Patent Application
20130220936
The present invention concerns a method to support an emission-free and deposit-free transport of sulphide in sewer systems to waste water treatment plants and agent for use therein
Waste water tends to get septic in pressure mains if not treated with an oxygen source. Once the waste water has turned septic anaerobic degradation processes will start generally resulting in the formation of hydrogen sulphide (H2S).
A common method to bind H2S is the addition of iron salts to the septic waste water whereby iron sulphide (FeS) is formed. Iron sulphide is a water insoluble solid, and its formation causes problems due to precipitation as well as by influencing the quality of separated sand and sludge in the waste water treatment plant. Other methods, like the addition of nitrate salts, lead to production of nitrogen gas, which may cause operational problems especially in pressure mains without degassing valves.
Waste water conditioning is a common technology to prevent emissions. Several different approaches are available and beneficial for most cases. When it comes to conditioning of waste water in pressure mains lying on the bottom of lakes a special problem limits so far the application of chemicals: The sewer is placed on the bottom of the lake so uneven, that it cannot be cleaned easily and gas will be captured in the pipe—what leads to a drastic lower flow rate and even swimming up of big sewers.
The first problem prohibits the use of common iron salts and the second problem the use of nitrate salts. However a treatment of such waste water is needed as corrosion, health risks and odour emissions are caused by H2S.
There are several processes known to separate and/or eliminate H2S from liquid phases, e.g. addition of ferric and/or ferrous iron chloride solution. U.S. Pat. No. 5,948,269 disclose the addition of alkaline iron in liquid and sludge waste systems to control concentration of hydrogen sulphide and other malodorous compounds. The process removes sulphide and suppresses the formation of further nuisance sulphide with a single application. Exemplified alkaline iron compounds are ferrous hydroxide, ferrous carbonate, ferrous bicarbonate, hydrated ferrous oxide, ferric hydroxide, ferric carbonate, ferric bicarbonate, ferric hydroxide oxide, hydrated ferric oxide, and mixtures thereof.
In U.S. Pat. No. 4,902,408 a process for removing hydrogen sulphide using a mixture of hydrocarbons of iron 2-ethylhexanoate, is disclosed.
There are also some processes known to dissolute or disperse iron sulphides, for example:
GB 2 257 428 is concerned with a chemical formulation for control of odour emission from sewage etc. There is disclosed a chemical formulation comprising one or more mono-terpene oils dissolved in alcohol mixed with at least 1-chloroanthroquinone and 2-chloroanthroquinone. An iron compound such as ferrous carbonate, ferrous chloride or ferric chloride may also be included. The formulation may be added to sludge to be processed in an anaerobic digester to reduce hydrogen sulphide production.
U.S. Pat. No. 1,873,083 concerns a method for treatment of oil well liquids involving the addition of a mixture of alkali metal salts and caustic alkali solution of tannin. Insoluble alkaline earth salt are precipitated from the well liquids in a pulverulent and non-scale building form.
U.S. Pat. No. 4,381,950 disclose a process for reducing hydrogen sulphide gas evolution during dissolution of ferrous sulphide with an aqueous acidic solution containing an effective amount of an additive comprising at least one member selected from the group consisting of maleic acid, maleic anhydride and the alkali metal and ammonium salts of maleic acid.
U.S. Pat. No. 4,276,185 is concerned with methods and compositions for removing deposits containing iron sulphide from surfaces with minimal hydrogen sulphide evolution. A composition comprised of a basic aqueous solution of a chelating agent elected from the group consisting of citric acid, oxalic acid, nitrilotriacetic acid, alkylene polyamine polyacetic acids and mixtures of such chelating agents having a pH in the range of from about 8 to about 10 is brought into contact with the deposits for a period of time sufficient for the deposits to be dissolved therein.
U.S. Pat. No. 6,926,836 is concerned with treatment of a water system containing or in contact with a metal sulphide scale to inhibit, prevent, reduce, dissolve or disperse iron sulphide deposits. A solution of tris(hydroxyorgano)phosphines (THP) and tetrakis (hydroxyorgano) phosphonium salts (THP+ salts) and (ii) sufficient of a chelant (amino-carboxylates or amino-phosphonate) to provide a solution containing from 0.1 to 50% by weight of said THP or THP+ salt and from 0.1 to 50% by weight of said chelant, is contacted with the metal sulphide scale thereby to dissolve at least part of said scale in said solution
US 2007/0108127 relates to a method of treating an aqueous system containing or in contact with metal sulphide scale. The method comprises adding to said system, separately or together, sufficient of a synergistic mixture comprising a THP+ salt, an aqueous solution of a strong acid (and optionally a source of nitrogen) to provide a solution containing from 0.1% to 30% by weight of the THP+ salt at a pH of less than about 1.0. The scale is contacted with said solution, (thereby dissolving at least part of said scale in said solution) and the dissolved sac le is withdrawn from the system.
Lignosulphonates (LS) are used in cement and concrete applications, where the molecules cover the cement particles and retard the hydration process. The process bases on formation of a cement particle paste, in a way that the hydration process starts only slowly. There are also other technical processes where lignosulphonates may be used to produce suspensions
JP 6305200 disclose a method wherein the generation of hydrogen sulphide is inhibited by adding iron salt (ferrous sulphate or ferric chloride) to sludge and allowing the iron salt to react with the sulphur content in a storage tank. In the reaction iron sulphide and sulphuric acid or hydrochloric acid is produced and thereby the generation of hydrogen sulphide is inhibited. The so reacted sludge from the storage tank is mixed with a high polymer flocculation agent and the dehydrating efficiency is enhanced.
Organic polyelectrolytes have been applied in water treatment in sludge thickening and coagulation/flocculation processes. According to Bolto, Brian A. et al (War. Sci. Tech. vol. 34, No 9. pp 117-124, 1996) can organic polymeric flocculants be used as primary coagulants, instead of inorganic salt, in the treatment of many industrial wastes that are further processes by flotation. It is stated that the charge density of the cationic polymer used must be carefully selected.
From prior art e.g. as cited above it is known to use polymers to support and facilitate flocculation and coagulation in separation processes, whereas in the present invention the polymer is added to facilitate dispersion.
Chack, J. J. et al ((1994) “Advanced primary treatment bridges the gap”. Water Env.
& Technol., 6, 49-53) disclose that test results showed that the addition of a limited amount of ferric chloride in the combination with an anionic polymer improved primary biochemical oxygen demand (BOD) and suspended solids (SS) removals without disrupting solids processing. The optimal dosage of ferric chloride was 50 ppm for 6 hours/day during daily maximum flows and 15 ppm for the remainder of the day in combination with an anionic polymer dosage of 1 ppm
The present invention provides an agent for the conditioning of septic waste water which comprises an iron salt and an anionic polymer.
Also provided by the present invention is a method for conditioning of septic waste water comprising the step of adding said agent to the septic waste water in need of treatment.
The iron salt reacts with sulphur containing compounds to form FeS and thus prevents the formation of hydrogen sulphide, while the anionic polymer interact with the formed FeS to a colloid sol stable to precipitation.
The chemical reaction between iron and sulphide is well known. The stoichiometric dosage is approximately 3.9 mg FeCl2 per 1 mg S2−. However, in general an overdose of 50% is necessary. An overdose of iron salt compared to the stoichiometric proportion has to be used since other constituents of waste-water may also react with iron ions. Using basically a 20% FeCl2 solution and considering a sulphide load of 1 mg/L this demands a dosage of 29 mg/L what equals approximately 21 ml/L.
The method of the invention uses besides iron salts the simultaneous addition of an anionic polymer, preferably a lignosulphonate (LS). The use of hydrophilic polymers as so-called protective colloids is described in the literature for protecting hydrophobic colloids against coagulation at high concentration of electrolytes by forming a hydrophilic sheath around the hydrophobic particles.
Following the invention sulphide from soluble sulphide compounds, especially H2S, reacts to FeS. With the simultaneously added anionic polymer, preferably lignosulphonate, a nano structured complex is formed, leading to a colloid sol stable against precipitation.
After being transported into the waste water treatment plants the complexes of FeS and anionic polymer e.g. lignosulphonate can be easily degraded under the influence of oxygen.
For achieving an emission-free and deposit-free transport of sulphide in sewer systems a blend of iron salt and an anionic polymer, preferably lignosulphonate is, according to the present invention, added to the waste water.
The reaction product is a solid FeS-LS complex of very small size, forming a colloid sol which prevents the precipitation of FeS. FeS does not deposit in sewers at common flow rates and turbulences and neither at times without movement.
Additional advantageous effects according to the invention are
i) that the small size of the particles supports an easier oxidation compared to larger particles occurring without the treatment according to the invention. This results in a faster oxidation of the iron sulphide and the polymer in the aerated sand trap or the aerated biological treatment plant.
ii) lignosulphonate has an inhibitory effect on growth of some micro organisms, e.g. fungi and bacteria. This effect further reduces the production of H2S.
The method may preferably be used in pressure mains through lakes, under ground and the like because here a precipitation-free as well as off-gas-free pre-conditioning method is particularly beneficial.
In one aspect of the invention an agent for conditioning of septic waste water is provided that comprises an aqueous solution of iron salts and an anionic polymer.
Several iron salts may be used in the agent and the iron salts selected from the group consisting of FeCl2, FeCl3, FeClSO4, FeSO4 and mixtures thereof are suitable particularly FeCl2, FeCl3, and mixture thereof.
Several anionic polymers are known in the art and may be used in the agent according to the invention. Iron lignosulphonate, sodium lignosulphonate and calcium lignosulphonate are however preferred.
In one embodiment of the invention an aqueous mixture of both an iron salt and an anionic polymer in the mass proportion of iron salt to anionic polymer, particularly lignosulphonate in the range of 1:0.5 to 1:1.5 calculated as substances free from water is provided.
The iron salts may be provided in an aqueous solution with a concentration of 20% to 40% by weight, and the anionic polymer e.g. lignosulphonate, may be provided as an aqueous solution with a concentration of 10% to 30% by weight.
In another aspect of the invention a method for the conditioning of septic waste water to prevent the formation of hydrogen sulphide and prevent subsequent precipitation of FeS is provided, wherein the step of adding simultaneously an aqueous solution of iron salts together with an anionic polymer to the septic waste water is comprised.
The dosage of the iron salt polymer solution equals the common dosage for an iron salt solution alone. Hence the dosing strategy or demand itself is not affected. For example a sulphide concentration of 1 mg/L demands a dosage of 21 mL/L.
The iron salts used in the method may be selected from the group consisting of FeCl2, FeCl3, FeClSO4, FeSO4 and mixtures thereof.
Further the preferred anionic polymer is selected from the group consisting of iron lignosulphonate, calcium lignosulphonate and sodium lignosulphonate.
In one embodiment of the method according to the invention an aqueous mixture of both iron salts and anionic polymer in mass proportion of iron salt to anionic polymer, particularly lignosulphonate, in the range of 1:0.5 to 1:1.5 calculated as substances free from water is provided.
In a further embodiment of the method according to the invention the iron salt solution and the anionic polymer solution are added as a mixture of both solutions.
In yet another embodiment of the method according to the invention the iron salt solution and anionic polymer solution are added simultaneously as separately solutions.
Certain embodiments of the invention are illustrated by the non-limiting examples below.
In a lab scale test batch reactors were used. Samples of conditioning fluids with FeCl2 as iron source were produced. In one reactor additionally LS was dosed. H25 was bubbled into the reactors containing dilutions of these conditioning fluids. After a certain time of experiment Fe2+ was consumed and the maximum of FeS formed. In the non-LS-treated reactors insoluble solids were produced. In the LS treated samples FeS was also formed (dark grey colour) but particles were invisible small—the liquid stayed clear.
In a lab scale test batch reactors were used. 400 ml tap water was mixed with 0.5 ml of a 11% FeCl2 solution. Different dosages of sodium lignosulphonate LS solution (20%) were added (0.0 ml, 0.1 ml, 0.25 ml and 0.5 ml). The samples were aerated with 50 ppm H2S in nitrogen gas. Whereas the non-LS containing sample turned turbid, the LS treated samples stayed clear independently from LS dosage. The content of mixed liquor suspended solids (MLSS) was measured using 0.8 μm filters. The result indicates strongly a linear dose response relationship between LS and suspended solids as the reduction of MLSS has a linear dependency to the ration of Na LS to FeCl2. The results are shown in
In a lab scale test batch reactors were used. 400 ml tap water was mixed with 0.5 ml of a 11% FeCl2 solution. Different dosages of sodium lignosulphonate solution (20%) were added (0.0 ml, 0.1 ml and 0.25 ml). The samples were aerated with 50 ppm H2S in nitrogen gas. The content of mixed liquor suspended solids (MLSS) was measured using 0.8 μm filters. The effect of keeping solids in solution seems to be time independent within at least one hour. The samples were aerated for additionally one hour. At that stage the LS treated samples had—following the LS addition—a more or less dark brown colour. Samples were stored for 48 h without H25 addition but air access via sample surface. After that period of time samples were visually checked: The non-LS treated sample was clear and solids had settled down. All the LS treated samples were clear without any precipitation and the colour in the LS treated samples had changed from brownish to green. The results are represented in
In a laboratory scale test it was found that both Ca-LS and Na-LS can be used with FeCl2 and FeCl3. Na-LS can additionally be used with FeClSO4 and FeSO4. Mixtures of Ca-LS and FeClSO4 or FeSO4 showed a reduced performance.
In laboratory and large scale tests different blended products were investigated on their practical handling. Especially the viscosity and possibility to dose the product with ordinary membrane pumps was tested. The investigation revealed that the iron salt concentration is preferably limited to 20% in the aqueous solution. This is mainly caused by the viscosity increase due to lignosulphonate and keeping the necessary ratio between iron salt and lignosulphonate.
A pressure main with a length of 5.2 km passes a lake of 1.5 km diameter. At the pumping pit at the beginning of the pressure main already septic waste water exists with a strong smell of hydrogen sulphide. An aqueous solution with 35% dissolved solids, containing 17.5% of FeCl2 and 17.6% of sodium lignosulphonate was dosed in a ratio of 400 ml/m3 waste water into the pit.
At the outlet of the pressure pipe no smell of hydrogen sulphide could be observed. Additionally a long term monitoring of the gas phase indicated no significant H2S emission. A sample of the waste water was given into a glass cylinder. There occurred no precipitation of FeS even after a period of 6 hours.
The waste water could be easily handled in the waste water treatment plant. There was no additional foam and the Fe/lignosulphonate complex was already oxidized in the sand trap and the primary settlement tank.
| Filing Document | Filing Date | Country | Kind | 371c Date |
|---|---|---|---|---|
| PCT/EP2010/067189 | 11/10/2010 | WO | 00 | 5/13/2013 |
