CA1274925A - Removing selenium from water - Google Patents
Removing selenium from waterInfo
- Publication number
- CA1274925A CA1274925A CA000513602A CA513602A CA1274925A CA 1274925 A CA1274925 A CA 1274925A CA 000513602 A CA000513602 A CA 000513602A CA 513602 A CA513602 A CA 513602A CA 1274925 A CA1274925 A CA 1274925A
- Authority
- CA
- Canada
- Prior art keywords
- selenium
- water
- reactor
- biomass
- nitrate
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B19/00—Selenium; Tellurium; Compounds thereof
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/286—Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2004/00—Particle morphology
- C01P2004/60—Particles characterised by their size
- C01P2004/62—Submicrometer sized, i.e. from 0.1-1 micrometer
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/80—Compositional purity
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10S—TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10S210/00—Liquid purification or separation
- Y10S210/902—Materials removed
- Y10S210/911—Cumulative poison
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10—TECHNICAL SUBJECTS COVERED BY FORMER USPC
- Y10S—TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y10S210/00—Liquid purification or separation
- Y10S210/902—Materials removed
- Y10S210/911—Cumulative poison
- Y10S210/912—Heavy metal
Abstract
ABSTRACT
Dissolved selenium is removed from water by treatment in a reactor containing microbial biomass to cause the hexavalent selenium to be converted to forms of selenium which can be readily removed from the water, and causing or allowing the removable forms of selenium to be removed from the water. Examples of removable forms of selenium include volatile organic selenium compounds, volatile inorganic selenium compounds, elemental selenium, entrainable organically-complexed selenium compounds, entrainable tetravalent selenium compounds, and entrainable bivalent selenium compounds. The volatile selenium compounds can be removed and recovered as a gas, while the entrainable forms of selenium can be extrained by larger particles and separated off, for example by fil-tration.
Dissolved selenium is removed from water by treatment in a reactor containing microbial biomass to cause the hexavalent selenium to be converted to forms of selenium which can be readily removed from the water, and causing or allowing the removable forms of selenium to be removed from the water. Examples of removable forms of selenium include volatile organic selenium compounds, volatile inorganic selenium compounds, elemental selenium, entrainable organically-complexed selenium compounds, entrainable tetravalent selenium compounds, and entrainable bivalent selenium compounds. The volatile selenium compounds can be removed and recovered as a gas, while the entrainable forms of selenium can be extrained by larger particles and separated off, for example by fil-tration.
Description
page 1 gkr/m&c50433 wango7~9C
REMOVI~G_SELENIUM FROM WAT~R
Backqround of the Invention The present invention relates to the removal of selenium from water, and more particularly but not exclusively ~o the treatment of drainage water containing selenium leached from soil.
Selenium is often present in water at concentrations of up to 0.5 mg/l, but a concentration of this order is undesirable for purposes such as drinking water or crop irrigation. For example, in the USA, the permitted maximum selenium level for drinking water is set at 10 ~g/l. In some selenium-containing waters such as certain irrigation drainage waters, a substantial proportion of the selenium is present as the selenate anion. [SeO4] These waters are especially difficult to treat because there is also a very high concentra~ion of sulphate.
In the USA, particular attention has focussed on treatment of the agricultural drainage water in the San Joaquin Valley. This Valley has about 1.1 million acres of extremely productive land which is under irrigation. The land iB generally low-lying and requires drainage in order to avoid high salinity in crop root zones. A major scheme to drain off subsurface watec after use for irrigation has been frustrated by discovery of high levels of ~5 contaminants. The drainage water i5 brackish, and has a relatively high concentration of salts and potentially toxic elements, with selenium representing a particular problem. Enviconmental concecn has led to a suspension page 2 of construc~ion work, a closure order on a large reservoir, and an extensive program of drain plugging.
With the plugging of the drains, the water table i6 beginning to rise, causing concern for growers in the valley-Methods are available for the purification of wa~er, butin general the known methods are not suited for use on a large scale wi~h brackish drainage water con~aining selenium and a range of other contaminants. Reverse lO osmosis is costly, and so also is ion exchange. In this respect, it i8 to be borne in mind that the in~ial aim in tceating the drainage water in the San Joaquin Valley and elsewhere is to render it suited for discharge. Hence, an economic process is paramount.
15 Methods are also described in the literature which are specifically concerned with the removal of selenium from water, but it is not apparent that such methods can be used economically on a large scale.
USA Patent 4405464 describes a process for the removal of selenium by a chemical trea~ment involving reduction of Se(VI) to Se(IV) using metallic iron which is itself oxidized and forms ferric hydroxide which then entrains the reduced selenium.
An article by Smith and Wiechers in Water SA (1981) 7, describes elimination o~ toxic metals from waste wa~er by an integrated wastewater treatment/water reclamation system. The system relies upon a combination of biological and chemical processes, including a bacteriological denitrification, clarification through formation o ferric hydroxide, and an anaerobic digestion.
page 3 ~n article by GeLsberg and Elkins in Proceedirlgs of Symposium on Selenium in the Environment, California State University, Fresno, June 10-12, 1905, describes selenium removal using an immobilized cell reactor containing Pseudomonas species immobilized in alginate. A selenium medium containing 1975 mg/l of selenium was recirculated through the reactor to give a final concen~ration of 1180 mg/l selenium. In further experiments with the Pseudomonas, removal efficiencies 10 of 44 and 68 % were achieved.
Obiects of the Invention The primary intention of the present invention is to provide a method for removing selenium from 15 water, in the sense of wholly or siqnificantly reducing the selenium level. Especially desired is the removal of selena-te from water containing high levels of sulphate, and in particular a me-thod which may be opera-ted economically on a 20 large scale.
A more specific object is to provide a method of water treatment which might be adopted to remove selenium and other contaminants from drainage water such as occurs in 25 the San Joaquin Valle~.
Summary of the Invention The present invention resides irl a method f or removing dissolved selenium from water. The method involves treating the water in a reactor containing a microbial 3~ biomass in which reducing activity can occur. The method is operated to cause the selenium to be converted page 4 to forms of selenium, including elemental selenium, which can be captured or entrained by larger particles. The discharge f rom the reactor can then be processad to remove particles with captured selenium.
Conversion of the selenium -to filterable form is accompanied by conversion to volatile selenium compounds, typically in-cluding hydrogen selenide, dime-thyl selenide and dimethyl diselenideO Such compounds can also be eliminated f~om the discharge of the reactor.
10 Thus, it has unexpectedly been discovered that biolo~ical treatment can readily convert dissolved selenate in a way which leads to massive reductions in the selenium level. The present method derives from an empirical discovery, and was.not predicted.
15 By adoption of the present invention, it becomes possible to treat selenium-containing water to eliminate selenium, and other toxic elements, giving a water which is more eeadily managed foc disposal or re-use.
Indeed, a preliminary evaluation of a pilot plant installed in the San Joaquin Valley to treat contaminated water indicates that the present invention can yield a water, albeit a salty water, which could be dischaeged safely either to evaporation ponds or to salt water sinks. The inclusion of a sulphate-removal step, 25 and further processing foc desalting, can give a treated water which is acceptable for re-use.
The method of the invention i6 potentially more economic than alterrlatives known to the Applicants. The majority of the selenium can be removed and the water purified.
30 Description of the Pre~erred Embodiments The water to be treated by the process of thls invention page 5 is preferably supplied to the reactor supplemented with a nutrient for the biomas6, especially an a~similable carbon source. The wa~er is sui~ably supplied in the substantial absence of free oxygen such that biological conversion proceeds anaerobically or anoxically. The reactor can take the form of a single- or multi-stage reactor, wi~h suitable reactor types including fixed-bed reactors, fluidised-bed reactors, sludge-blanket reactors, and stirred reactor~.
10 ~fter carrying out ~he biological conversion, the selenium is in different forms, including selenium which has become organically bound (probably in the form of a soluble complex compound), selenium which has in some way been captured by larger particles, selenium which L5 has been captured in some way by the biomass rstained in the reactor, and typically also selenium in the form of volatile organic and inorganic compounds. The selenium which has been captured by larger particles is removed, for example by filkration, as discussed in more detail 20 below. The volatile selenium compounds are caused or allowed to escape as gas ~rom the water, suitably to a contained environment for safe disposal or recovery.
More specifically, in a prePerred aspect, this invention resides in a method of removing dissolved hexavalent 25 selenium from water in order to yield a puri~ied wate~. The method suitably comprises treating the seleni~n-containing water in a reactor contain:ing microbial bianass and a nutr:ient for the biomass, substantially in the absence of free oxygen, to cause at least par~ of the 30 selenium to be captured by particles haviny a size of 0.1 micron or greater; and passing the discharge from the reactor through a filter in order to filter out particles which captured the selenium.
page 6 The instant method i6 suited for removing dir;solved hexavalent selenium from water which con~ains a hiyher weight concentration of nitrate than of hexavalent selenium (measured as selenium). In such a proce~s, -the concentra-tion of nitra-te in the water i5 lowered from say between 25 and 250 mg/l (measurecl as nitrogen N), typically between 50 and 200 mg/l nitrate, to 5 mg/l or below, typically 2 mg/1 or less; and the water is t~eated in a reactoc containing microbial biomass to ~emove selenium. The lowering of the nitrate concentration can be effected using biomass, which may be the same biomass which is employed to remove selenium.
Furthermore, the instant method is especially suited for removing dissolved hexavalent selenium from water which 15 contains a high concentration of sulphate, for example 500 to 10000 mg/l (measured as SO4), typically 2500 to 5000 mg/l sulphate.
The method of the present invention i6 particularly intended for use in treating water which contains at 20 least 0.05 mg/l selenium. Indeed, the wate~ can contain at least 0.5 mg/l, and typically around 0.2 to 0.5 rng/l of selenium. The method of -this invention can readily lower the selenium level to a more environmentally accep-table level. The selenium level is typ:ically lowered to10~ or less of the original value, with 5% or less being preferred. For example, a selenium ]evel of around 0.3 mg/l can be lowered to around 30 microg/l (-that is, about 10~ of the orlginal value) using a suitably ciesigned and operated reactor. A final treatment, for example with 30 an ion exchange resin, can be employed to achieve the standard of 10 ~ g/l.
page 7 The reaction mechanism of the present process i6 not known, though it is possible that during fermentation extca-cellular amino acids form organic complaxes with the selenium and these are subsequently as6imilated by the microorganisms in the biomass. Precipi~ation or co-precipitation may also occur. ThUS the particles might contain one or more organic complexes, some of which may be in suspension or some in solution, or in genecal complex molecules or molecules with the selenium 10 compounds absorbed or adsorbed on the surface, or colloidal particles, or rather larger microbial debris. The particles held back in a filter gave no reaction to the normal -test f~r selenate ions, and had to be oxidised with acidic potassiurn permanganate in order to 15 reform selenate ions. A proportion of the particle appeared to pass through a normal laboratory filter paper, even if the filter paper was first covered with precipitated aluminium hydroxide, special filters being eequiced to remove this fraction of the selenium in 2Q reactor e~luent.
The term "particles" is used in a general sense and includes particles which are invisible under the optical microscope, for example large molecules, and in this sense the above mentioned soluble complex compounds will 25 also be ~articles. However, more speci~ically, as particles having a size of below very roughly O.l micron can pass through most practicable physical filters, the particles concerned may have a size of very roughly O.l micron or greater so that it is found satisEactory to 30 use a filter of this retention size (though this is very imprecise). More generally, a minimum particle size of lO microns, especially l micron, is desirable.
In the present process, the reactor can be operated so that sulphate is not cemoved or reduced. This is in page ~
spite of the fact that in drainage waters there may be at least 500 mg/l sulphate ~measured as sulphate) and up to 12000 time6 more sulphate than 6elenate. The process may be workable because in effect the selenate is attacked before the sulphate. Indeed, without being bound by -theory, the presence of selenate in -the water might exert ~ control on -the redox reactions likely -to occur in the biomass.
Selenate is a known competitive inhibitor of sulphate 10 reduction, having a 40-fold greater affinity ~or the enzyme uptake sy6tem than the natural substrate, sulphate (Postgate J.R. (1984) The Sulphate-Reducing Bacteria, Cambridge University Press). This inhibition can confe~ certain advantageous features on the proces6 15 as operated. If significant sulphate reduction is prevented then it is unlikely that the redox potential will drop sufficiently to make it advantageou6 for the bacteria to use Se(VI) as a hydrogen dump (Huang et al.
(1982) Can. Tech. Rep. Fish. Aquat. sci. 1163: and see 20 also Jones et al. (19~4) F'EMS Microbiol Lett. 21, 133-36). The more mobile Se(IV? will not, therefore, be p~oduced, and any interactive mechanism with bactecia is more likely to involve organic matter complexation and mobilization.
25 If desired, a sulphate removal step can be included in the proces~, after removal of selenium. Typically such sulphate removal can be achieved thcough anaerobic digestion to give insoluble sulphides and hydrogen sulehide .
30 The growth of the biomass needs to be promoted, typically by supplementing the selenium-containing water with nutrient. The nutrient feed can be incorporated in the water to be treated, or can be in a separate feed page g to the reactor. The nutrient can include an assimilable carbon source, such as a suitable readily biodegradable organic compound, for example methanol, ethanol, sodium lactate, or a ~ype of mixture of 5 materials that may be present in many strong organic wastes. Some assimilable nitrogen and phosphorous may have to be added in order to generate and sustain the necessary biochemical activity, if they are not already sufficiently present in the water to be Created. The 10 method ideally should be operated so that there is eractically no nitrate-nitrogen nor organic nutrient left at the outlet. In the case of nitrate ~his appears to be desirable both for promoting removal of selenium, as well as for reducing the polluting 15 potential of the final effluent due to nitrate ~ se.
Remaining organic nutrient can be removed by well known methods, such as aerobic fermentation or, in the case of volatile nutrients, air-stripping.
In general terms, the bacterial biomass will be 20 heterotrophic but ~ill not be of a specific strain and is unlikely to be a pure culture: it will merely contain organisms growing from natural contamination, at least initially. Suitable bacteria are likely to include strains belonging to the genera HyPhomicrobium, 25 Corynebacterium, Salmonella, Pseudomonas and acillus.
There i6 no absolute need for special seeding of the reactor ~o~ing to the presence of microbial organisms), but in practice it is possible to save time by seeding with sludge from a sewage treatment plant, preferably 30 from an anoxic nitrate-removing reactor or an ordinary activated sludge reactor.
The bacteria will normally be tolerant of at least l mg/l of selenate, and probably be facultative anaerobes. If desired, suitable strains of bacteria page 10 can be selected by obtaining them from selenium-rich environments, such as selenium-polluted waters, but in practice this selection is not necessary. Thus, a naturally occuring mixed flora such as occurs in sewage 5 sludge provides an adequate source of bacteria:
operation of the present method with supply of a selenium-containing water will lead to natural selection and growth within the reactor.
Thè reactor is preferably operated with no free or 10 dissolved oxygen being present, oxygen only being available in combined form. There may be some oxygen initially, dissolved in the water. No coagulants or floculants, such as ferric chloride, need be added. A
reducing agent, such as ferrous sulphate, hydrazine, 15 sodium sulphide or sodium sulphite, could be introduced, preferably after the initial zone or for instance between two separate vessels defining diferent stages.
The throughput of the reactor will normally be selected to give loadings which are low enough to ensure that 20 little nitrate ~enetrates through the reactor and also that there is a sufficient growth of faculative biomasss to convert the selenium. Since the maximum rate of growth of biomass i6 limited by the nitrate content of the feed, it may occasionally be necessary to add 25 nitrate (and a coLresponding complement of oLganic nutLient) to maximise the biomass. This can be facilitated by operating in two stages, the performance o~ the first stage giving guidance for "tuning" the second.
30 Although it is preferred to remove nitra~es in an anaerobic or anoxic reactor, the nitrates can be removed in any suitable way prior to removing the selenium. It seems that the nitrate concentration must be relatively page 11 low (say 5mg/1 or less) before the ~elenium i8 converted. Nonetheless, selenium removal i6 po6sible before all the nitrate has been removed. There appear6 to be no definite upper limit to the content of nitrate that is acceptable in the feed water but it i~
advantageous to balance flows so that this concentration is at a reasonable uniform average of those likely to be encountered.
When operating a single-stage fixed-bed reactor in which 10 the support medium is inert (such as gravel or crushed rock) it appears that unless there is less than around l mg/l of nitrate (measured as nitrogen) at the outle~
from the reactor, there will be little conversion of the selenium to removable forms. The limit of 1 mg/l l5 nitrate concentration has not been accurately determined, and can vary greatly according to the materials and conditions in the reactor. For instance, when using steel wool as the support, a nitrate concentration of 5 mg/l (measured as nitrogen) at the 20 outlet can be tolerated (the total dissolved selenium concentration in the effluent being acceptable, say 0.01~ mg/l (14 ~g/l)) the acceptable nitrate concentration may be even higher. If the nitrate concentration at the outlet is too high but there is 25 adequate ~rganic nutrient present, reduction in the rate of flow through the reactor normally allows the conversion of selenium to proceed.
In the preferred arrangements, one, two or three reactor stages are used for the ~elenium removal, or nitrate 30 removal and selenium removal.
The ere~erred form of reactor has a fixed bed of support material. Initially it was found that when steel wool was used as the ~uepo~t in the ~eactor, the reaction page 12 ratas appeared to be fas~er, the overall removal greater, and nitrate tolerance greater. Con6umption of the steel wool was observed, and 60 the method may have to be operated using reactors in parallel, one o~ which S is being used and the other of which i6 being reloaded. Some of the iron thus goes into solution, but can be removed by for example a cross-flow filter.
The effect of the iron remains uncertain, but it may act as a catalyst or may decrease the redox potential.
10 Thus it may be possible to use other reducing agents, either in the form of solids or ~ossibly as solutions injected into the feed to the first or second reactor stages.
The physiaal arrangement of the iron need not be that of 15 steel wool, so long as the shape provides a high specific surface (high surface/volume ra~io) - thus steel scrap or swarf may be usable. Relative to conventional universal media (e.g. gravel, rock, slag), some improvement would be expected from substrates such 20 as plastic filaments which provided a higher specific surface to which the biomass would adhere.
For a fixed-bed reactor, in place of steel the support medium can be a substantially inert, inorganic wool such as glass wool or rock mineral fibre wool. The wool 25 fibre diameter is preferably from 3 to 20 ~m and a preferred packiny density is from 70 to 300 kg/m .
To date, the preferred diameter and packing density were about 10 ~m and about 230 kg/m2 bed volume.
Materials other than steel and glass wool or rock 30 mineral flbre wool can be used for the support of the biomass in fixed-bed reactors; in general, it is merely desired that a combination of large specific surface and adequate void space should be provided. The void space page 13 suitably amounts to 20 to 40~, for example 25 to 35% although higher amounts up to almost 100~ can be used. Further ex-amples of currently preferred suppor-t materials include stones, for example stones of 0.5 to 4, especially L -to 3 inches (say 1.25 to 10, especially 2.5 to 7.5 cm).
It is possible that the selenium removal occurs efficiently because the preferred bed is not homogeneous. In a packed bed, which i6 no~
homogeneous, there will be variou6 level6 of reducing 10 activity (redox potential) within the bed. In other words, there is probably a plurality of zones in which different reactions take place in the reactor. ~or reasons already indicated it is mo~t convenient to use a two- or more stage reactor (with separate vessels 15 defining the stages). With an inert-bed reactor, the nitrats apparently has to be removed first in order for selenium to be converted, and the initial stage can be operated foc the most efficient nitrate removal to allow selenium conversion then to take place. The subsequent 20 stages can be manipulated to grow further biomass to maximise conversion, especially enttainment or capturing in the form of suspended particles. Additional feed can be provided to the second stage. This feed can include nitrate, which does not ceverse previous 25 reactions in which seleniurn was captured but allows further growth of biomass, and thus allows improved capturing to take place.
Fluidised-bed reactors, sludge-blanket reactor6, stirred ceactors and othec reactor types can be used to carry 3~ out the process, as alterna~ives to fixed-bed reactors.
Any of the reactor stages may be in the form of fluidised beds using a particulate material for example on which the biomass orms a coating. Normally, upward-flow beds would be used (par-ticulate ma-terlal heavier thar water), -though it is possible to use downward-flow beds (particulat0 material lighter or heavier than water). In experimental work, a six inch diameter (150 mrn) fluidized bed was used for fluidizing, with sand as the particulate material. In order to recover the particula-te material which is carried over, the arrangement used at the Coleshill, England, experimental plant may be used, as reported in the paper ~'Sand~siomass Separation with Production of a concentrated Sludge" by Cooper et al, presented at a Water Research Centre/UMIST conference entitled "Biological Fluidized Bed Treatment of Water and Wastewater'~ at Manchester, April 14-17, 1980. However, fluidizing has advantages and disadvantages, one disadvantage being the extra power required. Continuously-stirred reactors may be just as economic in practice.
Cross-flow or other filtration can be used to produce concentrated biomass after selenium removal. A preferred type of filter is a cross-flow microfilter, preferably with an aluminium hydroxide or zirconium hydroxide membrane, for instance as described in PCT specification PCT/~B86/00143 and Canadian Patent Application No. 503944. filed March 12, 1986. It has been no-ted that selenium included in larger particles such as microbial debris is retained on a sand filter. It therefore appears possible to operate the method so that the ma;or part of the non-volatile seleniurn is included ln such debris or in general in suspended particles, in which case a simple sand filter or filter of equivalent slze can be used.
The concentrate from the filter can be passed back into the selenlum-removal reactor. Thls enables one to raise
REMOVI~G_SELENIUM FROM WAT~R
Backqround of the Invention The present invention relates to the removal of selenium from water, and more particularly but not exclusively ~o the treatment of drainage water containing selenium leached from soil.
Selenium is often present in water at concentrations of up to 0.5 mg/l, but a concentration of this order is undesirable for purposes such as drinking water or crop irrigation. For example, in the USA, the permitted maximum selenium level for drinking water is set at 10 ~g/l. In some selenium-containing waters such as certain irrigation drainage waters, a substantial proportion of the selenium is present as the selenate anion. [SeO4] These waters are especially difficult to treat because there is also a very high concentra~ion of sulphate.
In the USA, particular attention has focussed on treatment of the agricultural drainage water in the San Joaquin Valley. This Valley has about 1.1 million acres of extremely productive land which is under irrigation. The land iB generally low-lying and requires drainage in order to avoid high salinity in crop root zones. A major scheme to drain off subsurface watec after use for irrigation has been frustrated by discovery of high levels of ~5 contaminants. The drainage water i5 brackish, and has a relatively high concentration of salts and potentially toxic elements, with selenium representing a particular problem. Enviconmental concecn has led to a suspension page 2 of construc~ion work, a closure order on a large reservoir, and an extensive program of drain plugging.
With the plugging of the drains, the water table i6 beginning to rise, causing concern for growers in the valley-Methods are available for the purification of wa~er, butin general the known methods are not suited for use on a large scale wi~h brackish drainage water con~aining selenium and a range of other contaminants. Reverse lO osmosis is costly, and so also is ion exchange. In this respect, it i8 to be borne in mind that the in~ial aim in tceating the drainage water in the San Joaquin Valley and elsewhere is to render it suited for discharge. Hence, an economic process is paramount.
15 Methods are also described in the literature which are specifically concerned with the removal of selenium from water, but it is not apparent that such methods can be used economically on a large scale.
USA Patent 4405464 describes a process for the removal of selenium by a chemical trea~ment involving reduction of Se(VI) to Se(IV) using metallic iron which is itself oxidized and forms ferric hydroxide which then entrains the reduced selenium.
An article by Smith and Wiechers in Water SA (1981) 7, describes elimination o~ toxic metals from waste wa~er by an integrated wastewater treatment/water reclamation system. The system relies upon a combination of biological and chemical processes, including a bacteriological denitrification, clarification through formation o ferric hydroxide, and an anaerobic digestion.
page 3 ~n article by GeLsberg and Elkins in Proceedirlgs of Symposium on Selenium in the Environment, California State University, Fresno, June 10-12, 1905, describes selenium removal using an immobilized cell reactor containing Pseudomonas species immobilized in alginate. A selenium medium containing 1975 mg/l of selenium was recirculated through the reactor to give a final concen~ration of 1180 mg/l selenium. In further experiments with the Pseudomonas, removal efficiencies 10 of 44 and 68 % were achieved.
Obiects of the Invention The primary intention of the present invention is to provide a method for removing selenium from 15 water, in the sense of wholly or siqnificantly reducing the selenium level. Especially desired is the removal of selena-te from water containing high levels of sulphate, and in particular a me-thod which may be opera-ted economically on a 20 large scale.
A more specific object is to provide a method of water treatment which might be adopted to remove selenium and other contaminants from drainage water such as occurs in 25 the San Joaquin Valle~.
Summary of the Invention The present invention resides irl a method f or removing dissolved selenium from water. The method involves treating the water in a reactor containing a microbial 3~ biomass in which reducing activity can occur. The method is operated to cause the selenium to be converted page 4 to forms of selenium, including elemental selenium, which can be captured or entrained by larger particles. The discharge f rom the reactor can then be processad to remove particles with captured selenium.
Conversion of the selenium -to filterable form is accompanied by conversion to volatile selenium compounds, typically in-cluding hydrogen selenide, dime-thyl selenide and dimethyl diselenideO Such compounds can also be eliminated f~om the discharge of the reactor.
10 Thus, it has unexpectedly been discovered that biolo~ical treatment can readily convert dissolved selenate in a way which leads to massive reductions in the selenium level. The present method derives from an empirical discovery, and was.not predicted.
15 By adoption of the present invention, it becomes possible to treat selenium-containing water to eliminate selenium, and other toxic elements, giving a water which is more eeadily managed foc disposal or re-use.
Indeed, a preliminary evaluation of a pilot plant installed in the San Joaquin Valley to treat contaminated water indicates that the present invention can yield a water, albeit a salty water, which could be dischaeged safely either to evaporation ponds or to salt water sinks. The inclusion of a sulphate-removal step, 25 and further processing foc desalting, can give a treated water which is acceptable for re-use.
The method of the invention i6 potentially more economic than alterrlatives known to the Applicants. The majority of the selenium can be removed and the water purified.
30 Description of the Pre~erred Embodiments The water to be treated by the process of thls invention page 5 is preferably supplied to the reactor supplemented with a nutrient for the biomas6, especially an a~similable carbon source. The wa~er is sui~ably supplied in the substantial absence of free oxygen such that biological conversion proceeds anaerobically or anoxically. The reactor can take the form of a single- or multi-stage reactor, wi~h suitable reactor types including fixed-bed reactors, fluidised-bed reactors, sludge-blanket reactors, and stirred reactor~.
10 ~fter carrying out ~he biological conversion, the selenium is in different forms, including selenium which has become organically bound (probably in the form of a soluble complex compound), selenium which has in some way been captured by larger particles, selenium which L5 has been captured in some way by the biomass rstained in the reactor, and typically also selenium in the form of volatile organic and inorganic compounds. The selenium which has been captured by larger particles is removed, for example by filkration, as discussed in more detail 20 below. The volatile selenium compounds are caused or allowed to escape as gas ~rom the water, suitably to a contained environment for safe disposal or recovery.
More specifically, in a prePerred aspect, this invention resides in a method of removing dissolved hexavalent 25 selenium from water in order to yield a puri~ied wate~. The method suitably comprises treating the seleni~n-containing water in a reactor contain:ing microbial bianass and a nutr:ient for the biomass, substantially in the absence of free oxygen, to cause at least par~ of the 30 selenium to be captured by particles haviny a size of 0.1 micron or greater; and passing the discharge from the reactor through a filter in order to filter out particles which captured the selenium.
page 6 The instant method i6 suited for removing dir;solved hexavalent selenium from water which con~ains a hiyher weight concentration of nitrate than of hexavalent selenium (measured as selenium). In such a proce~s, -the concentra-tion of nitra-te in the water i5 lowered from say between 25 and 250 mg/l (measurecl as nitrogen N), typically between 50 and 200 mg/l nitrate, to 5 mg/l or below, typically 2 mg/1 or less; and the water is t~eated in a reactoc containing microbial biomass to ~emove selenium. The lowering of the nitrate concentration can be effected using biomass, which may be the same biomass which is employed to remove selenium.
Furthermore, the instant method is especially suited for removing dissolved hexavalent selenium from water which 15 contains a high concentration of sulphate, for example 500 to 10000 mg/l (measured as SO4), typically 2500 to 5000 mg/l sulphate.
The method of the present invention i6 particularly intended for use in treating water which contains at 20 least 0.05 mg/l selenium. Indeed, the wate~ can contain at least 0.5 mg/l, and typically around 0.2 to 0.5 rng/l of selenium. The method of -this invention can readily lower the selenium level to a more environmentally accep-table level. The selenium level is typ:ically lowered to10~ or less of the original value, with 5% or less being preferred. For example, a selenium ]evel of around 0.3 mg/l can be lowered to around 30 microg/l (-that is, about 10~ of the orlginal value) using a suitably ciesigned and operated reactor. A final treatment, for example with 30 an ion exchange resin, can be employed to achieve the standard of 10 ~ g/l.
page 7 The reaction mechanism of the present process i6 not known, though it is possible that during fermentation extca-cellular amino acids form organic complaxes with the selenium and these are subsequently as6imilated by the microorganisms in the biomass. Precipi~ation or co-precipitation may also occur. ThUS the particles might contain one or more organic complexes, some of which may be in suspension or some in solution, or in genecal complex molecules or molecules with the selenium 10 compounds absorbed or adsorbed on the surface, or colloidal particles, or rather larger microbial debris. The particles held back in a filter gave no reaction to the normal -test f~r selenate ions, and had to be oxidised with acidic potassiurn permanganate in order to 15 reform selenate ions. A proportion of the particle appeared to pass through a normal laboratory filter paper, even if the filter paper was first covered with precipitated aluminium hydroxide, special filters being eequiced to remove this fraction of the selenium in 2Q reactor e~luent.
The term "particles" is used in a general sense and includes particles which are invisible under the optical microscope, for example large molecules, and in this sense the above mentioned soluble complex compounds will 25 also be ~articles. However, more speci~ically, as particles having a size of below very roughly O.l micron can pass through most practicable physical filters, the particles concerned may have a size of very roughly O.l micron or greater so that it is found satisEactory to 30 use a filter of this retention size (though this is very imprecise). More generally, a minimum particle size of lO microns, especially l micron, is desirable.
In the present process, the reactor can be operated so that sulphate is not cemoved or reduced. This is in page ~
spite of the fact that in drainage waters there may be at least 500 mg/l sulphate ~measured as sulphate) and up to 12000 time6 more sulphate than 6elenate. The process may be workable because in effect the selenate is attacked before the sulphate. Indeed, without being bound by -theory, the presence of selenate in -the water might exert ~ control on -the redox reactions likely -to occur in the biomass.
Selenate is a known competitive inhibitor of sulphate 10 reduction, having a 40-fold greater affinity ~or the enzyme uptake sy6tem than the natural substrate, sulphate (Postgate J.R. (1984) The Sulphate-Reducing Bacteria, Cambridge University Press). This inhibition can confe~ certain advantageous features on the proces6 15 as operated. If significant sulphate reduction is prevented then it is unlikely that the redox potential will drop sufficiently to make it advantageou6 for the bacteria to use Se(VI) as a hydrogen dump (Huang et al.
(1982) Can. Tech. Rep. Fish. Aquat. sci. 1163: and see 20 also Jones et al. (19~4) F'EMS Microbiol Lett. 21, 133-36). The more mobile Se(IV? will not, therefore, be p~oduced, and any interactive mechanism with bactecia is more likely to involve organic matter complexation and mobilization.
25 If desired, a sulphate removal step can be included in the proces~, after removal of selenium. Typically such sulphate removal can be achieved thcough anaerobic digestion to give insoluble sulphides and hydrogen sulehide .
30 The growth of the biomass needs to be promoted, typically by supplementing the selenium-containing water with nutrient. The nutrient feed can be incorporated in the water to be treated, or can be in a separate feed page g to the reactor. The nutrient can include an assimilable carbon source, such as a suitable readily biodegradable organic compound, for example methanol, ethanol, sodium lactate, or a ~ype of mixture of 5 materials that may be present in many strong organic wastes. Some assimilable nitrogen and phosphorous may have to be added in order to generate and sustain the necessary biochemical activity, if they are not already sufficiently present in the water to be Created. The 10 method ideally should be operated so that there is eractically no nitrate-nitrogen nor organic nutrient left at the outlet. In the case of nitrate ~his appears to be desirable both for promoting removal of selenium, as well as for reducing the polluting 15 potential of the final effluent due to nitrate ~ se.
Remaining organic nutrient can be removed by well known methods, such as aerobic fermentation or, in the case of volatile nutrients, air-stripping.
In general terms, the bacterial biomass will be 20 heterotrophic but ~ill not be of a specific strain and is unlikely to be a pure culture: it will merely contain organisms growing from natural contamination, at least initially. Suitable bacteria are likely to include strains belonging to the genera HyPhomicrobium, 25 Corynebacterium, Salmonella, Pseudomonas and acillus.
There i6 no absolute need for special seeding of the reactor ~o~ing to the presence of microbial organisms), but in practice it is possible to save time by seeding with sludge from a sewage treatment plant, preferably 30 from an anoxic nitrate-removing reactor or an ordinary activated sludge reactor.
The bacteria will normally be tolerant of at least l mg/l of selenate, and probably be facultative anaerobes. If desired, suitable strains of bacteria page 10 can be selected by obtaining them from selenium-rich environments, such as selenium-polluted waters, but in practice this selection is not necessary. Thus, a naturally occuring mixed flora such as occurs in sewage 5 sludge provides an adequate source of bacteria:
operation of the present method with supply of a selenium-containing water will lead to natural selection and growth within the reactor.
Thè reactor is preferably operated with no free or 10 dissolved oxygen being present, oxygen only being available in combined form. There may be some oxygen initially, dissolved in the water. No coagulants or floculants, such as ferric chloride, need be added. A
reducing agent, such as ferrous sulphate, hydrazine, 15 sodium sulphide or sodium sulphite, could be introduced, preferably after the initial zone or for instance between two separate vessels defining diferent stages.
The throughput of the reactor will normally be selected to give loadings which are low enough to ensure that 20 little nitrate ~enetrates through the reactor and also that there is a sufficient growth of faculative biomasss to convert the selenium. Since the maximum rate of growth of biomass i6 limited by the nitrate content of the feed, it may occasionally be necessary to add 25 nitrate (and a coLresponding complement of oLganic nutLient) to maximise the biomass. This can be facilitated by operating in two stages, the performance o~ the first stage giving guidance for "tuning" the second.
30 Although it is preferred to remove nitra~es in an anaerobic or anoxic reactor, the nitrates can be removed in any suitable way prior to removing the selenium. It seems that the nitrate concentration must be relatively page 11 low (say 5mg/1 or less) before the ~elenium i8 converted. Nonetheless, selenium removal i6 po6sible before all the nitrate has been removed. There appear6 to be no definite upper limit to the content of nitrate that is acceptable in the feed water but it i~
advantageous to balance flows so that this concentration is at a reasonable uniform average of those likely to be encountered.
When operating a single-stage fixed-bed reactor in which 10 the support medium is inert (such as gravel or crushed rock) it appears that unless there is less than around l mg/l of nitrate (measured as nitrogen) at the outle~
from the reactor, there will be little conversion of the selenium to removable forms. The limit of 1 mg/l l5 nitrate concentration has not been accurately determined, and can vary greatly according to the materials and conditions in the reactor. For instance, when using steel wool as the support, a nitrate concentration of 5 mg/l (measured as nitrogen) at the 20 outlet can be tolerated (the total dissolved selenium concentration in the effluent being acceptable, say 0.01~ mg/l (14 ~g/l)) the acceptable nitrate concentration may be even higher. If the nitrate concentration at the outlet is too high but there is 25 adequate ~rganic nutrient present, reduction in the rate of flow through the reactor normally allows the conversion of selenium to proceed.
In the preferred arrangements, one, two or three reactor stages are used for the ~elenium removal, or nitrate 30 removal and selenium removal.
The ere~erred form of reactor has a fixed bed of support material. Initially it was found that when steel wool was used as the ~uepo~t in the ~eactor, the reaction page 12 ratas appeared to be fas~er, the overall removal greater, and nitrate tolerance greater. Con6umption of the steel wool was observed, and 60 the method may have to be operated using reactors in parallel, one o~ which S is being used and the other of which i6 being reloaded. Some of the iron thus goes into solution, but can be removed by for example a cross-flow filter.
The effect of the iron remains uncertain, but it may act as a catalyst or may decrease the redox potential.
10 Thus it may be possible to use other reducing agents, either in the form of solids or ~ossibly as solutions injected into the feed to the first or second reactor stages.
The physiaal arrangement of the iron need not be that of 15 steel wool, so long as the shape provides a high specific surface (high surface/volume ra~io) - thus steel scrap or swarf may be usable. Relative to conventional universal media (e.g. gravel, rock, slag), some improvement would be expected from substrates such 20 as plastic filaments which provided a higher specific surface to which the biomass would adhere.
For a fixed-bed reactor, in place of steel the support medium can be a substantially inert, inorganic wool such as glass wool or rock mineral fibre wool. The wool 25 fibre diameter is preferably from 3 to 20 ~m and a preferred packiny density is from 70 to 300 kg/m .
To date, the preferred diameter and packing density were about 10 ~m and about 230 kg/m2 bed volume.
Materials other than steel and glass wool or rock 30 mineral flbre wool can be used for the support of the biomass in fixed-bed reactors; in general, it is merely desired that a combination of large specific surface and adequate void space should be provided. The void space page 13 suitably amounts to 20 to 40~, for example 25 to 35% although higher amounts up to almost 100~ can be used. Further ex-amples of currently preferred suppor-t materials include stones, for example stones of 0.5 to 4, especially L -to 3 inches (say 1.25 to 10, especially 2.5 to 7.5 cm).
It is possible that the selenium removal occurs efficiently because the preferred bed is not homogeneous. In a packed bed, which i6 no~
homogeneous, there will be variou6 level6 of reducing 10 activity (redox potential) within the bed. In other words, there is probably a plurality of zones in which different reactions take place in the reactor. ~or reasons already indicated it is mo~t convenient to use a two- or more stage reactor (with separate vessels 15 defining the stages). With an inert-bed reactor, the nitrats apparently has to be removed first in order for selenium to be converted, and the initial stage can be operated foc the most efficient nitrate removal to allow selenium conversion then to take place. The subsequent 20 stages can be manipulated to grow further biomass to maximise conversion, especially enttainment or capturing in the form of suspended particles. Additional feed can be provided to the second stage. This feed can include nitrate, which does not ceverse previous 25 reactions in which seleniurn was captured but allows further growth of biomass, and thus allows improved capturing to take place.
Fluidised-bed reactors, sludge-blanket reactor6, stirred ceactors and othec reactor types can be used to carry 3~ out the process, as alterna~ives to fixed-bed reactors.
Any of the reactor stages may be in the form of fluidised beds using a particulate material for example on which the biomass orms a coating. Normally, upward-flow beds would be used (par-ticulate ma-terlal heavier thar water), -though it is possible to use downward-flow beds (particulat0 material lighter or heavier than water). In experimental work, a six inch diameter (150 mrn) fluidized bed was used for fluidizing, with sand as the particulate material. In order to recover the particula-te material which is carried over, the arrangement used at the Coleshill, England, experimental plant may be used, as reported in the paper ~'Sand~siomass Separation with Production of a concentrated Sludge" by Cooper et al, presented at a Water Research Centre/UMIST conference entitled "Biological Fluidized Bed Treatment of Water and Wastewater'~ at Manchester, April 14-17, 1980. However, fluidizing has advantages and disadvantages, one disadvantage being the extra power required. Continuously-stirred reactors may be just as economic in practice.
Cross-flow or other filtration can be used to produce concentrated biomass after selenium removal. A preferred type of filter is a cross-flow microfilter, preferably with an aluminium hydroxide or zirconium hydroxide membrane, for instance as described in PCT specification PCT/~B86/00143 and Canadian Patent Application No. 503944. filed March 12, 1986. It has been no-ted that selenium included in larger particles such as microbial debris is retained on a sand filter. It therefore appears possible to operate the method so that the ma;or part of the non-volatile seleniurn is included ln such debris or in general in suspended particles, in which case a simple sand filter or filter of equivalent slze can be used.
The concentrate from the filter can be passed back into the selenlum-removal reactor. Thls enables one to raise
2~
page 15 the concentration of biomass (expres6ed a6 a percentage weight per unit volume, the biomass being weighed dry) in the reactor. For example, in a reactor in which biomass i6 separa~ed by 6ettlement, the concentration i6 S usually limited to about 0.06%, and using cross-flow microfiltration for the return of concentrate in a third reactor, the concentration may be 4% and probably higher; in the latter case, large proportions of ~ludge are recirculated in the concentrate.
10 It has been noted that nitrogen bubble6 in the reactor, and in theory the nitrogen may contain some hydrogen selenide. It may be po6sible (especially by addition o~ suitable reducing agents ~o the .eed~ to operate the method so that mo6t of the 6elenium come6 off as 15 hydrogen selenide. In such circumstance6, none of the selenium, or only a small proportion of the selenium, would be included in larger particles, and the filtration or equivalent separation step might be eliminated.
Equally, elimination of the separation step might apply to 20 the production of volatile organic selenium compounds.
It is believed that the filtered outflow can be further treated by aeration with activated-61udge fed with a sugac such as glucose (or any 6uitable biodegradable organic compound) as a nut~ient, to further reduce the 25 dis601ved selenium.
Accordingly, the invention also provides a method of removing selenium from water by treating the selenium-containing water in a 6ingle-- or multi-stage ~eactor containing microbial biomass and a nutrient for 30 the biomass, in the substantial absence of oxygen, and then treating the water in a 6ingle- or multi-stage Leactor containing microbial biomass and a nutrient for the biomass, in the pLesence of oxygen. As above, the ~2~%~i page 16 discharge from the end reactor can be ~iltered, and the discharge from the each preceding reactor will normally be filtered.
Subsequent to sel0nium remoYal, further steps are possible, particularly if other contaminant~ are present. Ion-exchange can be used for a polishing, for instance for boron removal. It is also possible to arcange for boron to be removed in crofi6-flow filtration using suitable membranes.
10 The selenium itsel~ (elemental or compounds thereo) is a useful byproduct of the invention.
Applying the principle of the invention, it i8 also possible to reclaim selenium compounds from organically-complexed mixtures in sludge from treatment 15 plants or fLom reservoirs; specifically in the latter case, this enables mud on the bottom of the reservoir to be purified of selenium, and the selenium itself can be ce-complexed using the invention and recovered as a selenium-rich ~ludge or as selenium compound.
20 The ExamPles The present invention will now be illustrated by reference to some non-limiting Examples, in which reference is made to the accompanying drawings.
Description of the Drawinqs 25 Figure 1 is a schematic diagram of a plant for carrying out a method in accordance with the invention.
Figure 2 is a schematic diagram of a another plant for carrying out a method in accordance with the invention, page 17 where removal of sulphate and boron i6 desired as well as removal of 6elenium.
Referring to Figure 1, selenium-containing water from conduit 1 supplemented with me~hanol-based nutrient from 5 conduit 2 pass through two identical reactor stages 3, 4 (same cross-section and same contents), preferably with no recyling of feed water, and thence through a small ceactor 5, a pump 6 and a cross-flow microfilter 7.
Purified water is discharged through conduit 8 and lOconcentrate for waste disposal is discharged conduit 9, part of which can be returned as active biomas~ through a return line lo to the reactor 5.
The reactor stages 3, 4 aLe fixed film reactors and are filled near -to the -top with approximately 1 inch (2.5 cm) l5gravel (40% void space). The up-flow mode is preferred, as shown. The stages 3, 4 and the reactor 5 are seeded with activated sludge prior to start-up.
The stages 3 and 4 are operated anaerobically or anoxically. The reactor 5 has a sparge tube 11 for the 20addition of air in order to strip o~f surplus methanol supplied in the nutrient. The reactor 5 thus contain6 aerobic activated sludge.
As indicated by the valving, the stage 4 may be by-passed if the selenium content is considered to be 25sufficiently low at the outlet from the stage 3.
Alternatively, the stage 4 may be omitted altogether.
Referring now to Figure 2, like references are used for like parts. Pumps are indicated throughout as plain circles. Effluent is abstracted from a main drain Zl 30and is passed through biological reactor stages 3, 4 in series. These can be fixed film reactors as in Figure 1, oc one or both of them can be a stirred reactor or a page 1~
fluidised bed reactor. The outflow from the stage ~ i6 filtered in a cross-~low microfilter 7. The selenium concentra~e i6 fed through condui~ 9 and the liquid passing through the filter 7 i8 pumped in~o a reactor 5 22. At some point between the ef f luent feed and the inlet to the reactor 22, a carbon dose i6 added as a biomass nutrient. The reactor 2~ operates anaerobicaLly to destroy sulphates and to conver~ heavy metals to insoluble sulphides for collection in a second cross-flow microfilter 23. Sulphates destroyed in the reactor 22 generate hydrogen sulphide gas which i6 passed into a photosynthetic reactor 24, and elemental sulphur is produced. From the microfilter Z3, the heavy metal sulphides are removed through conduit 25 and 15the permeate passes through a collection tank 26 to an ion exchange unit 27 for boron removal. Treated water flows out at pipe 28.
Example 1 A synthetic water, similar in composition to the average 2C for farm drainage waters in the San Joaquin Valley, Cali-fornia, but with added phosphate, was -treated using the plan-t illustrated in Figure 1. In this and -the following Examples, the pll oE the feed water varied, but was always between 7.8 and 8.4 Relevant par-ts of the chemical analy-25 sis for this Example 1 were:
30 mg/1 nitrate (expressed as nitrogen);
0.36 mg/l selenium (as the selenate ion, expressedas selenium):
4000 mg/l sulphate (expressed as sulphate);
20 mg/l phosphate (expressed as phosphorus).
The flow rate was 3 l/hr. The nutrient feed for the biomass was 5% methanol at a flow ra~e of 0.03 i/hr.
For this Example, and Examples Z and 3, the initial ~-z~
page l9 biomass was anaerobically digested sludge taken from the sewage worlcs of the Thames Water Authority at Beddington, England. The reactor stages 3, 4 were operated at ambient tamperature, about 20C. The 5 residence time in each of the reactor stages 3, 4 was about 3.0 hours. Each reactor stage 3, 4 had a voids volume of lo litres.
The outflow was sampled at the exit of each of the reactor stages 3, 4. The liquid was filtered on a laboratory filter of about 5 micron pore size, the filtrate being dissolved or colloidal organic material with selenium and also dissolved inorganic ~elenium.
The amount of dissolved inorganic selenium was determined. Further selenium was either retained in 15the reactor stages 3, 4 with the biomass (not measured) or evolved as gaseous selenium compounds (not measured).
With the flow rates indicated above, which are believed to be close to the optimum flow rates, there was a peciod during which biomass was generated and the 20e~ficiency of the reaction improved. At the end of the period, the relevant contents of the water at the outlet from each reactor stage 3, 4 were (mg/l):
Reactor stage 3 Reactor stage 4 Selenium in filtrate 0.06 o.os 25 inorganic 0.00S o-005 organic complexed 0.055 0.0~5 Held back on filter not measured 0.06 Total Se in outflow not measured O.ll Nitrate (as N) 0.6 0.4 30Sulphate (as S04) 4000 ~000, unchanged The total held back and hence the total selenium in the ~27~25;
page 20 outlet of reactor stage 3 were not measured.
Example 2 Treated water from a ~wo-stage reactor as in Example 1 was filtered through glass-fibre filter paper in order 5 to remove suspende~ particles containing selenium (which in practice could be done on cross-flow filter 7 or by sand filtcation). The water was aerated for an hour with activated sludge fed with glucose. By appropriate vaeiation in the operating conditions, the supernatant 10after settling the sludge contained only 6 ~g Se/l compared with 30 ~g/l dissolved Se in the effluent from the two-stage reactor.
Example 3 One laboratory reactor column was used in the up-flow 15mode, filled half-way with steel wool. The column cross-section was 2000 mm and the volume filled with steel wool was 0.25 litres. The steel wool was a commercially available material. The threads of the wool wece o~ finishing grade 4 or 5, having a diameter 20Of 0.1 to 0.15 mm. The wool was made from a low carbon steel of the rimming variety, not silicon-killed, the chemical composition being stated to be with the limits (~ by weight): C 0.8-1.5: Mn 0.3-0.5: S 0.05 or more; P
0.05 or more 25The steel wool was inserted into the columns so as to ~ill the barrel of the column reasonably uniformly but without undue compaction of the wool. This gives a medium having enough void space to allow water to pass through readily but at the same time did not contain 30large passages which would permit short-circuiting and thus poor contact with the wool sur~aces. The bulk 2~;
page 21 density when in place is 60 * lo kg~m .
A feed of 250 ml/hr was passed through the ves6el (i.e, retention time one hour), ~he feed having the following composition (mg~
Cl 1500 Alkalinity (as CaC03) 180 Nitrate (as N) 30 Phosphate (as P) 4 Bocate (as B) 10 5elenate (as Se) 0.32 70% lactic acid Inutrient) S
Samples of the effluent water were taken over a period of 14 days. Results of analyses are as follows (concentrations in mg/l):
Time after Selenium (as Se)Nitrate start up Inorganic To~al Soluble(a~ N) (days) l 0.22 0.26 9 0.005 0.025 lo 0.006 0,0167.0 (anomalous) 2013 0.004 0.030 14 0.006 0.017 Example 4 Subsurface drainage water at Murietta Farms, Westlands Water District, near Mendota, California, USA, was treated usiny the plant of Figure 2. The biomass wa6 obtained from a local sewage works.
Be:Eore treatment, the water analysis showed lOg ppm N03 (measured as nitrogen; N), 3000-4500 ppm S04, 1800 Cl, ~-z~
page 22 6 ppm B, 0.06 ppm Cr, and 0.35-0.45 mg/l Se, among other contaminants. ~fter treatment, the selenium level was down to 3 to 5 ppb, along with impressive reductions in the level of nitrate, sulpha~e, heavy metals and boron.
A plant was constructed at Murietta Farm6 with three ~eactor stages and a cross-flow microfilter. The design capacity was 40 m /day. Each Leactor had a volume of about 7 m . The first and second reac-tors were filled with stones of diameter 1.5 to 2 inches ~say 3.~
to 5 cm)0 giving 35 % porosity, while steel wool was used to fill the third reactor.
The dcainage water as in Example 4 was fed at 30 l/m and su~plemented with a nutrient comprising concentrated Steffen's waste llqour (a waste liqour from a sugar beet factory). Phosphate was added to the concentrated Steffen's wa6te liquor at the level o~ 2 mg/l, and the waste liquo~ was fed at a rate corresponding to 187 mg carbon per litre of drainage water.
Redox potentials were measured in order to assess the oeerating modes of the three reactors. The drainage water itself typically showed a redox potential in the range -20 to ~20 mV, while the outflow from the first, second and third reactor6 wece respectively in the ranges -100 to -lqO mV, -140 to -175 mV~ and -200 to -300 mV.
The treated water from the third reactor showed less than 1 ppm nitrate and less than 30 p~b selenium. The water fcom the cross-flow microfilter contained less than 15 ppb selenium, and was passed through a resin page 23 exchange column for a final poli6hing, giving an efluent containing less than 10 ppb selenium.
OpeLation wa~ 6ustained for more than 3 months.
Example 6 Fu~ther modification of the plant amployed for Example S
is envisaged, particularly in view of the recent realisation that some of the selenium in the drainage water i~ being converted in the reactors to volatile organic selenium compounds such as dimethyl selenide or dimethyldiselenide. Such compounds represent a useful source oE selenium, and can readily be recovered by appropria-te containment design of the plant. More generally, the aim is to construct a plant capable of treating 1 million US
gallons per day.
page 15 the concentration of biomass (expres6ed a6 a percentage weight per unit volume, the biomass being weighed dry) in the reactor. For example, in a reactor in which biomass i6 separa~ed by 6ettlement, the concentration i6 S usually limited to about 0.06%, and using cross-flow microfiltration for the return of concentrate in a third reactor, the concentration may be 4% and probably higher; in the latter case, large proportions of ~ludge are recirculated in the concentrate.
10 It has been noted that nitrogen bubble6 in the reactor, and in theory the nitrogen may contain some hydrogen selenide. It may be po6sible (especially by addition o~ suitable reducing agents ~o the .eed~ to operate the method so that mo6t of the 6elenium come6 off as 15 hydrogen selenide. In such circumstance6, none of the selenium, or only a small proportion of the selenium, would be included in larger particles, and the filtration or equivalent separation step might be eliminated.
Equally, elimination of the separation step might apply to 20 the production of volatile organic selenium compounds.
It is believed that the filtered outflow can be further treated by aeration with activated-61udge fed with a sugac such as glucose (or any 6uitable biodegradable organic compound) as a nut~ient, to further reduce the 25 dis601ved selenium.
Accordingly, the invention also provides a method of removing selenium from water by treating the selenium-containing water in a 6ingle-- or multi-stage ~eactor containing microbial biomass and a nutrient for 30 the biomass, in the substantial absence of oxygen, and then treating the water in a 6ingle- or multi-stage Leactor containing microbial biomass and a nutrient for the biomass, in the pLesence of oxygen. As above, the ~2~%~i page 16 discharge from the end reactor can be ~iltered, and the discharge from the each preceding reactor will normally be filtered.
Subsequent to sel0nium remoYal, further steps are possible, particularly if other contaminant~ are present. Ion-exchange can be used for a polishing, for instance for boron removal. It is also possible to arcange for boron to be removed in crofi6-flow filtration using suitable membranes.
10 The selenium itsel~ (elemental or compounds thereo) is a useful byproduct of the invention.
Applying the principle of the invention, it i8 also possible to reclaim selenium compounds from organically-complexed mixtures in sludge from treatment 15 plants or fLom reservoirs; specifically in the latter case, this enables mud on the bottom of the reservoir to be purified of selenium, and the selenium itself can be ce-complexed using the invention and recovered as a selenium-rich ~ludge or as selenium compound.
20 The ExamPles The present invention will now be illustrated by reference to some non-limiting Examples, in which reference is made to the accompanying drawings.
Description of the Drawinqs 25 Figure 1 is a schematic diagram of a plant for carrying out a method in accordance with the invention.
Figure 2 is a schematic diagram of a another plant for carrying out a method in accordance with the invention, page 17 where removal of sulphate and boron i6 desired as well as removal of 6elenium.
Referring to Figure 1, selenium-containing water from conduit 1 supplemented with me~hanol-based nutrient from 5 conduit 2 pass through two identical reactor stages 3, 4 (same cross-section and same contents), preferably with no recyling of feed water, and thence through a small ceactor 5, a pump 6 and a cross-flow microfilter 7.
Purified water is discharged through conduit 8 and lOconcentrate for waste disposal is discharged conduit 9, part of which can be returned as active biomas~ through a return line lo to the reactor 5.
The reactor stages 3, 4 aLe fixed film reactors and are filled near -to the -top with approximately 1 inch (2.5 cm) l5gravel (40% void space). The up-flow mode is preferred, as shown. The stages 3, 4 and the reactor 5 are seeded with activated sludge prior to start-up.
The stages 3 and 4 are operated anaerobically or anoxically. The reactor 5 has a sparge tube 11 for the 20addition of air in order to strip o~f surplus methanol supplied in the nutrient. The reactor 5 thus contain6 aerobic activated sludge.
As indicated by the valving, the stage 4 may be by-passed if the selenium content is considered to be 25sufficiently low at the outlet from the stage 3.
Alternatively, the stage 4 may be omitted altogether.
Referring now to Figure 2, like references are used for like parts. Pumps are indicated throughout as plain circles. Effluent is abstracted from a main drain Zl 30and is passed through biological reactor stages 3, 4 in series. These can be fixed film reactors as in Figure 1, oc one or both of them can be a stirred reactor or a page 1~
fluidised bed reactor. The outflow from the stage ~ i6 filtered in a cross-~low microfilter 7. The selenium concentra~e i6 fed through condui~ 9 and the liquid passing through the filter 7 i8 pumped in~o a reactor 5 22. At some point between the ef f luent feed and the inlet to the reactor 22, a carbon dose i6 added as a biomass nutrient. The reactor 2~ operates anaerobicaLly to destroy sulphates and to conver~ heavy metals to insoluble sulphides for collection in a second cross-flow microfilter 23. Sulphates destroyed in the reactor 22 generate hydrogen sulphide gas which i6 passed into a photosynthetic reactor 24, and elemental sulphur is produced. From the microfilter Z3, the heavy metal sulphides are removed through conduit 25 and 15the permeate passes through a collection tank 26 to an ion exchange unit 27 for boron removal. Treated water flows out at pipe 28.
Example 1 A synthetic water, similar in composition to the average 2C for farm drainage waters in the San Joaquin Valley, Cali-fornia, but with added phosphate, was -treated using the plan-t illustrated in Figure 1. In this and -the following Examples, the pll oE the feed water varied, but was always between 7.8 and 8.4 Relevant par-ts of the chemical analy-25 sis for this Example 1 were:
30 mg/1 nitrate (expressed as nitrogen);
0.36 mg/l selenium (as the selenate ion, expressedas selenium):
4000 mg/l sulphate (expressed as sulphate);
20 mg/l phosphate (expressed as phosphorus).
The flow rate was 3 l/hr. The nutrient feed for the biomass was 5% methanol at a flow ra~e of 0.03 i/hr.
For this Example, and Examples Z and 3, the initial ~-z~
page l9 biomass was anaerobically digested sludge taken from the sewage worlcs of the Thames Water Authority at Beddington, England. The reactor stages 3, 4 were operated at ambient tamperature, about 20C. The 5 residence time in each of the reactor stages 3, 4 was about 3.0 hours. Each reactor stage 3, 4 had a voids volume of lo litres.
The outflow was sampled at the exit of each of the reactor stages 3, 4. The liquid was filtered on a laboratory filter of about 5 micron pore size, the filtrate being dissolved or colloidal organic material with selenium and also dissolved inorganic ~elenium.
The amount of dissolved inorganic selenium was determined. Further selenium was either retained in 15the reactor stages 3, 4 with the biomass (not measured) or evolved as gaseous selenium compounds (not measured).
With the flow rates indicated above, which are believed to be close to the optimum flow rates, there was a peciod during which biomass was generated and the 20e~ficiency of the reaction improved. At the end of the period, the relevant contents of the water at the outlet from each reactor stage 3, 4 were (mg/l):
Reactor stage 3 Reactor stage 4 Selenium in filtrate 0.06 o.os 25 inorganic 0.00S o-005 organic complexed 0.055 0.0~5 Held back on filter not measured 0.06 Total Se in outflow not measured O.ll Nitrate (as N) 0.6 0.4 30Sulphate (as S04) 4000 ~000, unchanged The total held back and hence the total selenium in the ~27~25;
page 20 outlet of reactor stage 3 were not measured.
Example 2 Treated water from a ~wo-stage reactor as in Example 1 was filtered through glass-fibre filter paper in order 5 to remove suspende~ particles containing selenium (which in practice could be done on cross-flow filter 7 or by sand filtcation). The water was aerated for an hour with activated sludge fed with glucose. By appropriate vaeiation in the operating conditions, the supernatant 10after settling the sludge contained only 6 ~g Se/l compared with 30 ~g/l dissolved Se in the effluent from the two-stage reactor.
Example 3 One laboratory reactor column was used in the up-flow 15mode, filled half-way with steel wool. The column cross-section was 2000 mm and the volume filled with steel wool was 0.25 litres. The steel wool was a commercially available material. The threads of the wool wece o~ finishing grade 4 or 5, having a diameter 20Of 0.1 to 0.15 mm. The wool was made from a low carbon steel of the rimming variety, not silicon-killed, the chemical composition being stated to be with the limits (~ by weight): C 0.8-1.5: Mn 0.3-0.5: S 0.05 or more; P
0.05 or more 25The steel wool was inserted into the columns so as to ~ill the barrel of the column reasonably uniformly but without undue compaction of the wool. This gives a medium having enough void space to allow water to pass through readily but at the same time did not contain 30large passages which would permit short-circuiting and thus poor contact with the wool sur~aces. The bulk 2~;
page 21 density when in place is 60 * lo kg~m .
A feed of 250 ml/hr was passed through the ves6el (i.e, retention time one hour), ~he feed having the following composition (mg~
Cl 1500 Alkalinity (as CaC03) 180 Nitrate (as N) 30 Phosphate (as P) 4 Bocate (as B) 10 5elenate (as Se) 0.32 70% lactic acid Inutrient) S
Samples of the effluent water were taken over a period of 14 days. Results of analyses are as follows (concentrations in mg/l):
Time after Selenium (as Se)Nitrate start up Inorganic To~al Soluble(a~ N) (days) l 0.22 0.26 9 0.005 0.025 lo 0.006 0,0167.0 (anomalous) 2013 0.004 0.030 14 0.006 0.017 Example 4 Subsurface drainage water at Murietta Farms, Westlands Water District, near Mendota, California, USA, was treated usiny the plant of Figure 2. The biomass wa6 obtained from a local sewage works.
Be:Eore treatment, the water analysis showed lOg ppm N03 (measured as nitrogen; N), 3000-4500 ppm S04, 1800 Cl, ~-z~
page 22 6 ppm B, 0.06 ppm Cr, and 0.35-0.45 mg/l Se, among other contaminants. ~fter treatment, the selenium level was down to 3 to 5 ppb, along with impressive reductions in the level of nitrate, sulpha~e, heavy metals and boron.
A plant was constructed at Murietta Farm6 with three ~eactor stages and a cross-flow microfilter. The design capacity was 40 m /day. Each Leactor had a volume of about 7 m . The first and second reac-tors were filled with stones of diameter 1.5 to 2 inches ~say 3.~
to 5 cm)0 giving 35 % porosity, while steel wool was used to fill the third reactor.
The dcainage water as in Example 4 was fed at 30 l/m and su~plemented with a nutrient comprising concentrated Steffen's waste llqour (a waste liqour from a sugar beet factory). Phosphate was added to the concentrated Steffen's wa6te liquor at the level o~ 2 mg/l, and the waste liquo~ was fed at a rate corresponding to 187 mg carbon per litre of drainage water.
Redox potentials were measured in order to assess the oeerating modes of the three reactors. The drainage water itself typically showed a redox potential in the range -20 to ~20 mV, while the outflow from the first, second and third reactor6 wece respectively in the ranges -100 to -lqO mV, -140 to -175 mV~ and -200 to -300 mV.
The treated water from the third reactor showed less than 1 ppm nitrate and less than 30 p~b selenium. The water fcom the cross-flow microfilter contained less than 15 ppb selenium, and was passed through a resin page 23 exchange column for a final poli6hing, giving an efluent containing less than 10 ppb selenium.
OpeLation wa~ 6ustained for more than 3 months.
Example 6 Fu~ther modification of the plant amployed for Example S
is envisaged, particularly in view of the recent realisation that some of the selenium in the drainage water i~ being converted in the reactors to volatile organic selenium compounds such as dimethyl selenide or dimethyldiselenide. Such compounds represent a useful source oE selenium, and can readily be recovered by appropria-te containment design of the plant. More generally, the aim is to construct a plant capable of treating 1 million US
gallons per day.
Claims (17)
PROPERTY OR PRIVILEGE IS CLAIMED ARE DEFINED AS FOLLOWS:
1. A method of removing dissolved hexavalent selenium from water which contains a higher weight concentration of nitrate than of hexavalent selenium, conprising: lowering the concentration of nitrate in the water to 5 mg/l or below (measured as nitrogen); then treating the water in a reactor containing microbial biomass and a nutrient for the biomass, in the substantial absence of free oxygen, to cause the selenium to be captured as particles larger than the forms of selenium originally present; and passing the discharge from the reactor through a filter in order to filter out particles with captured selenium.
2. The method of claim 1, wherein said water contains a high concentration of sulphate which is substantially greater than the concentration of selenium, and in which the method is operated so that the sulphate concentration is essentially maintained.
3. The method of claim 1, wherein nitrate is initially added to said water, the nitrate concentration subsequently being reduced by microbial mass prior to causing the selenium to be captured by said particles.
4. The method of claim 1, wherein said reactor contains microbial biomass in a non-homogeneous bed in which various differing levels of reducing activity occur.
5. The method of claim 4, wherein said lowering of nitrate concentration is effected using biomass.
6. The method of claim 5, wherein said lowering of nitrate concentration is effected in an anoxic reaction.
7. The method of claim 5, wherein said biomass for lowering of nitrate concentration and said biomass in said reactor are the same biomass.
8. The method of claim 5, wherein said reactor is selected from the group consisting of fluidised bed reactors, sludge-blanket reactors, stirred reactors and fixed bed reactors.
9. The method of claim 5, wherein said biomass in said reactor comprises facultative biomass.
10. The method of claim 1, wherein said reactor comprises at least two stages.
11. The method of claim 1, wherein said hexavalent selenium is converted into a removable form of selenium selected from the group consisting of recoverable volatile organic selenium compounds, recoverable volatile inorganic selenium compounds, elemental selenium, entrainable organically-complexed selenium compounds, entrainable tetravalent selenium compounds, entrainable bivalent selenium compounds, and mixtures thereof.
12. The method of claim 1, wherein said water containing hexavalent selenium contains nitrate in the range from 25 to 250 mg/l (measured as nitrogen, and said step of treating said water in said reactor with said biomass gives water containing 2 mg/l or less nitrate.
13. The method of claim 12, wherein said water containing hexavalent selenium also contains from 500 to 10000 mg/l sulphate.
14. The method of claim 12, wherein said water containing hexavalent selenium contains 0.2 to 0.5 mg/l selenium.
15. The method of claim 14, wherein the step of treating said water in said reactor with said biomass gives water containing selenium at 10% or less of the original concentration.
16. The method of claim 1, wherein the filtered water contains 30 mg/l or less of selenium.
17. A method of removing dissolved selenium from water which contains a higher weight concentration of nitrate than of hexavalent selenium, said method comprising the steps of:
providing a reactor containing microbial biomass capable of converting dissolved selenium to a removable form of selenium; rectifying any nutritional deficiencies in said water to render it nutritionally adequate and capable of sustaining said biomass; treating said nutritionally adequate water with said biomass in said reactor in the substantial absence of free oxygen, said treating step causing said nitrate to be lowered to a level of 5 mg/l or below (measured as nitrogen) and causing said selenium to be converted to at least one removable form, and removing said removable selenium from said water.
providing a reactor containing microbial biomass capable of converting dissolved selenium to a removable form of selenium; rectifying any nutritional deficiencies in said water to render it nutritionally adequate and capable of sustaining said biomass; treating said nutritionally adequate water with said biomass in said reactor in the substantial absence of free oxygen, said treating step causing said nitrate to be lowered to a level of 5 mg/l or below (measured as nitrogen) and causing said selenium to be converted to at least one removable form, and removing said removable selenium from said water.
Applications Claiming Priority (6)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| GB8517531 | 1985-07-11 | ||
| GB858517531A GB8517531D0 (en) | 1985-07-11 | 1985-07-11 | Removing selenium from water |
| GB8601763 | 1986-01-24 | ||
| GB868601763A GB8601763D0 (en) | 1986-01-24 | 1986-01-24 | Removing selenium from water |
| GB868612919A GB8612919D0 (en) | 1986-05-28 | 1986-05-28 | Removing selenium from water |
| GB8612919 | 1986-05-28 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CA1274925A true CA1274925A (en) | 1990-10-02 |
Family
ID=27262731
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CA000513602A Expired - Lifetime CA1274925A (en) | 1985-07-11 | 1986-07-11 | Removing selenium from water |
Country Status (9)
| Country | Link |
|---|---|
| US (1) | US4725357A (en) |
| EP (1) | EP0229145A1 (en) |
| AU (1) | AU590786B2 (en) |
| CA (1) | CA1274925A (en) |
| ES (1) | ES2000340A6 (en) |
| IE (1) | IE58648B1 (en) |
| NZ (1) | NZ216812A (en) |
| PT (1) | PT82969B (en) |
| WO (1) | WO1987000161A1 (en) |
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| US4910010A (en) * | 1987-03-20 | 1990-03-20 | Khalafalla S E | Method for accelerating recovery of selenium from aqueous streams |
| US4861482A (en) * | 1988-08-02 | 1989-08-29 | Frankenberger Jr William | Selenium detoxification |
| US4935146A (en) * | 1988-11-15 | 1990-06-19 | Aluminum Company Of America | Method for removing arsenic or selenium from an aqueous solution containing a substantial background of another contaminant |
| US4940549A (en) * | 1989-01-31 | 1990-07-10 | Santina Water Company | Method for removing toxic metals from agricultural drain water |
| US5733455A (en) * | 1992-07-06 | 1998-03-31 | Polytechnic University | Wastewater treatment process |
| US5651891A (en) * | 1989-08-02 | 1997-07-29 | Polytechnic University | Wastewater treatment process |
| US5128040A (en) * | 1989-08-02 | 1992-07-07 | Polytechnic University | Wastewater treatment process |
| US4971702A (en) * | 1989-08-22 | 1990-11-20 | Western Research Institute | Selenium adsorption process |
| US5271831A (en) * | 1989-10-30 | 1993-12-21 | The United States Of America As Represented By The Secretary Of The Interior | Selenate removal from waste water |
| US5009786A (en) * | 1989-10-30 | 1991-04-23 | The United States Of America As Represented By The Secretary Of The Interior | Selenate removal from waste water |
| EP0470931A3 (en) * | 1990-08-08 | 1992-05-13 | Ciba-Geigy Ag | Soil and waste water treatment |
| DE4027219A1 (en) * | 1990-08-24 | 1992-02-27 | Preussag Noell Wassertech | METHOD AND SYSTEM FOR THE REMOVAL OF HEAVY METALS FROM AQUEOUS MEDIA BY BIOADSORBER |
| US5200082A (en) * | 1991-07-02 | 1993-04-06 | Santina Water Company | Method for removing toxic substances from industrial and agricultural waste water |
| US5366891A (en) * | 1992-03-18 | 1994-11-22 | Associated Universities, Inc. | Biochemical solubilization of toxic salts from residual geothermal brines and waste waters |
| US5264133A (en) * | 1992-10-08 | 1993-11-23 | Shell Oil Company | Removal of selenium from aqueous media |
| US5487834A (en) * | 1993-02-09 | 1996-01-30 | The Regents Of The University Of California | Methods for microbial filtration of fluids |
| US5376262A (en) * | 1993-06-08 | 1994-12-27 | Exxon Research And Engineering Company | Concentration and/disposal of non-volatile inorganic contaminants from refinery waste water streams |
| FR2735037B1 (en) * | 1995-06-07 | 1997-09-19 | Ind De Construction D App Et R | SELECTIVE GAS FILTER FOR QUANTITATIVE AND QUALITATIVE DOSING OF TOXIC GAS |
| US5976376A (en) * | 1995-11-10 | 1999-11-02 | Mitsubishi Jukogyo Kabushiki Kaisha | Sewage treatment process |
| AU1212097A (en) * | 1995-12-29 | 1997-07-28 | Cheil Jedang Corporation | Method and system for the treatment of livestock wastewater |
| JP3445901B2 (en) * | 1996-03-19 | 2003-09-16 | オルガノ株式会社 | Method and apparatus for treating selenium-containing wastewater |
| US5888395A (en) * | 1996-08-30 | 1999-03-30 | The Regents Of The University Of California | Method for enhanced longevity of in situ microbial filter used for bioremediation |
| KR100231950B1 (en) * | 1997-02-28 | 1999-12-01 | 마스다 노부유키 | Sewage treatment process and apparatus |
| US6183644B1 (en) | 1999-02-12 | 2001-02-06 | Weber State University | Method of selenium removal |
| US6383395B1 (en) | 2000-01-04 | 2002-05-07 | Luxfer Group Limited | Water treatment method and apparatus |
| US6444126B1 (en) * | 2000-09-19 | 2002-09-03 | T. M. Gates, Inc. | System and method for treating sanitary wastewater for on-site disposal |
| US7318894B2 (en) * | 2001-08-29 | 2008-01-15 | Graham John Gibson Juby | Method and system for treating wastewater |
| US6855254B1 (en) * | 2003-12-19 | 2005-02-15 | Shalom Recycling Inc. | Magerle metal waste recovery process |
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| US7144362B2 (en) * | 2004-10-29 | 2006-12-05 | Heritage Environmental Servicers, Llc | Method for chemically stabilizing waste materials containing multivalent oxyanions |
| WO2007012181A1 (en) * | 2005-07-25 | 2007-02-01 | Zenon Technology Partnership | Apparatus and method for treating fgd blowdown or similar liquids |
| GB0518508D0 (en) * | 2005-09-10 | 2005-10-19 | Christian Stuart J | Treatment of waste |
| US7378022B2 (en) * | 2006-06-06 | 2008-05-27 | Honeywell International Inc. | System and methods for biological selenium removal from water |
| EP2207873A1 (en) * | 2007-10-08 | 2010-07-21 | Greenwatt | Flushed anaerobic digester with fixed biofilm |
| US7815801B2 (en) | 2007-12-17 | 2010-10-19 | APT Water, Inc. | Removal of selenium in contaminated wastewater streams |
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| US8361431B2 (en) * | 2009-06-29 | 2013-01-29 | Pacific Rare Specialty Metals & Chemicals, Inc. | Process for the recovery of selenium from minerals and/or acidic solutions |
| US8268285B2 (en) * | 2009-06-29 | 2012-09-18 | Pacific Rare Specialty Metals and Chemicals, Inc. | Process for the recovery of tellurium from minerals and/or acidic solutions |
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| US10125040B2 (en) | 2010-09-24 | 2018-11-13 | Evoqua Water Technologies Llc | Concentrating of wastewater to reduce flow rate, cost, and footprint of treatment system |
| CA2819771A1 (en) * | 2010-12-17 | 2012-06-21 | General Electric Company | Biochemical process for selenium recovery from bioremediation effluent or sludge |
| JP5730626B2 (en) * | 2011-03-17 | 2015-06-10 | 一般財団法人電力中央研究所 | Selenium-containing water reduction treatment apparatus and selenium-containing water reduction treatment method |
| US20120241376A1 (en) * | 2011-03-24 | 2012-09-27 | Baldwin Jr Robert Louis | Method of selenium removal from an aqueous source |
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| US20170313608A1 (en) * | 2013-03-14 | 2017-11-02 | Frontier Water Systems, Llc | Fail Safe Flushing BioReactor for Selenium Water Treatment |
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| CH176636A (en) * | 1934-04-28 | 1935-04-30 | Dickmann Heinz | Process for wastewater purification. |
| SE373116B (en) * | 1972-11-27 | 1975-01-27 | P S Delin | |
| NL7702236A (en) * | 1977-03-02 | 1978-09-05 | Rijkslandbouwhogeschool | PROCEDURE FOR THE REMOVAL OF ORGANIC SUBSTANCES AND NITROGEN COMPOUNDS FROM WASTE WATER. |
| JPS5452863A (en) * | 1977-10-03 | 1979-04-25 | Hokkaido Sugar Co | Method of treating steffen waste water |
| US4200523A (en) * | 1978-03-23 | 1980-04-29 | E. I. Du Pont De Nemours And Company | Process for removing sulfate ions from aqueous streams |
| NZ197992A (en) * | 1980-08-18 | 1984-07-31 | Unisearch Ltd | Anaerobic bacterial degradation of organic materials |
| DE3244483A1 (en) * | 1982-12-01 | 1984-06-07 | Linde Ag, 6200 Wiesbaden | METHOD AND DEVICE FOR KEEPING HEAVY METALS AWAY FROM WASTEWATER TREATMENT PLANTS |
| US4519913A (en) * | 1984-06-01 | 1985-05-28 | Kerr-Mcgee Corporation | Process for the removal and recovery of selenium from aqueous solutions |
| US4519912A (en) * | 1984-06-01 | 1985-05-28 | Kerr-Mcgee Corporation | Process for the removal of sulfate and metals from aqueous solutions |
-
1986
- 1986-07-11 EP EP86904289A patent/EP0229145A1/en active Pending
- 1986-07-11 CA CA000513602A patent/CA1274925A/en not_active Expired - Lifetime
- 1986-07-11 NZ NZ21681286A patent/NZ216812A/en unknown
- 1986-07-11 AU AU61397/86A patent/AU590786B2/en not_active Ceased
- 1986-07-11 PT PT8296986A patent/PT82969B/en not_active IP Right Cessation
- 1986-07-11 IE IE186686A patent/IE58648B1/en not_active IP Right Cessation
- 1986-07-11 WO PCT/GB1986/000404 patent/WO1987000161A1/en unknown
- 1986-07-11 ES ES8600268A patent/ES2000340A6/en not_active Expired
- 1986-07-11 US US06/884,390 patent/US4725357A/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| WO1987000161A1 (en) | 1987-01-15 |
| PT82969A (en) | 1986-08-01 |
| IE58648B1 (en) | 1993-11-03 |
| IE861866L (en) | 1987-01-11 |
| PT82969B (en) | 1988-11-30 |
| AU6139786A (en) | 1987-01-30 |
| EP0229145A1 (en) | 1987-07-22 |
| US4725357A (en) | 1988-02-16 |
| NZ216812A (en) | 1989-01-27 |
| ES2000340A6 (en) | 1988-02-16 |
| AU590786B2 (en) | 1989-11-16 |
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