Quantifying Invasion Pathways: Fish Introductions from the Aquarium Trade
Abstract
Introduction to Issue: Introduced species can cause significant economic and environmental harm. Therefore, researchers have developed risk assessment models based on biological characteristics of exotic species.
Gap in Research: Few studies have quantified propagule pressure, despite its significance in determining species establishment.
Focus of Study: This study specifically examines fishes introduced via the aquarium trade, which transports thousands of species worldwide.
Objective: Develop a method to estimate propagule pressure by:
Identifying and quantifying aquarium fishes sold.
Determining fish owner behaviors and disposal practices.
Quantifying uncertainty in the measurements.
Model System: The St. Lawrence Seaway.
Findings:
Only one non-established species, Tanichthys albonubes, with a propagule pressure of 117 per year, was likely capable of invasive potential in the region.
Over 10,000 fishes are released annually from Montreál (Quebec, Canada) alone.
Implications: The aquarium trade poses a significant risk in warmer habitats and should be assessed explicitly to inform population models estimating species establishment probabilities.
Introduction
Global Context: The world is experiencing increased international trade leading to the spread of biological organisms beyond their native ranges.
Role of Human Activity: Human actions have facilitated the introduction and spread of nonindigenous species (NIS) at an accelerated rate compared to past events (Mills et al. 1992; Hochberg and Gotelli 2005).
Consequences: Significant impacts include:
Economic damage estimated at 137 billion dollars annually in the US due to NIS (Pimentel et al. 2000).
Declining ecosystem functions and decreased global biodiversity (Miller 1989; Pimentel 2005).
Invasion Mechanism: NIS are a major driver in global biodiversity loss, surpassed only by habitat loss (Wilcove et al. 1998; Levine and D’Antonio 2003).
Risk Quantification: Proper management of NIS necessitates quantifying invasion risks through rigorous risk assessments integrating the complete invasion process:
Transport
Introduction
Establishment
Spread
Impact (Kolar and Lodge 2001).
Propagule Pressure Importance: Propagule pressure indicates the number introduced. The likelihood of successful invasion relates directly to propagule numbers (Kolar and Lodge 2001; Williamson 1996).
Research Gap
Previous studies have primarily concentrated on biological characteristics of NIS for risk assessments (Mandrak 1989; Kolar 2004; Copp et al. 2005) rather than quantifying introduction rates.
Assessing risk involves knowing species introductions through various pathways that necessitate focus on prevention strategies (Ricciardi and Rasmussen 1998; Kolar and Lodge 2002).
Identifying pathways of introduction is critical, with notable examples including:
Ballast water (Ricciardi and Rasmussen 1998; Rixon et al. 2005)
Aquarium releases, escape from aquaculture, live food markets, and intentional releases (Mills et al. 1992).
Methodology
Study Area: Montreál and the St. Lawrence Seaway, significant entry points for NIS into the Great Lakes (Environment Canada 1996).
Aquarium Trade Overview: Over 5,000 fish species traded internationally are typically non-native to the Great Lakes (Welcomme 1984; Chapman et al. 1997).
Data Collection Methods:
Store Inventories: Survey of aquarium and pet stores in Montreál to quantify fish species sold:
Visited over 75% of stores (18 total) from February to May 2006.
Derived counts through standing stock populations recorded at beginning and end of period.
Store Owner Surveys: Interviewed 20 store owners about unsold fish policies, confirming that unsold fish were either kept for sale or returned to distributors.
Customer Surveys: Conducted interviews with 86 customers outside 11 stores in October and November 2005 to explore fish ownership and disposal behaviors.
Data Analysis
The methodology integrated data from customer behavior into a propagule pressure model based on:
Overall Propagule Pressure Calculation: overallextpropagulepressure=MimesP(I)imesNimesP(R∣I) with parameters defined as follows:
M: Total number of households owning fish.
P(I): Probability that a person is a releaser.
N: Average number of fishes owned.
P(R|I): Probability that a fish is released given it is owned by a releaser.
Bayesian Statistical Approach: Used to incorporate uncertainty in estimates due to sample size (P(I), N, P(R|I)).
Model for Species-Specific Propagule Pressure:
species−specificextpropagulepressure=MimesP(I)imesNimesP(R∣I)imesr<em>ximescimess</em>x with variables defined as:
r_x: Relative rate of release due to species characteristics.
c: Correction factor.
s_x: Relative proportion of fishes of a certain species.
Results:
Total number of fish sold: 46,722 over 30 days across sampled stores.
Most sold species identified and their respective attributes analyzed for propagule pressure:
Species List Includes:
Goldfish (Carassius auratus)
Guppies (Poecilia reticulata)
Neon tetras (Paracheirodon innesi)
Others as listed in the study.
Results Analysis
Propagule pressure for each type of fish derived from customer surveys revealed:
6.98% of respondents reported releasing fish into the wild (P(I)).
Average release rate of 5.1% among those who have released fish into the wild (P(R|I)).
Aggressive behaviors and large size were significant factors influencing the proportion of disposed fishes based on survey data.
Conclusion
This study illustrates a simple method to quantify propagule pressure from the aquarium trade, emphasizing human behavior as a critical determinant.
Notable findings highlight that over 10,000 fishes are released annually from the Montreál aquarium trade, emphasizing environmental risks.
Recommendations for future studies to include comprehensive analyses on additional pathways of introduction and behaviors across different regions susceptible to invasions from the aquarium trade are critical moving forward.
Acknowledgments
Research funding from the Canadian Aquatic Invasive Species Network (CAISN) and contributions from Fisheries and Oceans Canada alongside academic collaborators provided necessary support for this project.
References
Complete references can be found at the end of the original document, providing a comprehensive bibliography of all cited works for further research.