The 2013 University of Oklahoma International WaTER Conference

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Transcription:

The 2013 University of Oklahoma International WaTER Conference Hand pump attachable iron removal plant for field implication in rural areas 12/2/2013 Poonam Gwala Senior Research Fellow CSIR- NEERI, Nagpur INDIA

Top Five Iron affected States in India Highest Habitation covered by Iron Contamination CGWB, MDWS, 2008

Occurrence Iron is common constituent in Soil and Ground Water It is contributed in Ground water mainly through weathering of ferroginous minerals such as hematide, magnetide, sulphide ores During rainfall, water seeps through the soil which absorbs the org. matter and iron, ultimately through layer of soils and percolates into the ground. It is present either as soluble Ferrous ion (Fe 2+ ) or insoluble Ferric ion (Fe 3+ ) Iron bacteria utilise ferrous iron as energy source & precipitate ferric hydroxide Energy utlized promotes growth of thread like slimes, which forms voluminous mass

Significance Iron is an essential element in human nutrition, minimum daily requirement range from about 10 to 50 mg/day Taste is not usually noticeable at iron concentrations below 0.3 mg/litre Turbidity and colour may develop in piped systems at levels above 0.05 0.1 mg/litre Laundry and sanitary ware stain at iron concentrations above 0.3 mg/litre. The average lethal dose of iron is 200 250 mg/kg of body weight Long term consumption of drinking water with high conc. of iron can lead to lever disease (hemosiderosis). Hemochromatosis symptoms include chronic fatigue, arthritis, heart disease, cirrosis, cancer, diabetes, thyroid, impotency, sterility etc. WHO, Geneva, 2003

Impacts of high iron content in groundwater Unpalatable metallic taste Yellowish color of water Stains laundry, plumbing fixtures and utensils Growth of iron bacteria leads to slimy deposition in distribution system Concentrations greater than 1.0 mg/l may lead to deposits in pipes Not much health impacts The guideline for iron USEPA and Canada : 0.3 mg/l BIS : 10500-2012 : 0.3 mg/l

Methods of Iron Removal Aeration Chemical addition - Chlorine - ph adjustment with lime - Potassium permanganate Catalysis Heterogeneous phase separation - Ion exchange - Manganese dioxide

Hand Pump Attachable Iron Removal Plant

Three Chambered Unit Areation Chamber Oxygenation of water Removal of carbon dioxide Removal of sulphur dioxide Sedimentation Tank Precipitation Sand Filter Transportation of unsettled particles Adsorption of particles

Hand Pump Attachable Iron Removal System Raw water inlet Aeration Flocculation Treated water outlet Filtration Sedimentation

Aeration Chamber Semi-circular body with perforated bottom plate holding 20 cm aeration media, gravel/stone of size 20-40 mm Fitted with a slotted PVC header and lateral pipes embedded firmly to the periphery of the chamber Carbon dioxide escapes and ferrous iron is oxidized and precipitates. The precipitated hydrated iron oxide forms a coat over the gravel/stone and accelerates subsequent conversion of ferrous iron.

Filter Chamber Semi-circular, partitioned out of sedimentation tank with a width of 50 cm. The filter has a 20 cm gravel column of 10-20 mm size (10 cm) and 3-6 mm size (10 cm) and 30 cm of 0.8 1.4 mm sand column. A nylobolt cloth is placed in the filter 5 cm below the top layer of sand. When the filter is chocked due to iron precipitate water above the sand bed is drained out and top 5 cm sand layer along with the nylobolt cloth is removed. Sand and cloth is washed with water and again placed on the filter bed and filtration is continued. This arrangement avoids the operation of filter backwashing, thereby reducing additional units like backwash water chamber and operation of additional valves.

Hand Pump Attachable IRP salient features Iron content reduced below 1 mg/l from 3.0-6.8 mg/l of iron in raw water Continuous operation system with 1 cu m/hour hydraulic loading 40 lpcd and 10 hours daily operation assumption Suitable for approx. 250 people population Based on contact bed aeration system in aeration chamber Cylindrical body easy for maintenance Collection / flocculation chamber Plant Dimensions Diameter : 135 cm Height : 150 cm 240 plants were installed at Assam during water Mission in 1992 Construction cost about Rs. 50,000

Hand Pump Attachable IRPs installed in different states in INDIA

NEERI-Zar - Domestic Iron Removal Unit NEERI-ZAR can also works as Domestic Iron Removal Unit KMnO4 is used as oxidizing agent to precipitate out iron in groundwater (0.5 mg per mg of iron) KMnO4 also works as disinfectant Suitable for iron affected remote places 20 units installed in Tadoba Reserve Forest, Chandrapur Dist. (M.S.) for supply of potable water to forest guards

email id: poonam.gwala28@gmail.com