阅读说明：本技术 一种氨基功能化纸张、破乳剂及其制备方法和应用 (Amino functionalized paper, demulsifier, and preparation method and application thereof ) 是由 米远祝 叶泛 于 2021-08-24 设计创作，主要内容包括：本发明公开一种氨基功能化纸张、破乳剂及其制备方法和应用。将纸张通过无溶剂策略接枝氨基,即制备得到所述氨基功能化纸张。所述氨基功能化纸张能作为破乳剂在含油废水中的应用,对含油废水乳液进行破乳处理,处理后水相的透光率可以达到89.6％,且除油率可高达99.15％。所述破乳剂具有用量少,破乳温度低、破乳效率高、时间短,无毒副作用,易于降解,对环境污染较小的特点,而且能适用于不同酸碱度和高盐度含油废水乳液,适应性好,具有较好的应用和推广前景。(The invention discloses amino functionalized paper, a demulsifier, a preparation method and application thereof. And (3) grafting amino on the paper by a solvent-free strategy to prepare the amino functionalized paper. The amino functional paper can be used as a demulsifier in the oil-containing wastewater to perform demulsification treatment on the emulsion of the oil-containing wastewater, the light transmittance of the treated water phase can reach 89.6%, and the oil removal rate can reach 99.15%. The demulsifier has the characteristics of small dosage, low demulsification temperature, high demulsification efficiency, short time, no toxic or side effect, easy degradation and less environmental pollution, can be suitable for the oil-containing wastewater emulsions with different pH values and high salinity, has good adaptability and has better application and popularization prospects.)

1. A preparation method of amino-functionalized paper is characterized by comprising the following steps: and grafting amino on the paper by a solvent-free strategy to prepare the amino functionalized paper.

2. The method of claim 1, wherein the step of grafting amino groups onto the paper by a solvent-free strategy comprises the steps of: uniformly dispersing paper into a polyamino compound existing in a liquid phase form, adding sodium nitrite, stirring for 0.5-2h, adding concentrated sulfuric acid, stirring for 0.5-24 h at 40-80 ℃, finally centrifuging, washing to be neutral, and freeze-drying a product.

3. The method for preparing amino-functionalized paper according to claim 2, wherein the paper, the sodium nitrite and the concentrated sulfuric acid are added in a mass ratio of 1: 10-30: 35-60 parts of;

the mass ratio of the polyamino compound to the paper is 20-50: 1.

4. the method of any one of claims 1 to 3, wherein the paper is at least one of office paper, toilet paper, and book paper, and may be discarded after use.

5. A method of making amino-functionalized paper according to any of claims 2 to 3, wherein the paper is subjected to a comminution treatment prior to grafting;

the polyamino compound is at least one of ethylenediamine, propylenediamine, polyethylenepolyamine and polyethyleneimine.

6. Amino-functionalized paper obtained by the method for the preparation of amino-functionalized paper according to any one of claims 1 to 5.

7. Use of the amino functionalized paper of claim 6 as a demulsifier in an emulsion in oily wastewater.

8. The application according to claim 7, characterized in that it comprises the following steps: dispersing the amino functionalized paper in water to obtain a suspension, mixing the suspension with the oily wastewater emulsion at room temperature, and standing for 10-30 min.

9. The use according to claim 8, wherein the mass fraction of the suspension is 0.1 wt% to 0.6 wt%, and the volume ratio of the suspension to the oily wastewater emulsion is 1: 10-20.

10. Use according to claim 9, wherein the suspension has a mass fraction of 0.3 to 0.6 wt%.

Technical Field

The invention belongs to the technical field of oil field demulsifiers, and particularly relates to amino functionalized paper, a demulsifier, and a preparation method and application thereof.

Background

With the continuous improvement of the crude oil exploitation technology, the water content of the crude oil is higher at present, and the crude oil is rich in colloid and asphaltene, so that the demulsification difficulty is greatly increased, and meanwhile, great difficulty is brought to the exploitation, gathering, transportation, processing and the like of the crude oil.

The main reason for the stable existence of crude oil emulsion is that natural surfactant forms a stable protective film at the oil-water interface, so that the liquid drops cannot be aggregated and separated. The key point of the demulsification process is to destroy the protective film of an oil-water interface, and the addition of the demulsifier is a common method for treating the oily wastewater. Common demulsifiers have hydrophilic groups and lipophilic groups, and can migrate to an oil-water interface and replace natural emulsifier molecules on an oil-water interface film, so that the strength of the interface film is reduced. After the protective layer at the oil-water interface is broken, the droplets largely coalesce together and separate from the continuous phase.

Wang et al nano Si0₂Dispersing into a polyether demulsifier TA1031, and forming the nano demulsifier by adopting an in-situ preparation method. When nano SiO₂When the proportion of the modified emulsion and TA1031 is 1:10, the demulsification efficiency is improved by about 20 percent, and the settling time is shortened. Nikkhah et al reported a method of treating a tumor with nano-sized Ti0 under ultrasonic conditions₂The demulsification rate of the particle modified commercial demulsifier is more than 90 percent, and the settling time is also shortened. Liu et al report a magnetic graphene oxide (M-GO) demulsifier which can be reused for 6-7 times and has demulsification efficiency of 99.98%. Xu et al prepared a series of functionalized Fluorinated Graphene (FG) and hydrazine hydrate modified graphene (HFG), and have excellent demulsification performance in acidic, alkaline and oily wastewater with different NaCl concentrations. Wang et al prepared a series of reduced graphene oxides (rGO) that settled for 30 minutes at room temperature to recover 99.97% oil from an oil-in-water emulsion.

Chinese patent CN105384927A discloses an oil-in-water emulsion demulsifier and a preparation method thereof, wherein a cationic polyether demulsifier is mainly prepared from acetic acid, diethylenetriamine, polyepichlorohydrin, dimethylamine and the like. Although these organic demulsifiers are highly effective, the demulsifiers remain after demulsificationTo either the oil or water phase, corresponding environmental concerns arise. Chinese patent CN109705896A discloses a preparation method of a composite demulsifier, which comprises AR type demulsifier, SP type demulsifier and AE type demulsifier, and the demulsifier prepared by the demulsifier composition can effectively demulsify the ternary complex flooding produced fluid containing high-content alkali, surfactant and polymer. Chinese patent CN107474873B discloses a super heavy oil demulsifier, which aims at super heavy oil in Liaohe oil field light oil extraction plant and has the characteristics of high demulsification efficiency, good stability, clean water and clean oil after demulsification, clear oil-water interface and the like. Chinese patent CN109054888A discloses a carbon nano tube/nano SiO₂The composite nano demulsifier can be used for quickly demulsifying stable crude oil emulsion. The demulsifier mainly has the problems of complex preparation process, higher raw material cost, potential toxic action of medicaments and the like.

Therefore, the search for a novel demulsifier with wide source, low cost and excellent performance still faces a great challenge.

Disclosure of Invention

The invention aims to overcome the technical defects, provides an amino functionalized paper, a demulsifier, and a preparation method and application thereof, and solves the technical problems of high raw material cost, narrow source selection range and poor performance of the demulsifier in the prior art.

The purpose of the invention is realized by the following technical scheme:

a method for preparing amino-functionalized paper comprises the following steps: and grafting amino on the paper by a solvent-free strategy to prepare the amino functionalized paper.

Preferably, the paper is at least one of office paper, toilet paper, and book paper, and may be discarded after use.

Preferably, the paper is subjected to a comminution treatment prior to grafting; more preferably, the crushing treatment is carried out until the fineness of the paper is 50-300 meshes.

Preferably, said means for grafting amino groups to paper by a solvent-free strategy comprises the following steps: uniformly dispersing paper into a polyamino compound existing in a liquid phase form, adding sodium nitrite, stirring for 0.5-2h, adding concentrated sulfuric acid, stirring for 0.5-24 h at 40-80 ℃, finally centrifuging, washing to be neutral, and freeze-drying a product.

Preferably, the mass ratio of the paper to the sodium nitrite to the concentrated sulfuric acid is 1: (10-30): (35-60).

Preferably, the mass ratio of the polyamino compound to paper is (20-50): 1.

preferably, the polyamino compound is at least one of ethylenediamine, propylenediamine, polyethylenepolyamine and polyethyleneimine.

The amino functional paper prepared by the preparation method of the amino functional paper.

The amino functionalized paper is used as a demulsifier in the emulsion of oily wastewater.

Preferably, the application comprises the following steps: dispersing the amino functionalized paper in water to obtain a suspension, mixing the suspension with the oily wastewater emulsion at room temperature, and standing for 10-30 min.

After demulsification is finished, most of the amino-functionalized paper absorbs oil, then the oil and the separated oil phase float on water, and a small part of the oil settles in water, so that the separation is simple through long-time settling or centrifugal separation.

Preferably, the mass fraction of the suspension is 0.1 wt% to 0.6 wt%, more preferably 0.3 wt% to 0.6 wt%.

Preferably, the volume ratio of the suspension to the oily wastewater emulsion is 1: (10-20).

Compared with the prior art, the invention has the beneficial effects that:

(1) according to the amino functionalized paper obtained by the solvent-free strategy, the surface of the amino functionalized paper has a large amount of amino groups and excellent interfacial activity, and the amino functionalized paper can rapidly migrate to an oil-water interface and adsorb asphaltene, so that an interfacial film consisting of the asphaltene is damaged, and the occurrence of a demulsification process is promoted.

(2) The invention can adopt the waste paper commonly used in daily office, the paper is rich in cellulose, the inorganic components in the paper are easy to remove, and the content of other lignin and the like is less, thus being more beneficial to modification. The invention can not only make the cellulose react with the asphaltene to demulsify but also promote the demulsification process through electrostatic neutralization by grafting the amino, belongs to waste utilization, is relatively easier in subsequent degradation, is environment-friendly and green, and has better application prospect.

Drawings

FIG. 1 is an infrared spectrum of the amino-functionalized paper of example 1 and the original A4 paper, wherein A4 corresponds to the original A4 paper, A4-NH₂Corresponding amino functionalized papers.

FIG. 2 is a scanning electron micrograph and an elemental surface scan (c) of an amino-functionalized paper sheet (a) and an A4 paper sheet (b) described in example 1.

Detailed Description

In order to make the objects, technical solutions and advantages of the present invention more apparent, the present invention is described in further detail below with reference to the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are merely illustrative of the invention and are not intended to limit the invention.

In the embodiment, the rotating speed of the pulverizer is 25000rpm, the fineness of the pulverizer is 50-300 meshes, and paper is made of common office A4 waste paper. The crude oil used in the examples was derived from a Tarim oil field. The concentrated sulfuric acid described in the examples is commercially available 98 wt% concentrated sulfuric acid.

Example 1

This example provides an amino-functionalized waste paper, which is obtained by:

crushing A4 paper by a crusher, adding 1g of crushed A4 paper into 22.5mL of ethylenediamine, stirring for half an hour to uniformly disperse the paper, adding 23g of sodium nitrite, continuously stirring for half an hour, dropwise adding 21mL of concentrated sulfuric acid, placing a pasty sample at 60 ℃, stirring for 1 hour, centrifugally washing to be neutral after the reaction is finished, and freeze-drying the product.

FIG. 1 is an infrared light spectrum of the amino-functionalized paper prepared in example 1 and the original A4 paperSpectra. As can be seen from fig. 1: after modification, the molecular weight is obviously 3126cm^-1Is in the form of-NH₂The absorption peak of (1).

FIG. 2 is a scanning electron micrograph of the amino-functionalized paper prepared in example 1 (FIG. a), A4 (FIG. b), and an elemental surface micrograph of the amino-functionalized paper (FIG. c). As can be seen from fig. 2: after modification, N element appears on the fiber obviously and the element proportion is 20.58%.

Example 2

This example provides an amino-functionalized waste paper, which is obtained by:

crushing A4 paper by a crusher, adding 1g of crushed A4 paper into 22.5mL of ethylenediamine, stirring for half an hour to uniformly disperse the paper, adding 23g of sodium nitrite, continuously stirring for half an hour, dropwise adding 21mL of concentrated sulfuric acid, placing a pasty sample at 80 ℃, stirring for 1 hour, centrifugally washing to be neutral after the reaction is finished, and freeze-drying the product.

Example 3

This example provides an amino-functionalized waste paper, which is obtained by:

crushing A4 paper by a crusher, adding 1g of crushed A4 paper into 22.5mL of ethylenediamine, stirring for half an hour to uniformly disperse the paper, adding 23g of sodium nitrite, continuously stirring for half an hour, dropwise adding 21mL of concentrated sulfuric acid, placing a pasty sample at 60 ℃, stirring for 10 hours, centrifugally washing to be neutral after the reaction is finished, and freeze-drying the product.

Example 4

This example provides an amino-functionalized waste paper, which is obtained by:

crushing A4 paper by a crusher, adding 1g of crushed A4 paper into 22.5mL of ethylenediamine, stirring for half an hour to uniformly disperse the paper, adding 30g of sodium nitrite, continuously stirring for half an hour, dropwise adding 30mL of concentrated sulfuric acid, placing a pasty sample at 60 ℃, stirring for 1 hour, centrifugally washing to be neutral after the reaction is finished, and freeze-drying the product.

Example 5

This example provides an amino-functionalized waste paper, which is obtained by:

crushing A4 paper by a crusher, adding 1g of crushed A4 paper into 22.5mL of polyethylene polyamine, stirring for half an hour to uniformly disperse the paper, adding 23g of sodium nitrite, continuously stirring for half an hour, dropwise adding 21mL of concentrated sulfuric acid, placing a pasty sample at 60 ℃, stirring for 1 hour, centrifugally washing to be neutral after the reaction is finished, and freeze-drying the product.

Example 6

Based on the amino-functionalized waste paper prepared in example 1 and example 5, the demulsification performance of the waste paper modified by different polyamino monomers in the oily wastewater emulsion is characterized.

Adding 5 weight parts of crude oil into 495 weight parts of deionized water, stirring and mixing, heating to 60 ℃, and stirring at the rotating speed of 11000r/min for 20 minutes to obtain stable oily wastewater emulsion (oil-in-water emulsion).

Adding the amino-functionalized waste paper prepared in the example 1 and the example 5 into water to prepare an amino-functionalized paper suspension with the mass fraction of 0.4%, and respectively recording the obtained samples as experimental groups 1-2;

1 part by volume of the experimental groups 1 to 2 was added to 20 parts by volume of the oily wastewater emulsion, followed by sufficient shaking and mixing, followed by standing at room temperature for 30min, and the light transmittance and oil removal rate were measured, and the results are shown in table 1.

TABLE 1 results of demulsification of experimental groups 1-2

Note: in the table, "amino-functionalized paper (mg/L)" refers to the concentration of amino-functionalized paper in the oily wastewater emulsion.

It can be seen from table 1 that the waste paper modified with different polyamino monomers does not differ much in demulsification performance.

Example 7

Based on the amino-functionalized waste paper prepared in example 1, suspensions with different concentrations are prepared and used for representing the demulsification performance of the amino-functionalized waste paper with different concentrations in the oily wastewater emulsion.

Adding 5 weight parts of crude oil into 495 weight parts of deionized water, stirring and mixing, heating to 60 ℃, and stirring at the rotating speed of 11000r/min for 20 minutes to obtain stable oily wastewater emulsion (oil-in-water emulsion).

Adding different weight parts of the amino-functionalized waste paper prepared in the example 1 into water to prepare amino-functionalized paper suspensions with the mass fractions of 0.6%, 0.5%, 0.4%, 0.3%, 0.2% and 0.1%, and respectively recording the obtained samples as experimental groups 3-8; the blank group is water and the sample is designated as test group 9.

1 part by volume of the experimental groups 3 to 9 was added to 20 parts by volume of the oily wastewater emulsion, followed by sufficient shaking and mixing, followed by standing at room temperature for 30min, and the light transmittance and oil removal rate were measured, and the results are shown in table 2.

Table 2 demulsification results of experimental group 39

Note: in the table, "amino-functionalized paper (mg/L)" refers to the concentration of amino-functionalized paper in the oily wastewater emulsion.

As can be seen from Table 2, the amino functionalized paper provided by the invention has good demulsification performance, and after the amino functionalized paper with the concentration of 200mg/L is settled for 30min at normal temperature, the light transmittance of the oily wastewater emulsion can reach 89.6%, and the oil removal rate is as high as 99.15%.

Example 8

Based on the amino-functionalized paper prepared in example 1, experimental groups 10-14 were sequentially established for characterizing the demulsification performance of the amino-functionalized paper at different pH values.

Adding 5 weight parts of crude oil into 495 weight parts of deionized water, stirring and mixing, adjusting the pH value by adding hydrochloric acid or sodium hydroxide, heating to 60 ℃, and stirring at the rotating speed of 11000r/min for 20 minutes to obtain stable oily wastewater emulsion (oil-in-water emulsion).

Adding the amino-functionalized paper prepared in example 1 into water to prepare amino-functionalized paper suspensions with the mass fractions of 0.4%, wherein the samples are respectively recorded as experimental groups 10-14;

1 part by volume of the amino-functionalized paper suspension is added into 20 parts by volume of oily wastewater emulsions with different pH values, then the mixture is sufficiently oscillated and uniformly mixed, and then the mixture is placed at normal temperature for 30min, and the light transmittance and the oil removal rate of the mixture are measured, and the results are shown in Table 3.

TABLE 3 results of demulsification of the experimental groups 10-14

Group of	pH	Light transmittance%	Oil removal rate%
				Experimental group 10	4	92.3	99.25
Experimental group 11	6	90.3	99.18
				Experimental group 12	7	89.6	99.16
Experimental group 13	8	67.2	98.47
				Experimental group 14	10	14.8	95.84

As can be seen from Table 3: the amino-functionalized waste paper provided by the invention has higher demulsification efficiency under acidic or alkaline conditions.

Example 9

Based on the amino-functionalized paper prepared in example 1, experimental groups 15-20 were sequentially established for characterizing the demulsification performance of the amino-functionalized paper at different salinity.

Adding 5 parts by weight of crude oil into 495 parts by weight of deionized water, stirring and mixing, adjusting salinity by adding sodium chloride, heating to 60 ℃, and stirring for 20 minutes at the rotating speed of 11000r/min to obtain stable oily wastewater emulsion (oil-in-water type emulsion) and obtain samples with different salinity, wherein the samples are respectively recorded as experimental groups 16-20; the blank group was not added with sodium chloride, and the sample was designated as experimental group 15.

The amino-functionalized paper prepared in example 1 was added to water to prepare amino-functionalized waste paper suspensions having a mass fraction of 0.4% each.

1 part by volume of the above amino-functionalized paper suspension was added to 20 parts by volume of each of the experimental groups 15 to 20, followed by sufficient shaking and mixing, followed by standing at room temperature for 30min, and the light transmittance and oil removal rate were measured, and the results are shown in table 4.

TABLE 4 results of demulsification of experimental groups 15-20

Note: the salinity (mg/L) in the table refers to the concentration of salt contained in the oil-containing wastewater emulsion.

As can be seen from Table 4: the amino functionalized paper provided by the invention can have higher demulsification efficiency under the condition of high salinity, which indicates that the demulsifier has high salt resistance.

The amino-functionalized paper provided by the invention is suitable for demulsification of an oil-containing wastewater emulsion, and has the characteristics of simple preparation method, wide raw material source, no pollution, easy degradation (amination is carried out on the basis of cellulose, the cellulose belongs to a product in the nature and can be decomposed by the nature), excellent demulsification performance and the like.

The above-described embodiments of the present invention should not be construed as limiting the scope of the present invention. Any other corresponding changes and modifications made according to the technical idea of the present invention should be included in the protection scope of the claims of the present invention.