Legal Aspects and Technical Alternatives for the Treatment of Reservoir Brines at the Activo Luna Oilfield, Mexico
Deep formation water, extracted as an undesired byproduct from on-shore production wells at the Activo Luna oilfield and processed in adjacent oil fields, are highly enriched in salt minerals, especially in sodium chloride (NaCl) (262 000 mg/L), but also in metals and nonmetals, such as strontium (S...
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description | Deep formation water, extracted as an undesired byproduct from on-shore production wells at the Activo Luna oilfield and processed in adjacent oil fields, are highly enriched in salt minerals, especially in sodium chloride (NaCl) (262 000 mg/L), but also in metals and nonmetals, such as strontium (Sr) (2068 mg/L), bromine (Br) (2034 mg/L), boron (B) (396 mg/L), iodine (I) (43.4 mg/L), selenium (Se) (3.74 mg/L), and arsenic (As) (0.55 mg/L). Direct reinjection of the brine underground is not possible because of elevated pressure conditions within the petroleum reservoir. The disposal into near shore areas of the Gulf of Mexico without treatment must be rejected because of a) elevated concentrations of some toxic elements, such as B, silver (Ag), thallium (Tl), Se and cadmium (Cd), which exceed permissible limits of environmental legislation for surface discharge (Official Mexican norms NOM-001-ECOL-1998 and CE-CCA-001/89), and b) differences in density that could cause the descent of hypersaline fluid to the ocean floor, potentially affecting the diversity and survival of the benthic ecosystem. Conventional treatment techniques, such as microfiltration or reverse osmosis, are not suitable for the Activo Luna brines because of their extreme mineralization, which will cause pressure conditions exceeding 200 bars across the membrane. As an alternative process, the evaporation of the entire brine volume of approximately 200${\rm m}^{3}/\text{day}$by solar ponds or industrial crystallization plants is suggested. The residual precipitated residuals are composed mainly of chlorine (Cl) (9460 tons/year), sodium (Na) (4230 tons/year), calcium (Ca) (1028 tons/year), potassium (K) (207 tons/year), and magnesium (Mg) (65.8 tons/year). As an alternative to its disposal on a dumpsite, some special minerals (especially NaCl, Mg, Sr, and Br) could be recovered for its economic value. |
doi_str_mv | 10.2175/106143005X41645 |
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Cid ; Aguilar, J. L. Fong</creator><creatorcontrib>Birkle, Peter ; Vázquez, Adolfo L. Cid ; Aguilar, J. L. Fong</creatorcontrib><description>Deep formation water, extracted as an undesired byproduct from on-shore production wells at the Activo Luna oilfield and processed in adjacent oil fields, are highly enriched in salt minerals, especially in sodium chloride (NaCl) (262 000 mg/L), but also in metals and nonmetals, such as strontium (Sr) (2068 mg/L), bromine (Br) (2034 mg/L), boron (B) (396 mg/L), iodine (I) (43.4 mg/L), selenium (Se) (3.74 mg/L), and arsenic (As) (0.55 mg/L). Direct reinjection of the brine underground is not possible because of elevated pressure conditions within the petroleum reservoir. The disposal into near shore areas of the Gulf of Mexico without treatment must be rejected because of a) elevated concentrations of some toxic elements, such as B, silver (Ag), thallium (Tl), Se and cadmium (Cd), which exceed permissible limits of environmental legislation for surface discharge (Official Mexican norms NOM-001-ECOL-1998 and CE-CCA-001/89), and b) differences in density that could cause the descent of hypersaline fluid to the ocean floor, potentially affecting the diversity and survival of the benthic ecosystem. Conventional treatment techniques, such as microfiltration or reverse osmosis, are not suitable for the Activo Luna brines because of their extreme mineralization, which will cause pressure conditions exceeding 200 bars across the membrane. As an alternative process, the evaporation of the entire brine volume of approximately 200${\rm m}^{3}/\text{day}$by solar ponds or industrial crystallization plants is suggested. The residual precipitated residuals are composed mainly of chlorine (Cl) (9460 tons/year), sodium (Na) (4230 tons/year), calcium (Ca) (1028 tons/year), potassium (K) (207 tons/year), and magnesium (Mg) (65.8 tons/year). As an alternative to its disposal on a dumpsite, some special minerals (especially NaCl, Mg, Sr, and Br) could be recovered for its economic value.</description><identifier>ISSN: 1061-4303</identifier><identifier>EISSN: 1554-7531</identifier><identifier>DOI: 10.2175/106143005X41645</identifier><identifier>PMID: 15765938</identifier><language>eng</language><publisher>Alexandria, VA: Water Environment Federation</publisher><subject>Alternatives ; Animals ; Applied sciences ; Brine ; Brines ; chemical composition ; Chemical Precipitation ; Crystallization ; Ecosystem ; environmental legislation ; Environmental policy ; Evaporation ; Exact sciences and technology ; Filtration ; Industrial wastewaters ; Industry ; Marine ecology ; Mexico ; ocean disposal ; Ocean dumping ; Oceans and Seas ; Oil fields ; Oil pools ; oilfield brine ; Petroleum ; Pollution ; Ponds ; Research Papers ; Reservoirs ; Salts ; Sea water ; Sodium Chloride ; State of Tabasco ; treatment techniques ; Waste Disposal, Fluid - methods ; Wastewaters ; Water - chemistry ; Water Purification - methods ; Water Supply ; Water treatment ; Water treatment and pollution</subject><ispartof>Water environment research, 2005-01, Vol.77 (1), p.68-77</ispartof><rights>Copyright 2005 The Water Environment Federation (WEF)</rights><rights>2005 Water Environment Federation</rights><rights>2005 INIST-CNRS</rights><rights>Copyright Water Environment Federation Jan/Feb 2005</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4508-970f70a493cf0843f63caf5160605477778870db28018c1b594e98a42a801fb83</citedby><cites>FETCH-LOGICAL-c4508-970f70a493cf0843f63caf5160605477778870db28018c1b594e98a42a801fb83</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/25045840$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/25045840$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,780,784,803,1416,27923,27924,45573,45574,58016,58249</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=17092752$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/15765938$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Birkle, Peter</creatorcontrib><creatorcontrib>Vázquez, Adolfo L. Cid</creatorcontrib><creatorcontrib>Aguilar, J. L. Fong</creatorcontrib><title>Legal Aspects and Technical Alternatives for the Treatment of Reservoir Brines at the Activo Luna Oilfield, Mexico</title><title>Water environment research</title><addtitle>Water Environ Res</addtitle><description>Deep formation water, extracted as an undesired byproduct from on-shore production wells at the Activo Luna oilfield and processed in adjacent oil fields, are highly enriched in salt minerals, especially in sodium chloride (NaCl) (262 000 mg/L), but also in metals and nonmetals, such as strontium (Sr) (2068 mg/L), bromine (Br) (2034 mg/L), boron (B) (396 mg/L), iodine (I) (43.4 mg/L), selenium (Se) (3.74 mg/L), and arsenic (As) (0.55 mg/L). Direct reinjection of the brine underground is not possible because of elevated pressure conditions within the petroleum reservoir. The disposal into near shore areas of the Gulf of Mexico without treatment must be rejected because of a) elevated concentrations of some toxic elements, such as B, silver (Ag), thallium (Tl), Se and cadmium (Cd), which exceed permissible limits of environmental legislation for surface discharge (Official Mexican norms NOM-001-ECOL-1998 and CE-CCA-001/89), and b) differences in density that could cause the descent of hypersaline fluid to the ocean floor, potentially affecting the diversity and survival of the benthic ecosystem. Conventional treatment techniques, such as microfiltration or reverse osmosis, are not suitable for the Activo Luna brines because of their extreme mineralization, which will cause pressure conditions exceeding 200 bars across the membrane. As an alternative process, the evaporation of the entire brine volume of approximately 200${\rm m}^{3}/\text{day}$by solar ponds or industrial crystallization plants is suggested. The residual precipitated residuals are composed mainly of chlorine (Cl) (9460 tons/year), sodium (Na) (4230 tons/year), calcium (Ca) (1028 tons/year), potassium (K) (207 tons/year), and magnesium (Mg) (65.8 tons/year). As an alternative to its disposal on a dumpsite, some special minerals (especially NaCl, Mg, Sr, and Br) could be recovered for its economic value.</description><subject>Alternatives</subject><subject>Animals</subject><subject>Applied sciences</subject><subject>Brine</subject><subject>Brines</subject><subject>chemical composition</subject><subject>Chemical Precipitation</subject><subject>Crystallization</subject><subject>Ecosystem</subject><subject>environmental legislation</subject><subject>Environmental policy</subject><subject>Evaporation</subject><subject>Exact sciences and technology</subject><subject>Filtration</subject><subject>Industrial wastewaters</subject><subject>Industry</subject><subject>Marine ecology</subject><subject>Mexico</subject><subject>ocean disposal</subject><subject>Ocean dumping</subject><subject>Oceans and Seas</subject><subject>Oil fields</subject><subject>Oil pools</subject><subject>oilfield brine</subject><subject>Petroleum</subject><subject>Pollution</subject><subject>Ponds</subject><subject>Research Papers</subject><subject>Reservoirs</subject><subject>Salts</subject><subject>Sea water</subject><subject>Sodium Chloride</subject><subject>State of Tabasco</subject><subject>treatment techniques</subject><subject>Waste Disposal, Fluid - methods</subject><subject>Wastewaters</subject><subject>Water - chemistry</subject><subject>Water Purification - methods</subject><subject>Water Supply</subject><subject>Water treatment</subject><subject>Water treatment and pollution</subject><issn>1061-4303</issn><issn>1554-7531</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2005</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNqFkU1vEzEQhi0EoqVw5gSykODE0vHX2nsMVQtIQZWqILitHGdMHW3WwfaW9t_jkIhKveDLWDPPO5-EvGTwgTOtThm0TAoA9UOyVqpH5JgpJRutBHtc_zXa1LA4Is9yXgMwzkE-JUdM6VZ1whyTNMefdqCzvEVXMrXjii7QXY_B7bxDwTTaEm4wUx8TLddIFwlt2eBYaPT0CjOmmxgS_ZjCWClb_kIzV0WRzqfR0ssw-IDD6j39irfBxefkibdDxhcHe0K-XZwvzj4388tPX85m88ZJBabpNHgNVnbCeTBS-FY46xVroQUldX3GaFgtuQFmHFuqTmJnrOS2OvzSiBPybp93m-KvCXPpNyE7HAY7YpxyzzRjQhtewTcPwHWc6txD7vmunGk7VqHTPeRSzDmh77cpbGy66xn0u1v0D25RFa8PaaflBlf3_GH5FXh7AGyu6_bJji7ke05Dx7Xa9Sf33O8w4N3_6vbfz6-gNl1lr_aydS4x_ZNxBVIZCeIPno6nJw</recordid><startdate>200501</startdate><enddate>200501</enddate><creator>Birkle, Peter</creator><creator>Vázquez, Adolfo L. 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Fong</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4508-970f70a493cf0843f63caf5160605477778870db28018c1b594e98a42a801fb83</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2005</creationdate><topic>Alternatives</topic><topic>Animals</topic><topic>Applied sciences</topic><topic>Brine</topic><topic>Brines</topic><topic>chemical composition</topic><topic>Chemical Precipitation</topic><topic>Crystallization</topic><topic>Ecosystem</topic><topic>environmental legislation</topic><topic>Environmental policy</topic><topic>Evaporation</topic><topic>Exact sciences and technology</topic><topic>Filtration</topic><topic>Industrial wastewaters</topic><topic>Industry</topic><topic>Marine ecology</topic><topic>Mexico</topic><topic>ocean disposal</topic><topic>Ocean dumping</topic><topic>Oceans and Seas</topic><topic>Oil fields</topic><topic>Oil pools</topic><topic>oilfield brine</topic><topic>Petroleum</topic><topic>Pollution</topic><topic>Ponds</topic><topic>Research Papers</topic><topic>Reservoirs</topic><topic>Salts</topic><topic>Sea water</topic><topic>Sodium Chloride</topic><topic>State of Tabasco</topic><topic>treatment techniques</topic><topic>Waste Disposal, Fluid - methods</topic><topic>Wastewaters</topic><topic>Water - chemistry</topic><topic>Water Purification - methods</topic><topic>Water Supply</topic><topic>Water treatment</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Birkle, Peter</creatorcontrib><creatorcontrib>Vázquez, Adolfo L. 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Cid</au><au>Aguilar, J. L. Fong</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Legal Aspects and Technical Alternatives for the Treatment of Reservoir Brines at the Activo Luna Oilfield, Mexico</atitle><jtitle>Water environment research</jtitle><addtitle>Water Environ Res</addtitle><date>2005-01</date><risdate>2005</risdate><volume>77</volume><issue>1</issue><spage>68</spage><epage>77</epage><pages>68-77</pages><issn>1061-4303</issn><eissn>1554-7531</eissn><abstract>Deep formation water, extracted as an undesired byproduct from on-shore production wells at the Activo Luna oilfield and processed in adjacent oil fields, are highly enriched in salt minerals, especially in sodium chloride (NaCl) (262 000 mg/L), but also in metals and nonmetals, such as strontium (Sr) (2068 mg/L), bromine (Br) (2034 mg/L), boron (B) (396 mg/L), iodine (I) (43.4 mg/L), selenium (Se) (3.74 mg/L), and arsenic (As) (0.55 mg/L). Direct reinjection of the brine underground is not possible because of elevated pressure conditions within the petroleum reservoir. The disposal into near shore areas of the Gulf of Mexico without treatment must be rejected because of a) elevated concentrations of some toxic elements, such as B, silver (Ag), thallium (Tl), Se and cadmium (Cd), which exceed permissible limits of environmental legislation for surface discharge (Official Mexican norms NOM-001-ECOL-1998 and CE-CCA-001/89), and b) differences in density that could cause the descent of hypersaline fluid to the ocean floor, potentially affecting the diversity and survival of the benthic ecosystem. Conventional treatment techniques, such as microfiltration or reverse osmosis, are not suitable for the Activo Luna brines because of their extreme mineralization, which will cause pressure conditions exceeding 200 bars across the membrane. As an alternative process, the evaporation of the entire brine volume of approximately 200${\rm m}^{3}/\text{day}$by solar ponds or industrial crystallization plants is suggested. The residual precipitated residuals are composed mainly of chlorine (Cl) (9460 tons/year), sodium (Na) (4230 tons/year), calcium (Ca) (1028 tons/year), potassium (K) (207 tons/year), and magnesium (Mg) (65.8 tons/year). As an alternative to its disposal on a dumpsite, some special minerals (especially NaCl, Mg, Sr, and Br) could be recovered for its economic value.</abstract><cop>Alexandria, VA</cop><pub>Water Environment Federation</pub><pmid>15765938</pmid><doi>10.2175/106143005X41645</doi><tpages>10</tpages></addata></record> |
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subjects | Alternatives Animals Applied sciences Brine Brines chemical composition Chemical Precipitation Crystallization Ecosystem environmental legislation Environmental policy Evaporation Exact sciences and technology Filtration Industrial wastewaters Industry Marine ecology Mexico ocean disposal Ocean dumping Oceans and Seas Oil fields Oil pools oilfield brine Petroleum Pollution Ponds Research Papers Reservoirs Salts Sea water Sodium Chloride State of Tabasco treatment techniques Waste Disposal, Fluid - methods Wastewaters Water - chemistry Water Purification - methods Water Supply Water treatment Water treatment and pollution |
title | Legal Aspects and Technical Alternatives for the Treatment of Reservoir Brines at the Activo Luna Oilfield, Mexico |
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