An Ultra-clean Multilayer Apparatus for Collecting Size Fractionated Marine Plankton and Suspended Particles

Summary

Plankton and suspended particles play a major role in the biogeochemical cycles in the ocean. Here, we provide an ultra-clean, low stress method for the collection of various sizes of particles and plankton at sea with the capability of handling large volumes of seawater.

Abstract

The distributions of many trace elements in the ocean are strongly associated with the growth, death, and re-mineralization of marine plankton and those of suspended/sinking particles. Here, we present an all plastic (Polypropylene and Polycarbonate), multi-layer filtration system for collection of suspended particulate matter (SPM) at sea. This ultra-clean sampling device has been designed and developed specifically for trace element studies. Meticulous selection of all non-metallic materials and utilization of an in-line flow-through procedure minimizes any possible metal contamination during sampling. This system has been successfully tested and tweaked for determining trace metals (e.g., Fe, Al, Mn, Cd, Cu, Ni) on particles of varying size in coastal and open ocean waters. Results from the South China Sea at the South East Asia Time-Series (SEATS) station indicate that diurnal variations and spatial distribution of plankton in the euphotic zone can be easily resolved and recognized. Chemical analysis of size-fractionated particles in surface waters of the Taiwan Strait suggests that the larger particles (>153 µm) were mostly biologically derived, while the smaller particles (10 - 63 µm) were mostly composed of inorganic matter. Apart from Cd, the concentrations of metals (Fe, Al, Mn, Cu, Ni) decreased with increasing size.

Introduction

Particles in the ocean play an important role in marine biogeochemical cycles¹. Most of the properties of particles, such as size, mineralogy, and composition, can change profoundly from one geological or hydrographical setting to another². In addition, the distributions of elements in the ocean are also associated with the life cycle of marine phytoplankton: growth, death, sinking, and re-mineralization^3,4. Marine particles span at least 4 orders of magnitude in size, ranging from submicron particles to large aggregates (>5 mm). Most particles are biologically derived, from processes such as viral lysis, exudation, secretion, fecal pellet production, etc. Other particles are formed from physical coagulation of cells, cellular debris, or lithogenic materials¹. Various chemical and biological characteristics of particles control both the geochemical cycles and biological processes occurring on and within the particles^4,5,6. These particles are important habitats as well as food sources for some organisms, such as zooplankton or saprotrophs. Accordingly, the fate of particles is often related to their size, which can be modified by biological processes on and around particles.

Sampling marine particles usually requires filtration, but this approach introduces a certain ambiguity in identifying the properties of particles, since marine particles are not homogenous in composition and size. Suspended particles, mainly composed of small and low density particles that are almost permanently in suspension, are mixed with varying amounts of larger and denser particles in suspension only for a short period of time, depending on hydrodynamic conditions⁷. The first reports of the trace metal composition of plankton samples were collected by plankton tows or suspending plankton nets on a research vessel⁸. The authors often found metal particles and paint chips in samples, suggesting a severe problem of contamination during marine particle sampling for chemical analysis. Other efforts include net towing by rubber rafts or using a polyvinyl chloride (PVC)-hand winch³. The difficulty of reliable sampling of particles makes progress in our understanding of the chemical composition of marine particles more difficult, especially for trace elements. As such, most crucial information on the concentration of trace elements in phytoplankton has come from culture studies^9,10. This recognition has motivated marine scientists to create new methods for studying particles in the sea over the past thirty years¹¹.

Oceanographers have used various sampling techniques, including shipboard filtration, in situ filtration, and sediment traps¹¹. The processing of large volumes of sea-water to collect non-contaminated samples can be challenging, especially for open ocean and deep waters in which the particle concentrations are very low (0.001 - 0.1 mg/L). It is also necessary to filter large volumes of sea-water to obtain an adequate quantity of particles to measure trace metal concentrations. Some researchers have used the size-fractionation method to separate suspended particles from sinking particles. However, particle size, porosity, density, and shape can all influence particle sinking velocities. Sediment traps are not practical tools to collect suspended particles, since those are designed for sinking particles. Therefore, it is important to develop sampling and treatment methods that can collect sufficient quantities of suspended particles with minimal contamination. Hence, size-fractionation by in situ filtration is still a promising tool in the oceanographer's sampling toolbox, since it can reveal critical information on marine particle dynamics. Here, we describe a successfully tested trace-metal-clean, multi-layer gravity filtration sampling apparatus, which can treat large volumes (120 - 240 L) of seawater on board in one pass from polytetrafluoroethylene (PTFE) coated water sampling bottles in a multi-bottle sampling array. This sampling apparatus uses acid-washed synthetic nylon nets in sequence, and the nets are enclosed within a polycarbonate container to gently collect size-fractionated suspended matter and phytoplankton^12,13,14,15 (Figure 1). The aim of this work is to provide a better tool for studying the metal-particle associations and their reaction dynamics in marine environments, and improve our understanding of the fate of a wide variety of planktons, particles, and trace metals in these environments.

Protocol

The following protocol involves working with harmful chemicals. Please read the Safety Data Sheets (SDS) carefully, and follow institutional chemical safety guidelines.

1. Multi-layer Gravity Filtration Sampler Preparation

1. Sampler cleaning
   1. Fill the tubing and filtration unit with 1% (w/v) of anionic protease enzyme detergent solution and soak it for 24 h. Flush the multi-layer gravity filtration sampler with reverse osmosis double distilled water (RO-DDW) thoroughly, then fill it with 0.1% (v/v) hydrochloric acid (HCl, Reagent Grade) and soak for 72 h.
   2. Thoroughly flush the multi-layer gravity filtration sampler with reverse osmosis double distilled deionized water (RO-DD-DIW) three to five times, at least 20 liters each time, and store the assemblage in plastic bags.
2. Particle sample container cleaning/preparation
   1. Use low density polyethylene (LDPE, 125 mL) or fluorinated ethylene propylene (FEP, 125 mL) bottles as containers for particles. Clean the bottles by soaking them first in alkaline detergent (Micro, 1%), then in 50% (v/v) nitric acid (HNO₃, Reagent Grade), then 10% (v/v) HCl solutions for at least 24, 48, and 24 h, respectively. Rinse the bottles with de-ionized water (RO-DD-DIW) between the two soaking steps.
   2. After a final HCl soaking, rinse the bottles thoroughly with de-ionized water (RO-DD-DIW), and dry the bottles in a clean room or class-100 clean bench.
      Attach the cleaned bottle to the multilayer gravity filtration sampler, or seal cleaned bottles in PE zippered bags and double-bag them for transport.
3. Assemblage of multi-layer gravity filtration sampler
   1. Connect six 4 m long chemically resistant thermoplastic elastomer tubes (outside diameter of 0.635 cm) to the six directional inlets on top of the sampler.
   2. Assemble the three different mesh nylon filters with low-density polyethylene sample containers (125 mL LDPE) in sequence in a clean room (bench) after they are cleaned (see below), with the 10 µm mesh filter positioned on the outside, the 63 µm mesh filter in the middle, and the 153 µm mesh filter on the inside. For transportation, store the multi-layer gravity filtration sampler in two layers of polyethylene (PE) bags, then place it in the polypropylene (PP) shipping container.

2. Sampling

1. Sample collection
   1. Upon arrival at the sampling site, have one person remove the multi-layer gravity filtration sampler from a shipping container on the deck of the research vessel and open the bag with the sampler. Then, have them put on the PE gloves, connect the six 4 m thermoplastic elastomer tubes to the water spigots of six 20 L PTFE-coated sampling bottles on the elevated multi-bottle sampling array, and guide the seawater into this filtration unit. The seawater will flow through the directional inlets, and the particles/plankton will be gently separated/fractionated through the nets and settle into the 125 mL LDPE bottles that are secured at the base of the nets.
   2. After the seawater has flowed through (usually 120 L for coastal sea water and 240 L for open ocean water), remove each net in sequence (firstly, the 153 µm, then the 63 µm, and finally the 10 µm) in a class-100 clean bench, then spray the net with trace-metal-clean 0.4 µm filtered seawater to rinse out any plankton stuck on the inner surface of the nets. Collect the seawater with concentrated particles/plankton in 125 mL polyethylene bottles.
   3. Unscrew these bottles from the nets, and filter the solutions with concentrated particles/plankton again through an acid-washed vacuum filtration apparatus with pre-weighed, acid-washed 47 mm, 10 µm pore-size polycarbonate filters under low-vacuum conditions (<5 kPa).
   4. To collect particles/plankton smaller than 10 µm, wait for at least 20 L of seawater to flow through the sampler, then after that, collect two to five L of water in the 5 L PE container, and filter these sample waters by an acid-washed vacuum filtration apparatus with pre-weighed, acid-washed, 47-mm, 0.4-µm pore size polycarbonate filters.
   5. After vacuum filtration, rinse the sample filters immediately with high purity DDW water to remove the residue of seawater, minimizing the influence of sea salts on determining the dry weights of particles/plankton. Keep the rinsing volume to only a couple of milliliters to prevent damaging the fragile plankton.
   6. Then, after this rinsing step, carefully remove the filter from the vacuum filtration unit, store the sample filters in acid-washed, pre-weighed acrylic plastic petri dishes, and seal in resealable plastic bags. Keep the bags in a -20 ˚C freezer onboard until returning back to a land-based laboratory for further sample pretreatment and chemical analysis.

3. Sample Treatment

1. Freeze drying and digestion of particles
   1. Place the filters with particle samples in the collector chamber of the freeze-drying machine, and turn on the machine. As the machine temperature reaches -40 °C, turn on the vacuum pump of the machine and start the freeze drying processes.
      NOTE: The vacuum level should be maintained steadily below 0.12 mBar. Please read the user manual carefully and follow the manufacturer's guidelines for each step.
   2. After 72 h, turn off the freeze-drying machine, remove the dried filters and weigh them. Then, place dried sample filters into pre-weighed perfluoroalkoxy alkane (PFA) vessels (60 mL capacity), and add 3 mL of concentrated ultrapure nitric acid into the vessels^2,3,6,7.
   3. Tighten the vessels with a torque wrench to a constant torque of 2.5 kg-m, and place the vessels in a conventional oven at 130 °C for 12 h for the first digestion sequence. After cooling, remove the vessels from the oven, open the vessels, and add 2 mL of ultrapure hydrofluoric acid into the vessels^2,3,6,7.
   4. Tighten the vessels with a torque of 2.5 kg-m, and place the vessels in a conventional oven at 130 °C for 12 h, which is the second digestion sequence. After cooling, open the vessels and add 16 mL of 4.5% ultra-pure boric acid solution into the vessels^2,3,6,7.
   5. Tighten the vessels to a constant torque of 2.5 kg-meters, and digest the samples in oven at 130 °C for 12 h for the final digestion sequence. After cooling, weigh each vessel and determine the final mass and specific mass of each digested solution to yield a final digestant volume.
      NOTE: Specific mass is determined by measuring the weight of exactly 1.00 mL of digestant.
   6. Carefully pour the digestant into 30 mL acid cleaned PE bottle for further trace metal analysis.
2. Trace Metal Analysis
   1. Determine trace metal concentrations (Cd, Cu, Fe, Mn, Ni, and Al) in digested solutions of particles using a graphite furnace atomic absorption spectrometer (GF-AAS)⁶.
   2. As an accuracy test, use certified reference material (CRM), such as marine sediment reference materials from the National Research Council of Canada, estuarine sediment standard reference material from the National Institute of Standards and Technology of the USA, and plankton reference material from the European Commission's science and knowledge service. The process gives 95% to 107% recovery of the certified value for the trace metals provided in the CRM.

Results

With the development of modern oceanography, it is now a common practice to use "clean techniques" to obtain accurate trace metal concentrations in marine particles or plankton. Since most particles in natural waters are in the low mg/L to µg/L range, the treatment of large volumes of seawater is necessary to investigate geochemical and biological effects of trace metals on various particles in ambient environments. With the use of clean, multi-layer gravity filtration ("CATNET") sampling...

Discussion

Obtaining reliable trace metal concentrations on plankton and suspended particles in natural waters, which are generally present at very low concentrations, requires great care during sample collection, processing, pretreatments, and analysis, with the aim of reducing contamination. Therefore, the procedures to design and prepare sampling gear, sample containers, and materials used to collect and process samples are all critical steps toward obtaining high-quality data for trace metals in marine environments. With the ad...

Materials

List of materials used in this article

Name	Company	Catalog Number	Comments
thermoplastic elastomer (C-Flex) Tubings	Cole Palmer	EW-06424-67	O.D. 0.635 cm, Opaque White 1/8"ID x 1/4"OD, 25 ft/pack
LDPE Bottle (Nalgene)	ThermoFisher Scientific	2103-0004	125 mL, Nalgene Wide-Mouth LDPE Bottles with Closure
anionic protease enzyme detergent detergent (Tergazyme)	Alconox	1104-1	1×4 lb box (1.8 kg)
Hydrochloric Acid	Sigma-Aldrich	258148	Reagent grade
Nitric acid	Sigma-Aldrich	695025	Reagent grade
alkaline detergnet (Micro)	Cole Palmer	EW-99999-14	Micro-90 Cleaning Solution
polycarbonate filter, 47 mm, 0.4 µm	Sigma-Aldrich	WHA111107	Whatman Nuclepore Track-Etched Membranes, diam. 47 mm, pore size 0.4 μm, polycarbonate
polycarbonate filter, 47 mm, 10 µm	Sigma-Aldrich	WHA111115	Whatman Nuclepore Track-Etched Membranes, diam. 47 mm, pore size 10 μm, polycarbonate
PFA vessel, 60 ml capacity	Savillex	300-060-03	60 mL Digestion Vessel, Flat Interior, Flat Exterior, Buttress Threaded Top
Nitric acid, ultrapure	Seastar Chemicals	N/A	BASELINE Nitric Acid
HF, ultrapure	Seastar Chemicals	N/A	BASELINE Hydrofluoric Acid
Boric acid, ultrapure	Seastar Chemicals	N/A	BASELINE Hydrobromic Acid
polyethylene (PE) gloves	Safty Zone	GDPL-MD-5	Clear Powder Free Polyethylene Gloves
Multiple layer filtering and collecting device	Sino Instrumnets Co. Ltd	not available	Multiple layer filtering and collecting device, CATNET
10 um Nylon filters, Nitex	Dynamic Aqua-Supply Ltd.	NTX 10	Nitex - Standard Widths (40 - 44 inches)
60 um Nylon filters, Nitex	Dynamic Aqua-Supply Ltd.	NTX 60	Nitex - Standard Widths (40 - 44 inches)
150 um Nylon filters, Nitex	Dynamic Aqua-Supply Ltd.	NTX 150	Nitex - Standard Widths (40 - 44 inches)
torque wrench	Halfords	200238	Halfords Professional Torque Wrench 8-60Nm
multi-bottle sampling array, Rosette	General Oceanics	Model 1018	Rosette Sampler
PTFE-coated sampling bottles, GO-Flo	General Oceanics	108020T	GO-Flo water sampler teflon coated
Marine sediment reference materials	National Research Council Canada	MESS-3
Estuarine sediment standard reference material	National Institute of Standards and Technology	1646a
Plankton reference material	The European Commission's science and knowledge service	CRM414