Abstract:
Widespread use of arsenic (As) contaminated water for irrigation to produce dry season
crop (mainly boro rice) poses threats to sustainable agriculture and to human health in
Bangladesh. Presence of As in irrigation water leads to elevated levels of As in soil, with
significant spatial and temporal variation. Monsoon flooding removes significant fraction
of As added to soil through irrigation each year. Reported soil-As data from non-flooded
areas show much higher retention of As added through irrigation water. So areas without
pronounced monsoon flooding are at greater risk of soil-As accumulation than seasonally
flooded paddy fields. This study makes an assessment of the potential of arsenic
accumulation through irrigation in soil where extensive boro rice cultivation is carried
out; the potential of arsenic accumulation has been presented in the form of a “Arsenic
Hazard Map”. The Arsenic hazard map has been prepared considering the hypothesis on
As deposition/ mobilization in paddy soils, using data on arsenic distribution in
groundwater, boro cultivation/ irrigation intensity, and flood inundation depth. This risk
level of arsenic accumulation in soils has been divided into seven categories: (a) Very
high-risk area, (b) High-risk area, (c) Moderate-risk area, (d) Moderate to low-risk area,
(e) Low-risk area, and (f) Very low-risk area. According to the Arsenic Hazard Map,
areas to the south-west and some areas in the north-east are at risk of higher accumulation
of arsenic, because of higher concentration of arsenic in irrigation water, higher intensity
of boro cultivation, and higher land elevation.
“Query analysis” of the hazard map reveals that 282,267 ha of highland used for boro
cultivation in 22 upazilas of the south-western region of Bangladesh are at “very high
risk” of arsenic accumulation, because of higher arsenic in STW irrigation water and low
flood inundation depth; and 382,001 ha of highland in 35 upazilas are at “high-risk”
status, where flood inundation depth is low , but arsenic concentration in STW irrigation
water is also relatively low. Areas in the northern parts of Bangladesh are at “low to no
risk” because of lower concentration of arsenic in irrigation water, despite higher
intensity of boro cultivation. Some areas in the south-central region of Bangladesh are at
“moderate to low risk” of arsenic accumulation because of higher elevation of these areas
(which results in lower flooding intensity). Soil-As data from primary (i.e., field sampling
and analysis) and secondary sources qualitatively validate the Arsenic Hazard Map
prepared in this study. Soil-As map prepared form collected primary and secondary data
shows that in most of the south western region, soil-As level exceed 30 mg/kg.
An assessment of the impact of arsenic accumulation in soil on rice yields in selected
high-risk areas has been made utilizing available data/ information correlating arsenic in
irrigation water and agricultural soil, and soil arsenic and crop yield. It appears that
significant rice yield reductions could result in the future due to accumulation of arsenic
in irrigated soil. Estimated yield reductions in nine high-risk upazilas varied for about 9
percent to 24 percent for the year 2020, and 12 percent to 53 percent for the year 2050.
Possible yield reduction due to elevated soil arsenic appears to be a potential threat to
food security and agricultural sustainability in Bangladesh, where rice is the main crop
and staple food, and boro rice accounts for over 50 percent of total rice productions.