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L1, 23 UnioPO Box 375
T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Grey
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and a m
monitor
are pres
Figure 1
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in data o
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ytown W
water flowsting discharg
maximum flow
red continuo
sented below
– Pond Influe
e years there
or potentially
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noticed, du
11 days from
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ring individu
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nd Central, Auckl51, New Zealand
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Wastew
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ent and Efflue
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ted in Janu
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ual years, the
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and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
ater TreQ
s allows for an
m3 per day to
operator1. F
nt Flow volum
several malf
data. These
ary 2011 an
sidered susp
riod a numb
26th of Decem
f January 20
1st of March
e compliance
red following equ000m
3 from Augu
Refer below for aZealand
10 Reports\Greytown
eatmenQuality
average disc
o the Papawa
Flow volume
mes between
functions of
e have been
nd the mete
pect and has
ber of spikes
mber 2011,
014.
2014.
e with discha
uipment failure inst 2011 has beenadditional detail.
Resource Consent App
nt Plant Review
charge volum
ai Stream. In
es recorded b
Jan 2009 and
the outlet m
documented
er was repla
s been remo
in data wer
arge limits is
n late 2011 and wn removed for pre
plication\GWWTP AEE
Effluenw
me of 1,350
nfluent and
between Jan
d Jun 2014
meter that ha
d to have occ
aced in Mar
ved. The iss
re recorded.
shown in the
which has been reesentation purpo
Final\Appendix 6 – MM
nt Quan
m3 per day (
effluent flow
nuary 2009 a
ave resulted
curred for:
rch 2011. D
sue was not
.
e following t
eplaced by outflooses. The result w
M_GWWTP Effluent Q
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tity and
annual mean
w volumes ar
and June 201
d in small gap
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w monitoring. was due to a pum
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L1, 23 UnioPO Box 375
T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Table 1 –
2009‐2
2010‐2
2011‐2
2012‐2
2013‐2Notes: *replacemfaulty pe
Across t
Table 2 –
Average
Median
Max dai
Summer
Winter d
Notes: co
It has b
contribu
understo
flows m
average
reasona
WastewConditioStream. based othe com
Table 2 ‐
Yea
Standa
2009‐2
2010‐2
2011‐2
2012‐2
2013‐2Notes: *
table pre
3 R. P. a. B.Treatment
on Street, Aucklan525, Auckland 11
374 1599 W wwwald New Zealand LimiteZL\Projects\1250_Comug14.docx
– GWWTP Ann
2010
2011*
2012
2013
2014 * As noted ament of the mriod may have
he period pr
– GWWTP Flo
e daily discha
Daily Discha
ly discharge
r daily averag
daily average
ount = 1914, *
been determ
uted to by in
ood that up
may be attrib
per capita
ble for typic
water Quaon 20 of the The measun 40 consec
mpliance resu
Flow monito
ar
Ge
rd
2010
2011
2012
2013
2014 Running Geo
esents the ave
. Ellwood, “Chapt
Collective, 2000,nd Central, Auckl51, New Zealand
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nual Flow mo
Averag
790
826
676
645
693 bove there w
meter. During e in fact comm
resented the
w monitoring
Ac
arge* 77
arge 65
7,
ge 70
e 84
* again it may
mined that a
nflow and in
to 42% of t
butable to I/
flows in Gr
al domestic
ality consent outurement of cutive samplults against C
oring data of d
TSS
omean
45
31
36
38
38
41 ometric mean
erage of these
ter 1: Sewage Eff
, pp. 1‐20. and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
onitoring stati
ge Max
17
66
31
16
19was a fault nthis faulty pemenced earlie
e flow monito
g data statisti
ctual
72m3 (728m3
56 m3 (648m3
018 m3 (6,67
03 m3 (605m3
47 m3 (847m3
be argued th
a reasonable
filtration (I/
the average
/I. This is n
reytown (39
wastewater
tlines the effcompliance es collected Condition 20.
discharge qua
90%ile
90
66
70
70
70
78 and 90th perc
e results for ea
luent Characteris
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istics for year
ximum C
769
670
141
665
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94 L/per/d)
schemes (21
fluent qualityis based onon monthly.
antities from G
B
Geomean
30
32
32
31
27
28 centile is base
ach monitorin
stics,” in New Zea
Resource Consent App
rs 2009 – 2014
Compliance
Yes
No
Yes
Yes
Yes the outlet meer of high reay thought and
s indicate th
ary 2009 to Ju
Consent limi
1,350m3
6,600m3
may have been
f inflow and
e network. B
entering the
mmon probl
are at the
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BOD
90%ile
60
56
53
51
43
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aland Guidelines f
plication\GWWTP AEE
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eter in early adings were md may have sta
e following:
une 2014
t Comp
Yes
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n related to th
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Based on th
plant and u
em in aging
higher end
er/d)3.
nts, prior to geometric med in Condit
e 2009 – June 2
Geome
5000
282
370
481
593
583 secutive samp
for Utilisation of S
Final\Appendix 6 – MM
2011 that rmade and wearted late 201
pliance achie
he faulty outf
low from th
eoretical ca
p to 61% of
g networks,
of the rang
discharge tomean and 9tion 18. Tab
2014
FC
ean 90
0 25
13
13
30
32
32ples collected
Sewage Effluent,
M_GWWTP Effluent Q
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resulted in the note that th10.
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low meter.
he GWWTP
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mpliance wit
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parameters.
Suspended
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th the geome
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and 1010, New Z
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ean BOD has
n collecting
fluent qualit
cument. The
SS)
January 200
age of 63mg
e seasonal va
algae growt
nal Assessm
erage conce
in the Opus
ncentrations (
nment, Effluent DWTP, May 2013.
Zealand
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s occurred du
effluent qu
ty data coll
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09 for TSS c
g/L. There is
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January 20
ess more clos
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ffects (AEE) p
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nt report.
uary 2009 to J
Ponds to Papaw
Final\Appendix 6 – MM
riod 2009 – 2
ntly than m
009 to June
sely the diff
the pond ef
reasing or d
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S concentrat
prepared by
to be correla
June 2014(full
wai Stream, Septe
M_GWWTP Effluent Q
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2012.
onthly, and
2014 is als
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ffluent range
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mber 1998.
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T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Figure 3
Total B
Monitoreffluent 118mg/
HoweveperformincreaseSimilarlythe warm
Figure 4
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374 1599 W wwwald New Zealand LimiteZL\Projects\1250_Comug14.docx
– GWWTP Su
BOD5
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er when commance declineed sludge acy to TSS, themer months
– BOD concen
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uspended sedi
sessed fromthe past fiveerage of 42m
mpared agaie in BOD5 efcumulation ere is some sand dilution
ntrations (mg
and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
iment concen
m January 20e and a half
mg/L (summe
nst the BECffluent conceand hence rseasonal varn during wint
g/L) from GWW
Zealand
10 Reports\Greytown
tration comp
009 for BODf years. Poner average of
CA (1998) asentration froreduced hydiability in BOter as a resu
WTP; January
Resource Consent App
liance (mg/L)
D5 concentratnd effluent Bf 48mg/L and
ssessment, tom the ponddraulic retenOD5, again mlt of inflow a
y 2009 to June
plication\GWWTP AEE
); June 2009 to
tions indicatBOD5 concend winter aver
there appeads. This is lition time in
most likely duand infiltratio
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Final\Appendix 6 – MM
o June 2014
tes a decreantrations ranrage of 33mg
ars to have ikely to be an the ponds ue to algae gon.
dataset)
M_GWWTP Effluent Q
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asing trend nge from 11g/L).
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T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Figure 5
Opus (20
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OD concentrat
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sessed fromperformance00 (no./100mo be attribue ponds (Opht improvemariability in pion is at its h
rt ‐ Greytown WWusted the calcula
and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
tion complian
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data, and co
ter tempera
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can be unde
m January 20e over the pmL) with an autable to incus, 2013). Cent in faecalpathogen rehighest.
WTP, May 2013ations in light of n
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nce (mg/L); Ju
assessment
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une 2009 to Ju
of the BOD
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account for
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.
plication\GWWTP AEE
une 2014
loading to th
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numbers inrs. Pond effedian of 570.lation and ECA (1998) a, although thents seen ove
Final\Appendix 6 – MM
he Greytown
f Pond 1 is a
g BOD load o
n provided b
unlikely to b
ndicate a sligfluent patho. This declinhence reduassessment, the log reducter summer
M_GWWTP Effluent Q
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approximate
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T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Figure 6
Recent mof geomSWDC apathoge
Figure 7
Other P
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by the c
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374 1599 W wwwald New Zealand LimiteZL\Projects\1250_Comug14.docx
– Faecal Colif
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– Faecal Colif
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form count fro
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form Complia
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strict Counci
analysis of th
and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
om GWWTP; J
aecal counts percentile pa UV disinfearge to wate
ance from GW
l have also s
hese results
Zealand
10 Reports\Greytown
January 2009
indicate comperformanceection planter and land.
WWTP; June 20
ampled a nu
is presented
Resource Consent App
9 to June 2014
mpliance withe (3,240 MPNt on the out
009 to June 20
umber of oth
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plication\GWWTP AEE
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014
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et)
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ers which are
M_GWWTP Effluent Q
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T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Total Ni
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Figure 8
Ammon
The resp
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Monitor
improve
to the lo
resulted
0.01 – 2
16.1mg/
the BECA
on Street, Aucklan525, Auckland 11
374 1599 W wwwald New Zealand LimiteZL\Projects\1250_Comug14.docx
itrogen (TN)
ring data assd in effluent9.4 (mg/L) w/L). There h1998) assessmmer monthe ponds cau
– Total Nitrog
niacal Nitrog
ponse in Am
with improvi
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ement has oc
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28.4 (mg/L)
/L). There h
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sessed from t TN over thewith an avehas also beenment. Therhs most likesed by algae
gen concentra
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mmoniacal N
ng nitrogen
ssessed from
ccurred in ef
ny spells we
mprovement
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has also bee
essment.
and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
January 200e past five aerage of 20mn little changre is seasonaly due to ene growth, and
ations (mg/L)
itrogen in th
removal in s
m January
ffluent qualit
e have exper
in ammonia
erage of 11.5
n little chan
Zealand
10 Reports\Greytown
09 for TN cond a half yemg/L (summge in TN efflal variabilitynhanced ammd nitrogen up
) from GWWT
he effluent
summer com
2009 for e
ty over the p
rienced in 2
a stripping.
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ge in NH4‐N
Resource Consent App
oncentrationars. Pond e
mer average luent conceny in TN concmonia strippptake by the
TP; January 20
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mpared with
effluent NH4
past five and
012/2013 an
Pond efflue
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effluent co
plication\GWWTP AEE
ns indicate reffluent TN coof 16.5mg/ntrations whcentrations, ping in summe pond’s biom
009 to June 20
concentratio
winter as e
4‐N concent
a half years.
nd 2013/201
ent NH4‐N co
ge of 6.5mg/
ncentrations
Final\Appendix 6 – MM
elatively littoncentration/L and wintehen comparewith improv
mer months mass.
014(total data
ons with obv
expected in p
trations indi
. This may b
14 which is
oncentration
g/L and wint
s when com
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aset)
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T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Figure 9
Total Ph
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from 2.5
4.8mg/L
quality i
(algae u
against t
Figure 10
on Street, Aucklan525, Auckland 11
374 1599 W wwwald New Zealand LimiteZL\Projects\1250_Comug14.docx
– Ammoniaca
hosphorus (T
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57 – 11.9 (m
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998) assessm
sphorus conce
and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
oncentrations
January 2009
over the pas
average of
rates a seas
nths, likely d
has also bee
ment.
entrations (m
Zealand
10 Reports\Greytown
s (mg/L) from
9 for effluen
st five and a
5.16mg/L (su
onal variatio
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en little chan
mg/L) from GW
Resource Consent App
GWWTP; Jan
t TP concent
half years. P
ummer aver
on in TP con
ase algae gro
nge in TP eff
WWTP; Januar
plication\GWWTP AEE
nuary 2009 to
trations indic
Pond effluen
age of 5.6mg
centrations
owth in the d
fluent concen
ry 2009 to Jun
Final\Appendix 6 – MM
o June 2014(to
cate a slight
nt TP concent
g/L and wint
with a decli
discharge du
ntrations wh
ne 2014(total
M_GWWTP Effluent Q
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otal dataset)
improvemen
trations rang
ter average o
ne in effluen
uring this tim
hen compare
dataset)
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T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Dissolve
The resp
DRP con
January
quality o
with an
Figure 11
Tempera
Figure 12
on Street, Aucklan525, Auckland 11
374 1599 W wwwald New Zealand LimiteZL\Projects\1250_Comug14.docx
ed Reactive P
ponse in DRP
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2009 for ef
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1 – DRP conce
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2 – Temperatu
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w.mottmac.com ed Registered in New Zmbined_Scheme_Revie
Phosphorus
P in the efflu
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ffluent DRP c
t five and a h
4.32mg/L (su
entrations (mg
ure from GWW
and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
(DRP)
uent mimics
er as would b
concentratio
half years. P
mmer avera
g/L) from GW
WTP; January
Zealand
10 Reports\Greytown
TP concentr
be expected
ons indicate
Pond effluent
age of 4.9 mg
WWTP; Januar
y 2009 to June
Resource Consent App
rations with
in pond sys
a marked im
t DRP concen
g/L and winte
ry 2009 to Jun
e 2014(total d
plication\GWWTP AEE
obvious seas
tems. Monit
mprovement
ntrations ran
er average o
ne 2014(total
dataset)
Final\Appendix 6 – MM
sonal trends
toring data a
t has occurr
nge from 1.3
of 3.5 mg/L).
dataset)
M_GWWTP Effluent Q
Pag
s of improvin
assessed fro
ed in effluen
4 – 6.6 (mg/
uality
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ng
m
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/L)
L1, 23 UnioPO Box 375
T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
Conduct
Figure 13
Dissolve
Figure 14
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374 1599 W wwwald New Zealand LimiteZL\Projects\1250_Comug14.docx
tivity
3 – Conductivi
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4 – Dissolved
nd Central, Auckl51, New Zealand
w.mottmac.com ed Registered in New Zmbined_Scheme_Revie
ity from GWW
Oxygen from
and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
WTP; January
GWWTP; Jan
Zealand
10 Reports\Greytown
y 2009 to June
nuary 2009 to
Resource Consent App
e 2014(total d
o June 2014(to
plication\GWWTP AEE
ataset)
otal dataset)
Final\Appendix 6 – MMM_GWWTP Effluent Q
Page
uality
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L1, 23 UnioPO Box 375
T +64 (0)9 3Mott MacDonaP:\Auckland\NAssessment_A
pH (labo
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In regar
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over the
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GWWTP; Janu
G)
and Grease fro
erature, Con
ures 12 – 16
he Beca (199
ears, whilst
ity.
and 1010, New Z
Zealand no. 3338812 ew\500 Deliverables\51
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GREYTOWN WWTP EFFLUENT DATA SUMMARY
S.S. Total Solids BOD5 Total BOD Soluble NH3-N TP DRP TN F.C. E.Coli pH Temp Conductivity DO TOG Outflow
mg/L mg/L mg/L m3/d
Minimum 8.0 13.0 11.0 1.5 0.01 2.57 1.34 8.37 8 8 6.4 6.9 231.0 0.1 2.5 0
Average 63.1 312.0 42.3 7.2 11.53 5.16 4.32 20.08 2317 1568 7.9 15.1 365.1 5.2 6.5 728
25%ile 36.3 259.0 24.0 3.0 5.00 4.27 3.17 14.60 260 138 7.5 10.5 308.1 1.8 2.5 508
Median 56.5 315.0 38.0 5.0 12.50 5.23 4.30 18.90 570 400 7.7 15.5 349.6 4.3 2.8 648
75%ile 77.5 367.0 56.1 8.0 17.40 5.89 5.50 26.30 2027 1253 8.1 19.1 418.4 7.7 7.8 867
90%ile 109.0 409.8 75.4 12.0 22.84 6.68 6.07 29.04 4240 3110 8.8 21.9 471.8 11.3 12.7 1144
Maximum 292.0 720.0 118.0 59.0 28.40 11.90 6.60 39.40 33000 22000 9.8 26.2 536.0 18.8 32.7 6670
Count 170 87 167 87 133 133 170 133 167 130 107 102 102 106 20 1824
Summer (Nov - Apr) S.S. Total Solids BOD5 Total BOD Soluble NH3-N TP DRP TN F.C. E.Coli pH Temp Conductivity DO TOG Outflow
TRUE m3/d
Average 73.0 350.8 48.5 8.6 6.5 5.6 4.9 16.5 1860 827 8.1 19.5 407.9 5.9 3.9 605
25%ile 49.8 310.0 29.0 3.0 1.3 4.8 4.1 11.4 215 110 7.6 17.9 349.3 1.8 2.5 432
Median 65.0 360.5 46.0 5.0 6.2 5.5 5.0 15.7 500 300 7.8 19.2 412.1 4.8 2.5 574
75%ile 80.5 384.5 62.2 8.3 10.7 6.2 6.0 19.9 1844 900 8.5 21.6 455.7 8.3 6.0 731
90%ile 128.5 417.3 82.4 15.2 13.2 7.1 6.2 24.1 3920 1400 9.1 22.9 484.9 13.9 6.2 905
Count 100 40 97 40 63 63 100 63 99 62 48 47 47 48 9 890
Winter(May - Oct) S.S. Total Solids BOD5 Total BOD Soluble NH3-N TP DRP TN F.C. E.Coli pH Temp Conductivity DO TOG Outflow
FALSE m3/d
Average 49.1 278.9 33.5 6.0 16.1 4.8 3.5 23.3 2982 2244 7.7 11.4 328.5 4.6 8.6 847
25%ile 26.5 226.0 21.3 3.0 13.2 3.8 2.6 18.7 340 200 7.5 8.8 293.4 1.5 2.5 585
Median 43.5 273.0 29.0 4.0 16.9 4.6 3.4 24.4 710 565 7.7 10.6 317.0 4.1 3.0 752
75%ile 69.5 331.0 41.8 6.5 21.4 5.6 4.3 27.5 2600 2000 7.9 13.7 358.6 6.8 11.3 998
90%ile 87.2 377.4 58.0 9.4 23.7 6.1 5.2 29.8 7354 4090 8.3 15.9 398.5 9.6 14.0 1303
Count 70 47 70 47 70 70 70 70 68 68 59 55 55 58 11 934
Notes:
‐ Only data from 2009 onwards has been used
‐ We have deleted all F.C. and E.Coli values <=10 because these results seemed unrealistic.
‐ Approximately 6.5 years of overlapping quality and flow data from March 2005 ‐ June 2013
‐ TP effluent quality data prior to May 2009 has been excluded as looks eroneous
GREYTOWN MASS LOADS
SS BOD TN NH4‐N TP DRP
Annual Mass Load kg/yr 16777 11228 5334 3064 1370 1148
Daily Mass Load kg/d 46.0 30.8 14.6 8.4 3.8 3.1
Summer Mass Load kg/summer 8056 5358 1818 715 617 537
Summer Daily Load kg/d 44.1 29.4 10.0 3.9 3.4 2.9
Winter Mass Load kg/winter 7585 5184 3604 2486 736 549
Winter Daily Load kg/d 41.6 28.4 19.7 13.6 4.0 3.0
The above mass load information has been based on average effluent concentrations and average flow rather than a detailed analysis of daily loads.
All Year
mg/L No./100mL
mg/L No./100mL
mg/L No./100mL