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Annex 1
Overview of the spatial analyses and data sources
This annex briefly describes the processing steps used to create the results of the spatial analyses presented in this technical paper.
1. Hardware and softwareThe GIS software used in this study was Manifold (CDA International Ltd.) and ArcGIS 9.3 (ESRI). Manifold, versions up to 8.0.27, was used because it is a very affordable (currently about one-fifth of the cost of the most widely used GIS software) but fully functional GIS. ArcGIS 9.3 was used to prepare the raw data and to perform more complex analysis.
The text below describes the conceptual steps necessary to replicate the analysis described in this technical paper. Readers should be aware that most of the ArcGIS analysis could not be done with the standard ArcGIS tools, and, therefore, required custom VBA (Visual Basic for Applications) functions (i.e. codes) were required to conduct the analysis. The VBA computer codes written for this technical paper are available upon request from the authors of this technical paper, but they will only be useful to readers using ArcGIS with VBA installed and licensed.
2. Spatial dataSpatial data used for this technical paper were: (i) exclusive economic zones (EEZ); (ii) bathymetry; (iii) current speeds; (iv) world ports; (v) sea surface temperature (SST); (vi) chlorophyll-a; (vii) marine protected areas; (viii) Global Administrative Area from the GADM database; and (ix) geographic zones (see Table A1.1 for details).
All data sets used in this study are presented in Section 4 of this Annex and are available for download in FAO’s GeoNetwork portal (www.fao.org/geonetwork). 3. Spatial analysisThis study identifies areas that satisfy criteria for offshore mariculture development. The criteria include the suitability of depth and current speed for sea cages and longlines, and the temperatures favouring grow-out of representative species: cobia (Rachycentron canadum), Atlantic salmon (Salmo salar) and blue mussel (Mytilus edulis), as well as chlorophyll-a concentration for the last species.
There were two important limitations to this study. First, only already-digitized or computer-ready data could be used for the analysis to save costs, and second, because offshore mariculture potential is being predicted for areas where it largely does not yet exist, verification was limited to using the location of a few offshore fish farms and relied mainly on comparisons of offshore potential with existing inshore mariculture. Another limitation was that the data had to be comparable for all maritime countries. In overview, this study consisted of three major analytical stages (Figure A1.1):
(i) data preparation;(ii) integration of data sets; and(iii) verification.
86 A global assessment of offshore mariculture potential from a spatial perspective
3.1 Data preparationVarious aspects of this analysis required analysing and processing data in both raster and vector formats. The general strategy with raster data was to do all analysis at the finest resolution of the data, and then to convert the final to vector format for further analysis. For example, if a particular analysis was required to identify regions that met thresholds using multiple rasters, then the new raster that was generated would have the same resolution as the finest resolution of the multiple input rasters. The new raster would then be converted to a polygon feature class7 for further analysis.
7 A polygon feature class is a geographic data set of polygonal vector objects (i.e. entities that cover an area, such as administrative units or analysis areas), plus associated attribute information for each polygon. Other examples of vector data sets include polyline feature classes (containing linear features such as roads or rivers) and point feature classes (containing such things as port locations).
FIGURE A1.1Major analytical stages
Note: Fail acknowledges that verification could be incomplete, or in some cases fail.Note: Areas with potential within EEZs, but presently outside of cost-effective areas for development were estimated by setting aside the cost-effective area for development (see Table 1, Criterion 4).
87
EEZ boundaries to define the spatial limits for near-future offshore developmentExclusive economic zone boundaries were taken from the Flanders Marine Institute (Vlaams Instituut voor de Zee, or VLIZ) data, Version 5.
Depth and current speed to define the spatial limits on offshore cages and longlinesRegions suitable for offshore cages and longlines were defined according to current speed and depth (Figures A1.2–A1.3) based on data from manufacturers and mariculture practice (Table A1.2 (depth) and A1.3a (current speed).
FIGURE A1.2Steps to define spatial limits on offshore cages and longlines
based on depth and current speed
Annex 1
88 A global assessment of offshore mariculture potential from a spatial perspective
Depth: bathymetric data were extracted from the 2008 version of General Bathymetric Chart of the Ocean (GEBCO), which is a raster data set with cell edge lengths of approximately 0.9 km. In all analyses using this bathymetric data, regions with depths in the desired ranges were converted to polygon feature classes for further analysis.
Horizontal cell size: the GEBCO bathymetric data had 43 200 columns covering 360 degrees of longitude (40 075 km equatorial circumference). This equals to 0.92766 km per cell width along the equator. This east-west distance decreases when moving towards the poles. The extreme north and south rows that actually had data were < 1 metre in width.
Vertical cell size: the GEBCO bathymetric data had 21 600 rows covering 180 degrees of latitude (20 004 km from the North Pole to South Pole), equal to 0.92611 km per cell. This north-south distance is constant for all cells.
Current speed: the current speed data (from HYCOM, representing current speed at 30 m depth) included separate monthly data sets over a 5-year period from 2004 to 2008. Therefore, data were pooled by month before calculating the confidence intervals. Note: the original HYCOM current speed units are in metres per second, so
FIGURE A1.3HYCOM current speed confidence intervals subprocess
89Annex 1
these values were converted to centimetres per second for the final threshold analysis. Summarized monthly mean, standard deviation and upper/lower 95 percent confidence limits for current speed were calculated as follows:
Horizontal cell size: HYCOM current speed data had 4 500 columns covering 360 degrees longitude (40 075 km equatorial circumference). This equals 8.90556 km per cell width along the equator. This east-west distance decreases when moving towards the poles. The extreme north and south rows that actually had data were < 2 km in width.
Vertical cell size: HYCOM current speed had 2 100 rows covering approximately 168 degrees latitude (~18,665 km from North Pole to –78°), equal to 8.88810 km per cell. This north-south distance is constant for all cells.
Distance from a port and reliable access to offshore spatially define the cost-effective area for offshore mariculture development
Cost-effective areas around ports: several steps were conducted to identify regions that were within 25 nm (46.3 km) of a port, intersected with depth range, current speed and VLIZ exclusive economic zone (Figure A1.4).
90 A global assessment of offshore mariculture potential from a spatial perspective
•Beginning with the 2009 World Port Index, 25 nm (46.3 km) buffer circles were first created around each port location using a custom VBA function. This function creates circles with 180 vertices distributed every 2° around the circle. Each vertex is created a specified distance and bearing from the port, and the new vertex locations are calculated accurately over the curved surface of the planet spheroid using spherical trigonometric functions so that the circles are undistorted by any projection issues.
•This study was only interested in the marine portion of the port buffers, so all land portions were clipped off based on Global Administrative Areas (GADM) polygons.
•This study was only interested in the portion of the port buffers that were within 25 nm travel distance from the ports, so the port buffers were further clipped to this region using a custom VBA function to create a cost-distance raster over each GADM-clipped port buffer polygon. This function calculates the cumulative distance from the port location, where travel is restricted to only the water. Note: this function is reasonably accurate but not perfect. Because of how cost-
FIGURE A1.4Steps to define cost-effective areas around ports
91Annex 1
distance functions work with raster surfaces, the final data set correctly identifies all locations within approximately 23.5 nm (43.5 km) of the port. It correctly identifies approximately half the locations between 23.5 and 25 nm of the port, and it incorrectly identifies approximately half the locations between 25 and 25.5 nm of the port. Therefore, there is some uncertainty about the area between 23.5 and 25.5 nm of the port. This problem is inherent in raster-based cost-distance algorithms and is unavoidable.
•The port buffer feature class was then intersected with GEBCO-derived Depth Range polygons (–1 m to –25 m), (–25 m to –100 m), (< –100 m).
•Finally, the port buffer feature class was intersected with VLIZ exclusive economic zone polygons.
•This final feature class reflects only maritime areas within 25 nm travel distance of ports, combined by country, and split by depth range and EEZ.
Eventually, the final feature class was intersected with areas favourable for the grow-out of the three species and integrated multitrophic aquaculture (IMTA).
Offshore mariculture potential of three representative species and IMTA of two of them spatially defined by environments favourable for grow-outChlorophyll-a, sea surface temperature and current speed: the raw data for chlorophyll-a (CHL2), sea surface temperature (SST) and current speed (CS) included mean values, number of observations and standard deviations per cell in raster format. Using a confidence level of = 0.05, these original rasters were used to generate 95 percent confidence intervals around the mean values. A location would be considered to fall within a threshold if the full confidence interval around the observed value at that location was completely within the upper and lower threshold values. For example, the temperature threshold for cobia was 22–32 °C. A location would only be considered to fall within this temperature range if both the lower confidence limit at that location was ≥ 22° and the upper confidence limit was ≤ 32°. Steps for identifying suitable regions for cobia, Atlantic salmon, blue mussel and IMTA are illustrated in Figures A1.5–A1.10.
92 A global assessment of offshore mariculture potential from a spatial perspective
FIGURE A1.5Steps to define regions favorable for cobia grow-out
93Annex 1
FIGURE A1.6Steps to define regions favorable for grow-out of Atlantic salmon
94 A global assessment of offshore mariculture potential from a spatial perspective
FIGURE A1.7Steps to define regions favorable for grow-out of blue mussel
95Annex 1
FIGURE A1.8Steps to define regions favorable for grow-outof Integrated Multi-Trophic Aquaculture (IMTA)
96 A global assessment of offshore mariculture potential from a spatial perspective
FIGURE A1.9Chlorophyll-a confidence intervals subprocess
FIGURE A1.10Sea surface temperature confidence intervals subprocess
97Annex 1
CHL2 data was often unavailable at extreme latitudes in the colder months of the year, which complicated the task of identifying areas that met CHL2 thresholds. Therefore, analyses of CHL2 were done both seasonally and by the full year. In the Northern Hemisphere, seasonal data sets were calculated that met threshold requirements for the combined months of March, April, May, June, July, August and September. In the Southern Hemisphere, data sets were calculated that met threshold requirements for the combined months of September, October, November, December, January, February, March and April. These monthly data sets are the monthly averages for the years 2003–2009 (i.e. the “March” data represents the average CHL2 of all the months of March from 2003 through 2009). The final analysis only used the seasonal CHL2 data sets.
The CHL2, CS, SST and bathymetry data were in raster format at different resolutions. The CS had cell edge lengths of approximately 8.9 km, SST cell sizes were ~4.9 km, and CHL2 cell sizes were ~4.6 km. When identifying regions that met various combinations of CHL2, CS and SST thresholds, the finest resolution data set was used to define the resolution of the final raster. For example, an analysis that incorporated both CS and SST rasters would produce a raster with a cell size equal to the SST data because SST had the finest resolution. Bathymetry was at the highest resolution (~0.9 km) and was always converted to a vector polygon feature class of polygons meeting various depth thresholds before additional analysis.
After deriving a final raster delineating all areas that met some combination of thresholds, this final raster was then converted to a polygon feature class for further analysis.
Sea surface temperature: the sea surface temperature data were available as monthly values and, therefore, did not require pooling any data across years. However, to convert them to degrees Celsius, they needed to be rescaled according to the following formula:
True Sea Surface (SST) = [Original SST from HDF files) * 0.075] - 3
Furthermore, original SST values of 1 indicated that they were on land, and values of 0 indicated missing data, so these regions were excluded from the analysis.
95 percent confidence intervals around the mean SST value were calculated according to the following definition:
98 A global assessment of offshore mariculture potential from a spatial perspective
Horizontal cell size: sea surface temperature data had 8 192 columns covering 360 degrees longitude (40 075 km equatorial circumference). This equals to 4.89197 km per cell width along the equator. This east-west distance decreases when moving towards the poles. The extreme north and south rows that actually had data were < 1 km in width.
Vertical cell size: sea surface temperature had 4 096 rows covering 180 degrees latitude (20 004 km from the North Pole to South Pole), equal to 4.88379 km per cell. This north-south distance is constant for all cells.
Chlorophyll-a: the Chlorophyll-a data were available as monthly values and, therefore, did not require pooling of any data. The 95 percent confidence intervals were calculated according to the following definition:
Horizontal cell size: chlorophyll-a data had 8 640 columns covering 360 degrees longitude (40 075 km equatorial circumference). This equals to 4.63831 km per cell width along the equator. This east-west distance decreases when moving towards the poles. The extreme north and south rows that actually had data were < 3 km in width.
Vertical cell size: chlorophyll-a had 4 320 rows covering 180 degrees latitude (20 004 km from the North Pole to the South Pole), equal to 4.63056 km per cell. This north-south distance is constant for all cells.
Marine protected areas: a data set of marine protected areas was derived from the World Dataset of Protected Areas. This data set was clipped so that it only represents marine areas, and was intersected with geographic zones.
Shorelines: the coastline length data were obtained from the Global Administrative Areas database of administrative boundaries (GADM, Version 1.0), available at www.gadm.org. The polyline data set of marine shorelines was derived by: (i) creating an “ocean” polygon data set by clipping out the GADM polygons from a general background polygon covering the entire earth; (ii) deleting all small polygons from the “ocean” data set that represented lakes or internal holes in the GADM data set; and then (iii) creating a coastline polyline data set by intersecting the GADM polygons with the ocean polygons. This last polyline data set is the linear intersection of all coastal countries with the oceans and, therefore, represents the coastline of all countries that face the ocean. This shorelines layer was essential to determine exactly how much shoreline each country has, and was intersected with other layers (such as the geographic zones data set) to determine how much shoreline lies within specific regions. The steps to generate shorelines are illustrated in Figure A1.11.
99Annex 1
3.2 Integration of data setsThe compiled spatial data were used in two ways: (i) to identify all of the areas meeting the thresholds associated with each criterion; and (ii) to estimate temperatures and chlorophyll-a concentrations at specific mariculture locations. This approach also allowed these suitability thresholds to be compared with temperatures and chlorophyll-a concentrations actually experienced in inshore mariculture practice and to measure temperature and chlorophyll-a offshore of inshore mariculture locations.
FIGURE A1.11Steps to define coastlines
100 A global assessment of offshore mariculture potential from a spatial perspective
Raster data sets were manipulated in ArcGIS 9.3 as described above, vectorized and imported to Manifold as shapefiles. In Manifold, the shapefiles became drawing (map) components in map projects. Each map project represented a separate analytical step (e.g. identifying the areas with depths suitable for cages and longlines). The output from each project consisted of a drawing and an associated table. Component outputs from individual projects were then sequentially integrated in subsequent projects (e.g. spatial integration of depths and current speeds) to obtain the results set out in Chapter 4. Topology overlay was the basic GIS tool used to spatially integrate the spatial data sets. Selection by query using spatial Structured Query Language was employed to organize the results into meaningful classes. Tables were exported to Microsoft Excel 2010, where the data were manipulated in pivot tables to provide the estimates of potential by EEZ and nation as surface area, which were then reported as tables and charts. Manifold also was used to arrange individual drawings into layers in maps and to add legends and labels to them, which were then exported as images that, in turn, became the map figures in this document.
The analysis conducted for this technical paper was primarily interested in cumulative areas that met various criteria (in which case slivers contributed very little to the cumulative total) and, therefore, the results were not significantly influenced by the potential effects of sliver8 polygons. The data were also not the types that typically cause large numbers of slivers.
3.3 Comparisons of offshore potential with inshore mariculture locations and verification
Comparisons of predicted offshore potential with inshore mariculture practice at national and subnational levels and verifications at offshore mariculture sites
Three kinds of comparisons were made: (i) national-level comparisons of mariculture production based on FAO statistics (FAO Statistics and Information Branch of the Fisheries and Aquaculture Department, 2012) of the three species with national-level offshore mariculture potential of the species; (ii) known inshore mariculture locations of cobia, Atlantic salmon and blue mussel, obtained through a literature review, contacts with government entities in British Columbia, Canada, Ireland, the Kingdom of Norway and the People’s Democratic Republic of China, and with commercial farmers in eastern Canada and several other countries, were compared with areas identified by the analyses as possessing offshore mariculture potential; and (iii) offshore mariculture potential was examined at several offshore cobia farm locations using locational information communicated by commercial farmers. For the first two kinds of comparisons, good correspondence between established inshore mariculture practice and offshore potential indicates that offshore mariculture could be more easily developed using the existing inshore experience, goods and services, and access to markets. Good correspondence also suggests that favourable conditions for grow-out (water temperature and also food availability for the blue mussel) are likely to be found offshore from existing inshore mariculture installations. The third kind of comparison actually tests predicted potential against the locations of functioning offshore farms. Results from this analysis are described in detail in Chapter 5 of the technical paper.
8 A sliver polygon is a small remnant polygon resulting from an intersection operation between two or more polygons.
101Annex 1
TAB
LE A
1.1
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103Annex 1
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.g. p
rop
ose
d).
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ud
es
MPA
Glo
bal
200
8 an
d a
ny
oth
er s
ites
th
at
hav
e b
een
iden
tifi
ed a
s h
avin
g a
“m
arin
e”
com
po
nen
t.
Dat
a ar
e p
rovi
ded
in s
hap
efile
fo
rmat
, an
d G
IS
cap
able
so
ftw
are
is r
equ
ired
to
vie
w it
. Dat
a ar
e fr
eely
do
wn
load
able
aft
er r
egis
trat
ion
.
ww
w.w
dp
a.o
rg/
Geo
gra
ph
ic z
on
esN
.A.
2010
Arc
tic,
No
rth
ern
Tem
per
ate,
Inte
rtro
pic
al,
Sou
ther
n T
emp
erat
e an
d A
nta
rcti
c Zo
nes
.Th
ese
po
lyg
on
s w
ere
gen
erat
ed w
ith
in t
his
stu
dy
bas
ed o
n t
he
Tro
pic
s o
f C
ance
r an
d C
apri
corn
, an
d
on
th
e A
rcti
c an
d A
nta
rcti
c C
ircl
es
GA
DM
dat
abas
e o
f G
lob
al A
dm
inis
trat
ive
Are
as,
Ver
sio
n 1
N.A
.20
10G
AD
M is
a f
reel
y d
ow
nlo
adab
le s
pat
ial d
atab
ase
of
the
loca
tio
n o
f th
e w
orl
d’s
ad
min
istr
ativ
e b
ou
nd
arie
s. T
he
dat
a ar
e av
aila
ble
in s
hap
efile
, ES
RI g
eod
atab
ase,
RD
ata
and
Go
og
le E
arth
km
z fo
rmat
.
htt
p://
gad
m.o
rg/h
om
e
Co
astl
ine
len
gth
(km
)N
.A.
2010
Dat
a b
y co
un
try
and
ter
rito
ry, d
eriv
ed f
rom
GA
DM
(G
lob
al A
dm
inis
trat
ive
Are
as)
v. 1
.C
alcu
lati
on
s m
ade
wit
hin
th
is s
tud
y. S
ee F
igu
re
A1.
11 a
bo
ve t
hat
des
crib
es t
he
app
roac
h in
det
ail
term
ino
log
y: N
.A. =
No
t ap
plic
able
as
they
are
in v
ecto
r fo
rmat
.
104 A global assessment of offshore mariculture potential from a spatial perspective
TAB
LE A
1.2
Dep
th c
har
acte
rist
ics
of
exp
erim
enta
l an
d c
om
mer
cial
sea
cag
e an
d lo
ng
line
inst
alla
tio
ns
and
sp
ecif
icat
ion
s fr
om
man
ufa
ctu
rers
Enti
tyLo
cati
on
Syst
em t
ype
Dep
th a
t si
te (
m),
o
r m
anu
fact
ure
r’s
spec
ific
atio
n
Sou
rces
Sea
cag
es f
or
fish
Snap
per
farm
, In
c.Pu
erto
Ric
o,
Un
ited
Sta
tes
of
Am
eric
a
SeaS
tati
on
™
off
sho
re
sub
mer
sib
le
30O
’Han
lon
et
al. (
2001
)
Cat
es In
tern
atio
nal
Haw
aii,
Un
ited
Sta
tes
of
Am
eric
a
SeaS
tati
on
™
off
sho
re
sub
mer
sib
le 3
000
31B
ybee
an
d B
aile
y-B
rock
, (20
03),
p. 1
21
Ko
na
Blu
e W
ater
Far
ms
Haw
aii,
Un
ited
Sta
tes
of
Am
eric
a
SeaS
tati
on
™
off
sho
re
sub
mer
sib
le 3
000
61–6
7K
on
a B
lue
Wat
er F
arm
s (2
003)
Un
iver
sity
of
New
Ham
psh
ire
New
Ham
psh
ire,
U
nit
ed S
tate
s o
f A
mer
ica
SeaS
tati
on
™
fish
cag
e (S
S600
)
52La
ng
an a
nd
Ho
rto
n (
2005
)
Gu
lf o
f M
exic
o O
ffsh
ore
Aq
uac
ult
ure
C
on
sto
rtiu
mM
issi
ssip
pi,
Un
ited
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tes
of
Am
eric
a
SeaS
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on
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fish
cag
e 60
0 m
3
25w
ww
.mas
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org
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ase%
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an S
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tern
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eden
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ww
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ex
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age)
SUB
flex
Op
en O
cean
Net
SPM
cag
es;
ww
w.s
ub
flex
.org
Oce
an F
arm
Tec
hn
olo
gie
s M
anu
fact
ure
r’s
spec
ific
atio
nA
qu
apo
d A
212,
A36
00,
A70
0020
–50
- 32
–50
- 35
–50
Oce
an F
arm
Tec
hn
olo
gie
s “A
qu
apo
d S
ite
Sele
ctio
n”
(ww
w.o
cean
farm
tech
.co
m)
and
C. S
tock
, per
son
al c
om
mu
nic
atio
n (
2009
)
Wo
rksh
op
on
op
en o
cean
aq
uac
ult
ure
Un
ited
Sta
tes
of
Am
eric
aSe
a ca
ges
w
ith
mu
ltip
le
anch
ors
Co
mm
ent:
Mo
ori
ng
> 1
00 m
a c
hal
len
ge
ow
ing
to
larg
e fo
otp
rin
t, c
apit
al
and
mai
nte
nan
ce c
ost
of
anch
ori
ng
sys
tem
Bro
wd
y an
d H
arg
reav
es (
2009
)
Asi
a-Pa
cifi
c O
cean
Res
earc
h C
ente
r, N
atio
nal
Su
n Y
at-s
en U
niv
ersi
tyTa
iwan
Pro
vin
ce o
f C
hin
aG
ravi
ty c
ages
30–5
0 id
eal r
ange
of
wat
er d
epth
fo
r n
et-c
age
imp
lem
enta
tio
n in
th
e o
pen
sea
H
uan
g, C
.C.,
Tan
g, H
.J. a
nd
Liu
, J.Y
. (20
08)
105Annex 1
TAB
LE A
1.3A
Cu
rren
t sp
eed
in m
aric
ult
ure
pra
ctic
e fo
r se
a ca
ges
an
d lo
ng
lines
Cu
rren
t sp
eed
(cm
/s)
Co
mm
ent
Cag
e ty
pe
Sou
rce
60N
ot
to e
xcee
dG
ener
al c
om
men
t to
avo
id d
efo
rmat
ion
B
ever
idg
e (1
996)
103–
129
No
t to
exc
eed
Farm
Oce
an 4
500
ww
w.f
arm
oce
an.s
e/G
ener
al.p
df
100
90%
of
cag
e vo
lum
e is
ret
ain
edO
cean
Sp
ar S
eaSt
atio
nSc
ott
an
d M
uir
(20
06);
h
ttp
://re
sso
urc
es.c
ihea
m.o
rg/o
m/p
df/
b30
/006
0065
1.p
df
150–
170
“An
ti-c
urr
ent”
off
sho
reD
FC t
ype
Ch
en e
t al
. (20
07)
in C
age
Aq
uac
ult
ure
(Ta
ble
4, p
. 59)
; w
ww
.fao
.org
/do
crep
/010
/a12
90e/
a129
0e00
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100–
120
“An
ti-c
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sem
i-o
pen
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ype
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nti
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cati
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HD
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ype
150
“An
ti-c
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ype
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mer
ged
ww
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libab
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atal
og
/116
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ed_S
tyle
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ater
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tml
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um
fo
r a
144–
625
m3
cag
eLM
S ty
pe
Hu
nte
r,Tel
fer
and
Ro
ss (
2006
), T
able
3.1
p. 1
4;
ww
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qua.
stir.
ac.u
k/pu
blic
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AP/
pdfs
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e
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ang
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r th
ree
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e m
od
els
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an F
arm
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gie
s A
qu
apo
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nd
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an F
arm
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gie
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qu
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ite
Sele
ctio
n”
dat
ed 6
/5/0
9 (w
ww
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anfa
rmte
ch.c
om
) an
d
e-m
ail d
ated
24
Jun
e 20
09 f
rom
Ch
ris
Sto
ck in
Ou
tlo
ok
Fold
er M
arn
e G
IS
100
Cu
rren
ts t
hat
exc
eed
100
cm
/s n
ot
gen
eral
ly
reco
mm
end
edSe
a ca
ges
in g
ener
alJa
mes
an
d S
lask
i (20
07)
(in
PN
A)
106 A global assessment of offshore mariculture potential from a spatial perspective
TAB
LE A
1.3B
C
urr
ent
spee
d in
mar
icu
ltu
re p
ract
ice
for
fin
fish
an
d m
uss
els
Cu
rren
t sp
eed
cm
/sC
om
men
tSp
ecie
sSo
urc
e
> 1
0To
ass
ure
suff
icie
nt w
ater
qua
lity
wit
hin
a ca
ge, c
urre
nts
shou
ld r
emai
n ab
ove
10 c
m/s
for
a m
ajor
par
t of
the
ti
dal c
ycle
.
Salm
on
Tlu
sty,
Pep
per
an
d A
nd
erso
n (
2005
) ci
tin
g P
uls
an
d
Sun
der
man
(19
90).
1–9,
1–7
, 1–2
2, 1
–10,
1–4
55–
10, 2
–6O
bse
rvat
ion
s at
fiv
e in
sho
re s
ea s
ites
an
d t
wo
lake
fa
rmin
g s
ites
tak
en d
uri
ng
tw
o v
isit
s, f
rom
5 t
o 8
h
ou
rs (
five
sit
es)
up
to
th
ree
day
s (t
wo
loca
tio
ns)
at
dep
ths
of
fro
m 2
2 to
75
m w
ith
rec
ord
er 1
–2 m
fro
m
the
bo
tto
m.
Atl
anti
c sa
lmo
nSo
to e
t al
. (20
03)
3–18
(av
erag
e)Tw
enty
sal
mo
n f
arm
s, B
ay o
f Fu
nd
y, C
anad
a, w
ith
24
-ho
ur
dep
loym
ents
co
rres
po
nd
ing
to
tw
o t
idal
cyc
les.
Atl
anti
c sa
lmo
nPe
ters
on
et
al. (
2001
);
htt
p://
pu
blic
atio
ns.
gc.
ca/c
olle
ctio
ns/
colle
ctio
n_2
012/
mp
o-d
fo/F
s97-
6-23
37-e
ng
.pd
f
42 (
max
imu
m)
Twen
ty s
alm
on
far
ms,
Bay
of
Fun
dy,
Can
ada,
wit
h
24-h
ou
r d
eplo
ymen
ts c
orr
esp
on
din
g t
o t
wo
tid
al c
ycle
s.A
tlan
tic
salm
on
Pete
rso
n e
t al
. (20
01);
h
ttp
://p
ub
licat
ion
s.g
c.ca
/co
llect
ion
s/co
llect
ion
_201
2/m
po
-dfo
/Fs9
7-6-
2337
-en
g.p
df
> 1
00“S
ites
wh
ere
curr
ent
spee
ds
exce
ed 1
00 c
m/s
fo
r ex
ten
ded
per
iod
s m
ay n
ot
be
suit
able
fo
r g
row
ing
sa
lmo
n”.
Atl
anti
c sa
lmo
nC
han
g, P
age
and
Hill
(20
05);
w
ww
.gn
b.c
a/00
27/A
qu
/pd
fs/B
arry
DFO
2585
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f
10–1
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stim
ated
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ge
of
no
less
th
an 1
0 cm
/s f
or
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ral
ho
urs
an
d n
o m
ore
th
an 1
10 c
m/s
fo
r m
ore
th
an 2
4 h
ou
rs”.
Rel
ates
to
Atl
anti
c sa
lmo
n a
nd
blu
e m
uss
el
amo
ng
oth
er s
pec
ies
con
sid
ered
Mac
leod
(20
07)
citi
ng M
assa
chus
etts
Bay
Env
iron
men
tal
Fore
cast
Sys
tem
Mo
del
, UM
ass
Bo
sto
n.
(M. J
ian
g, p
erso
nal
co
mm
un
icat
ion
, 200
7);
htt
p://
envs
tud
ies.
bro
wn
.ed
u/t
hes
es/a
rch
ive2
0062
007/
mer
riel
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acle
od
_th
esis
.pd
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10–6
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site
s co
nsi
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pti
mal
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r fi
sh f
arm
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pen
s h
ave
curr
ent
ran
ges
fro
m 1
0 to
60
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bu
t va
ries
wit
hin
th
is r
ang
e d
epen
din
g o
n s
ize
and
sp
ecie
s o
f fi
sh, s
tock
ing
den
sity
an
d c
age
des
ign
an
d
con
fig
ura
tio
n”.
Rel
ates
to
“m
arin
e o
r sa
lmo
nid
fis
h”
Ren
sell
et a
l. (2
007)
, p. 1
15;
ww
w.f
ra.a
ffrc
.go
.jp/b
ulle
tin
/bu
ll/b
ull1
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f
< 1
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urr
ent
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ds
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to 3
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ots
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. 154
cm
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(off
sho
re
site
). C
ob
ia
Aq
ual
ider
: w
ww
.aq
ual
ider
.co
m.b
r (o
ut
of
bu
sin
ess
late
201
0)
13–7
7 (r
ang
e)
Co
bia
Sn
app
erfa
rm, I
nc.
, Pu
erto
Ric
o,
Un
ited
Sta
tes
of
Am
eric
a; B
enet
ti e
t al
. (20
10)
< 2
6C
urr
ent
is v
aria
ble
bu
t m
ain
ly n
ort
h t
o s
ou
th w
ith
p
eaks
of
26 c
m/s
an
d d
ays
of
slac
k cu
rren
t.C
ob
ia; D
ou
ble
rin
g o
larc
irke
l, 40
, 60
and
10
0 m
cir
cum
fere
nce
Mar
ine
Farm
s B
eliz
e;
ww
w.m
arin
efar
msb
eliz
e.co
m
13–1
29C
urr
ent
0.25
kn
ot
(13
cm/s
) av
erag
e, m
ax 2
.5 k
no
ts
(129
cm
/s).
Co
bia
; Sea
Stat
ion
640
0, A
qu
apo
d 7
000
and
10
0 m
Aq
ual
ine
Op
en B
lue
Sea
Farm
s, P
anam
a;
ww
w.o
pen
blu
esea
farm
s.co
m
10–5
0Si
tin
g s
tud
y fo
r Sn
app
erfa
rm; m
ean
is 1
0 an
d m
ax is
50
ob
serv
ed.
Co
bia
Ren
sell,
Kie
fer
and
O’B
rien
(20
06);
ww
w.li
b.n
oaa
.go
v/re
tire
dsi
tes/
do
caq
ua/
rep
ort
s_n
oaa
rese
arch
/co
bia
_aq
uam
od
el_f
inal
_rep
ort
.pd
f
107Annex 1
Cu
rren
t sp
eed
cm
/sC
om
men
tSp
ecie
sSo
urc
e
< 5
0 M
ain
ly t
rad
itio
nal
co
bia
cag
es, b
ut
som
e o
ffsh
ore
ca
ges
at
11 lo
cati
on
s.C
ob
iaG
uan
gd
on
g a
nd
Hai
nan
pro
vin
ces,
Ch
ina.
(C
. Zh
u, p
erso
nal
co
mm
un
icat
ion
, 201
1)
55O
ffsh
ore
wat
ers
of
Pen
gh
u Is
lan
ds,
Tai
wan
Pro
vin
ce
of
Ch
ina.
Co
bia
Mia
o e
t al
. (20
09)
9O
ffsh
ore
wat
ers
of
Pin
gtu
ng
Co
un
ty, T
aiw
an P
rovi
nce
o
f C
hin
a.
70–1
04H
igh
est
spee
ds
enco
un
tere
d a
s o
cean
-gyr
e cu
rren
ts.
Seri
oal
a ri
volia
na;
Oce
an S
par
Sea
Stat
ion
ca
ges
inst
alle
d a
t K
eah
ole
Po
int,
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aii,
(Un
ited
Sta
tes
of
Am
eric
a) 1
.6 k
m o
ffsh
ore
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rich
(20
10)
31–1
03Se
aSta
tio
n 3
000
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.5 k
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ffsh
ore
, Je
ju p
rovi
nce
, Rep
ub
lic o
f K
ore
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rro
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h (
op
leg
nat
hu
s fa
scia
tus)
Lim
an
d L
ee (
no
dat
e); w
ww
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me.
org
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esen
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Im.p
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129
Des
ign
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ecif
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ilth
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am (
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us
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SU
Bfl
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ish
ler,
per
son
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om
mu
nic
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011)
.
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on
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eed
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nce
d.
51–7
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on
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t sp
eed
exp
erie
nce
d.
103
Max
imu
m e
xper
ien
ced
.10
3M
axim
um
exp
erie
nce
d.
5 –50
•“C
lass
I Pr
od
uct
ion
up
to
20
000
po
un
ds
per
yea
r (9
07
2 kg
per
yea
r).
•M
inim
um
dep
th o
f 35
fee
t (1
0.6
m)
for
a cu
rren
t ve
loci
ty o
f 5
cm/s
ec (
0.1
kno
ts)
to a
min
imu
m d
epth
o
f 20
fee
t (6
.1 m
) fo
r cu
rren
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loci
ties
of
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m/s
ec
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kn
ots
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r g
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er C
lass
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rod
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wee
n 2
0 00
0 to
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000
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ds
per
yea
r (9
072
to
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360
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per
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r).
•M
inim
um
dep
th o
f 45
fee
t (1
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m)
for
a cu
rren
t ve
loci
ty o
f 5
cm/s
ec (
.01
kno
ts)
to a
min
imu
m d
epth
o
f 25
fee
t (7
.6 m
) fo
r cu
rren
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loci
ties
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ec
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kn
ots
) o
r g
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er C
lass
III P
rod
uct
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ove
r 10
0 00
0 p
ou
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s p
er y
ear
(4
5 36
0 kg
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r).
• M
inim
um
dep
th o
f 60
fee
t (1
8.2
m)
for
a cu
rren
t ve
loci
ty o
f 5
cm/s
ec (
0.1
kno
ts)
to a
min
imu
m d
epth
o
f 40
fee
t (1
2.1)
fo
r cu
rren
t ve
loci
ties
of
50 c
m/s
ec
(1.0
kn
ots
) o
r g
reat
er.
Fin
fish
Lan
gen
bu
rg a
nd
Stu
rges
(19
99),
Tab
le 2
. Th
ere
is
an a
pp
end
ix w
ith
a c
har
t re
lati
ng
cu
rren
t sp
eed
, p
rod
uct
ion
an
d d
epth
fro
m w
hic
h t
he
dat
a o
n t
he
left
h
ave
bee
n d
eriv
ed. T
hes
e es
tim
ates
are
fro
m t
he
po
int
of
view
of
envi
ron
men
tal p
rote
ctio
n r
ath
er t
han
fro
m
max
imiz
ing
pro
du
ctio
n, i
t se
ems.
> 5
0Se
aSta
tio
n S
S600
an
d S
S300
0 ca
ges
10
km
off
sho
re o
f N
ew H
amp
shir
e, U
nit
ed S
tate
s o
f A
mer
ica,
wit
h c
urr
ent
spee
d “
oft
en e
xcee
din
g 5
0 cm
/s”.
Atl
anti
c h
alib
ut,
Atl
anti
c h
add
ock
, A
tlan
tic
cod
Fre
dri
ckss
on
et
al. (
2003
)
10–5
0O
pti
mal
wit
h le
sser
sp
eed
s af
fect
ing
fill
et q
ual
ity
and
g
reat
er s
pee
ds
resu
ltin
g in
a r
apid
incr
ease
of
the
feed
co
nve
rsio
n r
atio
wit
h c
ult
ivat
ion
bec
om
ing
fin
anci
ally
u
nat
trac
tive
.
Gilt
hea
d b
ream
Fe
rrei
ra, S
aure
l an
d F
erre
ira
(201
2)
108 A global assessment of offshore mariculture potential from a spatial perspective
Cu
rren
t sp
eed
cm
/sC
om
men
tSp
ecie
sSo
urc
e
N/A
“At
a cu
rren
t sp
eed
of
15 c
m/s
ec, t
he
wat
er a
t a
site
is
exch
ang
ed a
bo
ut
100
tim
es p
er d
ay. A
n e
xch
ang
e ra
te
of
2–3
tim
es is
typ
ical
ly n
eed
ed t
o k
eep
th
e le
vels
of
nu
trie
nts
in t
he
wat
er c
olu
mn
low
er t
han
th
e cr
itic
al lo
ad.”
N/A
Grø
ttu
m a
nd
Bev
erid
ge
(200
7), c
itin
g O
lsen
, Sla
gst
ad
and
Vad
stei
n (
2005
) p
. 148
.
5–20
go
od
; < 1
an
d >
50
po
or
No
t n
amed
Hal
ide
(200
8) A
pp
end
ix 1
(ap
pea
rs t
o b
e m
od
ellin
g f
or
un
nam
ed f
ish
sp
ecie
s in
tro
pic
al w
ater
s); h
ttp
://d
ata.
aim
s.g
ov.
au/c
ads/
CA
DS_
TOO
L_Te
chn
ical
_Gu
ide.
pd
f
< 5
Ver
y w
eak
curr
ent,
po
or
mas
s fl
ux
and
inco
nsi
sten
t cu
rren
t d
irec
tio
n. D
eple
tio
n li
kely
at
the
cen
tre
of
fa
rms.
On
ly s
uit
able
fo
r lo
w-d
ensi
ty f
arm
ing
or
spat
h
old
ing
.
pern
a ca
nal
icu
lus
and
Myt
ilus
gal
lop
rovi
nci
alis
Ing
lis, H
ayd
en a
nd
Ro
ss (
2000
), B
ox
tab
le, p
. 21
5–10
Wea
k cu
rren
t ve
loci
ties
of
gen
eral
ly w
idel
y va
ryin
g
dir
ecti
on
lead
ing
to
so
me
dep
leti
on
at
cen
tre
of
farm
.pe
rna
can
alic
ulu
s an
d M
ytilu
s g
allo
pro
vin
cial
isIn
glis
, Hay
den
an
d R
oss
(20
00),
Bo
x ta
ble
, p. 2
1
10–2
0M
od
erat
e-lo
w d
eple
tio
n t
hat
may
be
mo
re m
arke
d a
t d
ow
nst
ream
en
d o
f fa
rm. D
eple
tio
n is
mo
re li
kely
to
b
e o
bse
rved
in c
entr
e o
f fa
rmed
are
a.
pern
a ca
nal
icu
lus
and
Myt
ilus
gal
lop
rovi
nci
alis
Ing
lis, H
ayd
en a
nd
Ro
ss (
2000
), B
ox
tab
le, p
. 21
> 2
0St
ron
g c
urr
ent
flo
w. L
ittl
e d
eple
tio
n b
ut
cum
ula
tive
ef
fect
of
man
y ro
pes
lon
glin
es in
th
e d
irec
tio
n o
f fl
ow
co
uld
res
ult
in (
rem
ain
der
of
text
is m
issi
ng
fro
m t
he
ori
gin
al a
rtic
le).
pern
a ca
nal
icu
lus
and
Myt
ilus
gal
lop
rovi
nci
alis
Ing
lis, H
ayd
en a
nd
Ro
ss (
2000
), B
ox
tab
le, p
. 21
15–2
0B
ott
om
cu
ltu
re (
mo
der
ate
gro
w-o
ut
den
siti
es).
Myt
ilus
edu
lisN
ewel
l (20
01)
5Lo
ng
lines
, if
giv
en a
deq
uat
e sp
acin
g.
Myt
ilus
edu
lisN
ewel
l (20
01)
10–1
5R
afts
in o
rder
to
pre
ven
t d
eple
tio
n.
Myt
ilus
edu
lisN
ewel
l (20
01)
10–3
0O
ffsh
ore
lon
glin
e.M
ytilu
s ed
ulis
R. L
ang
an, p
erso
nal
co
mm
un
icat
ion
, 200
9
< 1
0; in
freq
uen
tly
up
to
50
Haw
ke B
ay, N
ort
h Is
lan
d,
New
Zea
lan
d.
Biv
alve
sh
ellf
ish
, in
clu
din
g g
reen
shel
l mu
ssel
s,
pern
a ca
nal
icu
lus
Ch
eney
et
al. (
2010
)
< 1
5–30
Op
oti
ki, N
ort
h Is
lan
d,
New
Zea
lan
d.
Biv
alve
sh
ellf
ish
, in
clu
din
g g
reen
shel
l mu
ssel
s,
pern
a ca
nal
icu
lus
Ch
eney
et
al. (
2010
)
109Annex 1
TAB
LE A
1.4A
Tem
per
atu
res
for
gro
w-o
ut
of
cob
ia
Tem
per
atu
re o
r ra
ng
eC
om
men
tLo
cati
on
Sou
rce
< 2
2 N
o g
row
thV
iet
Nam
Nh
u e
t al
. (20
09)
< 1
8 St
op
eat
ing
Vie
t N
amN
hu
et
al. (
2009
)
15 M
ass
mo
rtal
ity
Five
wee
ks in
200
8.V
iet
Nam
Nh
u e
t al
. (20
09)
22–3
0 M
ean
mo
nth
ly r
ang
eV
iet
Nam
Nh
u e
t al
. (20
09)
<16
Sev
ere
stre
ss, m
ort
alit
ies
Un
ited
Sta
tes
of
Am
eric
aM
. Ost
erlin
g, p
erso
nal
co
mm
un
icat
ion
, 201
1
16–3
2; >
20
pre
ferr
edC
on
dit
ion
s in
th
e w
ild.
No
t st
ated
Kai
ser
and
Ho
lt (
2005
)
> 2
6 O
pti
mal
gro
wth
Cu
ltu
re c
on
dit
ion
s.N
ot
stat
edK
aise
r an
d H
olt
(20
05)
21–2
2Fe
edin
g a
ctiv
ity
red
uce
d.
Taiw
an P
rovi
nce
of
Ch
ina
Mia
o e
t al
. (20
09)
19Fe
edin
g c
ease
s.Ta
iwan
Pro
vin
ce o
f C
hin
aM
iao
et
al. (
2009
)
< 1
6 an
d >
36
May
res
ult
in m
ass
mo
rtal
ity.
Taiw
an P
rovi
nce
of
Ch
ina
Mia
o e
t al
. (20
09)
22–3
2O
pti
mal
tem
per
atu
re r
ang
e.N
ot
spec
ifie
dM
iao
et
al.,
2009
, ci
tin
g C
han
g e
t al
., 19
99
25–2
7 m
ean
sp
rin
g t
o a
utu
mn
;21
–22
mea
n w
inte
r <
16
low
tem
per
atu
rePe
ng
hu
Arc
hip
elag
o, T
aiw
an P
rovi
nce
of
Ch
ina
Shih
, Ch
ou
an
d C
hia
u (
2009
)
27–2
9 A
mb
ien
t co
nd
itio
ns
Snap
per
farm
, Isl
a C
ule
bra
, U
nit
ed S
tate
s o
f A
mer
ica
Ren
sel,
Kie
fer
and
O’B
rien
, 20
06
< 1
6 H
igh
mo
rtal
ity
Pen
gh
u A
rch
ipel
ago
, Ta
iwan
Pro
vin
ce o
f C
hin
aLi
ao e
t al
. (20
04)
23.5
–28
year
ro
un
dSe
a ca
ge
area
s in
so
uth
ern
Tai
wan
Pro
vin
ce
of
Ch
ina
Liao
et
al. (
2004
)
28–3
2 H
igh
est
gro
wth
rat
es;
< 2
0 g
row
th r
ates
dec
reas
edFi
sh f
ed t
o s
atia
tio
n.
Pen
gh
u A
rch
ipel
ago
, Pr
ovi
nce
of
Ch
ina
Uen
g e
t al
. ( 2
001)
26 a
nd
ab
ove
On
gro
win
g.
No
t st
ated
Kai
ser
and
Ho
lt (
2007
); w
ww
.fao
.org
/fis
her
y/cu
ltu
red
spec
ies/
Rac
hyc
entr
on
_can
adu
m/e
n
27–2
8 ye
ar r
ou
nd
On
gro
win
g.
Op
en B
lue
Sea
Farm
s,
Pan
ama
B. O
’Han
lon
, per
son
al C
om
mu
nic
atio
n, 2
011
25–3
2O
n g
row
ing
.Sn
app
erfa
rm, I
nc.
, Pu
erto
Ric
o,
Un
ited
Sta
tes
of
Am
eric
aB
enet
ti e
t al
. (20
10)
110 A global assessment of offshore mariculture potential from a spatial perspective
TAB
LE A
1.4B
Tem
per
atu
res
for
gro
w-o
ut
of
Atl
anti
c sa
lmo
n
Tem
per
atu
re o
r ra
ng
eC
om
men
tLo
cati
on
Sou
rce
6–16
Gro
w b
est
in s
ites
wit
h
thes
e te
mp
erat
ure
ext
rem
es.
Gen
eral
ized
FAO
(20
11);
w
ww
.fao
.org
/fis
her
y/cu
ltu
red
spec
ies/
Salm
o_s
alar
/en
0.6–
15.6
Win
ter
and
su
mm
er t
emp
erat
ure
s n
ot
to b
e ex
ceed
ed f
or
any
len
gth
o
f ti
me.
Mai
ne,
Un
ited
Sta
tes
of
Am
eric
aU
niv
ersi
ty o
f M
ain
e;
ww
w.u
mai
ne.
edu
/mai
nes
ci/A
rch
ives
/Mar
ineS
cien
ces/
salm
on
-fa
rmin
g.h
tm
8–18
Op
tim
al r
ang
e fo
r cu
ltu
re.
Tasm
ania
, Au
stra
liaA
no
n, (
2002
);
ww
w.p
ir.sa
.go
v.au
/__d
ata/
asse
ts/p
df_
file
/001
0/33
895/
salm
on
_fs
.pd
f
12–1
6B
est
gro
wth
.Ta
sman
ia, A
ust
ralia
An
on
, (20
02);
w
ww
.pir.
sa.g
ov.
au/_
_dat
a/as
sets
/pd
f_fi
le/0
010/
3389
5/sa
lmo
n_
fs.p
df
0–21
Tole
rate
th
is r
ang
e.Ta
sman
ia, A
ust
ralia
An
on
, (20
02);
w
ww
.pir.
sa.g
ov.
au/_
_dat
a/as
sets
/pd
f_fi
le/0
010/
3389
5/sa
lmo
n_
fs.p
df
6–16
Gro
w-o
ut
ran
ge.
N/A
Ver
spo
or
et a
l. (2
007)
12–1
6Pr
efer
red
ran
ge.
Gip
psl
and
, Vic
tori
a, A
ust
ralia
Gip
psl
and
Aq
uac
ult
ure
Ind
ust
ry N
etw
ork
Inc.
(20
11);
h
ttp
://g
row
fish
.co
m.a
u/G
row
/Pag
es/S
pec
ies/
Tro
ut.
htm
> 2
2N
ot
reco
mm
end
ed f
or
farm
ing
if e
xcee
ded
on
a
reg
ula
r b
asis
.G
ipp
slan
d, V
icto
ria,
Au
stra
liaG
ipp
slan
d A
qu
acu
ltu
re In
du
stry
Net
wo
rk In
c. (
2011
);
htt
p://
gro
wfi
sh.c
om
.au
/Gro
w/P
ages
/Sp
ecie
s/Tr
ou
t.h
tm
0.7
Low
est
tem
per
atu
re
for
surv
ival
.B
ay d
’Esp
oir,
N
ewfo
un
dla
nd
, Can
ada
An
on
. (20
09);
w
ww
.dfo
-mp
o.g
c.ca
/sci
ence
/en
viro
/aq
uac
ult
ure
/acr
dp
-pcr
da/
fsh
eet-
ftec
hn
iqu
e/p
df/
02-e
ng
.pd
f
0–15
This
ran
ge,
alo
ng
wit
h s
tro
ng
cu
rren
ts a
nd
h
igh
tid
es, p
rovi
de
idea
l co
nd
itio
ns.
Mai
ne,
U
nit
ed S
tate
s o
f A
mer
ica
Mai
ne
Aq
uac
ult
ure
Inn
ova
tio
n C
ente
r (2
011)
; w
ww
.mai
nea
qu
acu
ltu
re.o
rg/in
du
stry
/sp
ecie
s.h
tml#
salm
on
0.5–
15.2
Mea
sure
men
ts f
rom
20
far
ms
ove
r tw
o y
ears
.B
ay o
f Fu
nd
y, C
anad
aPe
ters
on
et
al. (
2001
);
htt
p://
pu
blic
atio
ns.
gc.
ca/c
olle
ctio
ns/
colle
ctio
n_2
012/
mp
o-d
fo/F
s97-
6-23
37-e
ng
.pd
f
111Annex 1
TAB
LE A
1.4C
Tem
per
atu
res
for
gro
w-o
ut
of
blu
e m
uss
el
Tem
per
atu
re o
r ra
ng
e oC
No
teLo
cati
on
Sou
rce
-1.0
8–15
.6R
ang
e at
tw
o c
om
mer
cial
far
min
g s
ites
, wit
h
two
sta
tio
ns
per
sit
e.N
otr
e D
ame
Bay
, St
. Jo
hn
’s, N
ewfo
un
dla
nd
, Can
ada
Kh
an,
Parr
ish
an
d S
hah
idi (
2006
)
5.5–
16.3
Ran
ge
at s
hel
lfis
h f
arm
. W
est
Sco
tlan
d, U
nit
ed K
ing
do
mK
aray
uce
l an
d K
aray
uce
l (19
99 )
10–1
8R
ang
e at
co
mm
erci
al a
nd
exp
erim
enta
l sit
es
wit
h im
pro
ved
gro
wth
or
con
dit
ion
an
d
wh
ere
foo
d s
up
plie
s an
d/o
r n
utr
ien
ts w
ere
adeq
uat
e (n
ot
limit
ed t
o b
lue
mu
ssel
).
Wo
rld
wid
e re
view
Saxb
y (2
002)
16–2
2Ex
hib
it m
axim
um
gro
wth
in t
his
ran
ge.
Sou
th A
ust
ralia
An
on
. (20
00);
ww
w.p
ir.sa
.go
v.au
/__d
ata/
asse
ts/p
df_
file
/000
5/33
899/
mu
ssel
s_fs
.pd
f
4.4–
21.1
Ran
ge
for
cult
ure
.M
ain
e, U
nit
ed S
tate
s o
f A
mer
ica
Isla
nd
Inst
itu
te (
1999
).
The
Mai
ne
gu
ide
to r
aft
cult
ure
4.4–
10Id
eal f
or
cult
ure
.M
ain
e, U
nit
ed S
tate
s o
f A
mer
ica
Isla
nd
Inst
itu
te (
1999
).
The
Mai
ne
gu
ide
to r
aft
cult
ure
18.3
Beg
in t
o lo
se b
yssa
l str
eng
th.
Mai
ne,
Un
ited
Sta
tes
of
Am
eric
aIs
lan
d In
stit
ute
(19
99).
Th
e M
ain
e g
uid
e to
raf
t cu
ltu
re
21.1
Beg
in t
o s
uff
er m
ort
alit
y.
15.8
Op
tim
al t
emp
erat
ure
fo
r g
row
th
(mo
del
res
ult
).Pr
ince
Ed
war
d Is
lan
d, C
anad
aLa
uzo
n-G
uay
, et
al.
(200
6); w
ww
.int-
res.
com
/art
icle
s/m
eps2
006/
323/
m32
3p17
1.p
df
< 2
0Pr
even
t su
mm
er m
ort
alit
y.Ea
ster
n N
ort
h A
mer
ica
New
ell (
2001
)
5–20
Wel
l acc
limat
ed f
or
this
ran
ge.
Wo
rld
wid
e re
view
Go
ulle
tqu
er, P
. (20
09);
ww
w.f
ao.o
rg/f
ish
ery/
cult
ure
dsp
ecie
s/M
ytilu
s_ed
ulis
/en
0.3
0–15
.03
Win
ter
and
su
mm
er d
aily
mea
ns.
Lun
enb
urg
, No
va S
coti
a,C
anad
aH
atch
er, G
ran
t. a
nd
Sch
ofi
eld
(1
997)
-2–2
5O
ften
exp
ose
d t
o t
emp
erat
ure
s in
th
is r
ang
e.A
tlan
tic
Can
ada
New
Bru
nsw
ick
Pro
fess
ion
al S
hel
lfis
h G
row
ers
Ass
oci
atio
n (
2011
);
ww
w.a
cpn
b.c
om
/sta
tist
ics.
cfm
> 5
Req
uir
ed f
or
som
atic
an
d g
erm
inal
gro
wth
.Ea
ster
n N
ort
h A
mer
ica
New
ell a
nd
Mo
ran
(19
89)
5–16
Ran
ge
affe
ctin
g g
row
th
alo
ng
wit
h s
alin
ity,
fo
od
qu
anti
ty a
nd
qu
alit
y.10
km
off
sho
re n
ear
Port
smo
uth
, New
H
amp
shir
e, U
nit
ed S
tate
s o
f A
mer
ica
Lan
gan
an
d H
ort
on
(20
03)
112 A global assessment of offshore mariculture potential from a spatial perspective
TAB
LE A
1.4D
Ch
loro
ph
yll-
con
cen
trat
ion
s in
rel
atio
n t
o g
row
-ou
t o
f b
lue
mu
ssel
Ch
loro
ph
yll-
a co
nce
ntr
atio
n m
g/m
3N
ote
Loca
tio
nSo
urc
e
Mea
n 1
–10
Co
nce
ntr
atio
ns
pre
do
min
ant
at s
ites
wh
ere
biv
alve
s d
id
no
t ap
pea
r to
be
gre
atly
lim
ited
by
lack
of
nu
trie
nts
.G
lob
al r
evie
wSa
xby
(200
2)
> 1
Sig
nif
ican
t g
row
th o
f Pe
rna
can
alic
ulu
s o
ccu
rred
on
ly w
hen
ab
ove
th
is
con
cen
trat
ion
.M
arlb
oro
ug
h S
ou
nd
s,
New
Zea
lan
dH
awki
ns
et a
l. (1
999)
< 1
Ver
y p
oo
r to
po
or
Gro
wth
of
Pern
a ca
nal
icu
lus
in e
mb
aym
ents
as
gen
eric
gu
idel
ines
.N
ew Z
eala
nd
Ing
lis, H
ayd
en a
nd
Ro
ss (
2000
)
1–2
Mo
der
ate
Gro
wth
of
Pern
a ca
nal
icu
lus
in e
mb
aym
ents
as
gen
eric
gu
idel
ines
.N
ew Z
eala
nd
Ing
lis, H
ayd
en a
nd
Ro
ss (
2000
)
2–4
Go
od
Gro
wth
of
Pern
a ca
nal
icu
lus
in e
mb
aym
ents
as
gen
eric
gu
idel
ines
.N
ew Z
eala
nd
Ing
lis, H
ayd
en a
nd
Ro
ss (
2000
)
4–8
Idea
lG
row
th o
f Pe
rna
can
alic
ulu
s in
em
bay
men
ts a
s g
ener
ic g
uid
elin
es.
New
Zea
lan
dIn
glis
, Hay
den
an
d R
oss
(20
00)
> 8
Lit
tle
kno
wn
Gro
wth
of
Pern
a ca
nal
icu
lus
in e
mb
aym
ents
as
gen
eric
gu
idel
ines
.N
ew Z
eala
nd
Ing
lis, H
ayd
en a
nd
Ro
ss (
2000
)
> 1
M
uss
el s
hel
l gro
wth
bec
om
es f
aste
r w
ith
tem
per
atu
res
7–8
oC
.Lo
ch K
ish
orn
, Sc
otl
and
Kar
ayu
cel &
Kar
ayu
cel (
1999
)
< 1
– 5
Off
sho
re e
xper
imen
tal s
ite
wit
h g
oo
d r
esu
lts
for
gro
wth
an
d g
row
-ou
t.N
ear
Isle
s o
f Sh
oal
s,
New
Ham
psh
ire,
U
nit
ed S
tate
s o
f A
mer
ica
Lan
gan
an
d H
ort
on
(20
05)
113Annex 1
GADM database of global administrative areas
http://www.gadm.org/
Boundaries of sovereign nations
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= d8e81680-e070-11dc-9d70-0017f293bd28
Exclusive economic zones of the world - version 5
http://www.gebco.net/
General bathymetric chart of the Oceans
Depth and current speed as the fundamental criteria characterizing the technicallimits of present offshore submerged cage and longline culture systems
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 44752cb4-d5f9-4a61-a8ce-eab9bb6ab8f9
Regions with depths ranging from lower than 25 m,between 25–100 m and greater than 100 m
Regions with HYCOM current speedsat 30 m depth between 1 and 10 cm/s
for all months in the year
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 485bb2c1-f84c-40e8-83c6-0d1eb97a922a
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 73fee8e5-fcb6-47ad-bef0-365f8bd0368b
Regions with HYCOM current speeds at 30m depth between 1–10, 10–100 and > 100 cm/s
for all months in the year
4. Global data sets for estimates of offshore mariculture
114 A global assessment of offshore mariculture potential from a spatial perspective
Regions with HYCOM current speeds at 30m depth between 10 and 100 cm/s for all months in the year
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= acc9f071-d42f-4a5e-938b-d23f97f7d28f
Regions with no HYCOM current speed dataavailable 30m depth
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 88d32204-77e5-4ed6-9749-a7aada6895d7
GeoNetwork URL:www.fao.org/geonetwork/srv/en/main.home?uuid=4208693e-c4b8-448c-824f-ae3f4632305c
Regions with HYCOM current speeds at 30m depth> 100 cm/s for all months in the year
Areas within 25 nautical miles (46.3 km) of a port
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 626f7bfd-e11d-444b-9335-ba85f7474c62
Distance offshore from onshore infrastructure related to economic cost limitson transportation and on reliable access from a port to the sea
Note: Areas with no current speed data are those with depths less than 30m (i.e. all of the areas close to the shorelines) so they are difficult to see on a world map).
115Annex 1
Aqua MODIS climatology sea surface temperature (Spring 2002–2009)
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 85c03e2d-edce-4881-be4c-8ed240e1d4fb
Regions with sea surface temperatures, as defined by 95% confidence intervals, between 1.5 and 16°C
over entire year for Atlantic salmon
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= ae29adcb-5128-4fb9-adef-5a6440916031
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 10531883-6f07-47b0-88cf-67c3cd484a77
Regions with sea surface temperatures,as defined by 95% confidence intervals, between
22 and 32° C over entire year for Cobia
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 88cb7b48-7d13-4116-83c0-682ef3bb281c
Regions with sea surface temperatures, as defined by 95% confidence intervals, between 2.5 and 19°C
over entire year for blue mussel
Favourable offshore grow-out environment based on temperature requirementsof representative fish and mussels and on food availability measured as chlorophyllconcentration for the latter
Regions with chlorophyll 2 concentrations, asdefined by 95% confidence intervals, greater than
0.5 mg/m3 that were combined for the monthsavailable in each hemisphere for the blue mussel
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 34e73ea7-d62e-403c-9217-826cc2c314b5
116 A global assessment of offshore mariculture potential from a spatial perspective
2009 World database on protected areas
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= 5749f8b6-d36c-4cbc-9423-2fcc2fc22fcc
Competing, conflicting and complementary uses of ocean space
GeoNetwork URL:http://www.fao.org/geonetwork/srv/en/main.home?uuid= fcc3eb74-f3c9-484d-93e3-7c94e9226e2b
National and international marine protected areas within exclusive economic zones