| Basic Information | Biotope classification | Ecology | Habitat preferences and distribution | Species composition | Sensitivity | Importance |

Image Keith Hiscock - Current swept bed of Zostera marina. Image width ca 2 m in foreground.
Image copyright information
SS.SMp.SSgr.Zmar recorded (
) and expected (
) distribution in Britain and Ireland (see below)
| Click factor name to view rationale | Intolerance | Recoverability | Sensitivity | Species Richness | Evidence / Confidence |
|---|---|---|---|---|---|
| Substratum Loss | High | Very low / none | Very High | Major decline | Moderate |
| Smothering | High | Very low / none | Very High | Major decline | Moderate |
| Increase in suspended sediment | Intermediate | Moderate | Moderate | Decline | Moderate |
| Decrease in suspended sediment | |||||
| Desiccation | Intermediate | High | Low | Decline | Low |
| Increase in emergence regime | Intermediate | High | Low | Minor decline | Low |
| Decrease in emergence regime | |||||
| Increase in water flow rate | Intermediate | Moderate | Moderate | Minor decline | Low |
| Decrease in water flow rate | |||||
| Increase in temperature | Low | Very high | Very low | Minor decline | Low |
| Decrease in temperature | |||||
| Increase in turbidity | High | Very low / none | Very High | Major decline | Moderate |
| Decrease in turbidity | |||||
| Increase in wave exposure | High | Very low / none | Very High | Major decline | Low |
| Decrease in wave exposure | |||||
| Noise | Tolerant | Not relevant | Not sensitive | Minor decline | Very low |
| Visual Presence | Tolerant | Not relevant | Not sensitive | No change | Very low |
| Abrasion & physical disturbance | Intermediate | Moderate | Moderate | Decline | Low |
| Displacement | High | Low | High | Major decline | Low |
| Click factor name to view rationale | Intolerance | Recoverability | Sensitivity | Species Richness | Evidence / Confidence |
|---|---|---|---|---|---|
| Synthetic compound contamination | Intermediate | Moderate | Moderate | Decline | Moderate |
| Heavy metal contamination | Low | High | Low | No change | Low |
| Hydrocarbon contamination | Intermediate | High | Low | Decline | Moderate |
| Radionuclide contamination | Insufficient information | Insufficient information | Insufficient information | Insufficient Information | Not relevant |
| Changes in nutrient levels | High | Very low / none | Very High | Major decline | Moderate |
| Increase in salinity | Low | Very high | Very low | No change | Moderate |
| Decrease in salinity | |||||
| Changes in oxygenation | Intermediate | High | Low | Minor decline | Low |
| Click factor name to view rationale | Intolerance | Recoverability | Sensitivity | Species Richness | Evidence / Confidence |
|---|---|---|---|---|---|
| Introduction of microbial pathogens/parasites | High | Very low / none | Very High | High | |
| Introduction of non-native species | Intermediate | Low | High | Minor decline | Low |
| Extraction of this species | Intermediate | Moderate | Moderate | Decline | Low |
| Extraction of other species | Intermediate | Moderate | Moderate | Decline | Low |
| Zostera marina Key structural | Lacuna vincta Important structural | Hydrobia ulvae Important structural | |
| Substratum Loss | High | High | High |
| Smothering | High | Intermediate | Intermediate |
| Increase in suspended sediment | Intermediate | Low | Tolerant |
| Decrease in suspended sediment | |||
| Desiccation | Intermediate | Intermediate | Low |
| Increase in emergence regime | Intermediate | Intermediate | Low |
| Decrease in emergence regime | |||
| Increase in water flow rate | Intermediate | Intermediate | Intermediate |
| Decrease in water flow rate | |||
| Increase in temperature | Tolerant | Intermediate | Intermediate |
| Decrease in temperature | |||
| Increase in turbidity | High | Low | Tolerant |
| Decrease in turbidity | |||
| Increase in wave exposure | High | Intermediate | High |
| Decrease in wave exposure | |||
| Noise | Tolerant | Tolerant | Tolerant |
| Visual Presence | Tolerant | Tolerant | Tolerant |
| Abrasion & physical disturbance | Intermediate | High | Low |
| Displacement | High | Tolerant | Tolerant |
| Zostera marina Key structural | Lacuna vincta Important structural | Hydrobia ulvae Important structural |
|
| Synthetic compound contamination | Intermediate | Insufficient information | Low |
| Heavy metal contamination | Low | Insufficient information | Insufficient information |
| Hydrocarbon contamination | Low | Intermediate | Intermediate |
| Radionuclide contamination | Insufficient information | Insufficient information | Insufficient information |
| Changes in nutrient levels | High | Tolerant | Low |
| Increase in salinity | Low | Tolerant | Tolerant |
| Decrease in salinity | |||
| Changes in oxygenation | Low | Intermediate | Intermediate |
| Zostera marina Key structural | Lacuna vincta Important structural | Hydrobia ulvae Important structural |
|
| Introduction of microbial pathogens/parasites | High | Insufficient information | High |
| Introduction of non-native species | Intermediate | Insufficient information | Insufficient information |
| Extraction of this species | Intermediate | Not relevant | Not relevant |
| Extraction of other species | Intermediate | Intermediate | Tolerant |
| Zostera marina Key structural | Lacuna vincta Important structural | Hydrobia ulvae Important structural | |
| Substratum Loss | High | High | |
| Smothering | High | Very high | |
| Increase in suspended sediment | Moderate | Immediate | Not relevant |
| Decrease in suspended sediment | |||
| Desiccation | High | High | Immediate |
| Increase in emergence regime | High | High | Immediate |
| Decrease in emergence regime | |||
| Increase in water flow rate | Moderate | High | Very high |
| Decrease in water flow rate | |||
| Increase in temperature | Not relevant | High | Immediate |
| Decrease in temperature | |||
| Increase in turbidity | Very high | Not relevant | |
| Decrease in turbidity | |||
| Increase in wave exposure | High | High | |
| Decrease in wave exposure | |||
| Noise | Not relevant | Not relevant | Not relevant |
| Visual Presence | Not relevant | Not relevant | Not relevant |
| Abrasion & physical disturbance | Moderate | High | Very high |
| Displacement | Low | Not relevant | Not relevant |
| Zostera marina Key structural | Lacuna vincta Important structural | Hydrobia ulvae Important structural |
|
| Synthetic compound contamination | Moderate | Insufficient information | Immediate |
| Heavy metal contamination | Very high | Insufficient information | Insufficient information |
| Hydrocarbon contamination | Very high | High | Very high |
| Radionuclide contamination | Insufficient information | Insufficient information | Insufficient information |
| Changes in nutrient levels | Not relevant | Immediate | |
| Increase in salinity | Very high | Not relevant | Not relevant |
| Decrease in salinity | |||
| Changes in oxygenation | Very high | High | Very high |
| Zostera marina Key structural | Lacuna vincta Important structural | Hydrobia ulvae Important structural |
|
| Introduction of microbial pathogens/parasites | Insufficient information | High | |
| Introduction of non-native species | Low | Insufficient information | Insufficient information |
| Extraction of this species | Moderate | Not relevant | Not relevant |
| Extraction of other species | Moderate | High | Not relevant |
This review can be cited as follows:
Tyler-Walters, H. & Wilding, C.M. 2008. Zostera marina/angustifolia beds in lower shore or infralittoral clean or muddy sand. Marine Life Information Network: Biology and Sensitivity Key Information Sub-programme [on-line]. Plymouth: Marine Biological Association of the United Kingdom. [cited 24/05/2013]. Available from: <http://www.marlin.ac.uk/habitatsensitivity.php?habitatid=257&code=2004>