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

Image Mark Davies - A bed of Zostera noltii with Hydrobia ulvae visible on the mud surface. Image width ca 40 cm.
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LS.LMS.ZOS.Znol 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 | Low | High | Major decline | High |
| Smothering | High | Low | High | Major decline | Moderate |
| Increase in suspended sediment | Intermediate | Moderate | Moderate | Minor decline | High |
| Decrease in suspended sediment | |||||
| Desiccation | Intermediate | Moderate | Moderate | Minor decline | Moderate |
| Increase in emergence regime | Intermediate | Moderate | Moderate | Minor decline | Low |
| Decrease in emergence regime | Intermediate | Moderate | Moderate | Minor decline | Moderate |
| Increase in water flow rate | Intermediate | Moderate | Moderate | Minor decline | Low |
| Decrease in water flow rate | Intermediate | Moderate | Moderate | Minor decline | Moderate |
| Increase in temperature | Low | Very high | Very low | No change | Moderate |
| Decrease in temperature | Low | Very high | Very low | No change | Moderate |
| Increase in turbidity | Intermediate | Moderate | Moderate | Minor decline | Moderate |
| Decrease in turbidity | Tolerant* | High | Not sensitive* | No change | Low |
| Increase in wave exposure | High | Very low / none | Very High | Major decline | Low |
| Decrease in wave exposure | Low | High | Low | Rise | Low |
| Noise | Tolerant | Not relevant | Not sensitive | Not relevant | Moderate |
| Visual Presence | Tolerant | Not relevant | Not sensitive | Not relevant | Moderate |
| Abrasion & physical disturbance | Intermediate | Moderate | Moderate | Minor decline | Moderate |
| Displacement | High | Very low / none | Very High | Major decline | Moderate |
| Click factor name to view rationale | Intolerance | Recoverability | Sensitivity | Species Richness | Evidence / Confidence |
|---|---|---|---|---|---|
| Synthetic compound contamination | Intermediate | Moderate | Moderate | Minor decline | Low |
| Heavy metal contamination | Intermediate | High | Low | Minor decline | Moderate |
| Hydrocarbon contamination | Intermediate | Moderate | Moderate | Minor decline | Moderate |
| Radionuclide contamination | Insufficient information | Not relevant | Insufficient information | Insufficient Information | Not relevant |
| Changes in nutrient levels | High | Very low / none | Very High | Major decline | High |
| 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 | Intermediate | Moderate | Moderate | High | |
| Introduction of non-native species | Intermediate | Low | High | Minor decline | Low |
| Extraction of this species | High | Very low / none | Very High | Minor decline | Moderate |
| Extraction of other species | High | Very low / none | Very High | Major decline | High |
| Zostera noltii Key structural | Hydrobia ulvae Important functional | Littorina littorea Important functional | Cerastoderma edule Important other | Arenicola marina Important other | |
| Substratum Loss | High | High | High | High | High |
| Smothering | High | Intermediate | High | Intermediate | Tolerant |
| Increase in suspended sediment | Intermediate | Tolerant | Intermediate | Low | Low |
| Decrease in suspended sediment | |||||
| Desiccation | Low | Low | Low | Intermediate | Not relevant |
| Increase in emergence regime | Intermediate | Low | Low | Intermediate | Intermediate |
| Decrease in emergence regime | |||||
| Increase in water flow rate | Intermediate | Intermediate | Intermediate | Intermediate | Intermediate |
| Decrease in water flow rate | |||||
| Increase in temperature | Tolerant | Intermediate | Low | Intermediate | Intermediate |
| Decrease in temperature | |||||
| Increase in turbidity | Intermediate | Tolerant | Low | Tolerant | Low |
| Decrease in turbidity | |||||
| Increase in wave exposure | High | High | Intermediate | Intermediate | Intermediate |
| Decrease in wave exposure | |||||
| Noise | Tolerant | Tolerant | Tolerant | Tolerant | Tolerant |
| Visual Presence | Tolerant | Tolerant | Tolerant | Tolerant | Tolerant |
| Abrasion & physical disturbance | Intermediate | Low | Intermediate | Intermediate | Intermediate |
| Displacement | Intermediate | Tolerant | Tolerant | Low | Low |
| Zostera noltii Key structural | Hydrobia ulvae Important functional | Littorina littorea Important functional | Cerastoderma edule Important other | Arenicola marina Important other |
|
| Synthetic compound contamination | Intermediate | Low | Low | Intermediate | High |
| Heavy metal contamination | Low | Insufficient information | Intermediate | Intermediate | Low |
| Hydrocarbon contamination | High | Intermediate | High | Intermediate | Intermediate |
| Radionuclide contamination | Insufficient information | Insufficient information | Insufficient information | Insufficient information | Insufficient information |
| Changes in nutrient levels | Intermediate | Low | Tolerant | Intermediate | Intermediate |
| Increase in salinity | Low | Tolerant | Tolerant | Low | Low |
| Decrease in salinity | |||||
| Changes in oxygenation | Low | Intermediate | Low | High | Low |
| Zostera noltii Key structural | Hydrobia ulvae Important functional | Littorina littorea Important functional | Cerastoderma edule Important other | Arenicola marina Important other |
|
| Introduction of microbial pathogens/parasites | Intermediate | High | Insufficient information | Intermediate | Insufficient information |
| Introduction of non-native species | Intermediate | Insufficient information | Insufficient information | Insufficient information | Insufficient information |
| Extraction of this species | Intermediate | Not relevant | Intermediate | Intermediate | Intermediate |
| Extraction of other species | High | Tolerant | Tolerant | High | Intermediate |
| Zostera noltii Key structural | Hydrobia ulvae Important functional | Littorina littorea Important functional | Cerastoderma edule Important other | Arenicola marina Important other | |
| Substratum Loss | Low | High | High | High | High |
| Smothering | Low | Very high | High | High | Not relevant |
| Increase in suspended sediment | High | Not relevant | High | Immediate | Immediate |
| Decrease in suspended sediment | |||||
| Desiccation | Very high | Immediate | Immediate | High | Not relevant |
| Increase in emergence regime | High | Immediate | Immediate | High | Very high |
| Decrease in emergence regime | |||||
| Increase in water flow rate | High | Very high | High | High | Very high |
| Decrease in water flow rate | |||||
| Increase in temperature | Not relevant | Immediate | Immediate | High | Very high |
| Decrease in temperature | |||||
| Increase in turbidity | High | Not relevant | Very high | Not relevant | Immediate |
| Decrease in turbidity | |||||
| Increase in wave exposure | Low | High | High | High | Very high |
| Decrease in wave exposure | |||||
| Noise | Not relevant | Not relevant | Not relevant | Not relevant | Not relevant |
| Visual Presence | Not relevant | Not relevant | Not relevant | Not relevant | Not relevant |
| Abrasion & physical disturbance | High | Very high | High | High | Very high |
| Displacement | High | Not relevant | Not relevant | High | Immediate |
| Zostera noltii Key structural | Hydrobia ulvae Important functional | Littorina littorea Important functional | Cerastoderma edule Important other | Arenicola marina Important other |
|
| Synthetic compound contamination | High | Immediate | Very high | High | High |
| Heavy metal contamination | Very high | Insufficient information | High | High | Very high |
| Hydrocarbon contamination | High | Very high | High | High | High |
| Radionuclide contamination | Not relevant | Insufficient information | Insufficient information | Insufficient information | Not relevant |
| Changes in nutrient levels | High | Immediate | Not relevant | High | High |
| Increase in salinity | Very high | Not relevant | Not relevant | Very high | Immediate |
| Decrease in salinity | |||||
| Changes in oxygenation | Very high | Very high | Very high | High | Immediate |
| Zostera noltii Key structural | Hydrobia ulvae Important functional | Littorina littorea Important functional | Cerastoderma edule Important other | Arenicola marina Important other |
|
| Introduction of microbial pathogens/parasites | Very high | High | Insufficient information | High | Not relevant |
| Introduction of non-native species | Low | Insufficient information | Insufficient information | Insufficient information | Not relevant |
| Extraction of this species | High | Not relevant | High | High | Very high |
| Extraction of other species | Low | Not relevant | Not relevant | High | Very high |
This review can be cited as follows:
Tyler-Walters, H. & Wilding, C.M. 2008. Zostera noltii beds in upper to mid shore muddy sand. Marine Life Information Network: Biology and Sensitivity Key Information Sub-programme [on-line]. Plymouth: Marine Biological Association of the United Kingdom. [cited 23/05/2013]. Available from: <http://www.marlin.ac.uk/habitatsensitivity.php?habitatid=318&code=1997>
|
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