climatic change 7 a short geological and environmental

16
213 effect on floods and droughts in Australia', Climatic change, vol. 25, pp. 289–317. Wilby R L, 2005. 'Uncertainty in water resource model parameters used for climate change impact assessment', Hydrological Processes, vol. 19, pp. 3201–3219. Young P, 2003. 'Top-down and data-based mechanistic modelling of rainfall-flow dynamics at the catchment scale', Hydrological Processes, vol. 17, pp. 2195–2217. Young W, Brandis K & Kingsford R, 2006. 'Modelling monthly streamflows in two Australian dryland rivers: matching model complexity to spatial scale and data availability', Journal of Hydrology, vol. 331, pp. 242–256. Zhang L, Dawes W R & Walker G R, 2001. 'Response of mean annual evapotranspiration to vegetation changes a catchment scale', Water Resources Research, vol. 37, pp. 701–708. Zhang L, Walker G R & Fleming M, 2002. 'Surface water balance for recharge estimation', CSIRO publishing, Collingwood, Victoria. 214 7 A short geological and environmental history of the Sydney estuary, Australia Gavin Birch Abstract Sydney is blessed with one of the most beautiful harbours in the world. However, like many large, capital ports world-wide, this environment has been exposed to relentless stress due to a rapidly increasing population density and extensive residential, commercial and industrial expansion. In this chapter, we explain why the coastal zone is such an important environment, especially for the people of Australia, and describe changes to the Sydney estuary as an example of environmental transformation due to anthropogenic pressure. The geologic development of the Sydney estuary is briefly traced, showing how the feature was eroded into the Hawkesbury Sandstone, mainly during low sea levels of the glacial periods. The estuary and its catchment changed soon after Captain Philip landed in Sydney Cove. Early land clearing increased sedimentation in the waterway and rapid industrial growth, located mainly on the waterfront, resulted in increasing contamination of the estuary. At the University of Sydney, a novel collaboration between urban geographers working on changes in historical cadastral records of the city and environmental chemists studying estuarine sediments, have shown that as urbanisation and industrialisation spread through the catchment, so did the level and spatial extent of contamination in the estuary. The area of the estuary has been reduced by 22 per cent over 220 years of almost constant reclamation, resulting in ecological modification and possible additional contamination. The present contaminant status of the waterway is described in the concluding part

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Page 1: Climatic change 7 A short geological and environmental

213

effect on floods and droughts in Australia', Climatic change, vol. 25, pp. 289–317.

Wilby R L, 2005. 'Uncertainty in water resource model parameters used for climate change impact assessment', Hydrological Processes, vol. 19, pp. 3201–3219.

Young P, 2003. 'Top-down and data-based mechanistic modelling of rainfall-flow dynamics at the catchment scale', Hydrological Processes, vol. 17, pp. 2195–2217.

Young W, Brandis K & Kingsford R, 2006. 'Modelling monthly streamflows in two Australian dryland rivers: matching model complexity to spatial scale and data availability', Journal of Hydrology, vol. 331, pp. 242–256.

Zhang L, Dawes W R & Walker G R, 2001. 'Response of mean annual evapotranspiration to vegetation changes a catchment scale', Water Resources Research, vol. 37, pp. 701–708.

Zhang L, Walker G R & Fleming M, 2002. 'Surface water balance for recharge estimation', CSIRO publishing, Collingwood, Victoria.

214

7

A short geological and environmental history of the Sydney estuary, Australia Gavin Birch

Abstract Sydney is blessed with one of the most beautiful harbours in the world. However, like many large, capital ports world-wide, this environment has been exposed to relentless stress due to a rapidly increasing population density and extensive residential, commercial and industrial expansion. In this chapter, we explain why the coastal zone is such an important environment, especially for the people of Australia, and describe changes to the Sydney estuary as an example of environmental transformation due to anthropogenic pressure. The geologic development of the Sydney estuary is briefly traced, showing how the feature was eroded into the Hawkesbury Sandstone, mainly during low sea levels of the glacial periods. The estuary and its catchment changed soon after Captain Philip landed in Sydney Cove. Early land clearing increased sedimentation in the waterway and rapid industrial growth, located mainly on the waterfront, resulted in increasing contamination of the estuary. At the University of Sydney, a novel collaboration between urban geographers working on changes in historical cadastral records of the city and environmental chemists studying estuarine sediments, have shown that as urbanisation and industrialisation spread through the catchment, so did the level and spatial extent of contamination in the estuary. The area of the estuary has been reduced by 22 per cent over 220 years of almost constant reclamation, resulting in ecological modification and possible additional contamination. The present contaminant status of the waterway is described in the concluding part

Page 2: Climatic change 7 A short geological and environmental

21

5

of th

e ch

apte

r an

d a

plea

is m

ade

for

a ne

w e

ffort

for

rem

ediat

ion

and

rest

orat

ion

of th

is ico

nic

envi

ronm

ent.

Intro

duct

ion

Muc

h of

the

cha

ract

er,

and

inde

ed t

he b

eaut

y, of

Syd

ney

can

be

attri

bute

d to

its e

stua

ries.

Four

dee

ply-

incis

ed, f

lood

ed v

alley

s diss

ect t

he

raise

d co

asta

l m

argi

n of

the

reg

ion

prod

ucin

g on

e of

the

lon

gest

co

astli

nes

of a

ny c

apita

l cit

y in

the

wor

ld.

Thes

e be

autif

ul w

ater

way

s ha

ve ‘i

njec

ted’

a m

ariti

me

char

acte

r dee

p in

to th

e he

artla

nd o

f sub

urba

n Sy

dney

and

hav

e pr

ovid

ed a

n ex

tens

ive

shor

eline

alo

ng w

hich

man

y be

autif

ul h

istor

ic ho

mes

tead

s ha

ve b

een

built

. Th

ese

attri

bute

s ha

ve

been

vita

l in

the

deve

lopm

ent o

f Syd

ney

into

one

of t

he m

ost b

eaut

iful

cities

in th

e w

orld

. Th

ese

wat

erw

ays

have

also

pro

vide

d ex

celle

nt h

arbo

urs

for i

nter

natio

nal

trade

an

d th

us

the

city

is at

th

e in

ters

ectio

n of

do

mes

tic

and

inte

rnat

iona

l tra

nspo

rt. B

ecau

se o

f its

loc

ality

, Sy

dney

has

attr

acte

d pe

ople

and

indu

stry

from

man

y fa

r off

lands

. The

pop

ulat

ion

of S

ydne

y ha

s gr

own

rapi

dly

since

the

Sec

ond

Wor

ld W

ar a

nd n

ow e

xcee

ds f

our

mill

ion

– alm

ost

one

quar

ter

of t

he t

otal

popu

latio

n of

Aus

tralia

. The

w

ater

way

s ha

ve p

rovi

ded

easy

acc

ess

for

raw

mat

erial

s an

d ex

port

of

prod

uce

and

have

sup

plied

coo

lant

for

mac

hine

ry, b

ut t

hey

have

also

ac

ted

as a

con

veni

ent

rece

ptac

le fo

r w

aste

. A

ll se

wag

e an

d in

dust

rial

was

te w

as d

ischa

rged

dire

ctly

into

the

est

uarie

s un

til 1

898

whe

n th

ree

majo

r coa

stal

outfa

lls w

ere

cons

truct

ed to

disg

orge

effl

uent

dire

ctly

into

th

e su

rf z

one

offs

hore

from

Syd

ney.

Onl

y in

197

2 w

as d

ischa

rge

into

the

estu

aries

con

trolle

d by

the

Clea

n W

ater

way

s Act

and

, sin

ce 1

990,

sew

age

has

been

disp

erse

d in

to th

e se

a ab

out f

our

kilo

met

res

from

the

coas

t in

appr

oxim

ately

80

met

res o

f wat

er (B

irch

2000

).

Aus

tral

ian

popu

latio

n A

ustra

lia is

a v

ast i

sland

con

tinen

t with

an

area

of a

lmos

t 6 m

illio

n km

2 an

d a

popu

latio

n of

jus

t 21

mill

ion.

Thi

s ex

trem

ely l

ow a

vera

ge

popu

latio

n de

nsity

is

dece

ptiv

e as

vas

t ar

eas

of i

nter

nal

dese

rt an

d bu

shlan

d ar

e vi

rtuall

y un

inha

bite

d an

d ov

er

85

per

cent

of

th

e po

pulat

ion

live

in th

e co

asta

l zon

e (Z

ann

1996

). M

oreo

ver,

Aus

tralia

is

one

of th

e m

ost u

rban

ised

coun

tries

in th

e w

orld

with

67

per c

ent o

f the

21

6

natio

nal p

opul

atio

n liv

ing

in o

ne o

f th

e ei

ght s

tate

and

terr

itory

cap

ital

cities

, all

of

whi

ch,

exce

pt f

or C

anbe

rra,

are

loca

ted

on t

he c

oast

(P

hilli

ps,

et a

l 19

92).

Eve

n th

e ‘co

asta

l zo

ne’,

whi

ch i

s de

fined

as

a se

ctio

n of

land

thr

ee k

ilom

etre

s w

ide

runn

ing

para

llel t

o th

e co

astli

ne,

has

an e

xtre

mely

une

ven

popu

latio

n di

strib

utio

n: 8

2 pe

r ce

nt o

f th

e co

asta

l fr

inge

pop

ulat

ion

live

in j

ust

1170

km

, or

3.9

per

cen

t, of

co

astli

ne w

ith 7

2 pe

r cen

t of c

oast

hav

ing

zero

pop

ulat

ion

(McD

onald

et

al 19

93).

Aus

tral

ian

estu

arie

s Co

asta

l eco

syst

ems

supp

ort

a va

riety

of

vita

l bio

logi

cal,

econ

omic

and

cultu

ral f

unct

ions

; how

ever

, the

se s

yste

ms

are

unde

r co

nsid

erab

le an

d in

crea

sing

stre

ss

due

to

rapi

d ur

ban

and

indu

stria

l de

velo

pmen

t. E

stua

ries,

in p

artic

ular

, ar

e be

ing

thre

aten

ed f

rom

inc

reas

ing

hum

an

inte

rven

tion

due

to c

hang

es in

wat

er c

ircul

atio

n, s

edim

enta

tion,

hab

itat

loss

, de

cline

in

nativ

e sp

ecies

and

con

tam

inat

ion

by h

eavy

met

als,

orga

noch

lorin

e co

mpo

unds

an

d po

lycyc

lic

arom

atic

hydr

ocar

bons

. E

nviro

nmen

tal d

egra

datio

n ap

pear

s to

be

an in

evita

ble

cons

eque

nce

of

urba

nisa

tion

and

indu

stria

lisat

ion.

Port

Jac

kson

Th

e w

ater

way

has

a c

ompl

icate

d ge

olog

ical a

nd h

uman

hist

ory

and

even

th

e na

min

g of

the

est

uary

is

diffi

cult.

Roy

(19

81)

inclu

des

Mid

dle

Har

bour

, Por

t Jac

kson

, and

the

Lane

Cov

e an

d Pa

rram

atta

Riv

ers

in th

e de

finiti

on o

f ‘S

ydne

y H

arbo

ur’,

whe

reas

oth

ers

conf

ine

the

mea

ning

to

the

cent

ral h

arbo

ur a

rea,

inclu

ding

Circ

ular

Qua

y, D

arlin

g H

arbo

ur a

nd

Whi

te,

Roze

lle

and

Blac

kwat

tle

Bays

(M

cLou

ghlin

20

00).

‘Syd

ney

estu

ary’

will

be

used

in

the

pres

ent

text

to

inclu

de a

ll of

the

abo

ve

loca

tions

, inc

ludi

ng D

uck

Rive

r, an

d tri

buta

ries

up t

o th

e fr

esh

wat

er

limit

and

to th

e w

eirs o

n th

e D

uck

and

Parr

amat

ta R

iver

s. Po

rt Ja

ckso

n is

one

of 8

0 re

cogn

ised

harb

ours

and

970

est

uarie

s on

the

Aus

tralia

n se

aboa

rd (N

LWA

200

2). T

he e

stua

ry is

app

roxi

mat

ely 3

0 km

lo

ng,

2 km

wid

e an

d oc

cupi

es a

bout

50

km2 ,

whe

reas

the

tot

al

catc

hmen

t is

abou

t ten

tim

es th

e su

rfac

e ar

ea o

f th

e es

tuar

y (5

00 k

m2 ).

E

ight

y-six

per

cen

t of

the

Port

Jack

son

catc

hmen

t is

urba

nise

d an

d/or

in

dust

rialis

ed.

Sens

itivi

ty

to

envi

ronm

enta

l ha

rm

is gi

ven

by

the

Page 3: Climatic change 7 A short geological and environmental

21

7

relat

ions

hip

betw

een

the

area

of

the

estu

ary

and

that

of

the

catc

hmen

t. Th

e Sy

dney

est

uary

sho

uld

have

a l

ow s

ensit

ivity

to

anth

ropo

geni

c ef

fect

, ho

wev

er t

hat

is ov

erw

helm

ed b

y th

e hu

ge p

ropo

rtion

of

the

catc

hmen

t th

at i

s ur

bani

sed

(86%

), as

will

be

seen

in

the

follo

win

g di

scou

rse.

The

cent

ral

east

coa

st o

f A

ustra

lia i

s m

icro-

tidal

and

Port

Jack

son

expe

rienc

es a

max

imum

2.1

met

re t

idal

rang

e. Fl

ushi

ng t

imes

incr

ease

fr

om th

ree

to se

ven

days

in th

e lo

wer

har

bour

to se

ven

to te

n da

ys in

the

uppe

r es

tuar

y. W

ith s

uch

a sm

all c

atch

men

t, on

ly a

small

qua

ntity

of

fres

h w

ater

ent

ers t

he e

stua

ry u

nder

nor

mal

cond

ition

s and

Por

t Jac

kson

is

almos

t co

mpl

etely

sa

line.

How

ever

, du

ring

heav

y ra

infa

ll,

large

vo

lum

es o

f fr

esh

wat

er a

re d

elive

red

to t

he e

stua

ry q

uick

ly du

e to

the

sh

ort

lengt

h of

riv

ers.

At

thes

e tim

es,

wat

er i

n th

e ha

rbou

r be

com

es

stra

tified

with

a o

ne t

o tw

o m

etre

thi

ck la

yer

of t

urbi

d, b

uoya

nt, f

resh

w

ater

at

the

surf

ace

and

salty

wat

er b

elow

. The

se c

ondi

tions

for

low

- an

d hi

gh-ra

infa

ll pe

riods

are

unu

sual

for

estu

aries

, whi

ch a

re t

ypica

lly

mor

e m

ixed

with

fres

h an

d sa

line

wat

er.

Geo

logi

cal h

istor

y

Perm

o-Tr

iass

ic e

ra

Port

Jack

son

is lo

cate

d in

the

Sydn

ey B

asin

whi

ch is

Per

mian

to T

riass

ic

age

(300

–220

mill

ion

year

s).

The

mos

t di

stin

ctiv

e fe

atur

e of

the

Por

t Ja

ckso

n ca

tchm

ent

is th

e be

autif

ul o

utcr

ops

of H

awke

sbur

y Sa

ndst

one

into

whi

ch t

he e

stua

ry is

diss

ecte

d. M

ost

of t

he h

igh

land

in t

he o

uter

ca

tchm

ent

is co

mpr

ised

of

Ash

field

Sh

ale

whi

ch

over

lies

the

Haw

kesb

ury

Sand

ston

e. Th

e co

nfig

urat

ion

of P

ort

Jack

son

drain

age

syst

em,

the

orien

tatio

n of

bay

s an

d sh

oreli

ne a

re a

ll co

ntro

lled

by

unde

rlyin

g ge

olog

ical s

truct

ures

. Th

e Sy

dney

est

uary

is a

dro

wne

d riv

er v

alley

, whi

ch is

ero

ded

up to

85

met

res

into

the

Haw

kesb

ury

Sand

ston

e. H

owev

er,

the

orig

in a

nd

evol

utio

n of

suc

h a

large

riv

er v

alley

com

pare

d to

its

small

cat

chm

ent

area

has

alw

ays

been

diff

icult

to e

xplai

n. P

ossib

ly th

e Pa

rram

atta

Riv

er

was

onc

e co

nsid

erab

ly lar

ger t

han

it is

toda

y an

d ex

tend

ed w

estw

ards

to

be c

onne

cted

to th

e N

epea

n Ri

ver.

Perh

aps

the

Nep

ean

Rive

r w

as la

ter

21

8

‘capt

ured

’ by

the

Haw

kesb

ury

Rive

r le

avin

g th

e Pa

rram

atta

Ri

ver

cons

ider

ably

redu

ced

in s

ize

(Liu

198

9).

This

hist

ory

may

exp

lain

the

unus

ually

de

ep

eros

ion

asso

ciat

ed

with

w

hat

is cu

rren

tly

a sm

all

catc

hmen

t. Th

e an

cient

riv

er, w

hich

is n

ow P

ort J

acks

on, w

as a

n ol

d, m

atur

e riv

er

that

mea

nder

ed a

cros

s a

flat p

lain

80 m

illio

n ye

ars

ago.

Dur

ing

perio

ds

of u

plift

, the

riv

er e

rode

d do

wn

into

the

eleva

ted

coas

tal p

lain

form

ing

stee

p-sid

ed b

anks

and

at

times

cut

thr

ough

som

e of

the

mea

nder

s. D

urin

g in

terg

lacial

per

iods

, se

a lev

el ris

es a

nd t

he ‘

river

’ is

flood

ed,

leavi

ng t

he b

reac

hed

mea

nder

s as

islan

ds, o

f w

hich

the

re a

re 1

4 un

der

pres

ent s

ea le

vel c

ondi

tions

. The

gre

at d

epth

to b

edro

ck in

Por

t Jac

kson

is

attri

bute

d to

the

incis

ion

by th

e re

juve

nate

d pa

leo-P

ort J

acks

on st

ream

as

socia

ted

with

upl

ift d

urin

g an

d re

lated

to s

ea fl

oor s

prea

ding

whe

n th

e A

ustra

lian

plat

e m

oved

aw

ay fr

om th

e Lo

rd H

owe

Rise

Plat

e (L

iu 1

989)

. Se

dim

ent,

whi

ch a

ccum

ulat

ed i

n th

e va

lley

bed

durin

g hi

gh s

ea l

evel

st

ands

, w

as r

epea

tedl

y er

oded

and

flu

shed

fro

m t

he f

loor

of

Port

Jack

son

valle

y du

ring

sea

level

low

s. Th

e pr

esen

t-day

abs

ence

of

sedi

men

t in

dep

ress

ion

in t

he P

ort

Jack

son

chan

nel

is m

ainta

ined

by

high

wat

er v

elocit

ies a

nd s

cour

ing

by tu

rbul

ent c

urre

nts

mov

ing

arou

nd

head

lands

pro

trudi

ng in

to th

e es

tuar

y.

Qua

tern

ary

perio

d O

scill

atio

ns o

f sea

leve

l fro

m 5

m a

bove

to 1

20 m

belo

w th

e pr

esen

t day

po

sitio

n oc

curr

ed e

very

100

,000

to 1

50,0

00 y

ears

dur

ing

the

Qua

tern

ary

due

to

glob

al cli

mat

e ch

ange

an

d by

gl

aciat

ion.

Th

e pe

nulti

mat

e gl

aciat

ion

ende

d ab

out 1

35,0

00 y

ears

ago

with

the

succ

eedi

ng in

terg

lacial

ex

tend

ing

to a

bout

80,

000

year

s be

fore

the

pre

sent

. Se

dim

ents

whi

ch

accu

mul

ated

in e

stua

ries

in t

his

regi

on d

urin

g in

terg

lacial

s w

ere

erod

ed

durin

g in

terv

enin

g gl

acial

per

iods

. How

ever

, for

the

majo

rity

of th

e las

t 13

5,00

0 ye

ars,

sea

level

was

20

to 7

0 m

belo

w th

e pr

esen

t and

ther

efor

e er

osio

n of

est

uarie

s w

as m

ore

pron

ounc

ed t

han

depo

sitio

n du

ring

this

perio

d (R

oy 1

998)

.

Page 4: Climatic change 7 A short geological and environmental

21

9

Hol

ocen

e ep

och

The

wor

ld st

arte

d to

com

e ou

t of t

he g

rip o

f the

last

glac

ial p

erio

d ab

out

17,0

00 y

ears

ago

and

sea

lev

el st

arte

d to

rise

qui

ckly

(Tho

m &

Roy

19

85).

At t

his

time

the

coas

t was

abo

ut 2

5 to

30

km e

ast o

f its

pre

sent

po

sitio

n, b

ut, w

ith a

slo

pe o

f co

nsid

erab

ly le

ss t

han

one

degr

ee, s

mall

in

crea

ses

in s

ea l

evel

adva

nced

the

coa

stlin

e th

ousa

nds

of m

etre

s. By

10

,000

yea

rs b

efor

e th

e pr

esen

t, se

a lev

el ha

d ris

en to

25

met

res

belo

w

toda

y’s s

ea l

evel

and

only

3–5

km o

ff th

e pr

esen

t co

astli

ne.

The

sea

reac

hed

its p

rese

nt p

ositi

on a

bout

600

0 ye

ars a

go (R

oy e

t al 1

997)

. Si

nce

the

Aus

tralia

n A

borig

ines

hav

e in

habi

ted

the

cont

inen

t fo

r m

ore

than

40,

000

year

s, th

ey w

ould

hav

e ex

perie

nced

thi

s ra

pid

chan

ge i

n cli

mat

e an

d ra

pidl

y ad

vanc

ing

coas

tline

. It i

s ha

rd to

visu

alise

how

they

co

ped

with

suc

h a

rapi

dly

fluct

uatin

g co

astli

ne w

hich

wou

ld h

ave

been

hi

ghly

unst

able

even

ove

r de

cada

l per

iods

. As

the

sea

adva

nced

acr

oss

the

cont

inen

tal s

helf,

it p

roba

bly

‘swep

t’ ah

ead

of it

larg

e qu

antit

ies o

f sa

nd t

hat

had

accu

mul

ated

on

the

shel

f fr

om r

iver

s w

hich

disg

orge

d se

dim

ent a

s th

e riv

ers

flatte

ned

out a

nd lo

st th

eir e

nerg

y. Th

is sa

nd w

as

push

ed i

nto

emba

ymen

ts a

nd n

ow f

orm

the

bea

utifu

l go

lden

san

ds

whi

ch o

ccup

y th

e m

any

beac

hes

along

the

east

coa

st o

f Aus

tralia

. Som

e of

thi

s sa

nd w

as t

rans

porte

d by

wav

e en

ergy

into

the

mou

th o

f Po

rt Ja

ckso

n as

a t

idal

delta

. Mea

nwhi

le, a

s th

e se

a ad

vanc

ed in

to t

he n

ow

drow

ned

river

vall

ey,

sedi

men

t tra

nspo

rted

by r

iver

s st

arte

d to

be

depo

sited

in th

e up

per p

arts

of t

he e

stua

ry a

s a fl

uvial

delt

a. Fi

ne-g

rain

ed

sedi

men

ts, c

arrie

d m

ostly

in su

spen

sion

afte

r flo

ods,

are

depo

sited

in th

e m

iddl

e of

the

estu

ary

betw

een

the

tidal

and

fluvi

al de

ltas.

The

pres

ent-d

ay e

stua

ry c

ompr

ises

five

sedi

men

tolo

gica

l uni

ts. S

hallo

w

off-c

hann

el em

baym

ents

of

the

cent

ral

harb

our

are

cove

red

in t

hick

m

ud,

as i

s th

e 30

-met

re d

eep

basin

in

Mid

dle

Har

bour

. Th

e m

ain

chan

nel o

f th

e up

per

harb

our

is m

oder

atel

y de

ep, a

nd a

lso m

antle

d in

m

ainly

mud

dy s

and,

but

in

the

cent

ral

harb

our,

the

main

cha

nnel

is de

eply

scou

red.

Th

e sa

nd

cont

ent

of

botto

m

sedi

men

t in

crea

ses

grad

ually

dow

nstre

am a

nd th

e m

ain p

art o

f th

e lo

wer

har

bour

sea

war

d of

the

Sydn

ey H

arbo

ur B

ridge

is m

antle

d in

sand

y se

dim

ent.

22

0 Env

ironm

enta

l hist

ory

Early

Eur

opea

n oc

cupa

tion

1788

–180

0 A

lthou

gh th

e A

borig

ines

had

occ

upied

the

Port

Jack

son

estu

ary

area

for

ten

thou

sand

s of

yea

rs,

evid

ence

of

their

pre

senc

e is

hard

to

find.

H

owev

er, a

fter

the

arriv

al of

the

Eur

opea

ns in

178

8, t

he e

nviro

nmen

t ch

ange

d ra

pidl

y. So

on a

fter

settl

emen

t th

e E

urop

eans

em

bark

ed o

n ex

tens

ive

land

clear

ing,

but

bec

ause

of

the

poor

soi

ls ar

ound

Por

t Ja

ckso

n,

culti

vatio

n so

on

mov

ed

wes

twar

ds

to

the

Nep

ean

and

Haw

kesb

ury

Rive

rs. C

learin

g an

d po

or la

nd p

ract

ices

prom

oted

ero

sion,

an

d se

dim

enta

tion

rate

s in

crea

sed

mor

e th

an t

en t

imes

pre

-Eur

opea

n lev

els in

the

estu

ary.

The

Firs

t Flee

t, w

hich

had

dep

arte

d Po

rtsm

outh

on

13 M

ay 1

787,

land

ed

in B

otan

y Ba

y un

der t

he c

omm

and

of C

apta

in A

rthur

Phi

llip

betw

een

18

and

20 Ja

nuar

y 17

88. C

apta

in P

hilli

p qu

ickly

reali

sed

that

the

land

in th

e Bo

tany

Bay

are

a w

as n

ot fe

rtile

enou

gh to

supp

ort t

he 1

000-

stro

ng p

arty

of

the

Firs

t Fl

eet

and

decid

ed t

o m

ove

to P

ort

Jack

son

– “t

he f

ines

t ha

rbou

r in

the

wor

ld”.

On

26 Ja

nuar

y 17

88 C

apta

in P

hilli

p lai

d an

chor

in

a w

onde

rful

cov

e w

ith “

sprin

g w

ater

” w

hich

he

calle

d Sy

dney

Cov

e. Th

e ne

xt d

ay C

apta

in P

hilli

p es

tabl

ished

the

colo

ny a

nd to

ok p

osse

ssio

n of

N

ew S

outh

Wale

s, w

hile

the

conv

icts

bega

n cu

tting

dow

n tre

es.

The

Seco

nd a

nd T

hird

Fle

ets

arriv

ed i

n Ju

ne 1

790

and

July

–Aug

ust

1791

re

spec

tively

and

the

colo

ny s

prea

d ra

pidl

y. M

ore

ferti

le lan

d to

the

wes

t ar

ound

Par

ram

atta

and

fur

ther

aw

ay i

n th

e H

awke

sbur

y an

d N

epea

n Ri

vers

was

cul

tivat

ed a

nd se

ttled

(McL

ough

lin 2

000)

.

Indu

stria

lisat

ion

and

urba

niza

tion

1800

–185

4 In

dust

ries

bega

n to

tak

e sh

ape

on t

he b

anks

of

Dar

ling

Har

bour

in

abou

t 180

0 an

d so

on s

prea

d to

nea

rby

Cock

le, R

ozell

e an

d Bl

ackw

attle

Ba

ys c

lose

to

the

pres

ent-d

ay S

ydne

y ce

ntra

l bu

sines

s di

stric

t (C

BD).

Met

al fo

undr

ies w

ere

the

first

to b

e es

tabl

ished

and

the

num

ber o

f the

se

indu

strie

s in

crea

sed

from

thr

ee t

o 14

bet

wee

n 18

31 a

nd 1

851

(Tay

lor,

Birc

h &

Lin

ks 2

004;

Wals

h 19

63).

Tann

erie

s sta

rted

oper

atio

n in

180

3 in

th

e sa

me

area

and

wer

e so

on jo

ined

by

othe

r sm

all in

dust

ries.

By 1

828,

m

etal

foun

drie

s, co

pper

smith

s an

d pa

int m

anuf

actu

rers

wer

e es

tabl

ished

ad

jacen

t to

Blac

kwat

tle B

ay d

ue t

o re

adily

ava

ilabl

e w

ater

sup

ply

and

Page 5: Climatic change 7 A short geological and environmental

22

1

prox

imity

to th

e cit

y (M

acD

onne

ll 19

75).

The

regi

on s

outh

and

wes

t of

the

city

grew

rap

idly

durin

g th

e 18

20s

and

the

Dar

ling

Har

bour

Roze

lle B

ay a

rea

was

by

this

time

fully

dev

elope

d. B

y 18

48 t

his

envi

ronm

ent

had

beco

me

so d

egra

ded

that

leg

islat

ion

was

pas

sed

to

rem

ove

all t

anne

ries

and

pollu

ting

indu

strie

s ou

t of

the

city

to B

otan

y, W

illou

ghby

and

Par

ram

atta

.

Perio

d 18

54–1

889

Prio

r to

187

0, e

ffect

ively

all

indu

stria

l act

ivity

in th

e Sy

dney

reg

ion

was

lo

cate

d clo

se

to

the

pres

ent-d

ay

CBD

, bu

t st

eam

po

wer

led

to

co

nsid

erab

le gr

owth

in

Sy

dney

af

ter

this

time.

Met

al w

orki

ng,

engi

neer

ing,

bui

ldin

g m

ater

ials,

cloth

ing

and

text

iles

beca

me

majo

r in

dust

ries

betw

een

1861

and

189

0. T

he i

ntro

duct

ion

of t

ram

way

s, ra

ilway

s an

d m

ajor

brid

ges

in t

he l

ate

1880

s pr

ompt

ed r

apid

urb

an

expa

nsio

n. I

ndus

trial

activ

ity i

n th

e Ir

on C

ove

catc

hmen

t in

187

0 co

nsist

ed o

f on

ly on

e bl

acks

mith

sho

p, b

ut b

y 18

91 t

he n

umbe

r ha

d in

crea

sed

to 1

0 (L

inks

199

8; T

aylo

r, Bi

rch

& L

inks

200

4). A

lso a

t th

is tim

e, ch

emica

l in

dust

ries,

met

al w

orki

ng,

boat

bu

ildin

g,

dye

use,

elect

rical

and

glas

s m

anuf

actu

ring,

as

well

as

hors

e-dr

awn

vehi

cle

build

ing

had

take

n ro

ot in

the

Iro

n Co

ve c

atch

men

t. La

nd a

djac

ent

to

Hom

ebus

h Ba

y ha

s be

en u

sed

for

indu

stria

l pur

pose

s, in

clud

ing

a na

val

arm

amen

t st

ore

and

brick

wor

ks,

since

the

188

0s (

Hom

ebus

h Ba

y Co

rpor

atio

n 19

94; S

uh, B

irch

& H

ughe

s 20

04; S

uh, B

irch

& H

ughe

s 20

04; S

uh, B

row

n &

Birc

h 20

03; T

aylo

r, Bi

rch

& L

inks

200

4).

Perio

d 18

89–1

922

Sydn

ey sp

read

rapi

dly

wes

twar

ds b

etw

een

1889

and

192

2 an

d Ir

on C

ove,

Hen

an

d Ch

icken

an

d H

omeb

ush

Bays

be

cam

e ur

bani

sed

and

indu

stria

lised

. Det

ailed

land

use

map

ping

(Jol

ly 20

05) s

how

s Ir

on C

ove

catc

hmen

t ch

ange

d fr

om a

sub

urb

supp

ortin

g pr

edom

inan

tly l

arge

es

tate

s (3

0–40

% o

f th

e to

tal

area

) to

one

of

main

ly sm

all r

esid

entia

l bl

ocks

(57

% o

f lan

d us

e) i

n th

e pe

riod

1905

to

1930

. In

1916

majo

r ab

atto

irs w

ere

relo

cate

d fr

om R

ozell

e Ba

y to

Hom

ebus

h Ba

y. A

larg

e ba

se m

etal

foun

dry

and

a sm

elter

com

men

ced

oper

atio

ns o

n th

e sh

ores

of

Hen

and

Chi

cken

Bay

dur

ing

the

early

190

0s.

22

2

Indu

stry

rep

laced

agr

icultu

re i

n th

e Pa

rram

atta

Riv

er r

egio

n (P

owel

l 19

87) a

nd b

ecau

se th

e m

ovem

ent o

f im

porte

d go

ods

and

man

ufac

ture

d ite

ms

requ

ired

prox

imity

to

wat

erw

ays,

almos

t all

wat

erfr

ont

on t

he

shor

es o

f low

er P

arra

mat

ta R

iver

was

occ

upied

by

indu

stry

by

the

end

of

the

19th

cen

tury

.

1922

to th

e pr

esen

t Fa

ctor

ies m

anuf

actu

ring

heav

y ele

ctric

al eq

uipm

ent,

large

oil

refin

erie

s an

d po

wer

supp

ly st

atio

ns w

ere

cons

truct

ed c

lose

to th

e es

tuar

y be

twee

n th

e Fi

rst a

nd S

econ

d W

orld

War

s. M

any

heav

y in

dust

ries

situa

ted

in th

e in

ner,

mix

ed r

esid

entia

l/in

dust

rial

area

s of

the

city

wer

e re

loca

ted

outs

ide

the

Port

Jack

son

catc

hmen

t afte

r th

e Se

cond

Wor

ld W

ar (L

inks

19

98; T

aylo

r, Bi

rch

& L

inks

200

4). H

owev

er, t

hese

indu

strie

s wer

e so

on

repl

aced

with

lig

ht i

ndus

try,

who

lesale

rs a

nd t

rans

port

com

pani

es.

Furth

er d

ecen

tralis

atio

n of

indu

stry

occ

urre

d in

Syd

ney

afte

r the

Sec

ond

Wor

ld W

ar d

ue t

o a

mov

emen

t of

peo

ple

to t

he o

uter

sub

urbs

and

a

chan

ge i

n tra

nspo

rtatio

n, m

ainly

tow

ard

truck

ing

and

cont

ainer

isatio

n (W

ebbe

r &

Daly

197

1).

Hen

and

Chi

cken

Bay

cat

chm

ent

rem

ained

pr

edom

inan

tly a

gricu

ltura

l un

til a

fter

the

Seco

nd W

orld

War

whe

n it

chan

ged

to m

ediu

m-d

ensit

y ho

usin

g.

Ext

ensiv

e pa

rts o

f th

e H

omeb

ush

Bay

shor

eline

wer

e re

claim

ed.

The

wes

tern

sho

re w

as c

ompl

etely

rem

odifi

ed p

rior

to 1

955,

whe

reas

the

Rh

odes

Pen

insu

la, o

n th

e ea

ster

n sh

ore,

was

rec

laim

ed la

ter,

betw

een

1956

an

d 19

75,

crea

ting

oppo

rtuni

ties

for

hous

ing,

in

dust

rial,

com

mer

cial a

nd r

ecre

atio

nal r

edev

elopm

ents

. How

ever

, man

y of

the

se

indu

strie

s hav

e m

oved

aw

ay fr

om th

is re

gion

in re

cent

tim

es.

Fore

shor

e de

velo

pmen

t and

recl

amat

ion

in th

e ha

rbou

r Po

rt Ja

ckso

n ha

s be

en e

xten

sively

mod

ified

by

recla

mat

ion

over

the

last

200

year

s, es

pecia

lly in

the

uppe

r an

d ce

ntra

l est

uary

. App

roxi

mat

ely 7

7 km

of t

he 3

22 k

m o

f orig

inal

shor

eline

has

bee

n lo

st d

ue to

recla

mat

ion

and

infil

ling

of in

terti

dal a

reas

(Pitb

lado,

197

8). R

eclai

med

are

as a

re u

sed

main

ly fo

r in

dust

rial,

recr

eatio

nal a

nd r

esid

entia

l use

s an

d co

ver

a to

tal

11.3

5 km

2 of

the

tot

al 50

km

2 or

23%

of

the

estu

ary

(Birc

h &

Mur

ray

2007

; M

urra

y 20

03).

Nat

ural

fore

shor

es o

f m

ud f

lats

and

man

grov

es

have

giv

en w

ay to

sea

wall

s, w

harv

es a

nd b

uild

ings

. The

hea

d of

man

y

Page 6: Climatic change 7 A short geological and environmental

22

3

emba

ymen

ts h

ave

been

enc

lose

d by

san

dsto

ne w

alls

and

inte

rtida

l are

as

recla

imed

by

infil

ling.

Rec

lamat

ion

has

resu

lted

in a

los

s of

alm

ost

9 m

illio

n cu

bic

met

res

of w

ater

on

each

tida

l cyc

le, w

hich

has

res

ulte

d in

lar

ge c

hang

es i

n w

ater

mov

emen

t, w

ater

qua

lity,

sedi

men

tatio

n an

d ec

olog

y of

the

uppe

r har

bour

(Liu

198

9). S

ea w

alls h

ave

chan

ged

a ra

mp

fore

shor

e to

a v

ertic

al sh

oref

ace

alter

ing

the

hydr

olog

y an

d ec

olog

y of

th

e es

tuar

y. Th

e fo

llow

ing

hist

ory

of r

eclam

atio

n is

main

ly fr

om t

he

wor

k of

Mur

ray

(200

3).

Per

iod

1788

–185

4

F

igu

re 7

.1 O

nly

the

cent

ral a

rea

of S

ydne

y w

as u

rban

ised

by 1

860

and

fore

shor

e re

clam

atio

n w

as c

onfin

ed t

o Sy

dney

and

Far

m C

oves

. Th

e in

tens

ity o

f ind

ustri

al ac

tivity

can

be

judg

ed b

y th

e nu

mbe

r of s

hips

in a

ph

otog

raph

of S

ydne

y Co

ve ta

ken

abou

t thi

s dat

e (F

igur

e 7.

3). S

edim

ent

man

tling

Dar

ling

Har

bour

, Blac

kwat

tle B

ay a

nd R

ozell

e Ba

y be

gan

to

show

sign

s of h

eavy

met

al co

ntam

inat

ion

by th

is tim

e.

22

4

The

first

cha

nge

in t

he f

ores

hore

occ

urre

d w

hen

large

allo

tmen

ts w

ere

give

n ou

t to

the

mili

tary

, civ

ilian

adm

inist

ratio

n, w

ealth

y m

erch

ants

and

th

e cle

rgy

and

by 1

830

min

or r

eclam

atio

n ha

d st

arte

d fo

r w

harf

age

and

farm

ing

(God

den

Mac

kay

Pty

Ltd

1991

; Li

u 19

89).

The

first

majo

r re

clam

atio

n pr

ojec

t in

the

har

bour

occ

urre

d in

the

per

iod

1835

–185

4 w

hen

the

head

of

Sydn

ey C

ove

was

rem

odell

ed i

nto

a se

mi-c

ircul

ar

sand

ston

e qu

ay w

ith th

e Ta

nk S

tream

cha

nnell

ed a

nd b

uried

. Mor

t and

W

alsh

Bays

wer

e in

filled

and

the

ope

ning

of

the

Aus

tralia

n G

as L

ight

Co

mpa

ny tr

ansf

orm

ed D

arlin

g H

arbo

ur (G

odde

n M

acka

y Pt

y Lt

d 19

91,

1993

).

Per

iod

1854

–188

9

F

igu

re 7

.2 B

y 18

80, u

rban

isatio

n ha

d sp

read

to I

ron

Cove

and

mos

t of

the

bay

head

s in

the

sou

th,

cent

ral

part

of t

he e

stua

ry h

ad b

een

recla

imed

. At t

his

time,

sedi

men

ts o

f D

arlin

g H

arbo

ur, B

lackw

attle

Bay

an

d Ro

zelle

Bay

had

bec

ome

mod

erat

ely c

onta

min

ated

with

hea

vy

met

als.

Page 7: Climatic change 7 A short geological and environmental

22

5

The

intro

duct

ion

of tr

ams a

nd tr

ains l

ead

to a

boo

m in

dev

elopm

ent a

nd

an in

crea

sed

need

for

res

iden

tial,

indu

stria

l and

rec

reat

iona

l spa

ce. T

his

resu

lted

in r

eclam

atio

n of

em

baym

ents

clo

se t

o ce

ntra

l Syd

ney,

that

is

Sydn

ey

Cove

, Bl

ackw

attle

Ba

y, Py

rmon

t Ba

y, D

arlin

g H

arbo

ur,

Woo

lloom

oolo

o Ba

y an

d Ru

shcu

tters

Bay

(Fi

tzge

rald

& G

olde

r, 19

94;

God

den

Mac

kay

Pty

Ltd

1991

, 199

3; S

hore

198

1; S

teph

ense

n, 1

966)

. A

phot

ogra

ph t

aken

of

Sydn

ey C

ove

in t

he la

te 1

850s

sho

ws

num

erou

s sh

ips

and

inte

nse

indu

stria

l ac

tivity

in

this

area

dur

ing

thes

e tim

es

(Fig

ure

7.3)

. In

the

sec

ond

half

of t

he 1

8th

cent

ury,

dom

estic

was

te,

sew

erag

e, of

fal

and

dead

ani

mals

wer

e di

scar

ded

into

for

esho

re a

reas

co

nsid

ered

dum

ping

gro

unds

for u

nwan

ted

was

te (S

tring

er 1

984)

. It w

as

belie

ved

that

dise

ase

was

com

mun

icat

ed b

y no

xiou

s va

pour

s em

anat

ing

from

dam

p ar

eas

whe

re f

aeca

l was

te a

ccum

ulat

ed, a

nd o

dour

s an

d th

e fe

ar o

f di

seas

e em

itted

fro

m t

hese

wet

lands

con

tribu

ted

grea

tly t

o re

clam

atio

n du

ring

this

perio

d (S

ollin

g &

Rey

nold

s 197

7).

F

igu

re 7

.3 A

n ea

rly p

hoto

grap

h of

Syd

ney

Cove

take

n in

the

late

1850

s by

an

unkn

own

phot

ogra

pher

. Th

e nu

mbe

r of

shi

ps i

n th

e co

ve

dem

onst

rate

s th

e in

tens

ity o

f ac

tivity

in th

is pa

rt of

the

harb

our

at th

is tim

e. Th

e pe

riod

portr

ayed

in th

is ph

otog

raph

cor

relat

es w

ell w

ith d

ate

of o

nset

of

cont

amin

atio

n as

ind

icate

d in

a c

ore

take

n fr

om n

earb

y D

arlin

g H

arbo

ur s

how

n in

Fig

ure

7.6.

The

pho

togr

aph

is fr

om t

he

Mac

arth

ur A

lbum

title

d “S

ydne

y –

The

1850

s, th

e Lo

st C

ollec

tions

”, b

y

22

6

Barr

y G

room

and

War

ren

Wick

man

fro

m t

he H

istor

ic Ph

otog

raph

Co

llect

ion,

the

Uni

vers

ity o

f Syd

ney.

Per

iod

1889

–192

2

F

igu

re 7

.4 S

outh

of

the

harb

our,

urba

nisa

tion

had

spre

ad f

rom

the

es

tuar

y m

outh

to

Hom

ebus

h Ba

y by

191

7, a

nd t

he s

outh

ern

part

of

Nor

th S

hore

had

bec

ome

resid

entia

l. M

ost o

f the

upp

er e

nds o

f bay

s on

the

sout

hern

sho

res

of t

he e

stua

ry h

ad b

een

recla

imed

by

1922

. Se

dim

ents

in

Dar

ling

Har

bour

, Bl

ackw

attle

Bay

and

Roz

elle

Bay

had

beco

me

high

ly c

onta

min

ated

with

hea

vy m

etals

and

Iron

Cov

e, H

en a

nd

Chick

en

Bay

and

Hom

ebus

h Ba

y se

dim

ents

w

ere

mod

erat

ely

cont

amin

ated

by

1917

. Th

e co

ntin

ued

wid

espr

ead

disp

osal

of g

arba

ge i

n in

terti

dal

swam

ps

(Cow

ard

1988

) to

for

m i

ndus

trial

area

s an

d pa

rks

(DE

P 19

86)

was

a

majo

r con

tribu

ting

fact

or to

rat i

nfes

tatio

n an

d th

e ou

tbre

ak o

f bub

onic

pl

ague

in 1

898/

99. T

he S

ydne

y H

arbo

ur T

rust

(SH

T) w

as fo

rmed

und

er

pow

ers

give

n by

an

Act

of

Parli

amen

t in

190

0 to

res

ume

priv

ate

Page 8: Climatic change 7 A short geological and environmental

22

7

ente

rpris

es a

nd m

oder

nise

dila

pida

ted

fore

shor

es i

n W

alsh

Bay

and

Dar

ling

Har

bour

, whi

ch sh

elter

ed in

fest

atio

ns o

f rat

s (E

mer

y 19

65; M

SB

1974

). In

crea

sed

dem

and

for

acce

ssib

le w

ater

side

land

for

port

and

indu

stria

l fu

nctio

ns r

esul

ted

in e

xten

sive

recla

mat

ion

in C

anad

a Ba

y, K

ings

Bay

, Hen

and

Chi

cken

Bay

, Iro

n Co

ve (H

awth

orne

Can

al), W

hite

Ba

y, Ro

zelle

Bay

and

Ros

e Ba

y.

Per

iod

1922

–200

2

F

igu

re 7

.5 U

rban

isatio

n of

the

cat

chm

ent

is no

w a

lmos

t co

mpl

ete,

exce

pt f

or a

reas

set

asid

e fo

r re

crea

tion

and

bush

lan

d re

serv

es a

nd

fore

shor

e re

clam

atio

n ha

s all

but c

ease

d. S

edim

ents

in th

e up

per p

arts

of

bays

, es

pecia

lly a

long

the

sou

ther

n sh

ores

of

the

harb

our,

are

high

ly

cont

amin

ated

with

hea

vy m

etals

and

min

or c

onta

min

atio

n is

pres

ent i

n m

ost

sedi

men

t of

the

upp

er a

nd c

entra

l har

bour

, as

well

as

in M

iddl

e H

arbo

ur a

nd L

ane

Cove

.

22

8

The

mos

t ac

tive

perio

d of

rec

lamat

ion

took

plac

e in

Por

t Ja

ckso

n be

twee

n 19

22 a

nd 1

955

whe

n ab

out

5.7

km2

of l

and

was

cre

ated

ad

jacen

t to

Par

ram

atta

Ri

ver

at S

ilver

wat

er,

Hom

ebus

h Pe

nins

ula,

Gar

den

Islan

d, E

xile

Bay,

Kin

gs B

ay,

Iron

Cov

e, G

lebe

Isla

nd a

nd

Dar

ling

Har

bour

. Be

twee

n 19

55 a

nd 1

978

recl

amat

ion

was

main

ly by

the

use

of

landf

ill,

inclu

ding

indu

stria

l was

tes

(Cow

ard

1988

) in

low

-lyin

g ar

eas

adjac

ent t

o M

iddl

e H

arbo

ur, P

arra

mat

ta R

iver

and

Lan

e Co

ve R

iver

(M

cLou

ghlin

, 19

85).

The

last m

ajor

recla

mat

ion

perio

d w

as f

rom

196

4 to

198

1 w

hen

exte

nsiv

e fo

resh

ore

area

s w

ere

cons

truct

ed t

o ac

com

mod

ate

the

new

‘ro

ll-on

, rol

l-off’

con

tain

er s

hipp

ing

(Ang

lin &

Ass

ociat

es 1

990;

Bud

in

1990

; Fra

ser 1

989;

Pro

udfo

ot 1

996)

.

Rec

lam

atio

n as

a s

ourc

e of

pol

lutio

n Th

e to

tal m

ass o

f mat

erial

use

d to

und

erta

ke 1

1.35

km

2 of

recla

mat

ion

in

Port

Jack

son

has

been

est

imat

ed a

t ov

er 1

00 m

illio

n to

nnes

(M

t) (M

cLou

ghlin

200

0). T

he m

ost c

omm

on m

etho

d us

ed to

und

erta

ke th

is re

clam

atio

n w

as to

con

stru

ct a

sea

wall

and

infil

l beh

ind

the

barr

ier u

sing

garb

age,

indu

stria

l was

te a

nd s

edim

ents

rem

oved

fro

m th

e flo

or o

f th

e ad

jacen

t est

uary

. The

com

posit

ion

of m

ater

ial u

sed

as in

fill v

aried

with

lo

catio

n an

d da

te o

f re

clam

atio

n an

d alt

houg

h fe

w r

ecor

ds w

ere

mad

e, th

e co

mpo

sitio

n of

one

site

is w

ell k

now

n. T

he n

atur

e an

d ex

tent

of

was

te in

the

Hom

ebus

h Ba

y ar

ea is

well

doc

umen

ted

due

to c

lean-

up

oper

atio

ns a

ssoc

iated

with

the

Sydn

ey 2

000

Olym

pic

Gam

es.

Prio

r to

Eur

opea

n se

ttlem

ent,

this

area

com

prise

d ex

tens

ive

tidal

wet

lands

and

thick

woo

dlan

ds, w

hich

wer

e cle

ared

and

rec

laim

ed f

rom

th

e ea

rly 1

800s

for

far

min

g. T

he r

egio

n w

as u

sed

as a

rac

ecou

rse,

brick

wor

ks,

arm

amen

ts d

epot

and

an

abat

toir

betw

een

the

mid

-188

0s

and

1969

. Una

utho

rised

filli

ng w

as c

omm

onpl

ace

from

the

late

1960

s to

the

late

1970

s. D

urin

g th

is pe

riod

over

nin

e m

illio

n cu

bic

met

res

of

com

mer

cial,

dom

estic

and

indu

stria

l was

te w

as d

umpe

d in

the

area

(Suh

et

al 2

004)

. A 2

5 m

etre

-hig

h en

gine

ered

land

fill r

ose

abov

e th

e so

uthe

rn

bank

of H

aslam

s Cr

eek

and

only

30 p

er c

ent o

f the

Hom

ebus

h Ba

y sit

e re

tain

ed it

s nat

ural

top

soil

and

rem

nant

veg

etat

ion.

By

1970

Wen

twor

th

Bay

ceas

ed t

o ex

ist a

nd m

ost

of t

he lo

w-ly

ing

land

had

been

fill

ed b

y 19

78. F

inal

fillin

g alo

ng t

he n

orth

and

sou

th b

anks

of

Has

lams

Cree

k

Page 9: Climatic change 7 A short geological and environmental

22

9

took

plac

e be

twee

n 19

79 a

nd 1

988.

The

sig

nific

ant

ecol

ogica

l dam

age

had

been

reco

gniz

ed b

y 19

75 w

hen

licen

sing

of la

ndfil

ls be

cam

e law

, but

a

furth

er f

ive

year

s lap

sed

befo

re r

egul

atio

ns b

ecam

e fu

lly e

nfor

ced.

A

tota

l of $

137

mill

ion

was

allo

cate

d fo

r clea

n-up

of t

he s

ite in

one

of t

he

large

st r

emed

iatio

n pr

ojec

ts c

arrie

d ou

t in

Aus

tralia

(Su

h, B

irch

&

Hug

hes

2004

; Su

h,

Birc

h,

Mat

thai

et

al 20

04).

Was

te

com

prise

d pu

tresc

ible,

bu

ildin

g,

chem

ical

and

garb

age

mun

icipa

l w

aste

, co

nstru

ctio

n de

bris,

hou

seho

ld g

arba

ge, d

emol

ition

was

te, a

sh f

ill a

nd

dred

ged

sedi

men

t co

ntain

ing

heav

y m

etals

, as

best

os,

a ra

nge

of

hydr

ocar

bons

, in

cludi

ng d

ioxi

ns,

benz

ene,

tolu

ene,

ethy

lben

zene

and

xy

lene

(BTE

X)

com

poun

ds a

nd p

olyc

yclic

aro

mat

ic hy

droc

arbo

ns,

as

well

as

orga

noch

lorin

e pe

stici

des.

A t

otal

of 4

00 t

onne

s of

haz

ardo

us

was

te c

ompr

ising

dio

xins

, fur

ans

and

othe

r or

gano

chlo

rine

com

poun

ds

was

cla

ssifi

ed

as

Sche

duled

Ch

emica

l W

aste

w

hich

ha

d to

be

de

stro

yed

by a

the

rmal/

cata

lytic

treat

men

t un

der

NSW

RE

PA l

icens

e (B

irch,

et

al, 2

007)

. In

one

of

the

large

st s

urve

ys o

f its

kin

d, 4

531

so

il sa

mpl

es w

ere

colle

cted

by

corin

g th

roug

h th

e in

fill

for

chem

ical

analy

sis (

Suh,

Birc

h &

Hug

hes

2004

; Su

h, B

irch,

Mat

thai

et a

l 20

04).

Are

as

infil

led

with

es

tuar

ine

sedi

men

t fr

om

the

adjac

ent

bay

co

ntain

ed e

levat

ed c

once

ntra

tions

of h

eavy

met

als a

nd in

som

e ar

eas s

oil

met

al co

ncen

tratio

ns w

ere

cons

ider

ed h

igh

enou

gh t

o po

se a

thr

eat

to g

roun

dwat

er.

This

soil

was

rem

oved

and

con

solid

ated

int

o sm

all

man

agea

ble

area

s ca

pped

w

ith

impe

rmea

ble

clay

and

surr

ound

ed

by le

acha

te d

rain

s to

pro

tect

sur

roun

ding

aqu

ifers

. To

date

, mon

itorin

g of

th

e lea

chat

e dr

ains

indi

cate

co

ntam

inan

t co

ncen

tratio

ns

are

at

acce

ptab

le lev

els.

In a

pro

ject

spec

ially

desig

ned

to t

est

leach

ate

prod

uctio

n in

rec

laim

ed

lands

due

to

rain

wat

er f

iltra

tion

and

tidal

actio

n, S

uh, B

row

n &

Birc

h (2

003a

, 200

3b)

plac

ed s

ix b

oreh

oles

thr

ough

infil

l at

Bice

nten

nial

Park

ad

jacen

t to

Roze

lle B

ay. T

he P

ark

(1.0

1 ha

) was

recla

imed

bet

wee

n 19

72

and

1980

by

rem

oval

of a

ppro

xim

ately

31,

000

m3

of m

ater

ial f

rom

the

adjac

ent

bay,

prim

arily

to

atta

in n

avig

atio

n de

pths

. In

addi

tion

to t

he

mar

ine

sedi

men

ts,

the

fill

com

prise

d de

mol

ition

was

te,

cons

truct

ion

mat

erial

s an

d in

dust

rial a

nd d

omes

tic w

aste

. Res

ults

of

the

expe

rimen

t sh

owed

that

dur

ing

dry

perio

ds w

hen

wat

er ta

bles

rece

de, o

xyge

n in

gres

s m

ay l

ead

to d

ecre

asin

g ac

idity

(pH

) an

d an

ass

ociat

ed in

crea

se i

n th

e co

ncen

tratio

ns o

f so

me

heav

y m

etals

(co

pper

, lea

d, z

inc,

arse

nic

and

23

0

chro

me)

. Th

e re

sults

of

th

e fie

ld

stud

y w

ere

test

ed

unde

r co

ntro

lled

cond

ition

s in

the

labo

rato

ry b

y pe

rcol

atin

g fr

esh

and

salin

e w

ater

thr

ough

col

umns

con

tain

ing

soil

mat

erial

fro

m t

he p

ark

(Suh

, Br

own

& B

irch

2003

a, 20

03b)

. Alth

ough

the

par

allel

field

stu

dies

had

co

nsid

erab

ly hi

gher

con

cent

ratio

ns o

f m

etals

than

that

pro

duce

d in

the

labor

ator

y ex

perim

ent,

conc

entra

tions

wer

e or

ders

of m

agni

tude

gre

ater

th

an n

atur

al se

a w

ater

. It w

as c

onclu

ded

that

elev

ated

con

cent

ratio

ns o

f he

avy

met

als p

roba

bly

ente

r th

e es

tuar

y by

tid

al ac

tion

and

durin

g pe

riods

of r

ainfa

ll.

Alth

ough

it

has

been

dem

onst

rate

d in

the

fiel

d an

d in

con

trolle

d lab

orat

ory

stud

ies th

at th

e m

ater

ial u

sed

for i

nfill

ing

is a

sour

ce o

f hea

vy

met

als t

o th

e es

tuar

y, th

e pr

oces

s ha

s no

t ye

t be

en q

uant

ified

. Th

e ju

xtap

ositi

on o

f hi

gh c

onta

min

ant

conc

entra

tions

in

sedi

men

ts a

t th

e he

ads

of

mos

t es

tuar

y em

baym

ents

an

d ex

tens

ive

recla

mat

ion

in

adjac

ent

lands

has

obv

ious

im

plica

tions

. H

owev

er,

stor

mw

ater

can

als

also

disc

harg

e to

the

est

uary

at

thes

e lo

catio

ns (

Barr

y, Ta

ylor

& B

irch

1999

, 200

1; B

irch

et a

l 199

9) a

nd d

iffer

entia

ting

the

relat

ive

mag

nitu

de

of e

ach

sour

ce i

s co

mpl

ex a

nd h

as n

ot y

et b

een

atte

mpt

ed.

The

extra

ordi

nary

mas

ses

of m

ater

ials

dred

ged

from

the

est

uary

flo

or f

or

infil

ling

and

recla

mat

ion

arou

nd P

ort

Jack

son

give

s an

ide

a of

the

po

tent

ial m

agni

tude

of

this

poss

ible

sour

ce. A

lmos

t a m

illio

n to

nnes

of

cont

amin

ated

sed

imen

t fr

om I

ron

Cove

was

use

d fo

r re

clam

atio

n at

th

e m

outh

s of

Haw

thor

ne a

nd I

ron

Cove

Cre

eks;

4.6

Mt i

n H

omeb

ush

Bay

and

anot

her

2.8

Mt

on

the

bank

s of

th

e Pa

rram

atta

Ri

ver

(McL

ough

lin 2

000)

.

Ecol

ogic

al e

ffect

s of

recl

amat

ion

It is

not s

urpr

ising

that

, with

23

per c

ent o

f the

are

a of

Por

t Jac

kson

lost

to

rec

lamat

ion,

app

roxi

mat

ely

50 p

er c

ent o

f th

e sh

ore

is co

mpo

sed

of

reta

inin

g se

awall

s or

oth

er b

uilt

habi

tats

(Ch

apm

an &

Bul

leri

2003

). A

ltere

d sh

oreli

nes,

parti

cular

ly th

e co

nstru

ctio

n of

lon

g st

retc

hes

of

seaw

alls,

have

majo

r ec

olog

ical

impa

cts.

The

Cent

re f

or R

esea

rch

on

Eco

logi

cal I

mpa

cts o

f Coa

stal

Citie

s at t

he U

nive

rsity

of S

ydne

y is

doin

g so

me

exce

llent

wor

k on

und

erst

andi

ng th

e ec

olog

ical r

ole

that

sea

wall

s an

d ot

her

inte

rtida

l st

ruct

ures

hav

e on

urb

anise

d es

tuar

ies (

Bloc

kley

, Ch

apm

an i

n pr

ess;

Chap

man

& B

uller

i 20

03;).

Sea

wall

s di

ffer

from

na

tura

l roc

ky s

hore

s be

caus

e th

ey a

re u

suall

y st

eep

and

they

hav

e fe

wer

Page 10: Climatic change 7 A short geological and environmental

23

1

crev

ices

and

over

hang

s th

an r

ocky

sho

res

and

som

e ha

bita

ts (

e.g. r

ock

pool

s) a

re a

bsen

t. A

lso, v

ertic

al se

awall

s ha

ve a

com

pres

sed

inte

rtida

l ar

ea (1

–2 m

) in

cont

rast

to n

atur

al sh

ores

with

low

er g

radi

ents

(10s

of

met

res)

. The

se fa

ctor

s affe

ct th

e di

strib

utio

n an

d ab

unda

nce

of in

terti

dal

orga

nism

s. A

t mid

- and

hig

h-sh

ore

levels

ther

e ar

e fr

eque

nt d

iffer

ence

s be

twee

n as

sem

blag

es o

n na

tura

l sho

res a

nd se

awall

s, bu

t, at

low

er le

vels,

di

ffere

nces

bet

wee

n as

sem

blag

es a

re c

onsid

erab

ly sm

aller

. Th

e lo

nges

t sea

wall

s in

Por

t Jac

kson

hav

e be

en c

onst

ruct

ed to

sup

port

recla

mat

ion

activ

ities

at

the

head

s of

em

baym

ents

, fo

r ex

ampl

e Fa

rm

Cove

, W

oollo

omoo

loo

Bay

and

Iron

Cov

e. Th

ese

area

s w

ere

once

m

uddy

, m

angr

ove

and

saltm

arsh

wet

lands

with

gen

tle s

lope

s. Th

e m

arke

d ch

ange

in h

abita

t in

thes

e ar

eas

has

resu

lted

in m

ajor

alter

atio

n to

eco

logi

cal

func

tion,

not

to

men

tion

the

redu

ctio

n in

bio

logi

cal

prod

uctiv

ity a

nd c

hang

es in

hyd

rolo

gy a

nd p

hysio

-che

mica

l attr

ibut

es o

f th

e in

terti

dal z

one.

His

toric

effe

ct o

f urb

anis

atio

n an

d in

dust

rialis

atio

n on

th

e Po

rt J

acks

on e

stua

ry

The

hist

oric

effe

ct o

f in

crea

sing

anth

ropo

geni

c ac

tivity

in

the

Port

Jack

son

catc

hmen

t on

the

adj

acen

t es

tuar

ine

envi

ronm

ent

has

been

es

tabl

ished

thr

ough

an

unus

ual

colla

bora

tion

by s

tude

nts

and

staf

f in

ur

ban

geog

raph

y an

d en

viro

nmen

tal

chem

istry

in

the

Env

ironm

enta

l G

eolo

gy G

roup

in

the

Scho

ol o

f G

eosc

ience

s at

the

Uni

vers

ity o

f Sy

dney

(Bi

rch

& M

urra

y 20

07; J

olley

200

5; L

inks

199

8; M

urra

y 20

03;

Taylo

r, Bi

rch

& L

inks

200

4).

Stud

ies o

f ch

angi

ng la

nd u

se, d

evelo

pmen

t of

indu

stry

and

rec

lamat

ion

in P

ort

Jack

son,

wer

e un

derta

ken

by t

he S

choo

l of

Geo

scien

ces

at t

he

Uni

vers

ity o

f Sy

dney

to

dete

rmin

e po

tent

ial a

dver

se e

ffect

s on

the

es

tuar

y by

hum

an a

ctiv

ity in

the

adjac

ent c

atch

men

t (Jo

lley

2005

; Lin

ks

1998

; M

urra

y 20

03;

Taylo

r, Bi

rch

& L

inks

200

4).

Botto

m s

edim

ents

w

ere

used

to d

eter

min

e po

ssib

le e

ffect

s on

the

estu

ary

and

to e

stab

lish

whe

ther

tem

pora

l ch

ange

s in

the

cat

chm

ent

coul

d be

rec

orde

d in

su

bsur

face

sed

imen

t in

the

est

uary

(Ta

ylor

, Bi

rch

& L

inks

200

4).

Sedi

men

t ad

sorb

s co

ntam

inan

ts f

rom

the

ove

rlyin

g w

ater

col

umn

and

thus

has

the

abi

lity

to t

ime

inte

grat

e an

d to

rec

ord

the

influ

x of

co

ntam

inan

ts in

to a

wat

er b

ody.

Beca

use

sedi

men

ts a

re d

epos

ited

layer

-

23

2

by-la

yer

in a

reg

ular

chr

onol

ogic

sequ

ence

, thi

s se

dim

ent ‘

mem

ory’

can

be u

sed

as a

n hi

stor

ic re

cord

of c

onta

min

ant f

lux,

whi

ch in

turn

refle

cts

anth

ropo

geni

c ch

ange

s in

the

adjac

ent c

atch

men

t (Ta

ylor 2

000)

. To

test

th

is co

ncep

t in

Port

Jack

son,

12

sedi

men

tary

cor

es w

here

take

n in

nin

e hi

ghly

cont

amin

ated

em

baym

ents

and

dow

n-ho

le sa

mpl

es w

ere

analy

sed

for

cont

amin

ants

and

dat

ed u

sing

radi

oiso

tope

s lea

d 21

0 an

d ca

esiu

m

137

(Tay

lor 2

000;

Tay

lor,

Birc

h &

Lin

ks 2

004)

. Th

ree

of t

he 1

2 co

res,

one

each

fro

m B

lackw

attle

Bay

(Co

re 1

), Ir

on

Cove

(Co

re 2

) an

d H

omeb

ush

Bay

(Cor

e 3)

are

rep

rodu

ced

in F

igur

e 7.

6. T

hese

bay

s ar

e all

man

tled

in h

ighl

y co

ntam

inat

ed s

edim

ent a

nd a

re

loca

ted

with

in

crea

sing

dist

ance

fr

om

cent

ral

Sydn

ey,

that

is,

ap

prox

imat

ely 2

, 5 a

nd 1

2 km

, res

pect

ively

. All

thre

e co

res

show

low

co

ncen

tratio

n of

hea

vy m

etals

(cop

per,

lead

and

zinc

) at t

he b

otto

m o

f th

e co

re a

nd a

t som

e de

pth

conc

entra

tions

incr

ease

mar

kedl

y. In

som

e ca

ses

conc

entra

tions

tow

ards

the

top

of

the

core

rem

ain c

onst

ant,

cont

inue

to

in

crea

se,

or

begi

n to

de

crea

se.

The

dept

h at

w

hich

co

ncen

tratio

ns

begi

n to

in

crea

se

is th

e po

int,

or

time,

whe

re

cont

amin

ants

sta

rt to

be

disc

harg

ed f

rom

the

cat

chm

ent,

that

is,

the

onse

t of

co

ntam

inat

ion

is fa

ithfu

lly

reco

rded

in

th

e se

dim

ent.

Cont

amin

atio

n co

mm

ence

d in

abo

ut 1

860

in B

lackw

attle

Bay

(Co

re 1

) an

d in

app

roxi

mat

ely 1

910

in I

ron

Cove

(Co

re 2

). Co

re 3

fro

m

Hom

ebus

h Ba

y re

cord

s ad

vers

e ef

fect

s of

hum

an a

ctiv

ity b

egin

ning

at

abou

t 192

5. T

he sp

read

of u

rban

izat

ion

and

the

deve

lopm

ent o

f ind

ustry

ou

twar

ds fr

om c

entra

l Syd

ney

(Fig

ures

1, 2

, 4 a

nd 5

) are

refle

cted

in th

e ex

pans

ion

of c

onta

min

ated

sedi

men

t in

the

adjac

ent e

stua

ry.

The

date

of

onse

t of

con

tam

inat

ion,

as

depi

cted

in

the

core

s, sh

ows

appr

oxim

ately

th

e sa

me

timin

g as

th

at

of

urba

nisa

tion

and

indu

stria

lisat

ion

in t

he a

djac

ent

catc

hmen

ts. M

oreo

ver,

the

seve

rity

of

cont

amin

atio

n in

the

sedi

men

t pro

file

also

decr

ease

s aw

ay f

rom

cen

tral

Sydn

ey

with

de

crea

sing

urba

n in

tens

ity.

For

exam

ple,

zinc

in

se

dim

ent

from

the

cor

e ta

ken

close

st t

o ce

ntra

l Sy

dney

(Co

re 1

) in

Bl

ackw

attle

Bay

is a

t a m

axim

um o

f ab

out 2

000

μg/g

and

for

the

core

ta

ken

in I

ron

Cove

(Cor

e 2)

it is

app

roxi

mat

ely 1

500

μg/g

, whe

reas

in

Hom

ebus

h Ba

y th

e m

axim

um z

inc

conc

entra

tion

in t

he s

edim

ent

is ap

prox

imat

ely 1

000

μg/g

.

Page 11: Climatic change 7 A short geological and environmental

23

3

The

data

pro

vide

d he

re a

re f

or h

eavy

met

als,

but

the

sam

e tre

nd i

s ev

iden

t for

org

anic

cont

amin

ants

as

well

(Tay

lor,

Birc

h &

Lin

ks 2

004)

. O

rgan

ochl

orin

e co

mpo

unds

ar

e en

tirely

ar

tifici

al in

sect

icide

s an

d he

rbic

ides

and

the

se c

hem

icals

cam

e in

to u

se i

n A

ustra

lia a

fter

the

Seco

nd W

orld

War

. The

ons

et o

f the

se o

rgan

ic co

ntam

inan

ts in

the

core

pr

ofile

s ar

e da

ted

at 1

945,

alm

ost

prec

isely

whe

n th

ey w

ere

intro

duce

d in

to th

e ca

tchm

ent.

Th

ese

resu

lts p

rovi

de c

onfid

ence

in th

e m

etho

dolo

gy a

nd th

e sc

ience

of

the

curr

ent

appr

oach

. Alth

ough

sim

ilar

resu

lts h

ave

been

obt

ained

for

in

divi

dual,

sit

e-sp

ecifi

c st

udies

, th

is is

the

only

catc

hmen

t-wid

e de

mon

stra

tion

of th

is ap

proa

ch.

Fig

ure

7.6

Cor

es fr

om B

lackw

attle

Bay

, Iro

n Co

ve a

nd H

omeb

ush

Bay

show

the

ver

tical

dist

ribut

ion

of h

eavy

met

al co

ncen

tratio

ns i

n th

e se

dim

ent.

At

the

botto

m o

f ea

ch c

ore,

the

conc

entra

tion

of m

etals

is

unifo

rmab

ly lo

w, b

ut a

t so

me

dept

h m

etal

levels

incr

ease

rap

idly.

Thi

s de

pth

(mar

ked

with

an

arro

w) i

s th

e da

te o

f ons

et o

f con

tam

inat

ion.

In

Core

1, f

rom

Blac

kwat

tle B

ay c

lose

to th

e cit

y, on

set o

f co

ntam

inat

ion

was

in a

bout

186

0, a

nd o

nset

dat

es a

re la

ter f

or C

ores

2 (I

ron

Cove

) and

3

(Hom

ebus

h Ba

y), w

hich

are

loca

ted

furth

er fr

om th

e cit

y ce

ntre

. Thi

s sp

read

of

cont

amin

atio

n de

mon

stra

tes

how

the

est

uary

res

pond

ed t

o en

croa

chin

g ur

bani

satio

n ac

ross

the

catc

hmen

t.

23

4 Rec

ent e

nviro

nmen

tal h

isto

ry

Mor

e hi

stor

ic in

form

atio

n ca

n be

glea

ned

from

cor

es s

uch

as th

ese.

It is

evid

ent f

rom

Cor

e 1

that

zin

c co

ncen

tratio

ns a

ttain

ed a

max

imum

in th

e se

dim

ent

in

abou

t 19

55

and

conc

entra

tions

ha

ve

been

ge

nera

lly

decr

easin

g sin

ce t

hat

time.

In f

act,

conc

entra

tions

are

alm

ost

half

the

max

imum

at p

rese

nt, w

here

as c

oppe

r con

tinue

s to

incr

ease

in se

dim

ents

at

thi

s lo

catio

n. T

here

is

evid

ence

fro

m t

he c

ore

prof

ile t

hat

the

conc

entra

tion

of

lead

has

star

ted

to

decli

ne

in

rece

nt

times

in

Bl

ackw

attle

Ba

y. Th

ere

appe

ars

to

have

be

en

two

phas

es

of

cont

amin

atio

n in

thi

s ba

y: a

perio

d of

mod

erat

e co

ntam

inat

ion

from

18

75 to

191

0, fo

llow

ed b

y a

perio

d of

hig

h co

ntam

inat

ion

from

191

0 to

th

e pr

esen

t. In

Iro

n Co

ve (

Core

2),

zinc

con

cent

ratio

ns r

each

ed a

m

axim

um in

app

roxi

mat

ely 1

960

and

have

rem

ained

hig

h to

the

pres

ent

day.

Copp

er a

nd le

ad a

lso a

ttain

ed a

max

imum

in Ir

on C

ove

at th

is tim

e, bu

t w

hile

lead

appe

ars

to b

e de

crea

sing

sligh

tly, c

oppe

r co

ncen

tratio

ns

have

rem

ained

hig

h an

d co

nsta

nt. C

ore

3 fr

om H

omeb

ush

Bay

show

s co

ntam

inat

ion

reac

hing

max

imum

con

cent

ratio

ns in

abo

ut 1

970

for z

inc

and

copp

er, b

ut th

e m

axim

um le

ad c

once

ntra

tion

occu

rred

ear

lier i

n th

e 19

40s,

perh

aps

due

to th

e in

trodu

ctio

n of

indu

stry

man

ufac

turin

g lea

d-ba

sed

prod

ucts

on

th

e sh

ores

of

th

e ba

y. In

crea

sing

copp

er

conc

entra

tions

in r

ecen

t tim

es is

com

mon

ly ob

serv

ed in

sed

imen

ts o

f Sy

dney

Har

bour

, pe

rhap

s du

e to

the

con

tinue

d us

e of

cop

per-b

ased

an

tifou

ling

boat

pain

ts, w

here

as d

eclin

ing

lead

over

the

last 1

5 ye

ars

has

been

attr

ibut

ed to

the

intro

duct

ion

of u

nlea

ded

petro

l. Th

e m

ain s

ourc

e of

zin

c is

vehi

cular

em

issio

ns a

nd c

ompo

nent

wea

r and

is tr

ansp

orte

d to

th

e es

tuar

y by

stor

m w

ater

. Re

gion

al tre

nds

in

cont

amin

atio

n ha

ve

been

in

vest

igat

ed

by

the

Env

ironm

enta

l G

eolo

gy G

roup

in

the

Scho

ol o

f G

eosc

ience

s at

the

U

nive

rsity

of

Sydn

ey u

sing

a co

nsid

erab

ly lar

ger

core

dat

abas

e in

co

njun

ctio

n w

ith

seve

ral

vint

ages

of

su

rfac

e se

dim

ent

met

al co

ncen

tratio

ns fr

om a

bout

the

mid

-197

0s to

the

pres

ent.

Dat

a fr

om th

e co

res

and

surf

icial

sedi

men

ts s

how

tha

t, in

gen

eral,

con

cent

ratio

ns o

f m

etals

in b

otto

m se

dim

ent h

ave

been

dec

linin

g in

the

uppe

r par

ts o

f the

es

tuar

y, w

est o

f the

Syd

ney

Har

bour

Brid

ge, b

ut h

ave

been

incr

easin

g in

th

e lo

wer

har

bour

, in

Lane

Cov

e an

d M

iddl

e H

arbo

ur o

ver

the

last 2

5 ye

ars

(Birc

h &

Tay

lor 2

004)

. The

dec

reas

e in

met

al co

ncen

tratio

ns s

ince

th

e lat

e 19

70s

is co

nsist

ent w

ith th

e in

trodu

ctio

n of

the

Clea

n W

aters

Act

Page 12: Climatic change 7 A short geological and environmental

23

5

whi

ch re

quire

d in

dust

ry to

disc

harg

e w

aste

into

the

sew

erag

e sy

stem

and

to

redu

ce w

aste

gen

erat

ion.

A d

ecisi

on b

y in

dust

ry to

relo

cate

out

of t

he

Sydn

ey H

arbo

ur c

atch

men

t ove

r the

last

25

year

s has

also

con

tribu

ted

to

redu

ctio

n of

met

al flu

x to

the

har

bour

. Relo

catin

g in

dust

ry a

way

fro

m

high

-land

valu

e re

al es

tate

on

the

wat

er fr

ont w

ith h

igh-

dens

ity h

ousin

g ha

s un

doub

tedl

y als

o re

duce

d co

ntam

inan

t lo

ads

disc

harg

ed d

irect

ly to

th

e es

tuar

y. Th

e m

ove

has

also

chan

ged

appr

eciat

ion

of t

he h

arbo

ur

from

form

er w

orki

ng c

lass

subu

rbs t

o hi

gh-v

alue,

mid

dle

clas

s are

as, f

or

exam

ple

Balm

ain a

nd W

oolw

ich.

Incr

ease

d m

etals

co

ncen

tratio

n ov

er

the

sam

e 25

-yea

r pe

riod

in

sedi

men

ts o

f Lan

e Co

ve a

nd M

iddl

e H

arbo

ur h

ave

been

attr

ibut

ed to

a

rapi

d ex

pans

ion

of r

esid

entia

l an

d co

mm

ercia

l pr

oper

ty,

as w

ell a

s in

crea

sed

trans

port

serv

ices

in t

he C

hats

woo

d an

d N

orth

Ryd

e ar

eas

(Tay

lor,

Birc

h &

Li

nks

2004

). H

igh

conc

entra

tions

of

m

etals

in

se

dim

ents

of

river

s an

d cr

eeks

dra

inin

g th

ese

area

s su

ppor

t th

is vi

ew

(Birc

h &

Tay

lor 2

004)

.

Pres

ent s

tatu

s of

Por

t Jac

kson

Se

dim

ent i

n so

me

parts

of P

ort J

acks

on is

the

mos

t con

tam

inat

ed o

f any

ha

rbou

r w

orld

wid

e. Se

dim

ents

m

antli

ng

the

estu

ary

cont

ain

high

co

ncen

tratio

ns

of

a w

ide

rang

e of

co

ntam

inan

ts

over

ex

tens

ive

ar

eas,

inclu

ding

he

avy

met

als,

orga

noch

lorin

e pe

stici

des,

polyc

yclic

ar

omat

ic hy

droc

arbo

ns

(PA

Hs)

, po

lychl

orin

ated

bi

phen

yls

(PCB

s),

polyc

hlor

inat

ed d

iben

zo-p

-dio

xins

and

dib

enzo

fura

ns (

Birc

h &

Tay

lor,

1999

, 200

0; B

irch

et a

l 200

6; Ir

vine

& B

irch,

199

8; M

cCre

ady

et a

l 200

0).

The

orig

in o

f th

ese

subs

tanc

es c

an b

e br

oadl

y gr

oupe

d as

rela

ted

to

indu

stria

l act

iviti

es, p

ast a

nd c

urre

nt s

torm

wat

er d

ischa

rge

and

leach

ates

fr

om r

eclai

med

lan

d. T

he i

ndus

trial

sour

ce i

s du

e lar

gely

to h

istor

ical

poor

pra

ctice

s, w

here

as s

torm

wat

er a

nd le

acha

te s

ourc

es a

re p

ast

and

cont

empo

rary

. Ear

ly in

dust

ry w

as lo

cate

d on

the

sho

relin

e of

the

por

t fo

r co

nven

ience

and

che

ap d

elive

ry o

f ra

w m

ater

ials,

as w

ell a

s fo

r re

ducin

g ha

ulag

e co

sts

for

coal

to p

ower

sta

tions

. E

xpor

t of

hea

vy,

bulk

y m

anuf

actu

red

good

s w

as a

lso e

asy

and

inex

pens

ive

for

shor

e-ba

sed

indu

strie

s. Co

ntam

inat

ion

of

adjac

ent

sedi

men

t by

w

aste

as

socia

ted

with

the

mov

emen

t of

goo

ds,

and

from

che

ap d

ispos

al of

w

aste

dire

ctly

into

the

har

bour

, acc

ount

s fo

r m

ost

of p

ast

indu

stria

lly-

sour

ced

cont

amin

atio

n.

23

6

Sam

plin

g of

riv

ers

and

cree

ks

disc

harg

ing

to

Port

Jack

son

has

show

n th

at

stor

mw

ater

co

ntin

ues

to

prov

ide

large

qu

antit

ies

of

cont

amin

ants

, main

ly he

avy

met

als to

the

rece

ivin

g ba

sin. A

lthou

gh it

is

know

n th

at

cont

amin

ants

ar

e be

ing

sour

ced

from

w

aste

m

ater

ial

cont

ained

w

ithin

re

claim

ed

lands

su

rrou

ndin

g th

e ha

rbou

r, th

e m

agni

tude

of

this

supp

ly re

main

s un

quan

tified

, as

with

oth

er d

iffus

e so

urce

s, su

ch a

s atm

osph

eric

depo

sitio

n.

The

majo

rity

of t

hese

con

tam

inan

ts a

re a

ssoc

iated

with

the

par

ticul

ate

phas

e, bu

t the

pro

cess

es w

here

by th

ese

parti

cle-b

ound

con

tam

inan

ts a

re

trans

porte

d w

ithin

the

estu

ary

and

the

effe

cts

of th

ese

mat

erial

s on

flor

a an

d fa

una

are

poor

ly kn

own

and

are

the

subj

ect

of c

urre

nt s

tudi

es.

Rece

nt la

rge

ecot

oxico

logi

cal s

tudi

es (M

cCre

ady

et a

l 200

4; M

cCre

ady

et

al 20

05; M

cCre

ady,

Birc

h &

Lon

g 20

06; M

cCre

ady

et a

l 200

6a 2

006b

, 20

06c)

hav

e sh

own

that

sedi

men

t in

high

impa

ct a

reas

of t

he h

arbo

ur a

re

toxi

c to

som

e be

nthi

c an

imals

, as

was

pre

dict

ed b

y ea

rlier

inve

stig

atio

ns

of s

edim

ent q

ualit

y (B

irch

& T

aylo

r, 20

02a,

2002

b, 2

002c

). To

dat

e lit

tle

wor

k ha

s be

en d

one

on t

he t

rans

fer

of c

onta

min

ants

in

the

wat

er

colu

mn

and

botto

m s

edim

ent

to b

enth

ic an

d pe

lagic

anim

als,

term

ed

‘bio

accu

mul

atio

n’, o

r on

the

mov

emen

t of

the

se m

ater

ials

up t

he f

ood

chain

, call

ed ‘b

iom

agni

ficat

ion’

. E

arly

stud

ies d

etec

ted

high

tota

l PCB

con

cent

ratio

ns in

mul

let c

augh

t in

Port

Jack

son

(Woo

llard

& S

ettle

197

8), b

ut m

ean

valu

es a

ppea

r to

hav

e de

crea

sed

since

the

n (R

ichar

dson

198

5).

In a

mor

e re

cent

stu

dy o

f ch

lorin

ated

hy

droc

arbo

ns

in

the

tissu

e of

se

ven

fish

type

s, co

ncen

tratio

ns

exce

eded

N

atio

nal

Food

A

utho

rity

Max

imum

Re

sidue

Lim

its f

or t

wo

spec

ies i

n D

uck

Rive

r, H

omeb

ush

Bay

and

Ir

on C

ove

and

one

spec

ies i

n Pa

rram

atta

Riv

er (

Roac

h &

Run

cie

19

98).

Hig

h co

ncen

tratio

ns o

f po

lychl

orin

ated

dib

enzo

- p-d

ioxi

ns a

nd

polyc

hlor

inat

ed d

iben

zofu

rans

in

sedi

men

t in

Hom

ebus

h Ba

y ha

ve

resu

lted

in u

nacc

epta

bly

high

tiss

ue c

once

ntra

tion

in fi

n fis

h. In

198

9 fin

fis

hing

was

ban

ned

in t

he b

ay a

nd in

the

fol

low

ing

year

the

ban

was

ex

pand

ed to

incl

ude

the

who

le u

pper

third

of t

he h

arbo

ur. M

ore

rece

nt

mon

itorin

g sa

w t

he N

SW F

ood

Aut

horit

y po

sing

a 3-

mon

th b

an o

n co

mm

ercia

l fin

fish

ing

in th

e w

hole

harb

our

in D

ecem

ber,

2005

, whi

ch

in J

anua

ry t

he f

ollo

win

g ye

ar w

as e

xten

ded

to in

clude

pra

wn

traw

ling.

Page 13: Climatic change 7 A short geological and environmental

23

7

Thes

e ba

ns w

ere

mad

e pe

rman

ent

in F

ebru

ary

2006

. Bl

ood

test

s of

pr

awn

fishe

rmen

sho

wed

one

ind

ivid

ual

with

fou

r-tim

es t

he a

vera

ge

diox

in c

once

ntra

tions

and

his

son

with

sev

en ti

mes

ave

rage

leve

ls. O

ne

gran

dfat

her h

ad c

once

ntra

tions

10

times

ave

rage

valu

es. H

owev

er, t

hese

lev

els w

ere

not d

eem

ed d

etrim

enta

l to

hum

an h

ealth

. Stu

dies

con

tinue

to

dete

rmin

e th

e ex

tent

of

the

prob

lem a

nd h

ow b

est

to r

educ

e bo

ttom

se

dim

ent

conc

entra

tions

to

leve

ls w

here

fish

and

pra

wn

tissu

e lev

els

decli

ne to

acc

epta

ble

valu

es.

The

appr

opria

te a

nd su

cces

sful

gov

erna

nce

of th

is es

tuar

y re

quire

s hig

h-qu

ality

, scie

nce-

base

d in

form

atio

n. T

he c

urre

nt c

halle

nges

for

scie

ntist

s ar

e to

id

entif

y an

d qu

antif

y so

urce

s, un

ders

tand

th

e m

echa

nism

s co

ntro

lling

the

fat

e of

con

tam

inan

ts,

dete

rmin

e th

e ef

fect

s of

the

se

subs

tanc

es o

n liv

ing

reso

urce

s an

d co

nstru

ct m

anag

emen

t to

ols

base

d on

rob

ust

scie

nce.

Mod

ellin

g th

e so

urce

, fa

te a

nd e

ffect

s of

the

se

cont

amin

ants

in P

ort J

acks

on w

ill e

nabl

e m

anag

ers a

nd p

lanne

rs to

mak

e de

cisio

ns o

n su

ch is

sues

as

stor

mw

ater

rem

ediat

ion

optio

ns, r

elaxa

tion

times

(nat

ural

clean

up),

and

the

amou

nt o

f dr

edgi

ng r

equi

red

to r

educ

e tis

sue

conc

entra

tions

to

acce

ptab

le lim

its a

nd t

o se

t m

axim

um d

aily

load

ing

for

cree

ks e

nter

ing

the

wat

er w

ay. I

n re

cent

tim

es, c

onsid

erab

le ef

fort

has

resu

lted

in r

educ

ed i

ndus

trial

was

te e

nter

ing

Port

Jack

son.

N

ow is

an

appr

opria

te t

ime

to in

itiat

e a

new

con

certe

d en

viro

nmen

tal

effo

rt to

ins

tall

seco

nd g

ener

atio

n re

med

ial d

evice

s to

red

uce

curr

ent

stor

mw

ater

con

tam

inan

t inp

uts.

It is

also

time

to u

nder

take

app

ropr

iate

rem

edial

wor

k in

the

cat

chm

ent

and

in t

he e

stua

ry t

o re

stor

e th

e

harb

our

to a

con

ditio

n in

whi

ch it

can

sup

port

a co

mpl

ete

and

healt

hy

ecol

ogica

l com

mun

ity.

Ack

now

ledge

men

ts

Fund

ing

for

210 P

b an

d 13

7 Cs

radi

oiso

topi

c da

ting

of s

edim

ent c

ores

was

pr

ovid

ed b

y th

e A

ustra

lian

Inst

itute

of N

uclea

r Scie

nce

and

Tech

nolo

gy.

The

auth

ors

than

k H

enk

Heij

nis

and

And

rew

Je

nkin

son

of

the

Env

ironm

enta

l Rad

ioiso

tope

Lab

orat

ory

at A

ustra

lian

Nuc

lear

Scien

ce

and

Tech

nolo

gy O

rgan

isatio

n, L

ucas

Heig

hts

for

thei

r ad

vice

with

ra

dioi

soto

pic

datin

g. T

he a

utho

r th

anks

Mar

co O

lmos

for

dra

fting

the

fig

ures

to

this

man

uscr

ipt

and

to P

hil M

cMan

us f

or c

omm

ents

on

an

early

dra

ft of

the

man

uscr

ipt.

23

8 Refe

renc

es

Ang

lin a

nd A

ssoc

iates

, 19

90.

Sydn

ey H

arbo

ur:

Mar

itime

Serv

ices

Boar

d H

erita

ge an

d Co

nserv

ation

Regi

ster:

Hist

ory,

vol

1, A

nglin

Ass

ociat

es,

Sydn

ey.

Barr

y S

C, T

aylo

r S

E &

Birc

h G

F,

1999

. ‘H

eavy

met

als i

n ur

ban

stor

mw

ater

can

als e

nter

ing

Port

Jack

son,

Aus

tralia

and

their

impa

ct

on

the

estu

arin

e en

viro

nmen

t’,

Proc

eedi

ngs

of

the

Eig

hth

Inte

rnat

iona

l Con

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Sto

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Sydn

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E &

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001.

‘Hea

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Po

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n E

stua

ry, A

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lia b

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wat

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Aus

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Wat

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54.

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99.

‘Sou

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Aus

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the

Eig

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Inte

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Stor

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Sydn

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999.

‘Sou

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mph

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on

cent

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New

So

uth

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s es

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ies

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cont

inen

tal

mar

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tiona

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‘The

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chlo

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ban

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Port

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‘Pos

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se

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Po

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Sydn

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Aus

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‘Ass

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diox

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NSW

Dep

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he ci

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Mun

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a. ‘G

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s af

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leach

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com

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rom

soi

ls in

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laim

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and

usin

g lab

orat

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fres

hwat

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nd s

aline

wat

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n ex

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’, M

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d Fr

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4, p

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93.

Suh

J, Br

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F, 2

003b

. ‘H

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geoc

hem

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char

acte

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s an

d im

porta

nce

of n

atur

al an

d an

thro

poge

nic

influ

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s on

soil

and

grou

ndw

ater

in a

rec

laim

ed la

nd a

djac

ent t

o Po

rt Ja

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n, S

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Mar

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reshw

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Resea

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4, p

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79.

Suh

J, Bi

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004a

. ‘Sp

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rec

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the

venu

e of

the

2000

Oly

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c G

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, Syd

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New

Sou

th W

ales’,

A

ustra

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f Ear

th S

cienc

es, v

ol. 5

1, p

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24

3

Suh

J, Bi

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G F

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s K

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4b. ‘

Hyd

roch

emist

ry in

rec

laim

ed

lands

of t

he 2

000

Olym

pic

Gam

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ite, S

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y, A

ustra

lia’,

Jour

nal o

f Co

asta

l Rese

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, vol

. 20,

no.

3, p

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09–7

21.

Taylo

r S

E,

2000

. Th

e so

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and

rem

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satio

n of

con

tam

inat

ed

sedi

men

t in

Por

t Ja

ckso

n, A

ustra

lia. P

hD t

hesis

, the

Uni

vers

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f Sy

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, Syd

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Taylo

r S

E, B

irch

G F

, & L

inks

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004.

‘Hist

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l cat

chm

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hang

es

and

tem

pora

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pact

on

sedi

men

t of

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rec

eivin

g ba

sin,

Port

Jack

son,

New

Sou

th W

ales’,

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n Jo

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l of E

arth

Scie

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vol

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2, p

p. 2

33–2

46.

Thom

B

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P S,

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85.

‘Rela

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d co

asta

l se

dim

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tion

in s

outh

east

Aus

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Hol

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e’, J

ourn

al of

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ry Pe

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l. 55

, pp.

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. W

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G P

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3. ‘T

he G

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g in

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1788

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51’,

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Hist

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vol.

3, n

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, pp.

20–

52.

Web

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971.

‘Loc

atio

n of

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ufac

turin

g gr

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with

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e m

odel

for S

ydne

y 19

54–1

966’

, Roy

al A

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lian

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ning

In

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te Jo

urna

l, vo

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pp.

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oolla

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H, 1

978.

‘PCB

resid

ues

in m

ullet

, Mug

il cep

halus

fed

to c

aptiv

e E

aste

rn A

ustra

lian

wat

er r

ats,

Hyd

romy

s ch

rysog

aster

’, Bu

lletin

of E

nviro

nmen

tal C

onta

mina

tion

and

Toxi

colog

y, vo

l. 20

, pp.

606

–61

2.

Zan

n L

P, 1

996.

‘Th

e st

ate

of t

he m

arin

e en

viro

nmen

t re

port

for

Aus

tralia

(SO

ME

R). P

roce

ss, f

indi

ngs

and

pers

pect

ive’,

Ocea

n an

d Co

asta

l Man

agem

ent,

vol.

33, p

p. 1

–3 &

63–

86.

24

4 8 Ene

rgy

from

offs

hore

win

d: a

n ov

ervi

ew

Don

g-Sh

eng

Jen

g an

d Y

un

Zh

eng

Abs

tract

Re

new

able

ener

gy

has

attra

cted

a

grea

t de

al of

at

tent

ion

amon

g go

vern

men

ts, i

ndus

tries

, aca

dem

ics a

nd s

ociet

ies t

hrou

ghou

t th

e w

orld

in

rece

nt ti

mes

. Offs

hore

win

d en

ergy

is a

rene

wab

le en

ergy

sou

rce

that

ha

s gr

eat

pote

ntial

in

en

ergy

m

arke

ts

wor

ldw

ide

as

our

curr

ent

know

ledge

of

offs

hore

eng

inee

ring

tech

nolo

gy m

akes

it

read

y fo

r im

plem

enta

tion

imm

ediat

ely.

In t

his

chap

ter,

offs

hore

win

d en

ergy

is

com

pare

d w

ith o

ther

ren

ewab

le en

ergy

sou

rces

, and

exi

stin

g of

fsho

re

win

d en

ergy

pro

jects

thro

ugho

ut th

e w

orld

are

revi

ewed

. Cur

rent

des

ign

code

s of

offs

hore

win

d en

ergy

are

out

lined

and

a s

et o

f cr

iteria

for

the

selec

tion

of a

ppro

priat

e sit

es fo

r offs

hore

win

d en

ergy

is e

stab

lishe

d fo

r A

ustra

lia. F

inall

y, po

tent

ial s

ites

in A

ustra

lia a

re e

valu

ated

and

bas

ed o

n ou

r an

alysis

, the

sou

ther

n pa

rt of

Wes

tern

Aus

tralia

(W

A)

is th

e m

ost

appr

opria

te si

te fo

r win

d fa

rms.

Intro

duct

ion

Due

to th

e w

orld

’s ris

ing

ener

gy c

onsu

mpt

ion,

lim

ited

exist

ence

of f

ossil

en

ergy

so

urce

s an

d dr

amat

ic ch

ange

s to

th

e w

orld

’s cli

mat

e, th

e ex

tens

ion

of r

enew

able

ener

gy h

as d

raw

n a

grea

t dea

l of a

ttent

ion

from

go

vern

men

ts,

indu

strie

s an

d ac

adem

ics w

orld

-wid

e. Re

new

able

ener

gy

has

cons

ider

able

pote

ntial

and

cou

ld t

heor

etica

lly p

rovi

de a

nea

rly

unlim

ited

supp

ly of

rela

tively

clea

n an

d m

ostly

loca

l ene

rgy.

Rece

ntly,

gl

obal

rene

wab

le en

ergy

sup

ply

has

been

gro

win

g st

rong

ly; t

he a

nnua

l gr

owth

for

win

d en

ergy

, fo

r ex

ampl

e, ha

s be

en a

roun

d 30

per

cen

t re

cent

ly, fr

om a

ver

y lo

w b

ase

of 6

.29

per c

ent o

f tot

al re

new

able

ener

gy

reso

urce

s. In

rela

tive

term

s, ho

wev

er, t

he s

hare

of

mod

ern

rene

wab

le