Spread of invasive species into Scotland: study

A horizon scanning study involving analysis of pathways of spread of invasive non-native species into Scotland. It considers species having the highest likelihood of arrival and establishment and the magnitude of their potential negative impact on biodiversity and ecosystems over the next 10 years.


Results

Horizon scanning

The compiled long-lists of INNS predicted to arrive, establish and impact biodiversity and ecosystem services, human health and economies are presented in Annexes 3, 4 and 5 respectively. In total 171, 27 and 47 species were included in the long-lists of INNS predicted to have impacts on biodiversity and ecosystem services, human health and economies respectively. The top 10 list, derived through review of the long-list of INNS predicted to have impacts on biodiversity and ecosystems in consultation with NatureScot experts, included two groups of species (flatworms and Dreissena species) alongside a further eight species spanning terrestrial, freshwater and marine environments (Table 2). Five INNS within the top 10 list were freshwater species. Only one marine species was included.

Table 2. Top 10 list of invasive non-native species predicted to arrive, establish and impact biodiversity and ecosystem services noting that the flatworms are grouped together as are the two Dreissena species (further information is provided in the text on the differences between these species). The Horizon Scanning ( HS) Expert Group refers to the thematic group that considered the invasive non-native species. All species were attributed the maximum scores for likelihood of arrival, establishment and impact on biodiversity and ecosystems. Two further species also received these high scores, but both are considered separately within plant health (Agrilus planipennis, emerald ash borer) or animal health (Gyrodactylus salaris, salmon fluke) legislation, so not included on the list. The table is ordered alphabetically within thematic groups.
Species Name English Name HS Expert Group
Anemanthele lessoniana [8] Pheasant's-tail Terrestrial plants
Corbicula fluminea Asian clam Freshwater
Dreissena polymorpha Zebra mussel Freshwater
Dreissena rostriformis bugensis Quagga mussel Freshwater
Australoplana sanguinea Australian flatworm Terrestrial invertebrates
Caenoplana variegata (formerly known as C. bicolor) Southampton flatworm Terrestrial invertebrates
Kontikia andersoni Brown Kontikia flatworm Terrestrial invertebrates
Obama nungara Obama flatworm Terrestrial invertebrates
Hydrocotyle ranunculoides Floating pennywort Freshwater
Muntiacus reevesi Reeve's muntjac Terrestrial vertebrates
Myriophyllum aquaticum Parrot's feather Freshwater
Procyon lotor Raccoon Terrestrial vertebrates
Vaccinium corymbosum (and hybrids) Highbush blueberry Terrestrial plants
Crepidula fornicata Mollusc Marine

One-third of the INNS on the top 30 list (Table 3) were freshwater species while only three of the species were from the marine environment. There were eight terrestrial invertebrates listed and six terrestrial plants with the remaining three species being terrestrial vertebrates. Most of the top 30 list were assigned the highest impact score of five.

Table 3. Top 30 list of invasive non-native species ( INNS) predicted to arrive, establish and impact biodiversity and ecosystem services. The Horizon Scanning Expert Group refers to the thematic group that considered the INNS. Scores of 1-5 were given for likelihood of arrival, establishment and impact on biodiversity and ecosystems (noting that scores were not included for human health and economic impacts). The long list of 171 species with at least medium likelihood of arrival, establishment and impact on biodiversity and ecosystems is in Annex 3. A full spreadsheet of all species scored by the groups was also compiled for INNS with impacts on biodiversity and ecosystem services. Table ordered by overall score, expert group and then alphabetically by species name. Kontikia andersoni was not included in the top 30 but was with the other flatworms in the top 10 for communication campaigns.
Species name English name HS expert group Arrival Estab. Bio. impact Overall score
Corbicula fluminea Asian clam Freshwater 5 5 5 125
Dreissena polymorpha Zebra mussel Freshwater 5 5 5 125
Dreissena rostriformis bugensis Quagga mussel Freshwater 5 5 5 125
Gyrodactylus salaris Salmon fluke Freshwater 5 5 5 125
Hydrocotyle ranunculoides Floating pennywort Freshwater 5 5 5 125
Myriophyllum aquaticum Parrot's feather Freshwater 5 5 5 125
Crepidula fornicata Mollusc Marine 5 5 5 125
Agrilus planipennis Emerald ash borer Terrestrial invertebrates 5 5 5 125
Australoplana sanguinea Flatworm Terrestrial invertebrates 5 5 5 125
Caenoplana variegata (formerly known as C. bicolor) Southampton flatworm Terrestrial invertebrates 5 5 5 125
Corythucha arcuata Oak lace bug Terrestrial invertebrates 5 5 5 125
Obama nungara Obama flatworm Terrestrial invertebrates 5 5 5 125
Vespa velutina Asian hornet Terrestrial invertebrates 5 5 5 125
Anemanthele lessoniana Pheasant's-tail Terrestrial plants 5 5 5 125
Baccharis halimifolia [9] Tree groundsel Terrestrial plants 5 5 5 125
Vaccinium corymbosum (and hybrids) Highbush blueberry Terrestrial plants 5 5 5 125
Muntiacus reevesi Reeve's muntjac Terrestrial vertebrates 5 5 5 125
Procyon lotor Raccoon Terrestrial vertebrates 5 5 5 125
Eriocheir sinensis Chinese mitten crab Freshwater 5 5 4 100
Ludwigia grandiflora Water primrose Freshwater 5 5 4 100
Sander lucioperca Zander Freshwater 4 5 5 100
Silurus glanis Wels catfish Freshwater 4 5 5 100
Agarophyton vermiculophyllum (previously Gracilaria vermiculophylla) Alga Marine 5 5 4 100
Homarus americanus American lobster Marine 5 5 4 100
Ips sexdentatus Terrestrial invertebrates 5 5 4 100
Thaumetopoea processionea Oak processionary Terrestrial invertebrates 5 5 4 100
Acer negundo Box-elder Terrestrial plants 5 5 4 100
Ailanthus altissima Tree of heaven Terrestrial plants 5 4 5 100
Elaeagnus pungens Thorny olive Terrestrial plants 5 5 4 100
Nyctereutes procyonoides Raccoon dog Terrestrial vertebrates 5 5 4 100

Comprehensive Pathways Analysis

The INNS on the top 10 and top 30 lists were predicted to arrive through a range of pathways (Figure 2). Escape from confinement dominated on both lists with the ornamental and horticultural pathways being the most important pathways in relation to the number of species associated with these pathways.

Figure 2. Total numbers of species on the top 10 and top 30 lists derived through the horizon scanning for each CBD pathway (for pathway codes see Table 1).
A barchart showing the total numbers of invasive non-native species for each CBD pathway for species on the top 10 and top 30 lists derived through the horizon scanning. The escape from confinement pathways dominate both lists and the horticultural and ornamental pathways are the most important pathways in relation to the number of species associated with these pathways. Escape of pets, escapes from botanical gardens and zoos, aesthetic releases and habitat material contaminants are also important pathways for species on both lists as is unaided dispersal of non-natives from neighbouring regions (e.g. spread of non-native species from England into Scotland).

The version of the horizon scanning long list used in the pathway analysis contained three plant species that were later excluded from the long list. This was due to the decision that they were probably now established based on a re-examination of records in the Botanical Society of Britain and Ireland recording database.

The breakdown of pathways associated with species that are established in Scotland, for all established species (1096 species) and also for only established species that were first recorded in Scotland since 1950 (483 species, hereafter referred to as recently established) is shown in Figure 3. The top 10 pathways for established species and their relative and cumulative contributions are shown in Table 4.

The pathways associated with the highest number of species (for both all established and recently established species) were the horticulture and ornamental pathways ranked 1st and 2nd respectively (Figure 3). These two pathways combined contributed over 50% of the total number of species (52% and 60% for all established and recently established species respectively, see Table 4).

Although notably lower than the horticulture and ornamental pathways, the agriculture, seed contaminant, aesthetic release, and other release pathways were still associated with substantial numbers of established species. These pathways were ranked 3rd, 4th, 5th and 6th for all established species and with 5th, 6th, 3rd and 4th respectively for recently established species. These top six pathways together contributed 76% of total number of species scores.

Figure 3. Total numbers of established species associated with each CBD pathway for a) all established species, b) only established species that were first recorded in Scotland since 1950. The top 10 ranked pathways are labelled with their rank in the bars.
Two barcharts. The first barchart shows the total number of all established invasive non-native species associated with each CBD pathway. The horticultural pathway ranks first and the ornamental pathway ranks a close second. The agriculture, seed contaminant, aesthetic release and other release pathways are notably lower and rank third, fourth, fifth and sixth respectively. The food contaminant, other contaminant, natural dispersal and habitat material contaminant pathways rank seventh, eighth, ninth and tenth respectively. The second barchart shows the number of established species first recorded in Scotland from 1950 onwards that are associated with each CBD pathway. Again the horticultural pathway ranks first and the ornamental pathway ranks a close second. The aesthetic release, other release, agriculture escape and seed contaminant pathways are much lower and rank third, fourth, fifth and sixth respectively. The hull fouling pathway ranks seventh, the natural dispersal and animal contaminant pathways rank joint eighth and the plant contaminant pathway ranks tenth.
Table 4. Top 10 ranked pathways for established species based on the number of species associated with each pathway for all established species or only established species first recorded in Scotland from 1950 onwards. For each pathway the proportion of the data associated with that pathway and the cumulative proportion (combined total of pathways ranked equal to or higher than the current pathway expressed as a proportion of the total dataset) are also shown.
Rank Pathway No. Species Proportion Cumulative Proportion
All established species 1 Horticulture 750 0.278 0.278
2 Ornamental 672 0.249 0.526
3 Agriculture 186 0.069 0.595
4 Seed contaminant 178 0.066 0.661
5 Aesthetic release 171 0.063 0.724
6 Other release 105 0.039 0.763
7 Food contaminant 56 0.021 0.784
8 Other contaminant 52 0.019 0.803
9 Natural dispersal 49 0.018 0.821
10 Habitat material contaminant 48 0.018 0.839
Established species first recorded since 1950 1 Horticulture 366 0.317 0.317
2 Ornamental 327 0.283 0.600
3 Aesthetic release 84 0.073 0.673
4 Other release 37 0.032 0.705
5 Agriculture 35 0.030 0.735
6 Seed contaminant 30 0.026 0.761
7 Hull fouling 29 0.025 0.786
8 Contaminant of animals 25 0.022 0.808
8 Natural dispersal 25 0.022 0.829
10 Contaminant of plants 24 0.021 0.850

In the top 10 ranked pathways the only other pathway in common between the analyses of all established species and recently established species was the natural dispersal pathway which was ranked 9th and 8th (tied) respectively. The remaining pathways in the top 10 ranked pathways for all established species were food contaminant (7th with 56 spp.), other contaminant (8th with 52 spp.) and habitat material contaminant (10th with 48 spp.), while those for the recent established species were; hull fouling (7th with 29 spp.), contaminant of animals (tied 8th with 25 spp.) and contaminant of plants (10th with 24 spp.).

The number of species associated with each pathway for the species on the horizon scanning long list are shown in Figure 4. As with established species, the predominant pathways associated with species on the horizon scanning list were the horticulture and ornamental pathways (Figure 4). This was the case both when using all possible pathway information or only pathways the expert groups considered relevant for Scotland. The extent to which these two pathways dominated, however, was noticeably less for the horizon scanning species with only 23% percent of the total number of species being contributed by these pathways compared with more than 50% for established species (Tables 4 and 5).

After the ornamental and horticultural pathways, the most important pathways in terms of the number of species for horizon scanning species were natural dispersal and pet pathways, though the ranks differed depending on whether the analysis used all pathways or only those provided by the expert groups (ranked 3 and 4 or 4 and 3 respectively). Other pathways that were ranked in the top 10 for the horizon scanning list were, ballast water; habitat material contaminant; fishing equipment; ship excluding ballast water or hull fouling; hull fouling and contaminant of animals, though their exact ranks differed depending upon whether the analysis used all pathways or only expert contributed information on pathways.

Overall, for the 171 horizon scanning species (noting exclusion of three plant species considered established based on a re-examination of records in the Botanical Society of Britain and Ireland recording database) the contributions made by pathways other than horticulture and ornamental were notably larger and more evenly distributed amongst pathways than was the case for the established non-native species, where much of the data was dominated by relatively few pathways. As an example, the stowaway pathway appeared to be associated with a greater proportion of the species from the horizon scanning list than for species already established in Scotland. Indeed, four stowaway pathways (fishing equipment, ship excluding ballast water or hull fouling, ballast water and hull fouling) make the top 10 (Table 5). This is in contrast to the established species where only one stowaway pathway (hull fouling) made the top 10 (7th) and this was only in the analysis restricted to recent established species. In addition, pathways such as pet and natural dispersal were much more important for the horizon scanning species, where they were both high in the top 10, than for the established non-native species where only natural dispersal is in the top 10.

Figure 4. The total number of horizon scanning species associated with each CBD pathway using a) all pathway data, b) only pathways expert groups thought applicable to Scotland. The top 10 ranked pathways are labelled with their rank.
Two barcharts. The first barchart shows the total number of horizon scanning species associated with each CBD pathway using all pathway data. As with established species, the predominant pathways associated with species on the horizon scanning list are the horticulture and ornamental pathways, ranked first and second respectively. The extent to which these pathways dominate is noticeably less than in the case of established species. The natural dispersal, pet escapes, ballast water and habitat material contaminant pathways rank third, fourth, fifth and sixth respectively. The ship excluding hull fouling and ballast water, hull fouling and fishing equipment pathways rank joint seventh while the animal contaminant pathway ranks tenth. The second barchart shows the total number of horizon scanning species associated with each CBD pathway using only pathways expert groups thought applicable to Scotland. The horticultural pathway ranks first and the ornamental pathway ranks a close second. Again, the extent to which these pathways dominate is noticeably less than in the case of established species. The pet escapes and natural dispersal pathways rank third and fourth respectively and the fishing equipment and habitat material contaminants pathways rank joint fifth. The ship excluding hull fouling and ballast water, ballast water, hull fouling, pathways rank seventh, eighth and ninth respectively while the animal contaminant and botanical gardens and zoos escapes pathway rank joint tenth.
Table 5. Top 10 ranked pathways for species on the horizon scanning long list based on the number of species associated with each pathway, based on all pathway data or only pathways experts thought applicable to Scotland during the horizon scanning exercise. For each pathway the proportion of the data associated with that pathway and the cumulative proportion (combined total of pathways ranked equal to or higher than the current pathway expressed as a proportion of the total dataset) are also shown.
Rank Pathway No. Species Proportion Cumulative Proportion
All pathways 1 Horticulture 76 0.117 0.117
2 Ornamental 74 0.114 0.231
3 Natural dispersal 45 0.069 0.300
4 Pet 35 0.054 0.354
5 Ballast water 30 0.046 0.400
6 Habitat material contaminant 28 0.043 0.443
7 Fishing equipment 25 0.038 0.482
7 Ship exc. ballast water or hull fouling 25 0.038 0.520
7 Hull fouling 25 0.038 0.558
10 Contaminant of animals 23 0.035 0.594
Expert pathways 1 Horticulture 50 0.124 0.124
2 Ornamental 43 0.107 0.231
3 Pet 30 0.075 0.306
4 Natural dispersal 29 0.072 0.378
5 Habitat material contaminant 24 0.060 0.438
5 Fishing equipment 24 0.060 0.498
7 Ship excluding ballast water or hull fouling 23 0.057 0.555
8 Ballast water 22 0.055 0.609
9 Hull fouling 17 0.042 0.652
10 Botanical gardens & Zoos 12 0.030 0.682
10 Contaminant of animals 12 0.030 0.711

Analysis using weighted number of species

The relative importance of pathways using the weighted species score was similar to that using the unmodified number of species scoring, though rankings of some pathways changed slightly (Figure 5). This appears to be the case when considering all established species or only established species that were first recorded after 1950.

Figure 5. The weighted numbers of established species associated with each CBD pathway for a) all established species, b) only established species that were first recorded in Scotland since 1950. The top 10 ranked pathways are labelled with their rank.
Two barcharts. The first barchart shows the weighted species scores for established species associated with each CBD pathway for all established invasive species. The horticultural pathway ranks first and the ornamental pathway ranks second. The seed contaminant, agriculture and aesthetic release pathways are much lower and rank third, fourth and fifth respectively. The other release, contaminants of plants, food contaminant, habitat material contaminant, and other contaminant pathways rank sixth, seventh, eighth, ninth and tenth respectively. The second barchart shows the weighted species scores of established species associated with each CBD pathway for established species that were first recorded in Scotland since 1950. Again the horticultural pathway and ornamental pathway rank first and second respectively. The aesthetic release, plant contaminant and other release pathways are significantly lower and rank third, fourth and fifth respectively. The hull fouling, seed contaminant, agriculture escapes, contaminants of animals and ballast water pathways rank sixth, seventh, eighth, ninth and tenth respectively.

The horticulture and ornamental pathways were the most important pathways, ranked 1st and 2nd respectively. Together these pathways contributed a notable proportion of the total weighted species scores. The contribution of these pathways appeared to be slightly greater when using the weighted species score, with them explaining 56% (all established) and 64% (recently established) of the total weighted scores compared with 53% and 60% for the unmodified number of species scores (Tables 4 and 6).

For all established species the pathways in the top 10 using the weighted scores were almost the same as when using the unmodified total number of species, though the ranks changed slightly, and the natural dispersal category was lost while the contaminant of plants was gained. The agriculture and seed contaminant pathways switched ranks (ranked 4th and 3rd respectively), while the food contaminant and other contaminant pathways were ranked lower (now 8th and 10th) and habitat material contaminant increased to 9th position.

The natural dispersal category was also lost from the top 10 for the recently established species, though in this case the new pathway in the top 10 was the ballast water pathway which appeared at 10th place. For recently established species the other changes in the top 10 using weighted species score instead of the raw total number of species is the reduction in ranks of the other release (4th to 5th), agriculture (5th to 8th) and the contaminant of animals pathways (8th to 9th) along with the increase in ranks of the contaminant of plants (10th to 4th) and hull fouling pathway (7th to 6th).

The proportion of data cumulatively explained by pathways in the top 10 was relatively independent of whether the rankings used the raw number of species or weighted species scores, with the values now being 85% and 86% for all established species and recent established species respectively (Table 6).

Table 6. Top 10 ranked pathways for established non-native species based on the total weighted number of species score associated with each pathway for all established non-native species or only established species first recorded in Scotland from 1950 onwards. For each pathway the proportion of the data associated with that pathway and the cumulative proportion (combined total of pathways ranked equal to or higher than the current pathway expressed as a proportion of the total dataset) are also shown.
Rank Pathway Weighted No. Species Score Proportion Cumulative Proportion
All established species 1 Horticulture 323.6 0.304 0.304
2 Ornamental 268.4 0.253 0.557
3 Seed contaminant 73.3 0.069 0.626
4 Agriculture 70.8 0.067 0.693
5 Aesthetic release 53.8 0.051 0.743
6 Other release 37.0 0.035 0.778
7 Contaminant of plants 23.6 0.022 0.800
8 Food contaminant 22.3 0.021 0.821
9 Habitat material contaminant 17.5 0.016 0.838
10 Other contaminant 17.1 0.016 0.854
Established species first recorded since 1950 1 Horticulture 166.9 0.351 0.351
2 Ornamental 138.3 0.291 0.642
3 Aesthetic release 27.4 0.058 0.700
4 Contaminant of plants 14.4 0.030 0.730
5 Other release 12.2 0.026 0.756
6 Hull fouling 11.4 0.024 0.780
7 Seed contaminant 11.2 0.023 0.803
8 Agriculture 11.1 0.023 0.827
9 Contaminant of animals 8.4 0.018 0.845
10 Ballast water 7.6 0.016 0.860

Although the general patterns in the relative contributions of the pathways were similar between the two scoring metrics (raw number of species and weighted species score) for the data for horizon scanning species, the exact rankings for pathways did vary more (Figure 6). The horticulture and ornamental pathways were still the top 2 pathways ranked 1st and 2nd respectively. Together, these pathways explained a notable proportion of the total weighted score (28% and 26%) for all pathways and only expert supplied pathways, respectively (Table 7). These values were similar to those obtained using the raw number of species to rank pathways which was 23% for both. The other pathways, and their relative ranks, within the top 10 were less consistent.

Figure 6. The weighted numbers of horizon scanning species associated with each CBD pathway using a) all pathway data, b) only pathways expert groups thought applicable to Scotland. The top 10 ranked pathways are labelled with their rank. For full pathway names see Table 1.
Two barcharts. The first shows the weighted species scores for horizon scanning species associated with each CBD pathway using all pathway data. In this case the ornamental pathway ranks first while the horticultural pathway ranks a very close second. The natural dispersal, ballast water, pet escapes and hull fouling pathways rank third, fourth, fifth and sixth respectively. The contaminant of animals, other release, seed contaminant and habitat material contaminant pathways rank seventh, eighth, ninth and tenth respectively. The second barchart shows the weighted species scores for horizon scanning species associated with each CBD pathway using only pathways expert groups thought applicable to Scotland. Again the ornamental pathway ranks first while the horticultural pathway ranks a very close second. The pet escapes, ballast water, natural dispersal and hull fouling pathways rank third, fourth, fifth and sixth respectively. The habitat material contaminant, ship excluding hull fouling and ballast water, fishing equipment and wild fishery pathways rank seventh, eighth, ninth and tenth respectively.

Based on all pathways data for the horizon scanning species three pathways, seed contaminant, angling and ship excluding ballast water or hull fouling, were lost from the top 10 and two gained, other release (8th) and seed contaminant (9th), when changing the scoring metric from the raw number of species to the weighted species scores. A similar situation was found for the rankings using only the expert supplied pathways where two pathways dropped out of the top 10, botanical gardens & zoos and contaminant of animals, and one, fishery in the wild (10th), gained.

Table 7. Top 10 ranked pathways for species on the horizon scanning long list based on the total weighted species score for each pathway, based on all pathway data or only pathways experts thought applicable to Scotland during the horizon scanning exercise. For each pathway the proportion of the data associated with that pathway and the cumulative proportion are also shown.
Rank Pathway Weighted No. Species Score Proportion Cumulative Proportion
All pathways 1 Ornamental 24.4 0.141 0.141
2 Horticulture 24.0 0.139 0.280
3 Natural dispersal 9.8 0.057 0.336
4 Ballast water 9.8 0.057 0.393
5 Pet 9.1 0.053 0.446
6 Hull fouling 8.0 0.047 0.492
7 Contaminant of animals 6.6 0.038 0.530
8 Other release 6.3 0.037 0.567
9 Seed contaminant 5.6 0.032 0.599
10 Habitat material contaminant 5.4 0.031 0.631
Expert pathways 1 Ornamental 13.7 0.132 0.132
2 Horticulture 13.3 0.128 0.259
3 Pet 7.7 0.074 0.333
4 Ballast water 7.6 0.073 0.406
5 Natural dispersal 6.6 0.064 0.469
6 Hull fouling 6.3 0.060 0.530
7 Habitat material contaminant 4.7 0.045 0.575
8 Ship excluding ballast water or hull fouling 4.6 0.045 0.619
9 Fishing equipment 4.1 0.040 0.659
10 Fishery in the wild 3.7 0.036 0.694

Biodiversity impact and overall horizon scanning score

The breakdown of pathways based upon total biodiversity impact scores (Figure 7) and the overall horizon scanning scores (Figure 8) were very similar to those obtained based on the uncorrected number of species with generally the same pathways being shown as most important (Tables 8-9).

Figure 7. The total biodiversity impact associated with each CBD pathway for horizon scanning species using a) all pathway data, b) only pathways expert groups thought applicable to Scotland. The top 10 ranked pathways are labelled with their rank. For full pathway names see Table 1.
Two barcharts. The first barchart shows the total biodiversity impact associated with each CBD pathway for horizon scanning species using all pathway data. The horticultural pathway ranks first and the ornamental pathway ranks a very close second. The natural dispersal and pet escape pathways rank third and fourth respectively while the habitat material contaminant and ballast water pathways rank joint fifth. The fishing equipment, ship excluding hull fouling and ballast water, hull fouling and contaminant of animals pathways rank seventh, eighth, ninth and tenth respectively. The second barchart shows the total biodiversity impact associated with each CBD pathway for horizon scanning species using only pathways expert groups thought applicable to Scotland. The horticultural pathway ranks first and the ornamental pathway ranks second. The pet escapes, natural dispersal and habitat material contaminant pathways rank third, fourth and fifth respectively. The fishing equipment, ship excluding hull fouling and ballast water, ballast water, hull fouling, contaminant of animals pathways rank sixth, seventh, eighth, ninth and tenth respectively.
Table 8. Top 10 ranked pathways for species on the horizon scanning long list based on the total biodiversity impact score for each species associated with that pathway, using either all pathway data or only pathways experts thought applicable to Scotland during the horizon scanning exercise. For each pathway the proportion of the data associated with that pathway and the cumulative proportion are also shown.
Rank Pathway Biodiversity Impact Score Proportion Cumulative Proportion
All pathways 1 Horticulture 283 0.112 0.112
2 Ornamental 272 0.108 0.220
3 Natural dispersal 177 0.070 0.290
4 Pet 142 0.056 0.346
5 Habitat material contaminant 116 0.046 0.392
5 Ballast water 116 0.046 0.438
7 Fishing equipment 101 0.040 0.478
8 Ship excluding ballast water or hull fouling 99 0.039 0.517
9 Hull fouling 92 0.036 0.553
10 Contaminant of animals 87 0.034 0.588
Expert pathways 1 Horticulture 195 0.123 0.123
2 Ornamental 163 0.103 0.225
3 Pet 121 0.076 0.302
4 Natural dispersal 115 0.072 0.374
5 Habitat material contaminant 101 0.064 0.438
6 Fishing equipment 96 0.060 0.498
7 Ship excluding ballast water or hull fouling 92 0.058 0.556
8 Ballast water 86 0.054 0.610
9 Hull fouling 62 0.039 0.649
10 Contaminant of animals 49 0.031 0.680
Figure 8. The total biodiversity impact associated with each CBD pathway for horizon scanning species using a) all pathway data, b) only pathways expert groups thought applicable to Scotland. The top 10 ranked pathways are labelled with their rank. For full pathway names see Table 1.
Two barcharts. The first barchart shows the total biodiversity impact associated with each CBD pathway for horizon scanning species using all pathway data. The horticultural pathway ranks first and the ornamental pathway ranks a very close second. The natural dispersal, pet escape and habitat material contaminant pathways rank third, fourth and fifth respectively. The ballast water, hull fouling, fishing equipment, ship excluding hull fouling and ballast water, and aesthetic release pathways rank sixth, seventh, eighth, ninth and tenth respectively. The second barchart shows the total biodiversity impact associated with each CBD pathway for horizon scanning species using only pathways expert groups thought applicable to Scotland. The horticultural pathway ranks first and the ornamental pathway ranks second. The natural dispersal, pet escape, and habitat material contaminant pathways rank third, fourth and fifth respectively. The fishing equipment, ship excluding hull fouling and ballast water, ballast water, hull fouling and contaminant of animals pathways rank sixth, seventh, eighth, ninth and tenth respectively.
Table 9. Top 10 ranked pathways for species on the horizon scanning long list based on the total overall horizon scanning score for each species associated with that pathway, using either all pathway data or only pathways experts thought applicable to Scotland during the horizon scanning exercise. For each pathway the proportion of the data associated with that pathway and the cumulative proportion are also shown.
Rank Pathway Horizon Scanning Score Proportion Cumulative Proportion
All pathways 1 Horticulture 5237 0.113 0.113
2 Ornamental 5012 0.108 0.221
3 Natural dispersal 3582 0.077 0.298
4 Pet 2345 0.051 0.348
5 Habitat material contaminant 2250 0.048 0.397
6 Ballast water 2033 0.044 0.441
7 Hull fouling 1780 0.038 0.479
8 Fishing equipment 1751 0.038 0.517
9 Ship excluding ballast water or hull fouling 1734 0.037 0.554
10 Aesthetic release 1698 0.037 0.591
Expert pathways 1 Horticulture 3806 0.128 0.128
2 Ornamental 3138 0.106 0.234
3 Natural dispersal 2232 0.075 0.310
4 Pet 1960 0.066 0.376
5 Habitat material contaminant 1930 0.065 0.441
6 Fishing equipment 1626 0.055 0.496
7 Ship excluding ballast water or hull fouling 1614 0.054 0.550
8 Ballast water 1421 0.048 0.598
9 Hull fouling 1277 0.043 0.641
10 Contaminant of animals 911 0.031 0.672

Correlations between rankings

The relative importance of the pathways, particularly for the higher ranking pathways was similar between all and recently established species (Figure 9a), with a reasonably high correlation coefficient (τ = 0.821). This suggests that the rankings of the pathways associated with the recently established species are similar to those associated with all of the established species, although there are differences as represented by the points lying further away from the dotted 1:1 line (Figure 9a). The rankings obtained using weighted scores were also found to be highly correlated (τ = 0.869) with rankings using the raw number of species (Figure 9b). Similarly, for horizon scanning species the rankings were highly correlated (τ = 0.819) when comparing rankings using all pathway data against that using only expert supplied pathways (Figure 9c), though there was more divergence from the 1:1 for the pathways near the bottom of the rankings (i.e., least important).

Figure 9. Correlations between pathway rankings for the different importance scoring methods and or subsets of data, specifically; a) all established species and species established since 1950, b) total number of species and weighted number of species, c) all pathways and only pathways suggested by expert groups as likely for Scotland, d) established species and horizon scanning species, e) number of species and total biological impact for horizon scanning species, and f) number of species and overall total horizon scanning score for horizon scanning species. Each plot also shows the Kendall’s correlation coefficient between the pairs of ranks (a value of τ = 1 indicates a perfect match, τ = -1 a perfect inverse match and τ = 0 no relationship, i.e., random).
A set of six scatter plots showing the correlations in the rankings for pathways when using different sets of species and or scoring methods. Each plot also shows the Kendall’s correlation coefficient (tau) between the pairs of ranks for each pathway. A correlation coefficient of 1 indicates a perfect match, -1 a perfect inverse match and 0 implies no relationship between ranks, i.e. random. Figure 9a shows a strong positive correlation between the rankings for the number of all established species and the number of established species arriving since 1950 with a correlation coefficient of 0.821. Figure 9b shows a strong positive correlation in rankings between the numbers of established species arriving since 1950 and the weighted number of established species arriving since 1950 with a correlation coefficient of 0.869. Figure 9c shows the strong positive correlation in ranking between the numbers of horizon scanning species when using all potential pathways for that species globally and those just using pathways suggested by experts during the horizon scanning as being likely pathway(s) of introduction to Scotland with a correlation coefficient of 0.819. Figure 9d shows a positive correlation between the numbers of established species arriving since 1950 and the number of species on the horizon scanning list (all potential pathways) with a correlation coefficient of 0.617. Figure 9e shows an extremely strong positive correlation in rankings between ranking for the number of horizon scanning species and the horizon scanning bio impact scores with a correlation coefficient of 0.978. Figure 9f shows an extremely strong positive correlation in rankings between the number of horizon scanning species and the overall total horizon scanning scores for the horizon scanning species with a correlation coefficient of 0.936.

Although there was a correlation (τ = 0.617) between the pathway ranks for recently established species and the horizon scanning species, it was much lower than that for the other pairing and the plot for this pair showed much scatter around the 1:1 line (Figure 9d). The rankings obtained using the biodiversity score and overall horizon score were very highly correlated (τ = 0.978 and 0.936, respectively) with the ranks that used the raw number of species (Figures 9e and 9f).

Contact

Email: invasive_non-native_species@gov.scot

Back to top