Conservation and management of northeast Atlantic and Mediterranean maerl beds

被引:151
作者
Barbera, C
Bordehore, C
Borg, JA
Glémarec, M
Grall, J
Hall-Spencer, JM
De la Huz, C
Lanfranco, E
Lastra, M
Moore, PG [1 ]
Mora, J
Pita, ME
Ramos-Espla, AA
Rizzo, M
Sánchez-Mata, A
Seva, A
Schembri, PJ
Valle, C
机构
[1] Univ Marine Biol Stn, Millport KA28 0EG, Isle Of Cumbrae, Scotland
[2] Univ Alicante, E-03080 Alicante, Spain
[3] Univ Malta, Dept Biol, Msida, Malta
[4] Inst Univ Europeen Mer, UMR CNRS Ecol Benth 6539, F-29280 Plouzane, France
[5] Univ Plymouth, Sch Biol Sci, Plymouth PL4 8AA, Devon, England
[6] Univ Vigo, Dept Ecol & Biol Anim, Fac Ciencias, Vigo 36200, Spain
[7] Univ Santiago de Compostela, Dept Biol Anim, Fac Biol, Santiago De Compostela 15706, Galicia, Spain
关键词
maerl; rhodoliths; Atlantic; Mediterranean; Habitats Directive; SPABIM; anthropogenic impacts;
D O I
10.1002/aqc.569
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
1. Maerl beds occur worldwide and are formed by an accumulation of unattached calcareous red algae (Rhodophyta). 2. Maerl-forming algae grow in a superficial living layer on sediments within the photic zone. 3. Maerl beds are spatially complex habitats with a high degree of species and trophic group diversity. 4. The European Commission's 'Habitats Directive' mandates the conservation management of two of the main European maerl-forming species, Phymatolithon calcareum and Lithothamnion corallioides. 5. Mediterranean maerl beds are to be considered for inclusion in national inventories of sites of conservation interest, as required by the SPABIM Protocol of the Barcelona Convention. 6. In spite of their importance, and the requirement for their conservation management, European maerl grounds suffer a variety of anthropogenic perturbations including direct exploitation through extraction, fishing impacts and chemical pollution by organic matter and excess nutrients. 7. The ecology of northeast Atlantic and Mediterranean maerl beds has received little attention, in contrast to other marine communities (e.g. kelp forests, sea-grass meadows). 8. Key conservation and management measures proposed include: the recognition that maerl beds are non-renewable resources and cannot sustain direct exploitation; prohibitions on the use of towed gear on maerl grounds; moratoria on the issue of further permits for the siting of aquaculture units above maerl grounds; monitoring of existing exploited or impacted maerl beds; the designation of,no-take' reserves; measures to limit the impacts that might affect water quality above maerl beds; a programme of monitoring of the 'health' of European maerl beds; an awareness campaign on the biological importance of maerl beds; a higher conservation status for maerl habitats and maerl-forming species in European legislation; and further research on maerl ecosystems. Copyright (C) 2003 John Wiley Sons, Ltd.
引用
收藏
页码:S65 / S76
页数:12
相关论文
共 62 条
[1]  
Ballesteros E, 1989, COLLECT BOT BARCELON, V17, P161, DOI DOI 10.3989/COLLECTBOT.1989.V17.137
[2]  
Basso D, 1996, B SOC PALEONTOLOGICA, V3, P1
[3]  
BELLANSANTINI D, 1994, BIOCENOSES MARINES L
[4]  
*BIOMAERL TEAM, 1998, P 3 EUR MAR SCI TECH, V1
[5]  
Birkett DA, 1998, OVERVIEW DYNAMIC SEN, VV
[6]   COMPOSITION OF MAERL FROM GLENAN-ISLANDS OF SOUTHERN BRITTANY [J].
BLUNDEN, G ;
FARNHAM, WF ;
JEPHSON, N ;
FENN, RH ;
PLUNKETT, BA .
BOTANICA MARINA, 1977, 20 (02) :121-125
[7]  
BOHSANCK JA, 1996, OCEANOGRAPHY, V9, P73
[8]  
Bordehore C, 2000, 1 MED S MAR VEG REG
[9]  
BORDEHORE C, 1999, P 1 INT WORKSH MAR R
[10]  
BORG JA, 1998, ICES C EC EFF FISH H