{"id":13611,"date":"2018-06-27T11:45:19","date_gmt":"2018-06-27T03:45:19","guid":{"rendered":"https:\/\/research.utm.my\/ipasa\/?page_id=13611"},"modified":"2018-06-27T23:43:29","modified_gmt":"2018-06-27T15:43:29","slug":"struvite-precipitation-for-the-recovery-of-ammonium-nitrogen-from-landfill-leachate","status":"publish","type":"page","link":"https:\/\/research.utm.my\/ipasa\/struvite-precipitation-for-the-recovery-of-ammonium-nitrogen-from-landfill-leachate\/","title":{"rendered":"STRUVITE PRECIPITATION FOR THE RECOVERY OF AMMONIUM NITROGEN FROM LANDFILL LEACHATE"},"content":{"rendered":"<p>[et_pb_section admin_label=&#8221;section&#8221;]<br \/>\n\t\t[et_pb_row admin_label=&#8221;row&#8221;]<br \/>\n\t\t\t[et_pb_column type=&#8221;4_4&#8243;]<br \/>\n\t\t\t\t[et_pb_text admin_label=&#8221;Text&#8221;]<br \/>\n\t\t\t\t\tBy: Mohamad S. Darwish, Azmi Aris, Mohd. Hafiz Puteh<\/p>\n<p>Struvite (MgNH<sub>4<\/sub>PO<sub>4<\/sub>.6H<sub>2<\/sub>O, MAP) precipitation is an effective method to recover ammonium nitrogen (NH<sub>4<\/sub>-N) from wastewater into a valuable and environmental friendly material. It is crystallized by a chemical reaction between NH<sub>4<\/sub>-N, Mg and P, which is affected by several factors, mainly pH, molar ratios, foreign ions and mixing intensity (<em>G<\/em>). Landfill leachate (LL) contains high concentration of NH<sub>4<\/sub>-N that should be treated properly to avoid the environmental pollution problems. Therefore, the aim of this study is to develop a sustainable approach for NH<sub>4<\/sub>-N recovery from municipal LL via MAP precipitation technology. The study investigated a low-cost P source, optimized NH<sub>4<\/sub>-N recovery in terms of pH, Mg:N, K:N and <em>G<\/em>, studied the effect of organic matter and determined the effect and sorption mechanism of cadmium (Cd) and nickel (Ni) during MAP precipitation. Three types of waste bones were tested for low-cost P source; fish, chicken and cow waste bone ash. Fish bone ash contained the highest P content (17% wt.). The P extraction by acidic leaching was optimized by Response Surface Methodology (RSM) and the results showed that applying 2M H<sub>2<\/sub>SO<sub>4<\/sub> and 1.25 kg H<sub>2<\/sub>SO<sub>4<\/sub>\/kg ash resulted with extracting 95% of P. The extracted P solution (150 g-P\/L) was applied successfully in MAP precipitation. Recovery of NH<sub>4<\/sub>-N in synthetic LL was optimized by RSM. Maximum NH<sub>4<\/sub>-N recovery (90%) was achieved at pH 8.5, Mg:N = 1.25, K:N = 0.1 and <em>G<\/em> = 95 s<sup>-1<\/sup>. The effect of organic matter on MAP recovery was determined using synthetic and actual LL (filtered and unfiltered). Propionic, butyric and acetic acids formulated the organic content in synthetic LL, in which an insignificant effect was noticed with minor removal of total organic carbon (TOC) (6.30-13.96%). For actual LL, NH<sub>4<\/sub>-N recovery efficiencies were 93%, 71% and 28% using MgCl<sub>2<\/sub>+Na<sub>2<\/sub>HPO<sub>4<\/sub>, MgO+P solution and MgO+Na<sub>2<\/sub>HPO<sub>4<\/sub>, respectively. It was also found that Cd and Ni were co-precipitated with MAP, forming struvite analogues, which could affect the purity of MAP. Sustainability of NH<sub>4<\/sub>-N recovery has to be further improved to be efficient for large-scale applications of LL treatment.<\/p>\n<p style=\"text-align: center\"><a href=\"https:\/\/research.utm.my\/wp-content\/uploads\/sites\/22\/2018\/06\/SEM.png\"><img loading=\"lazy\" decoding=\"async\" class=\"alignnone size-full wp-image-13613 aligncenter\" src=\"https:\/\/research.utm.my\/wp-content\/uploads\/sites\/22\/2018\/06\/SEM.png\" alt=\"\" width=\"672\" height=\"505\" \/><\/a>SEM images of precipitates after Mg-P mixture<\/p>\n<p style=\"text-align: center\"><a href=\"https:\/\/research.utm.my\/wp-content\/uploads\/sites\/22\/2018\/06\/Struvite.png\"><img loading=\"lazy\" decoding=\"async\" class=\"size-full wp-image-13612\" src=\"https:\/\/research.utm.my\/wp-content\/uploads\/sites\/22\/2018\/06\/Struvite.png\" alt=\"\" width=\"579\" height=\"269\" \/><\/a><\/p>\n<p style=\"text-align: center\"><a name=\"_Toc488535211\"><\/a>Harvested struvite from filtered actual LL sample (left) and synthetic LL (right)<\/p>\n<p>\t\t\t\t[\/et_pb_text]<br \/>\n\t\t\t[\/et_pb_column]<br \/>\n\t\t[\/et_pb_row]<br \/>\n\t[\/et_pb_section]<\/p>\n","protected":false},"excerpt":{"rendered":"<p>By: Mohamad S. Darwish, Azmi Aris, Mohd. Hafiz Puteh Struvite (MgNH4PO4.6H2O, MAP) precipitation is an effective method to recover ammonium nitrogen (NH4-N) from wastewater into a valuable and environmental friendly material. It is crystallized by a chemical reaction between NH4-N, Mg and P, which is affected by several factors, mainly pH, molar ratios, foreign ions [&hellip;]<\/p>\n","protected":false},"author":11240,"featured_media":0,"parent":0,"menu_order":0,"comment_status":"closed","ping_status":"closed","template":"","meta":{"_et_pb_use_builder":"on","_et_pb_old_content":"By: Mohamad S. Darwish, Azmi Aris, Mohd. Hafiz Puteh\r\n\r\nStruvite (MgNH<sub>4<\/sub>PO<sub>4<\/sub>.6H<sub>2<\/sub>O, MAP) precipitation is an effective method to recover ammonium nitrogen (NH<sub>4<\/sub>-N) from wastewater into a valuable and environmental friendly material. It is crystallized by a chemical reaction between NH<sub>4<\/sub>-N, Mg and P, which is affected by several factors, mainly pH, molar ratios, foreign ions and mixing intensity (<em>G<\/em>). Landfill leachate (LL) contains high concentration of NH<sub>4<\/sub>-N that should be treated properly to avoid the environmental pollution problems. Therefore, the aim of this study is to develop a sustainable approach for NH<sub>4<\/sub>-N recovery from municipal LL via MAP precipitation technology. The study investigated a low-cost P source, optimized NH<sub>4<\/sub>-N recovery in terms of pH, Mg:N, K:N and <em>G<\/em>, studied the effect of organic matter and determined the effect and sorption mechanism of cadmium (Cd) and nickel (Ni) during MAP precipitation. Three types of waste bones were tested for low-cost P source; fish, chicken and cow waste bone ash. Fish bone ash contained the highest P content (17% wt.). The P extraction by acidic leaching was optimized by Response Surface Methodology (RSM) and the results showed that applying 2M H<sub>2<\/sub>SO<sub>4<\/sub> and 1.25 kg H<sub>2<\/sub>SO<sub>4<\/sub>\/kg ash resulted with extracting 95% of P. The extracted P solution (150 g-P\/L) was applied successfully in MAP precipitation. Recovery of NH<sub>4<\/sub>-N in synthetic LL was optimized by RSM. Maximum NH<sub>4<\/sub>-N recovery (90%) was achieved at pH 8.5, Mg:N = 1.25, K:N = 0.1 and <em>G<\/em> = 95 s<sup>-1<\/sup>. The effect of organic matter on MAP recovery was determined using synthetic and actual LL (filtered and unfiltered). Propionic, butyric and acetic acids formulated the organic content in synthetic LL, in which an insignificant effect was noticed with minor removal of total organic carbon (TOC) (6.30-13.96%). For actual LL, NH<sub>4<\/sub>-N recovery efficiencies were 93%, 71% and 28% using MgCl<sub>2<\/sub>+Na<sub>2<\/sub>HPO<sub>4<\/sub>, MgO+P solution and MgO+Na<sub>2<\/sub>HPO<sub>4<\/sub>, respectively. It was also found that Cd and Ni were co-precipitated with MAP, forming struvite analogues, which could affect the purity of MAP. Sustainability of NH<sub>4<\/sub>-N recovery has to be further improved to be efficient for large-scale applications of LL treatment.\r\n<p style=\"text-align: center\"><a href=\"https:\/\/research.utm.my\/wp-content\/uploads\/sites\/22\/2018\/06\/SEM.png\"><img class=\"alignnone size-full wp-image-13613 aligncenter\" src=\"https:\/\/research.utm.my\/wp-content\/uploads\/sites\/22\/2018\/06\/SEM.png\" alt=\"\" width=\"672\" height=\"505\" \/><\/a>SEM images of precipitates after Mg-P mixture<\/p>\r\n<p style=\"text-align: center\"><a href=\"https:\/\/research.utm.my\/wp-content\/uploads\/sites\/22\/2018\/06\/Struvite.png\"><img class=\"size-full wp-image-13612\" src=\"https:\/\/research.utm.my\/wp-content\/uploads\/sites\/22\/2018\/06\/Struvite.png\" alt=\"\" width=\"579\" height=\"269\" \/><\/a><\/p>\r\n<p style=\"text-align: center\"><a name=\"_Toc488535211\"><\/a>Harvested struvite from filtered actual LL sample (left) and synthetic LL (right)<\/p>","_et_gb_content_width":"","ngg_post_thumbnail":0,"footnotes":""},"class_list":["post-13611","page","type-page","status-publish","hentry"],"_links":{"self":[{"href":"https:\/\/research.utm.my\/ipasa\/wp-json\/wp\/v2\/pages\/13611","targetHints":{"allow":["GET"]}}],"collection":[{"href":"https:\/\/research.utm.my\/ipasa\/wp-json\/wp\/v2\/pages"}],"about":[{"href":"https:\/\/research.utm.my\/ipasa\/wp-json\/wp\/v2\/types\/page"}],"author":[{"embeddable":true,"href":"https:\/\/research.utm.my\/ipasa\/wp-json\/wp\/v2\/users\/11240"}],"replies":[{"embeddable":true,"href":"https:\/\/research.utm.my\/ipasa\/wp-json\/wp\/v2\/comments?post=13611"}],"version-history":[{"count":0,"href":"https:\/\/research.utm.my\/ipasa\/wp-json\/wp\/v2\/pages\/13611\/revisions"}],"wp:attachment":[{"href":"https:\/\/research.utm.my\/ipasa\/wp-json\/wp\/v2\/media?parent=13611"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}