4种破乳剂在石油树脂沉降水洗生产中的运用

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• 32 .卢建国等4种破乳剂石油树脂沉降水洗生产中的运用研究与开发
4种破乳剂在石油树脂沉降水洗生产中的运用
卢建国,赵洪福
(新疆天利石化控股集团有限公司,新疆克拉玛依833699)
摘要针对石油树脂生产水洗沉降系统经常产生大量碱泥,各沉降水洗罐压差增大,
导致管线堵塞等的问题,考察了4种破乳剂的破乳效果及对废水的影响。结果表明,A
型和D型破乳效果相当,沉降水洗系统的油相中没有W/O乳状液,水相中没有0/W乳
状液。未加破乳剂前的废水,C0D>5g/L、油的质量浓度>40m g/L,碱泥产生量>2
t/d,加入A型或D型破乳剂(加入量0.15~0.550m g/L)后外排污水C O D<1.2g/L、油
的质量农度<30 m g/L,碱泥产生量<1.5 1/d,大大降低了后期的污水处理成本。该方
法指导工业装置生产。
关键词聚偏氟乙烯;悬浮聚合;分散剂;形貌;粒径:
中图分类号 TQ326.8+2 文献标识码 A D O I10.3969/j.issn. 1006-6829.2019.01.009
间戊二烯石油树脂在生产过程中,原料按照一 定的配比进人到聚合反应釜,聚合反应后,经过碱 洗和水洗系统脱出催化剂,然后在经过脱出溶剂和 低聚物即得到间戊二稀石油树脂。碱洗、水洗所用 的催化剂无水三氯化铝被裹在聚合液粗树脂中,这 部分无水三氯化铝无法与碱液中和,悬浮在沉降水 洗系统的中间层,形成大量碱泥,造成沉降水洗系 统内各个沉降水洗罐之间压差增大,常会导致管线 堵塞,沉降水洗系统无法运行,运行周期缩短,一般 3个月就得停工,进行沉降水洗系统管线的疏通。另外,沉降水洗系统水洗后的污水,都存在水包油 (0/W型乳化液),造成外排污水COD大于5 g/L,水 中油的质量浓度大于40 m g/L。基于这些生产问 题,探索通过加人不同的破乳剂来改善和解决碱泥 过多、污水各项指标超标等问题。
1实验部分
1.1破乳剂
破乳剂分为水溶性破乳剂和油溶性破乳剂2大 类[1]。破乳剂属表面活性剂类型,破乳剂分子由亲 油、亲水基团组成,亲油部分为碳氢基团,特别是长 链碳氢基团构成;而亲水部分则由离子或非离子型 的亲水基所构成。在石油树脂生产中,主要加入的 是非离子型水溶性破乳剂。
实验所用4种破乳剂,A型破乳剂主要成分是 乙氧基化丙氧基化聚合物,是亲水基破乳剂,其亲 水基是通过分子中的羟基(_ OH)、醚基(_ 0_ )与 7J C作用形成氢键而达到亲水的目的,进而达到油水 分离的目的[2];B型稠油破乳剂由多种非离子聚醚通 过改性交联复配制得;C型破乳剂主要成分为聚醚; D型破乳剂是一种高效表面活性剂,具有破乳、缓蚀 和阻垢等作用。
1.2实验方法
将不同类型的非离子水溶性破乳剂加人到水 洗沉降系统中。在第1次的碱洗、7jC洗过程中,通 过搅拌器对聚合液进行首次的物理机械破乳,再 通过化学方法,加人非离子型水溶性破乳剂进行二次破乳。
在石油树脂生产工艺参数不变的前提下,聚合 液中破乳剂按质量浓度0.1〜0.6 g/L加人,通过加人 不同种破乳剂和不同的数量,来考察对石油树脂污 水的影响,及评定破乳剂使用的效果。
2结果与讨论
2.1 A型破乳剂
石油树脂生产工艺操作参数不变,聚合液中破 乳剂A加入质量浓度p(A)为0.18、0.36 g/L,实验结果见表1。
收稿日期:2018-12-03;修回日期:2018-12-09
表1破乳剂A加入量对石油树脂水洗污水的影响Tab 1Effect of demulsifier A addition on
petroleum resin washing wastewater
P(破)/ (g'L1)
水性墨水COD/
(m g-L1)
藤蔓根茎
p(油)/
(m g-L1)
w(碱泥)/
(k g'd1)
0.1872923.3  2.7
0.1851517.6  2.5
0.1882021.8  3.2
0.3672623.1  1.5
0.3657020.3  2.0
0.3683420.9  2.5
由表1可知,加人A型破乳剂后石油树脂水洗 污水的COD、油含量大幅降低,与0.36 g/L的用量相 比,0.18 g/L的用量碱泥的变化不大。且2种加人量 对污水中的COD和油含量影响不大。
对沉降水洗系统内的油相和水相取样,进行静 置分层,观察油相中没有W/0乳状液,水相中没有 O/W乳状液,在表面活性剂破乳剂的作用下,油相 中W/O乳状液通过破乳剂在油水界面大量聚集,形 成中间乳化层。
经核算,树脂A型破乳剂单耗0.65 kg/t,成本 34 元/t〇
2.2B型破乳剂
石油树脂生产工艺操作参数不变,聚合液中B 型破乳剂加人质量浓度p(B)为0.18 g/L,实验结果见 表2〇
表2破乳剂B加入量对石油树脂水洗污水的影响
Tab 2 Effect of demulsifier B addition on
petroleum resin washing wastewater
COD/(mg-L')p(油M mg-L-1)w(碱泥y fe.c T1) 78918.31131
138424.2905
132520.51358
由表2可知,B型破乳剂加人后碱泥大量增加, 平均每天产生碱泥1.131 t,l个月产生碱泥33.93 t,操作人员的劳动强度加大,存在人身伤害隐患,后续处理压力大。且碱泥的增加,每月树脂产量减少 301。
对污水的COD和油含量影响不大。试用B型 6个月后停止使用。
对于沉降水洗系统操作,沉降水洗系统污水线 频繁堵塞,造成生产波动;其次,污水收集池,有大 量的油气自污水中溢出,挥发性有机物(VOCs)含 量严重超标。2.3C型破乳剂
石油树脂生产工艺操作参数不变,破乳剂加入 质量浓度P(A)为0.11、0.18 m g/L,实验结果见表3。
表3破乳剂C加入量对石油树脂水洗污水的影响
Tab 3 Effect of demulsifier C addition on
petroleum resin washing wastewater
p(破)/
(g'L1)
COD/
(m g.L1)
p(油)/
(m g-L1)
m(碱泥)/
金银花采摘机(k g'd1)
0.11120623.18
3d蓝光播放器
0.1857020312
0.3870230.123
由表3可知,在使用C型破乳剂后,碱泥数量开 始增加;提高加人量后,碱泥数量依然在增加,说明 C型破乳效果不好。对污水的COD和油含量影响 不大。
对沉降水洗系统内的油相和水相取样,进行静 置分层,观察油相中存在明显的W/0乳状液,水相 中存在明显的O/W乳状液。
馈线卡2.4D型破乳剂
石油树脂生产工艺操作参数不变,破乳剂加入 质量浓度/3(D)为0.540、0.405、0.180外,实验结果见
表4。
表4破乳剂D加入量对石油树脂水洗污水的影响
Tab 4 Effect of demulsifier D addition on
petroleum resin washing wastewater
p(破)/
(g'L')
COD/
(m g.L1)
p(油y
(mg-L-1)
w(碱泥)/
(k g-d.自动泄压阀
0.18040318.45
0.18049322.52
0.40573017.48
0.40548124.45
0.54056321.45
0.540102223.15
0.54033729.75
由表4可知,D型破乳剂加入量增大对石油树 脂污水的COD、油含量影响不大。
对沉降水洗系统内的油相和水相取样,进行静 置分层,观察油相中没有W/0乳状液,水相中没有 0/W乳状液,在表面活性剂破乳剂的作用下,油水 界面没有中间乳化层,说明D型破乳剂破乳速度快,很快能够将聚合液与水分层。
经核算,树脂D型礙關单耗1kg/t,鉢17元/t。
(下转第45页)
水洗样品;在90 T:下在2 m o l/L的H2S04中熟化1h;水洗并干燥样品。
2)评估在70丈下在质量分数30%的H20+质量 分数2〇x1〇_6的Fe2+(FeS04)介质里30 h的抗氧化 性。如果失量不超过5%,则样品通过测试。试验结 束以后,冷却样品到室温,用蒸馏水洗涤,用滤纸干 燥,完全脱除水滴,在1min内称量,精确度达到0.2 m g〇实验结果见表1。
表1氟改性聚合物材料样品的氧化稳定性
Tab 1Oxidation stability of the samples
of polymer materials modified with fluorine
薄膜改性方法
nalg
氧化前
Am/
氧化后%
SM C〇F3(80 T)0.1770.1760.6 ST C〇F3(80 t)0.1450.1440.7 ST未处理0.0880.084  5.1 SM未处理0.0760.072  5.3表2为样品热处理l h的结果。
表2聚合物材料经处理的样品热稳定性
Tab 2 Thermal stability of the treated samples
of p olymer materials
薄膜改性方法
mlg
-表面外观起始H O T:120 T:
SM c〇f3(8〇r.)0.176 0.1760.176没有改变
ST C〇F3(80 ■〇0.147 0.1440.144在120 T;下熔化由表2可知,用高价过渡金属氟化物改性的薄 膜在氧化和高温下是稳定的。
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(上接第33页)
3结论
1)4种破乳剂对石油树脂污水的COD和水中油 影响不大,较不加人破乳剂污水中COD和水中油明 显降低。
2)B型和C型破乳剂破乳效果不好,沉降水洗 系统内的油相中存在明显W/0乳状液,7jC相中存在 明显0/W乳状液;污水收集池,有大量的油气自污 水中溢出;沉降水洗系统形成的碱泥多,污水管线 频繁堵塞,石油树脂转化率降低。
3) A型和D型破乳效果相当。沉降水洗系统的
油相中没有W/0乳状液,水相中没有O/W乳状液,
沉降水洗系统形成的碱泥少。
4) 单从破乳剂单耗上考虑,A型单耗低于D型; 从成本考虑,D型吨树脂成本是A型的一半。
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