Plant algae method for arsenic removal from arsenic
contaminated groundwater
Mupenzi Jean de la Paix, Li Lanhai, Habumugisha Jean de Dieu
and Maina Nyongesah John
ABSTRACT
Field studies were carried out in Urumqi River Basin in Northwest China. The study focused on
experimentation on a plant algae method that was tested by taking various water chemistries into
consideration. The results from a greenhouse experiment evaluated for four doses of P (0, 100, 200,
and 300 μmol/L) using two ferns (30 and 60 day old) on 15 L of contaminated groundwater per plant
revealed that the biomass of 30-day old ferns gained was higher than 60-day fern. As solution-P
increased from 0 to 450 μmol/L, Phosphorus concentration in the fronds increased from 1.9 to
3.9 mg/kg and 1.95 to 4.0 mg/kg for 30-d and 60-d ferns respectively. This study showed that the
plant algae method may be a good solution to maximize arsenic uptake in the short term under
normal climatic conditions.
Mupenzi Jean de la Paix (corresponding author)
Li Lanhai
Maina Nyongesah John
State Key Laboratory of Desert and Oasis Ecology,
Xinjiang Institute of Ecology and Geography,
Chinese Academy of Sciences,
818 Beijing Road South,
Urumqi, Xinjiang, 830011,
China
E-mail: mupenzi2ms.xjb.ac.cn/lilh@ms.xjb.ac.cn
Mupenzi Jean de la Paix
Habumugisha Jean de Dieu
Institut Politechinique de Byumba (IPB),
25 Byumba, Gicumbi,
Rwanda
Mupenzi Jean de la Paix
Independent Institute of Lay Adventists of Kigali
(INILAK), PO Box 6392 Kigali,
Rwanda
Key words | arsenic, groundwater, plant algae, water contamination
INTRODUCTION
Occurrence of arsenic in drinking water is problematic in
some parts of the world especially in China due to rapid
industrialization in recent years. Like phosphorus, arsenic
exhibits allotropy, although only the gray allotrope is
important under normal conditions; it can lead to death
in chronic intakes (Daneshvar et al. ). Several studies
have revealed that arsenic and its compounds are poiso-
nous, highly toxic and carcinogenic to humans. Plant
biomass and other methods have been proven to be able
to treat wastewaters from different sources such as textile
industries, food and protein production, soluble oil wastes,
restaurants, metal finishing and lately arsenic containing
wastewater and groundwater (Beck et al. ; NRC
; Mills ; Smedley & Kinniburgh ; Gomes
et al. ; Park et al. ; Ghosh et al. ;
Balasubramanian et al. ). Arsenic in water can be
removed by microbiological processes and two main
types of metal–microbe interactions can be potentially
used for the removal of arsenic from groundwater,
which are: (a) microbial oxidation of arsenic(III) to
arsenic(V) to facilitate its removal by conventional arsenic
removal processes, and (b) bioaccumulation of arsenic by
microbial biomass (Sutton et al. ; Chen et al. ;
Rahman & Ravenscroft ; Kumar et al. ; Parga
et al. ). In China, acute scarcity of safe water
supply and improper water resource management has
resulted in the consumption of high arsenic-contaminated
groundwater. More than half a billion of its population is
exposed to dangerously high-arsenic poisoning emanating
from the use of arsenic-contaminated groundwater for
drinking and irrigation purposes (Guo & Wang ; Li
et al. ). For a long time, groundwater has been the
major source of water supply in this country. Through
investigations in Xinjiang autonomous regions in North-
west China, a 1,900 μg/L rise in arsenic concentration
was identified in groundwater, with an average concen-
tration of 350 μg/L and these exceeded the standard of
10 μg/L as revealed by the World Health Organization
(WHO) (Matteson et al. ; Chen et al. ; Holt
et al. ; Jiang et al. ; Tu et al. ; Wachinski
et al. ). The main goal of this investigation was to
ameliorate the As(III and V) removal from groundwater
using a plant algae method, which is believed to be
among the most simple, efficient and promising technol-
ogies for the removal of the two forms of As from
contaminated water. It has been proven to be very
927 © IWA Publishing 2012 Water Science & Technology | 65.5 | 2012
doi: 10.2166/wst.2012.875