Removal of Atrazine from Wastewater
Sanja Grabar MSc, Hazardous Waste Management Agency Ltd.,
Environmental Services, Savska cesta 41/IV, HR-10000
Zagreb, Croatia, Tel: +385 1 6311 999, Fax: +385 6176 734,
sanja.grabar@apo.hr
Natalija Koprivanac PhD and Dinko Vujević, MSc,
University of Zagreb, Faculty of Chemical Engineering and
Technology, Department of Polymer Engineering and Organic
Chemical Technology, Marulićev trg 19, HR-10000
Zagreb, Croatia, Tel: +385-1-4597 124, Fax:
+385-1-4597-143, nkopri@marie.fkit.hr, dvujev@marie.fkit.hr
Pesticides represent the group of organic synthetic compounds
with the high risk to the environment and human health as
well. Among herbicides, a type of pesticides, the most
used one is atrazine, which can be often found in natural
waters with concentration above maximum permissible level;
0.1 mg/dm3
according to EC Directives [1]. In order to decrease the
amount of atrazine in wastewater on the level determined
by regulatives, the adsorption of atrazine on chosen types
of zeolites and activated carbon has been investigated in
the samples prepared as simulated wastewaters. Also,
degradation of atrazine by Advanced Oxidation Processes (AOPs),
Fenton and Fenton “like” as well as combination of
adsorption and AOPs with Fenton and Fenton “like”
reagents have been studied. The efficiency of atrazine
removal and degradation after the physical and/or chemical
treatment has been estimated on the basis of TOC and HPLC
analyses. Activated carbon has been shown as the most
efficient adsorbent but also 76.2% of atrazine has been
removed from simulated wastewater by using zeolite HY at
the atmospheric conditions after 2 hours of contact and
96% after 72 hours respectively. These very good results
obtained by HY zeolite preferable the application of the
zeolites as adsorbents instead of activated carbon. The
use of zeolites has advantage because of the cost
efficiency and possibility of reusing. The kinetic of
atrazine degradation in applied AOPs has been monitored
simultaneously. A mathematical model, describing kinetic
of atrazine degradation has been developed. Experimental
data have been compared with those ones predicted by
model. It has been estimated that degradation of atrazine
can be described with kinetic of pseudo-first order rate.
To achieve even better ecoefficiency, the adsorption with
zeolites can be used as a pretreatment method for the
removal of atrazine from wastewater and Fenton and Fenton
“like” processes as polishing step in wastewater
treatment.
[1]
J.M. Sayre, J.Am.Water Works Assoc. 80 (1988) 53
Behavior and Fate of Chlorpyrifos Introduced into Soil-crop
Systems by Irrigation
Ligang Wang, Ph.D., Institute of Subtropical
Agriculture, Chinese Academy of Science (CAS), Changsha
410125, P.R.China, Tel: 86-13973195586,
Email: lgwang0827@yahoo.com.cn
Xin Jiang, Institute of Soil Science, CAS, Nanjing 210008,
P.R.China
The effect of chlorpyrifos introduced into red soil on the
growth of wheat and oilseed-rape seedlings, together with
their uptake of chlorpyrifos, was studied using pot
cultivation. The results show that, if the initial
concentration of chlorpyrifos introduced into red soil by
irrigation water containing chlorpyrifos was 1–10 µg/g,
absorption of chlorpyrifos residue from soil by wheat
seedlings leads to a concentration of 0.257–4.50 µg/g
20 days later from irrigation day on; with the same
initial concentration, oilseed-rape seedlings reach a
concentration of 0.249–2.02 µg/g 20 days later from
irrigation day on. An
initial concentration of chlorpyrifos in red soil that is
equivalent to or below 10 µg/g did not significantly
influence the growth of wheat seedlings. Similarly, an
initial concentration equivalent to or below 5 µg/g did
not significantly influence the growth of oilseed-rape
seedlings. The degradation rate of chlorpyrifos was
1.4–4.2 times more in oilseed-rape rhizosphere soil than
in unvegetated soil. The amount of bacteria and fungi in
oilseed-rape rhizosphere soil was 3.18 times and 1.84
times, respectively, as much as in unvegetated soil.
However, there was no considerable difference in levels of
actinomyces between the rhizosphere soil and the
unvegetated soil. Compared with unvegetated soil, the pH
in rhizosphere soil was lowered by 0.19–0.23 pH unit.
Key words: Red soil; Chlorpyrifos; Wheat; Oilseed-rape;
Rhizosphere
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