Wednesday, 13 April 2016

HARVEST NITROGEN IN SEWAGE - DON'T KILL IT

62.  HARVEST NITROGEN IN SEWAGE – DON’T WASTE MONEY TO KILL IT !


This Commentary is a rejoinder to a recent Notification from the Karnataka State Pollution Control Board revising standards for quality of treated sewage.  More specifically the KSPCB has introduced NH4-N ( Ammonia Nitrogen) and Total Nitrogen and set limits of 5 mg/L and 10 mg/L respectively for these parameters in treated domestic sewage.  The new standards are made applicable to all STP’s including those in Residential Apartment Complexes, Commercial Complexes and the Large STP’s of Urban Local Bodies ( ULB) such as City Municipal Corporation, Town Municipal Corporation etc. in Karnataka. 

The KSPCB  takes refuge under the plea that the Notification has been issued following a Direction from the Central Pollution Control Board – Delhi ( CPCB ) dt. 21-08-2015 to enforce these new Rules.

Let me explain why I feel both agencies, and the KSPCB in particular have missed the Wood for the trees and why this is a Knee Jerk reaction similar to several others which we have now come to expect from such “Expert” bodies constituted by the Government.  Md. Bin Tughlaq would have been immensely pleased to have such worthies in his Durbar.

1. From a reading of the brief narration given of the CPCB Direction, it is clear that the Rules must be made applicable to Large STP’s of ULB’s and not to distributed , decentralized small, mini and micro STP’s in Residential apartment Complexes.

2. Has the KSPCB got any expert technical opinion or has it conducted any public consultation before applying the Rules across the board to all STP’s ?

3. Has the KSPCB done even a cursory study on the technical and practical feasibility of enforcing these Rules in the Micro and Mini STP’s ?

4. Has the KSPCB explored other alternative technologies, methods and means of reducing Nitrogen pollution in the lakes and water bodies ?  Is Nitrogen control in the STP at great cost, expenditure of energy and chemicals the only solution ?

The Answers to all these questions can only be a resounding NO. 

Here is an alternative method  to beneficially harvest Nitrogen in sewage and make money instead of pouring money down the STP drain.

About 25 years ago, I was summoned by Sri. Srihari Khoday, the liquor Baron of the day in  Karnataka to study  treatment plants in their breweries and distilleries.  When the main discussions concluded, as an aside, Mr. Khoday asked me for my opinion on the technical feasibility of harvesting Water Hyacinth ( Eichhornia Crassipes) on a commercial scale from lakes in Bangalore, more particularly Bellandur ( Yes – Bellandur was polluted even in those days).  Water Hyacinth takes up huge quantities of Nitrogen and phosphorus for growth and becomes biomass which then can be anaerobically digested to generate Methane and energy therefrom and supply power to nearby industries. The largest consumer in the vicinity was Hindustan Aeronautics Limited ( HAL).  Twenty five years ago, this struck me as a revolutionary idea, and out of the box thinking of a visionary businessman with great commercial acumen.

Maybe the Babus in  those days were equally insular to practical ideas and solutions as they are even to this day : Srihari Khoday’s idea could not find wings to take off.  I have myself proposed very economical, practical and executable solutions to resuscitating defunct STP’s in Bangalore to all the authorities in the Government directly concerned.  Needless to say, they have fallen only on deaf ears.


Dr. Ananth S Kodavasal                                                                                      April 13, 2016


Abstract

Water hyacinth, Eichhornia crassipes, growth and nutrient uptake rates, as influenced by different N sources and N transformations, were measured using microcosm aquaculture systems. Net productivity was highest in the system receiving equal amounts of $NH_{4}{}^{+}$ and NO3 - (at 10 mg N l-1 each) and decreased in the order of NO3 -, $NH_{4}{}^{+}$, urea (added at 20 mg N l-1 each), and methane digestor effluent (at 6 mg N l-1). During the first 7-wk study (average ambient air temperature was 26-28°C), biomass yields were in the range of 19-53 g dry wt $m^{-2}\ day^{-1}$, while between the 8th and 12th wk (average ambient air temperature was 16-22°C), biomass yields were in the range of 10-33 g dry wt $m^{-2}\ day^{-1}$. In the systems with either $NH_{4}{}^{+}$ or NO3 -, or both added in equal proportions, about 14-20% of the total yield was contributed by roots, whereas in the system with urea and digestor effluent, roots contributed about 23 and 44% of the total yield, respectively. Nitrogen and P uptake per unit area followed trends similar to biomass yields. Nitrogen uptake rates were in the range of 533-2,161 mg N $m^{-2}\ day^{-1}$ for the systems receiving $NH_{4}{}^{+}$, NO3 -, and urea, while uptake rates were in the range of 124-602 mg N $m^{-2}\ day^{-1}$ for the system receiving methane digestor effluent. Phosphorus uptake rates were found to be in the range of 59-542 mg P $m^{-2}\ day^{-1}$. Under the most favorable conditions, maximum recorded biomass yield was 53 g dry wt $m^{-2}\ day^{-1}$, with N and P removal rate of 2,161 mg N $m^{-2}\ day^{-1}$ and 542 mg P $m^{-2}\ day^{-1}$, indicating the potential of water hyacinth to produce large amounts of biomass which can be potentially used as a feedstock to produce methane.


Economic Botany © 1983 New York Botanical Garden Press

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