CN104356730B - 一类丁烯酸内酯化合物在制备抗海洋生物污损涂料中的应用 - Google Patents

一类丁烯酸内酯化合物在制备抗海洋生物污损涂料中的应用 Download PDF

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CN104356730B
CN104356730B CN201410583640.XA CN201410583640A CN104356730B CN 104356730 B CN104356730 B CN 104356730B CN 201410583640 A CN201410583640 A CN 201410583640A CN 104356730 B CN104356730 B CN 104356730B
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漆淑华
农旭华
张晓勇
徐新亚
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Abstract

本发明公开了一类丁烯酸内酯在制备抗海洋生物污损涂料中的应用。本发明的butyrol actone V,aspernolide A,butyrolactone IV,aspernolide B,butyrolactone II,4‑(4‑Hydrox yphenyl)‑5‑(4‑hydroxyphenylmethyl)‑2‑hydroxyfurane‑2‑one,5,6‑dihydropenicillic acid,5,6‑dihydro‑6‑hydroxy‑penicillic acid具有抗海洋生物污损活性,能用于制备抗海洋生物污损涂料,如将其单独或组合渗入或扩散于成膜天然树脂,聚乙烯乙酸乙酯共聚物以及其它可水解,可溶或不溶性树脂等聚合物中,制成抗污损涂料,抗污损涂料能释放出足够量的有效成分至表面达到防污作用,并且这些化合物是天然活性成分,而且均不易溶于水,极易溶于氯仿、乙酸乙酯、甲醇等有机溶剂,具有良好的亲油性,因此可单独或组合应用于制备海洋防污剂中,具有良好的应用前景。

Description

一类丁烯酸内酯化合物在制备抗海洋生物污损涂料中的应用
技术领域:
本发明属于生物领域,具体涉及一类丁烯酸内酯化合物在制备抗海洋生物污损涂料中的应用。
背景技术:
在开发海洋、利用海洋的历史进程中,人类一直面临着防除海洋附着生物的问题。海洋污损生物(marine fouling organism)是海洋生物种栖息或附着在船舶和各种水下人工设施上,对人类经济活动产生不利影响的各种动物、植物和微生物的总称。全世界海洋污损生物共4000余种,我国沿海记录614种,其中最主要的类群是藤壶、藻类、水螅、尤介虫(石灰虫)、双壳类和海鞘等。海洋污损生物在船体、水管、渔箱、油井等各种物体表面附着、生长以至形成群落,造成海洋生物污损,严重影响和阻碍了人们对海洋资源的探索与利用。
20世纪70年代以后由于汞、砷等防污剂的禁用,大部分船体的防污一直都基于防污漆释放廉价且持续时间长的有机锡。20世纪80年代,人们发现有机锡在鱼类、贝类体内会积累,导致遗传变异甚至还有可能进入食物链,于是到80年代末,各国纷纷立法,禁用或限用有机锡防污涂料。国际海事组织(IMO)于2001年10月通过了国际协定即控制船体防污中有害防污剂的应用,到2008年全面禁止在防污涂料中使用有机锡。随后在市场占主导地位的防污涂料是低释放率的含铜防污涂料,然而,重金属元素会在海洋中,特别是在海港中大量聚集,导致海藻的大量死亡,影响鲤鱼、虾、蟹及各种软体、背囊动物的胚胎生长,破坏其血细胞,从而破坏其生态平衡,因此也最终将会被禁用。开发无毒防污剂已经成为国际上急需解决的重要课题,这方面的研究突破将具有全球性的影响,同时将会占有全球市场。海洋天然产物防污剂属于无毒防污剂,是海洋生物自身产生的具有防污活性的次级代谢产物,这些天然化合物能很快降解,且不危害海洋生物的生命,有利于保持生态平衡,因此,研制开发海洋天然产物防污剂已成为获得高效无毒防污剂的重要途径之一。
式(1)-式(8)所示的化合物是一类丁烯酸内酯类化合物。其中式(1)所示的化合物,其为butyrolactone V,公开于文献[1].Lin,Ting;Lu,Chunhua;Shen,Yuemao.Secondary metabolites of Aspergillus sp F1,a commensal fungal strainof Trewia nudiflora.Natural Product Research,2009,23(1):77-85;[2].Nagia,Mohamed Ms;El-Metwally,Mohammad Magdy;Shaaban,Mohamed;El-Zalabani,Soheir M;Hanna,Atef G.Four butyrolactones and diverse bioactive secondary metabolitesfromterrestrial Aspergillus flavipes MM2:isolation and structuredetermination.Organic and medicinal chemistry letters,2012,2(1):2-9.[3].Haritakun,Rachada;Rachtawee,Pranee;Chanthaket,Rungtiwa;Boonyuen,Nattawut;Isaka,Masahiko.Butyrolactones from the Fungus Aspergillus terreus BCC4651.Chemical&Pharmaceutical Bulletin,2010,58(11):1545-1548中。式(2)所示的化合物,其为aspernolide A,公开于文献Parvatkar,Rajesh R.;D'Souza,Celina;Tripathi,Ashootosh;Naik,Chandrakant G.Aspernolides A and B,butenolides from a marine-derived fungus Aspergillus terreus,Phytochemistry,2009,70(1):128-132中。式(3)所示的化合物,其为butyrolactone IV,公开于文献Rao,K.V.;Sadhukhan,A.K.;Veerender,M.;Ravikumar,V.;Mohan,E.V.S.;Dhanvantri,S.D.;Sitaramkumar,M.;Babu,J.M.;Vyas,K.;Reddy,G.O.Butyrolactones from Aspergillus terreus.Chemical&Pharmaceutical Bulletin,2000,48(4):559-562中。式(4)所示的化合物,其为aspernolide B,公开于文献Parvatkar,Rajesh R.;D'Souza,Celina;Tripathi,Ashootosh;Naik,Chandrakant G.Aspernolides A and B,butenolides from a marine-derived fungus Aspergillus terreus,Phytochemistry,2009,70(1):128-132中。式(5)所示的化合物,其为butyrolactone II,公开于文献[1].Nitta,K;Fujita,N;Yoshimura,T;Arai,K;Yamamoto,Y.Metabolic Products of Aspergillus terreus.IX.Biosynthesisof Butyrolactone Derivatives isolated from Strains IFO 8835and 4100.Chemical&Pharmaceutical Bulletin,1983,31(5):1528-1533;[2].Rao,K.V.;Sadhukhan,A.K.;Veerender,M.;Ravikumar,V.;Mohan,E.V.S.;Dhanvantri,S.D.;Sitaramkumar,M.;Babu,J.M.;Vyas,K.;Reddy,G.O.Butyrolactones from Aspergillus terreus.Chemical&Pharmaceutical Bulletin,2000,48(4):559-562;[3].Haritakun,Rachada;Rachtawee,Pranee;Chanthaket,Rungtiwa;Boonyuen,Nattawut;Isaka,Masahiko.Butyrolactonesfrom the Fungus Aspergillus terreus BCC 4651.Chemical&PharmaceuticalBulletin,2010,58(11):1545-1548中。式(6)所示的化合物,其为4-(4-Hydroxyphenyl)-5-(4-hydroxyphenylmethyl)-2-hydroxyfurane-2-one,公开于文献Cotelle,P.;Cotelle,N.;Teissier,E;Vezin,H.Synthesis and antioxidant properties of a new lipophilic ascorbic acidanalogue.Bioorganic&Medicinal Chemistry,2003,11(6):1087-1093中。式(7)所示的化合物,其为5,6-dihydropenicillic acid,公开于文献Kimura,Y;Nakahara,S;Fujioka,S.Aspyrone,a nematicidal compound isolated from thefungus,Aspergillus melleus.Bioscience Biotechnology and Biochemistry,1996,60(8):1375-1376中。(8)所示的化合物,其为5,6-dihydro-6-hydroxy-penicillic acid,公开于专利Maruhashi M,Ito M,Hanada K.Penicillin analog.Japan:03-184968,1991-12-08中。
发明内容:
本发明的目的是提供如式(1)-式(8)所示的任一丁烯酸内酯类化合物在制备抗海洋生物污损涂料中的应用。
本发明通过抗海洋大型污损生物藤壶幼虫附着活性测试发现,本发明的式(1)-式(8)所示的丁内酯类化合物butyrolactone V(式1),aspernolide A(式2),butyrolactoneIV(式3),aspernolide B(式4),butyrolactone II(式5),4-(4-Hydroxyphenyl)-5-(4-hydroxyphenylmethyl)-2-hydroxyfurane-2-one(式6),5,6-dihydropenicillic acid(式7),5,6-dihydro-6-hydroxy-penicillic acid(式8)抑制藤壶幼虫附着的EC50值分别为22.13μg/mL,7.37μg/mL,7.37μg/mL,16.07μg/mL,20.27μg/mL,11.32μg/mL,19.29μg/mL,10.08μg/mL;除了式(7)的EC50/LC50值为36外,其它化合物的EC50/LC50值均大于100,具有良好的无毒性的抗海洋生物污损活性。
因此本发明提供式(1)-式(8)所示的任一丁烯酸内酯类化合物在制备抗海洋生物污损涂料中的应用。
优选,式(1)-式(8)所示的任一丁烯酸内酯类化合物在制备抗藤壶幼虫附着涂料中的应用。
优选,式(8)所示的丁烯酸内酯类化合物在制备抗石灰虫、管虫、海鞘和牡蛎附着涂料中的应用。
将本发明丁内酯化合物butyrolactone V(式1),aspernolide A(式2),butyrolactone IV(式3),aspernolide B(式4),butyrolactone II(式5),4-(4-Hydroxyphenyl)-5-(4-hydroxyphenylmethyl)-2-hydroxyfurane-2-one(式6),5,6-dihydropenicillic acid(式7),5,6-dihydro-6-hydroxy-penicillic acid(式8)单独或组合渗入或扩散于成膜天然树脂,聚乙烯乙酸乙酯共聚物以及其它可水解、可溶或不溶性树脂等聚合物中,制成抗污损涂料,抗污损涂料能释放出足够量的有效成分至表面达到防污作用。
本发明的丁烯酸内酯化合物butyrolactone V(式1),aspernolide A(式2),butyrolactone IV(式3),aspernolide B(式4),butyrolactone II(式5),4-(4-Hydroxyphenyl)-5-(4-hydroxyphenylmethyl)-2-hydroxyfurane-2-one(式6),5,6-dihydropenicillic acid(式7),5,6-dihydro-6-hydroxy-penicillic acid(式8)都是从真菌中分离得到的,属于天然活性成分,而且均不易溶于水,极易溶于氯仿、乙酸乙酯、甲醇等有机溶剂,具有良好的亲油性,因此可单独或组合应用于制备海洋防污剂等。
本发明的丁烯酸内酯化合物butyrolactone V(式1),aspernolide A(式2),butyrolactone IV(式3),aspernolide B(式4),butyrolactone II(式5),4-(4-Hydroxyphenyl)-5-(4-hydroxyphenylmethyl)-2-hydroxyfurane-2-one(式6),5,6-dihydropenicillic acid(式7),5,6-dihydro-6-hydroxy-penicillic acid(式8)具有抗海洋生物污损活性,能用于制备抗海洋生物污损药物,如将其单独或组合渗入或扩散于成膜天然树脂,聚乙烯乙酸乙酯共聚物以及其它可水解,可溶或不溶性树脂等聚合物中,制成抗污损涂料,抗污损涂料能释放出足够量的有效成分至表面达到防污作用,并且这些化合物是天然活性成分,而且均不易溶于水,极易溶于氯仿、乙酸乙酯、甲醇等有机溶剂,具有良好的亲油性,因此可单独或组合应用于制备海洋防污剂中,具有良好的应用前景。
附图说明
图1是实施例2的实验结果图。
具体实施方式:
以下实施例是对本发明的进一步说明,而不是对本发明的限制。
实施例1:式(1)-式(8)所示的丁烯酸内酯类化合物的抗海洋大型污损生物藤壶幼虫附着活性测试
活性测试模型是采用目前实验室最常用的海洋污损生物模型之一纹藤壶虫金星幼虫(Barnacles larvae)的附着抑制试验。藤壶成虫以纤细角毛藻(Chaetocerosgracilis Schutt)为食物,在0.22μm过滤海水中将藤壶的无节幼体培养到金星幼体阶段,每毫升2个幼虫,培养温度28℃。用产生的金星阶段幼体进行活性试验。采用24孔聚苯乙烯板测定化合物的抗幼虫附着活性。将化合物butyrolactone V(式1)溶于DMSO,用无菌过滤海水稀释成不同的浓度溶液(60–140μg/mL)作为测试液。每个孔中加入1mL测试液和20±2个成熟的藤壶幼虫,每个浓度设5个重复样,无菌过滤海水做空白对照。将24孔细胞培养板置于30℃培养箱中放置24小时。在显微镜下统计附着的幼虫数,用spss 11.0软件进行统计分析,计算EC50值。
其它单体化合物aspernolide A(式2),butyrolactone IV(式3),aspernolide B(式4),butyrolactone II(式5),4-(4-Hydroxyphenyl)-5-(4-hydroxyphenylmethyl)-2-hydroxyfurane-2-one(式6),5,6-dihydropenicillic acid(式7),5,6-dihydro-6-hydroxy-penicillic acid(式8)参照上述方法进行抗海洋大型污损生物藤壶幼虫附着活性测试。
实验结果显示,式(1)~式(8)所示的丁烯酸内酯类化合物抑制藤壶幼虫附着的EC50值为分别为22.13μg/mL,7.37μg/mL,7.37μg/mL,16.07μg/mL,20.27μg/mL,11.32μg/mL,19.29μg/mL,10.08μg/mL;除了式(7)的EC50/LC50值为36外,其它化合物的EC50/LC50值均大于100,由此说明式(1)~式(8)所示的丁烯酸内酯类化合物具有抗藤壶幼虫附着活性且无毒性,能用于制备抗海洋生物污损涂料中。
实施例2:式(8)所示的丁烯酸内酯类化合物的野外海上挂板活性测试
野外海上挂板试验采用传统的抗污损生物野外海上挂板试验方法。分别将0.2g和0.4g含式(8)所示的丁烯酸内酯类化合物用1mL的甲醇完全溶解,然后与10mL含45%polyurethane的树脂充分混合后平铺于干燥的PVC(10×10×0.3cm)板上,风干后悬挂于深圳大亚湾扇贝养殖海区(东经114°32’59,北纬22°40’37)。把含0.2g式(8)所示的丁烯酸内酯类化合物的PVC作为处理组1,含0.4g式(8)所示的丁烯酸内酯类化合物的PVC作为处理组2。每个处理设三个平行。取1mL甲醇10mL含45%polyurethane的树脂充分混合后涂板作为对照。挂板于第2个月取出,检查污损生物的种类并测量污损生物所占整块PVC板的面积百分比。用SPSS 11.0软件进行统计分析对照板上与处理板上污损生物所占面积百分比大小的差异性(t检验)。
实验结果如图1显示:挂板2个月后,对照板上已经附着了大量的污损生物藤壶、石灰虫、管虫、海鞘和牡蛎等污损生物(污损生物占整块板的面积百分比为87.43),而处理组1(处理1)板上只有少量的藤壶和石灰虫等污损生物(污损生物占整块板的面积百分比为43.41),而处理组2(处理2)板上有更少量的藤壶和石灰虫等污损生物(污损生物占整块板的面积百分比为21.65)。由此说明式(8)所示的丁烯酸内酯类化合物具有抗藤壶、石灰虫、管虫、海鞘和牡蛎等海洋污损生物的附着活性,能用于制备抗海洋污损涂料中。

Claims (3)

1.式(7)-式(8)所示的任一丁烯酸内酯类化合物在制备抗海洋生物污损涂料中的应用;
2.根据权利要求1所述的应用,其特征在于,式(7)-式(8)所示的任一丁烯酸内酯类化合物在制备抗藤壶幼虫附着涂料中的应用。
3.根据权利要求1所述的应用,其特征在于,式(8)所示的丁烯酸内酯类化合物在制备抗石灰虫、管虫、海鞘和牡蛎附着涂料中的应用。
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