我的英文资料
-
毕业设计
(
论文
)
外文资料翻译
学
院:
自动化工程学院
姓
名:
孟祥光
专
业:
∨
□<
/p>
自动化
学号:
2
□测控技术与仪器
班级:
自动
126
外文出处:
资料
1
:<
/p>
Hydrolysis
Mechanism
of
Fe(
Ⅲ
)Solution
(
用外文写
)
Containing Phosphate
资料
2
:
desalination 275 (2011) 17-25
附
件:
资料
1
:
1.
翻译
译文;
2.
外文原文。
资料<
/p>
2
:
1.
翻译译
文;
2.
外文原文。
指导教师评语:
签名:
2012
年
4
月
6
日
附件
1<
/p>
:外文资料翻译译文
含磷酸根的三价铁盐水解机理的研究
摘
要
:
p>
含有少量磷酸根的三价铁盐的水解过程是相当复杂的
,
它可分为两个阶段
,
即
:<
/p>
成核前的水解机理和成核后的水解机理
.
前一个阶段的水解机理可用逐时络合
比色法进行研究
.
此法把三价铁水解过程中的形态区分为
Fe(a)
、
Fe(b)
和
Fe(c)
三
类
,
它们分别代表了
三价铁盐水解产生的不同聚合度的聚合物
.
后一个阶段的水解<
/p>
机理用磷钼兰法、高倍透射电镜和
XPS
图谱等进行了探索
.
结果表明
,
当含磷酸根的
三价铁盐水解、聚合时
,
由于部分磷酸根可能被包裹于其中
,
因此成核
速率和相转化
速率大大降低
.
关键词
:
磷酸根
;
纺
锤形
α
Fe
2
O
3
粒子
;
水解机理
椭球的赤铁矿颗粒生产高
品位的磁介质是由于其光滑的理想材料,在室内没有
磁极的无孔表面。目前,它们的制备
定量方法包括铁盐溶液的强制水解法和水热合
成法。这两种方法都需要少量的磷酸盐离子
作为生长调节剂。分离
α
Fe
2
o
3
椭球颗粒
强制水
解,没有文献试图说明三价铁的水解过程含有磷酸已找到解决方案。为了了
解水解过程中
,三价铁的变化是有磷酸盐的存在还是不存在,其水解过程中聚合物
与络合离子定时法研
究该三价铁的约束的原因也阐述了。
1.1
材料
分析纯试剂和双蒸馏水进行实验。
测
定了其使用前的铁溶液和磷酸盐的浓度。制备
0.2%
(质量分
数)试剂溶液,
浓
HNO
3
溶液双蒸馏水稀释后的三倍。
氟化钠氯化亚锡溶液制备:
24
克氟化钠溶解在
100 ml
热水;冷却后,加入
2
克氯化亚锡进行;然后混合物过滤。
1.2
铁水解过程中形态分布的测定
三价铁溶液和磷酸溶液分别进行水解反应在沸腾时,将
300<
/p>
毫升加入
500
毫升
瓶,这是由电磁搅拌器加热,和一个
700
毫米全球回流冷
凝器的安装。样品溶液沸
腾时开始。然后,他们在几分钟内采取了一次,直到初始磷应运
而生。采用络合离
子定时分光光度法在分光光度计在波长
600
nm
的样品的吸收率。可以计算出铁
(甲)
、铁(铁)和铁(铁)的含量。
Fe
(
a
)包括游离三价铁离子和单羟基聚合物;
Fe
(
b
)
,过渡传统的低聚
合物种类和
Fe
(
c
< br>)
,数百三价铁聚合物离子。
1.3
测定水解过程中的磷酸盐浓度
上面提到的实验装置也被使用。一旦最初的沉淀出现,第一个
样品立即被带到
α
Fe
2
O
3
椭球粒子完全形成
ED
,
即磷酸盐浓度基本不发生变化。
通用
高速离心机是用
来除去沉淀。沉淀物洗涤多次洗涤溶胶执行加入母液。然后,将母液稀释
到一定体
积。通过对磷钼蓝分光光度法测定该溶液的吸收率在波长为
660
纳米的波长相同的
可测量的程序。
< br>
1.4
实验为后一种机制
<
/p>
为了阐明成核的机制,
高分辨率透射电子显微镜进行了
600
个仪器。
椭球
α<
/p>
Fe
2
O
3
p>
颗粒
XPS
能谱也与
ESCA labmk 2
×
RA
患
者进行
2
结果与讨论
2.1
的水解过程
Fe
(
NO
3
)
3
和
Fe
(
NO
3
)
3
质量体系
当水解
0.097 1 mol/L
的
Fe
(
NO
3
)
3
溶液发生在
100
℃,反应液采样前的初始
沉淀的
0
、
3
、
8
、
15
min
、
20
h
和三价
Fe
浓度
< br>n
,当每个样品混合与溶液定期测量。
三价
Fe
浓度随时间的变化,给出了不同的样本。
2.2
在椭球
α
Fe
2
O
3
颗粒生长的磷的吸附与解吸
磷的吸附与解吸曲线在
0.2
mol/L
的
Fe
(
NO3
)
和
2.4
×
10-3
mol/L<
/p>
,
1.8
×
10
-3
mol/L
磷酸二氢钠混合煮沸回流,分别为水解。
p>
3
结论
(
1
)
Fe
的变化(
a
)
,
Fe
(
b
)和(
p>
c
)铁
Fe
(
p>
NO
3
)
3
的水解过程中溶液中含有磷酸
根离子被络合离子的分光光度法测定复杂
时间。
它被显示磷酸根离子会阻止
Fe
(
NO
3
)
因
为一些磷酸盐离子可能包括在聚合物的三价
Fe
聚集,
三价
Fe
解决
3
溶液的水解。
方案无法转化直到磷离子被羟基取代或改变了结构。其结
果是,水解率降低。
(
2
)可以证明,椭球形颗粒被溶解结晶聚集的条件下,较小的等比个亚基组成聚
集形成。
在椭圆
α
Fe
2
O
3
颗粒表面的一些磷酸
盐离子在椭球粒子的形成时是根据磷的
吸附与解吸曲线,
XPS
谱嗯,椭球
α
Fe
2
O
3
颗粒和高分辨率
TEM
。磷酸根离子在三价
铁的水解过程相当复杂
溶液中含有磷酸。
附件
1
:外
文原文
E
Hydrolysis
Mechanism of Fe(
Ⅲ
)Solution
Containing Phosphate
Abstract:
The hydrolysis
process of Fe(
Ⅲ
)solution is
rather complicated
when
small
amounts
of
phosphate
ions
are
present.
Two
mechanisms
can
be
used
to
describe
the
process,
i.e.,
those
before
nucleation
and
after
nucleation.
The former was
studied by the Ferron complex ion timed
spectrophotometric
method
and
the
aqueous
species
of
Fe(
Ⅲ
)
were
classified
into
three
categories,
which
represent
respectively
different
polymers
during
hydrolysis.
The
latter
was
investigated
by
the
phosphomolybdate
blue
method,
high
resolution TEM and XPS spectrum. It was concluded
that the rate of
nucleation
and
the
rate
of
phase
transformation
were
decreased
because
some
phosphate
ions
were
possibly
included
in
the
polymer
when
the
primary
particles of
α
Fe
p>
2
O
3
hydrolyzed and aggregated.
Key
words:
phosphate;
ellipsoidal
α
Fe2O3particles;
hydrolysis mechanism
Ellipsoidal
hematite
particles
are ideal
materials
to produce high grade
magnetic recording medium due to their
smooth, hole free surface with no
magnetic
pole
in
the
interior.
At
present,
their
preparation
methods
include
the forced
hydrolysis method of ferric salt
solutions
[1
~
3]
and hydrothermal
synthesis
[4]
.
Both
methods
need
little
phosphate
ions
as
a
growth
regulating
gh
the
preparation
of
el
lipsoidal
α
_Fe
2
O
3
particles
with
forced
hydrolysis has been
reported
[5,6]
,no literature
attempting to illustrate the
hydrolysis
process
of
Fe(
Ⅲ
)solutions
containing
phosphate
has
been
found.
In
order
to
understand
the
hydrolysis
process,
the
change
of
Fe(
Ⅲ
)polymers
during the hydrolysis in the presence
or absence of phosphate was studied
with
the
Ferron
complex
ion
timed
spectrophotometric
method
[7]
and
the
reason
for
the
restraint
of
Fe(
Ⅲ
)solutions
hydrolysis
in
the
presence
of
phosphate
was also expounded
in this paper.
1
Materials
and Methods
1.1
Materials
The analytically pure reagents and
doubly distilled water were needed in
the experiment.
The
concentrations of
Fe(
Ⅲ
)solution and that
containing phosphate were
measured
before
their
uses.
The
preparation
of
0.2%(in
mass)Ferron
solution
was the same as
that.
The concentrated
HNO
3
solution was trebly
diluted with doubly distilled
water.
The preparation of NaF
SnCl
2
solution as follows:
24 g NaF were dissolved
in 100 mlhot
water; after cooling, 2 g SnCl
2
were added; then the mixture
was filtered. The solution was only
used on the day.
1.2
Measurement of Morphology Distribution
of Fe(
Ⅲ
)in the Hydrolysis
Process
The solution with
Fe(
Ⅲ
)only and the solution
containing phosphate were
respectively
hydrolyzed
under
boiling
reflux.300
mL
reactant
was
added
into
a
500
mL
three
neck
flask,
which
was
heated
by
electromagnetic
stirrer,
and
a
700 mm global reflux condenser was installed. The
samples were taken at
once
when
the
solutions
tarted
boiling.
Then
they
were
taken
once
in
several
minutes
till
the
initial
precipitates
came
into
being.
The
sample
absorptivity was measured by Ferron
complex ion timed spectrophotometric
method
on
spectrophotometer
at
a
wavelength
of
600
nm. The
contents
of
Fe(a),
Fe(b)and Fe(c)could
be calculated. Fe(a)includes free
Fe(
Ⅲ
)ions and all
monomeric hydroxyl polymer; Fe(b),
transitional low polymeric species and
Fe(c), polymer of several hundreds
Fe(
Ⅲ
)ions.
1
.3
Measurement
of Phosphate Concentration in the Hydrolysis
Process
The experimental
installation mentioned above was also used. As
soon as
the initial precipitates
appeared, the first sample was immediately taken
till
α
Fe
2
O
3
ellipsoidal
particles
were
completely
formed,
i.e.,
the
phosphate
concentration
did
not
change
speed
universal
centrifuges were used to remove the
precipitates. The precipitates were
washed
for
several
times
and
the
washing
solution
was
added
into
the
mother
solution. Then, the
mother solution was diluted to a definite volume.
The
absorptivity of
this
solution
was
measured by
phosphomolybdate blue
method
on the spectrophotometer at a
wavelength of 660 nm with same measurable
procedures
。
1.4
Experiment for the
Latter Mechanism
In
order
to
elucidate
the
mechanism
after
nucleation,
high
resolution
TEM
was performed with an H 600 instrument.
XPS spectrum of ellipsoidal
α
Fe
2
O
3
particles
was
also
performed
with
ESCA
LabMK
2
X
ray
photoelectron
spectroscopy
using MgK
α
radiation.
2
Results and Discussion
2.1
Hydrolysis Process of
Fe(NO
3
)
3
and
Fe(NO
3
)
3
< br>NaH
2
PO
4
System
When
the
hydrolysis
of
0.097
1
mol/L
Fe(NO
3
)
3
solution
took
place
at
100
℃
,
reacting solution
was
sampled
before the emergency
of initial precipitates
at
0, 3, 8, 15 min and 20 h and
Fe(
Ⅲ
)concentration was
measured regularly
as soon as every
sample was mixed with Ferron solution. The changes
of
Fe(
Ⅲ
)concentra
tion with time are given for different samples.
2.2
Phosphate Adsorption and
Desorption in the Growth of Ellipsoidal
α
_Fe
2
O
3
Particles
The
curve
of
phosphate
adsorption
and
desorption
are
given when
0.2
mol/L
-3
-3
Fe(NO
3
)
p>
3
and
2.4
×
10
mol/L,
1.8
×
10
mol/L
NaH
2
PO
4
were mixed with boiling
reflux, respectively, for the
hydrolysis.
3
Conclusions
(1)
The changes of Fe(a), Fe(b) and Fe(c)during the
hydrolysis of
Fe(NO
3
)
3
solutions containing phosphate ions was
measured by the Ferron complex ion
timed spectrophotometric method. It was
shown that phosphate ions might
prevent
the
hydrolysis
of
Fe(NO
3
)
3
solutions.
Because
some
phosphate
ions
were
possibly
included
in
the
polymers
by
Fe(
Ⅲ
)aggregation,
the
Fe(
Ⅲ
)
solutions
could not be
transformed into nuclei until phosphate ions were
replaced by