Download (20MB) - Repository@Napier
Download (20MB) - Repository@Napier Download (20MB) - Repository@Napier
esulting community at any stage of succession is likely to depend upon the timing of the initial disturbance (Zajac and Whitlatch, 1982a; 1982b). Drum Sands is an ideal location in which to explicitly test certain aspects of population and community responses to disturbances. For example, it has been shown that the study area within Drum Sands contains a mosaic of communities in different successional stages with some species, for example, P. elegans, exhibiting pronounced patchiness (see Chapter 2). P. elegans has the ability to affect the hydrodynamics of near-bed flow and therefore the potential to affect settlement. Furthermore, this species has been shown to have a wide repertoire of reproductive strategies which was investigated in Chapter 3. Therefore, this system allowed certain questions about initial colonisation to be addressed. These were: 1 - do tube-bed areas have different early successional dynamics from non tube-bed areas?. This will be examined by comparing the initial communities of P. elegans patches with those of non-patch areas after a small-scale disturbance; 2 - does the successional stage of a community affect the colonisation mode of early colonisers?. This will be addressed by assessing the dispersal mode of the most abundant species to recently disturbed sediments within P. elegans patches with those from disturbances within non-patch sediments; 3 - can sediment disturbance lead to P. elegans patch formation on Drum Sands?. 133
METHODS Experimental design - Eighty P. elegans patches were individually numbered from within the 250x400m study area (Chapter 1) so that patches could be selected randomly for experimentation. Six P. elegans patches (hereafter referred to as 'patch' plots) were randomly chosen and a 1m 2 area marked within each by a small cane at each corner. The patches themselves were approximately 1-1.5m 2 in area (Chapter 2). Similarly, 6 plots were chosen outside P. elegans patches (hereafter referred to as 'non-patch' plots) by random co-ordinates within the study area and a 1m 2 area marked in the same way as for patch plots. Six replicates were chosen as this was decided to be the most that could be logistically sampled with respect to the amount of work involved and this was a sufficient number to allow non-parametric statistical analyses to be carried out if necessary. None of these plots had macroalgal mat cover either at the time of sediment implantation or at the time of sampling. Sediment was obtained by inserting 12 corers, 10cm diameter, into the sand within the study area from non-patch sediments to a depth of 12cm. The sediment was kept in the corers and frozen at -20°C for 3 days, thawed for 1 day and then refrozen. Sediment defaunation by freezing at this temperature has been successfully achieved in many studies (e.g., Bonsdorff and Osterman, 1984; Savidge and Taghon, 1988; Bonsdorff, 1989; Frid, 1989; Thrush et al., 1992). This freeze-thawing was repeated 6 times for each core. After treatment, no animals were found alive (n=6) and all the invertebrate taxa killed by this process were so severely damaged that they could easily be distinguished from invertebrates alive at the time of subsequent sampling (except nematodes). Any P. elegans tubes protruding from the treated sediment surfaces were removed. The sediment cores were kept intact throughout the freeze- thawing process, maintaining the original sediment structure was thought to reduce erosion when later replaced in the sand. The 12 defaunated sediments were implanted on the 18th April 1997, ensuring that the tops were flush with the surrounding sediment surface. One defaunated sediment core was inserted into each of the 6 patch plots and 6 non-patch plots (see Figure 6.1). A 1m2 quadrat was located on the predefined 1m 2 areas (see above), divided into 100 sections (10x10cm) with string and the defaunated sediments inserted after the 134
- Page 98 and 99: CHAPTER 4 THE EFFECTS OF MACROALGAL
- Page 100 and 101: studies may have been completely di
- Page 102 and 103: METHODS Study site - The exact posi
- Page 104 and 105: 1 C N W 4----111" 1.5m 2 NW C Contr
- Page 106 and 107: sediment sampling, together with re
- Page 108 and 109: RESULTS Species abundances - The me
- Page 110 and 111: ; 15 35 — 30 — 25 — 10 — 5
- Page 112 and 113: statistical difference from net plo
- Page 114 and 115: Pygospio elegans size distribution
- Page 116 and 117: used, approximately equivalent to t
- Page 118 and 119: artefacts associated with the metho
- Page 120 and 121: present in high numbers around sewa
- Page 122 and 123: lack, hydrogen sulphide-smelling se
- Page 124 and 125: CHAPTER 5 THE EFFECTS OF MACROALGAL
- Page 126 and 127: METHODS Survey design - During late
- Page 128 and 129: The sediments could not be sampled
- Page 130 and 131: RESULTS Species abundances - Table
- Page 132 and 133: 90 — 80 — "-e-' 70 — 60 — 4
- Page 134 and 135: 35 — *** 30 25 — 1.) = .-c‘l
- Page 136 and 137: Pygospio elegans size distributions
- Page 138 and 139: which is difficult to compare with
- Page 140 and 141: eason why some invertebrates showed
- Page 142 and 143: This study did not set out to expli
- Page 144 and 145: This reliance upon the early establ
- Page 146 and 147: CHAPTER 6 INITIAL COLONISATION OF D
- Page 150 and 151: ambient sediment had been removed.
- Page 152 and 153: emoved since they were the only tax
- Page 154 and 155: All statistics were performed using
- Page 156 and 157: RESULTS Univariate analysis of spec
- Page 158 and 159: 3.5 3 5 2 11 5 1 0.5 0 40 35 Ca 30
- Page 160 and 161: of non-patch areas (Figure 6.3(vi))
- Page 162 and 163: the individuals colonising patch az
- Page 164 and 165: Multivariate analysis of community
- Page 166 and 167: Month Sample statistic (Global R) N
- Page 168 and 169: 2NP 3NP 4NP .•,, 6NP 5NP 6P 1NP i
- Page 170 and 171: Figure 6.8: Two-dimensional MDS ord
- Page 172 and 173: - - 5P ... 4P . 6P • .‘2NP 1NP
- Page 174 and 175: I 50. 1 60. 70. 80. 90. 100. BRAY-C
- Page 176 and 177: 'P2-AZ P3-AZ N2-AZ .- - - " .„ ..
- Page 178 and 179: o • o -o + 350 — 300 = 250 7 g
- Page 180 and 181: The importance of the ambient commu
- Page 182 and 183: In April, when P. elegans larval av
- Page 184 and 185: not only for errant polychaetes, bu
- Page 186 and 187: observed in this study. How crucial
- Page 188 and 189: Micro-scale spatial patterns of mac
- Page 190 and 191: METHODS Experimental design - A pre
- Page 192 and 193: study. These individuals would not
- Page 194 and 195: RESULTS Pilot survey - The pilot su
- Page 196 and 197: Transect survey - Micro-scale patte
METHODS<br />
Experimental design - Eighty P. elegans patches were individually numbered from<br />
within the 250x400m study area (Chapter 1) so that patches could be selected<br />
randomly for experimentation. Six P. elegans patches (hereafter referred to as 'patch'<br />
plots) were randomly chosen and a 1m 2 area marked within each by a small cane at<br />
each corner. The patches themselves were approximately 1-1.5m 2 in area (Chapter 2).<br />
Similarly, 6 plots were chosen outside P. elegans patches (hereafter referred to as<br />
'non-patch' plots) by random co-ordinates within the study area and a 1m 2 area<br />
marked in the same way as for patch plots. Six replicates were chosen as this was<br />
decided to be the most that could be logistically sampled with respect to the amount of<br />
work involved and this was a sufficient number to allow non-parametric statistical<br />
analyses to be carried out if necessary. None of these plots had macroalgal mat cover<br />
either at the time of sediment implantation or at the time of sampling.<br />
Sediment was obtained by inserting 12 corers, 10cm diameter, into the sand within the<br />
study area from non-patch sediments to a depth of 12cm. The sediment was kept in<br />
the corers and frozen at -20°C for 3 days, thawed for 1 day and then refrozen.<br />
Sediment defaunation by freezing at this temperature has been successfully achieved<br />
in many studies (e.g., Bonsdorff and Osterman, 1984; Savidge and Taghon, 1988;<br />
Bonsdorff, 1989; Frid, 1989; Thrush et al., 1992). This freeze-thawing was repeated 6<br />
times for each core. After treatment, no animals were found alive (n=6) and all the<br />
invertebrate taxa killed by this process were so severely damaged that they could<br />
easily be distinguished from invertebrates alive at the time of subsequent sampling<br />
(except nematodes). Any P. elegans tubes protruding from the treated sediment<br />
surfaces were removed. The sediment cores were kept intact throughout the freeze-<br />
thawing process, maintaining the original sediment structure was thought to reduce<br />
erosion when later replaced in the sand.<br />
The 12 defaunated sediments were implanted on the 18th April 1997, ensuring that the<br />
tops were flush with the surrounding sediment surface. One defaunated sediment core<br />
was inserted into each of the 6 patch plots and 6 non-patch plots (see Figure 6.1). A<br />
1m2 quadrat was located on the predefined 1m 2 areas (see above), divided into 100<br />
sections (10x10cm) with string and the defaunated sediments inserted after the<br />
134