Fast Capture of Fluoride by Anion-Exchange Zirconium–Graphene

May 5, 2019 - Fluoride contamination is a severe problem affecting the safety of drinking water around the world. High-rate adsorbent materials are ...
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Interfaces: Adsorption, Reactions, Films, Forces, Measurement Techniques, Charge Transfer, Electrochemistry, Electrocatalysis, Energy Production and Storage

Fast capture of fluoride by anion-exchange zirconium-graphene hybrid adsorbent Jing Zhang, Yueqi Kong, Yang Yang, Nan Chen, Chuanping Feng, Xiaodan Huang, and Chengzhong Yu Langmuir, Just Accepted Manuscript • DOI: 10.1021/acs.langmuir.9b00589 • Publication Date (Web): 05 May 2019 Downloaded from http://pubs.acs.org on May 13, 2019

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Langmuir

Fast capture of fluoride by anion-exchange zirconium-graphene hybrid adsorbent Jing Zhang†,‡, Yueqi Kong‡, Yang Yang‡, Nan Chen†, Chuanping Feng†, and Xiaodan Huang‡*, Chengzhong Yu‡* †. School of Water Resources and Environment, China University of Geosciences (Beijing), Beijing 100083, China ‡. Australian Institute for Bioengineering and Nanotechnology, The University of Queensland, Brisbane QLD 4072, Australia

ABSTRACT Fluoride contamination is a severe problem affecting the drinking water safety around the world. High-rate adsorbent materials

are

particularly

desirable

for

potable

water

defluoridation. Current research on fluoride adsorbent materials is

primarily

capacities.

focused

But

they

on

metal-based

generally

suffer

adsorbents from

slow

with

high

adsorption

kinetics due to the adsorption mechanism of sluggish exchange between coordinated hydroxyl groups and fluoride ions. Designing metal-based adsorbents to mimic the rapid ion exchange behavior of anion-exchange resins is a promising approach to integrate fast adsorption and high capacity for fluoride removal. Herein,

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a

ZrO(OH)1.33Cl0.66-rGO

chloride

ions

was

hybrid

Page 2 of 38

adsorbent

synthesized

with

containing the

exchangeable

assist

of

cation-π

interaction. Unlike most adsorbents requiring high surface area, this composite has a negligible surface area (1.45 m2 g-1), but can

deliver

a

fast

fluoride

capture

performance

(reaching

equilibrium in 5 mins) with high adsorption rate constants of 1.05 min-1 and 0.171 mg·g-1·min-1, around 10 times faster than the best result reported in literature. Besides, ZrO(OH)1.33Cl0.66-rGO can also demonstrate a high fluoride uptake (44.14 mg g-1) and high removal efficiency (94.4 %) in 35 mg L-1 fluoride solution, both among the highest performances for fluoride adsorption.

Introduction Fluoride

contamination

in

groundwater

is

one

of

the

most

serious environmental issues on the worldwide basis.1 Consumption of water containing excess fluoride can cause adverse health effects, such as fluorosis and metabolism disorders.1,2 The World Health Organization recommends a maximum fluoride concentration in drinking water of 1.5 mg L-1.3 Adsorption technology has been extensively

investigated

contaminated

water,

cost.4-6

Metal-based

hydroxides11

and

for

because

of

adsorbents

metal-organic

the its

treatment high

including frameworks

of

fluoride

efficiency metal (MOFs)12

and

low

oxides,7-10 have

been

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Langmuir

developed for water defluoridation due to their high binding affinities towards fluoride. It

has

been

recognized

that

the

mechanism

of

metal-based

fluoride adsorbents is the exchange between fluoride ions and surface hydroxyl groups of the adsorbents.9-12 The hydroxyl groups either

exist

on

metal

hydroxides

surface

or

can

be

formed

through the hydroxylation of metal oxides and MOFs in aqueous environments.13 centres,

They

resulting

consequently

oxide

materials

for

usually

in

retarded

zirconium

fluoride

are

stably

sluggish

dissociation

(ZrO2)

is

water

defluoridation.9,10,16-19

adsorbents

such

as

of

the

most

ZrO2-carbon

to

metal

processes

kinetics13-15.

adsorption one

coordinated

and

For

example,

widely

studied

Zirconium-based composite,9

ZrO2

mesoporous fibers10 and Fe-Zr/Fe-Ca-Zr hybrid oxides17 have been recently

developed

and

delivered

high

adsorption

capacities

(e.g. ZrO2 mesoporous fibers: 297.7 mg g-1 at 300 mg L-1 fluoride solution10). However, they usually required around 50 to 100 mins to

reach

the

equilibrium

adsorption,

owing

to

the

sluggish

fluoride to hydroxyl group exchange mechanism.9,10,16-18 Zhang et al.

recently

composite

reported

adsorbent

with

a a

zirconium-chitosan/graphene combined

adsorption

oxide

mechanism

of

fluoride to hydroxyl exchange and a minor fluoride to chloride ion

exchange

to

accelerate

the

adsorption

process,19

but

it

remains suffering from its intrinsic slow adsorption kinetics

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(45

mins

become

equilibrium a

major

time).

The

impediment

Page 4 of 38

slow to

adsorption develop

process

has

high-throughput

defluoridation systems for either centralized water treatments or point-of-use water filtrations. Other

high

capacity

fluoride

adsorbents,

such

alumina,20

as

layered double hydroxides11,21 and MOFs,12,18 also have the slow adsorption

problem,

due

to

the

same

hydroxyl

group

exchange

mechanism. This problem would grow worse when coping with the real contaminated waters, because the low-concentration fluoride pollutants in them (