Demersal fin fish, shrimp,
Nephrops
|
Beam
trawling,
Otter Trawling
|
·
Trawl tracks visible for varying amount of
time, depending on substrate, gear and tidal
conditions ie. days or months.
·
Top 10 - 60 mm of substrate disturbed.
·
Resuspension of sediment.
·
Sediment structure may change from coarse
grained sand/gravel to fine sand/coarse silt.
·
Significant reduction in biomass of target
and non-target species immediately after fishing
operation. Likely to be more pronounced with
extended recovery times, ie. many months,
in areas with diverse communities and stable
conditions.
·
Considerable variation in damage or mortality
to affected species. Fragile, long lived,
slow moving or sedentary species most vulnerable.
·
Repeated trawling may cause benthic community
structure to change, favouring more mobile
species, rapid colonisers and juvenile stages.
·
Influx of scavenging species post fishing
operation.
·
Biogenic reefs, eg. Sabellaria, and
species that stabilise sediments, eg. eel
grass, may be severely damaged resulting in
resuspension of sediment.
|
Demersal fin fish
|
Gill
nets |
·
!
Incidental catch of marine life including
marine mammals and birds.
·
'Ghost fishing', dependent on condition of
gear. In rocky less exposed areas may be active
for months, on clean exposed ground, days
to weeks.
|
Razor shell
|
Hydraulic
dredge |
·
Subtidal dredge tracks, deeper than a conventional
hydraulic cockle dredge (eg. 0.5 - 3.5 m wide,
0.25 - 0.6 m deep) visible for months in mobile
sediments.
·
Substantial physical disturbance of substrate
·
Significant reduction in abundance of non
target species immediately after fishing operation.
Weeks/months to recover to pre fishing levels
in mobile sediment.
|
Scallops
|
Scallop
dredge |
·
Dredge tracks visible for varying amount
of time ie. days or months in stable conditions
a relatively minor fishery may have a significant
cumulative effect on bottom micro topography.
·
Top 60 -100 mm of substrate disturbed.
·
Resuspension of sediment.
·
Significant reduction in biomass of target
and non target species immediately after fishing
operation. Likely to be more pronounced with
extended recovery times, ie many months, in
areas with diverse communities and stable
conditions.
·
Maerl crushed, smothered and killed.
·
Associated biota of maerl either caught, damaged
or smothered by sediment.
|
Aquaculture
|
Finfish
cages |
·
Impact on benthic communities through
deposition of organic material (faeces and
waste food).
·
Development of anoxic conditions in sediment
and water column in low energy site with subsequent
outgassing of hydrogen sulphide and ammonia.
·
Potential for hypernutrifiaction in low energy
locations.
·
Potential effects of sea lice treatments,
antibiotics and antifoulants.
|
Aquaculture
|
Shellfish
cultivation |
·
Increased sedimentation and effects on infauna
beneath mussel cultures.
· Manila clam cultivation in lays increases
density of benthic species, changes in infauna
and increased sedimentation.
·
Harvesting with hand raking reduces species
diversity and abundance by 50 %, suction
dredging reduces species abundance by 80-90%.
Recovery to pre-harvesting levels may take
long periods eg. 7 months.
·
Trenching up to 10 cm deep, may take months
to fill eg. 4 months in one study.
·
Accidental introduction of alien species.
|