Analysing data hom post-impact studies using asymmetrical analyses of variance: A case study of epibiota on marinas

被引:134
作者
Glasby, TM [1 ]
机构
[1] Univ Sydney, Marine Ecol Labs, Inst Marine Ecol, Sydney, NSW 2006, Australia
来源
AUSTRALIAN JOURNAL OF ECOLOGY | 1997年 / 22卷 / 04期
关键词
beyond BACI; environmental impact assessment; epibiota; marinas; pilings; statistics;
D O I
10.1111/j.1442-9993.1997.tb00696.x
中图分类号
Q14 [生态学(生物生态学)];
学科分类号
071012 ; 0713 ;
摘要
Several recent methods have been developed for detecting anthropogenic perturbations. Most have been analyses of data collected before and after some anthropogenic disturbance. It may, however, be more common that data can be collected only after a disturbance has occurred. In such situations, the only appropriate sampling design to use will often be an asymmetrical design because it will avoid problems of spatial confounding. Here, I describe in detail the steps involved in constructing asymmetrical analyses of variance using a case study of subtidal epibiota around marinas as an example. Differences between the marina and control locations were detected for a number of taxa, but this was often only possible after post-hoc pooling of non-significant terms. Marina and control locations varied greatly from estuary to estuary and consequently it was not possible to identify suites of species that were typical of either type of location. This result highlighted the need for multiple control locations near each marina to allow a reliable estimate of the variability among controls. Large variability among controls would mean that if differences existed between disturbed and control locations they would rarely be detected. These and other problems associated with analysing 'after data' are discussed in addition to the precautions to take when designing environmental sampling regimes.
引用
收藏
页码:448 / 459
页数:12
相关论文
共 62 条
[1]  
ANDREW NL, 1987, OCEANOGR MAR BIOL, V25, P39
[2]  
BAIRD D, 1981, S AFR J ZOOL, V16, P21
[3]  
BERNSTEIN BB, 1983, J ENVIRON MANAGE, V16, P35
[4]   SCIENTIFIC UNCERTAINTY AND THE PRECAUTIONARY PRINCIPLE [J].
BODANSKY, D .
ENVIRONMENT, 1991, 33 (07) :4-&
[5]   Development and long term dynamics of a fouling assemblage of sessile marine invertebrates [J].
Butler, AJ ;
Connolly, RM .
BIOFOULING, 1996, 9 (03) :187-209
[7]   VARIABILITY AT DIFFERENT SPATIAL SCALES BETWEEN A SUBTIDAL ASSEMBLAGE EXPOSED TO THE DISCHARGE OF SEWAGE AND 2 CONTROL ASSEMBLAGES [J].
CHAPMAN, MG ;
UNDERWOOD, AJ ;
SKILLETER, GA .
JOURNAL OF EXPERIMENTAL MARINE BIOLOGY AND ECOLOGY, 1995, 189 (1-2) :103-122
[8]   NONPARAMETRIC MULTIVARIATE ANALYSES OF CHANGES IN COMMUNITY STRUCTURE [J].
CLARKE, KR .
AUSTRALIAN JOURNAL OF ECOLOGY, 1993, 18 (01) :117-143
[9]  
Crowder MJ, 1990, ANAL REPEATED MEASUR
[10]   COMPARISONS OF TREATMENTS AFTER AN ANALYSIS OF VARIANCE IN ECOLOGY [J].
DAY, RW ;
QUINN, GP .
ECOLOGICAL MONOGRAPHS, 1989, 59 (04) :433-463