with K
f
values ranging from 0.21–1.88 (metsulfuron-methyl) and
0.37–1.17 (sulfosulfuron) (Singh and Singh, 2012). These character-
istics make them prone to leaching and runoff losses and they have been
detected in the surface water as well as in the ground water (Sarmah
et al., 2000; Sondhia, 2009; Singh et al., 2014). Even though PYRAZO
has a high octanol-water partition coefficient (P
ow
- 3.16), has been
shown to be poorly sorbed in the same sandy loam soil that was used in
the present study with a Freundlich adsorption coefficient (K
f
) of
0.22 μg
(1–1/n)
g
-1
mL
1/n
(Manna and Singh, 2015). Application of
wheat and rice straw biochars, even at agronomically feasible rates
(0.01–0.02 mg kg
-1
), significantly increased the herbicide sorption and
the rice straw biochars were nearly 1.5 times better than the corre-
sponding wheat straw biochars (Manna and Singh, 2015). No in-
formation is available on PYRAZO's leaching behavior in soils. How-
ever, Chu et al. (2002) reported half-life values of 16–27 days in soil
and 9–16 days in water; while, Singh et al. (2012) reported half-life (t
1/
2
) of 5.4 and 0.9 days in soil and water, respectively. Ok et al. (2012)
observed that temperature affected PYRAZO's persistence in the paddy
water and the t
1/2
in spring and summer were 3.1 and 1.6 days,
https://doi.org/10.1016/j.geoderma.2018.07.032
Received 16 April 2018; Received in revised form 3 July 2018; Accepted 21 July 2018
⁎
Corresponding author.
E-mail address: drneerasingh@yahoo.com (N. Singh).
Geoderma 334 (2019) 63–71
0016-7061/ © 2018 Elsevier B.V. All rights reserved.
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